TITLE 30. ENVIRONMENTAL QUALITY

PART 1. TEXAS COMMISSION ON ENVIRONMENTAL QUALITY

CHAPTER 60. COMPLIANCE HISTORY

30 TAC §60.1, §60.2

The Texas Commission on Environmental Quality (commission or TCEQ) proposes amendments to 30 Texas Administrative Code (TAC) §60.1 and §60.2.

Background and Summary of the Factual Basis for the Proposed Rules

The commission proposes revisions to Chapter 60 to implement certain requirements of Senate Bill (SB) 1397, regarding compliance history. SB 1397, 88th Legislature, 2023, Section 13, amended Texas Water Code (TWC) §5.754 requiring the commission to consider major, moderate, and minor violations when determining repeat violators. This proposed rulemaking also addresses management recommendations adopted by the Sunset Advisory Commission that were not included in SB 1397 for the commission to review and update the agency's compliance history rating formula to ensure it accurately reflects a regulated entity's record of violations, including considerations of site complexity and cumulative violations or repeating violations; and to regularly update compliance history ratings.

Section by Section Discussion

§60.1, Compliance History

The commission proposes revisions to §60.1(a)(6) and (7) to establish the effective date of the proposed rule. The commission will continue to use the version of the rule in effect at the time the compliance history classification was calculated in accordance with §60.1(b). For example, when an application for a permit is received by the executive director, the version of Chapter 60 in effect at the time the application is received will be the version used for compliance history purposes. The commission may consider new compliance history information as it deems necessary.

The proposal amends §60.1(b) to change the compliance period for enforcement actions to be calculated from the initial enforcement screening date. The compliance history period for an enforcement action is currently based on the date of the initial mailing of the enforcement settlement offer or petition, whichever occurs first. Since complicated cases may take substantial time to develop, the compliance history period could change while the settlement offer or petition is being drafted. Changing the start of the compliance period to the initial screening of an enforcement action means the compliance history will more closely reflect the performance of the site at the time the violations were documented as opposed to several months later. This provides greater certainty to the regulated community as to how an entity is performing at the time an enforcement action begins. This also means a site's compliance history will remain the same throughout the drafting and review process of the initial proposed agreed order or the petition instead of requiring additional reviews to verify whether the compliance history has changed during the process. In addition, clarification is made on how Notices of Violation are considered consistent with changes to §60.2(f).

Proposed §60.1(c)(8) changes the language referencing the Texas Environmental, Health, and Safety Audit Privilege Act. The Act was amended by the 85th Legislature in 2017 and the proposed language recognizes this change.

§60.2, Classification

The proposal amends §60.2(a) to change the frequency that the executive director shall evaluate the compliance history of each site from annually to bi-annually. This implements a management recommendation adopted by the Sunset Advisory Commission to regularly update an entity's compliance history rating. The commission proposes that compliance histories be evaluated on March 1st and September 1st each year. Since 2002, when the rule originally established an annual review, technological advances have made it possible for the agency to increase the number of reviews per year without overburdening agency resources. Bi-annual reviews will allow for appropriate planning for announced and unannounced investigations, as well as increased oversight of unsatisfactory performers. More frequent evaluations better allow the commission to consider whether proceedings should be initiated to revoke a permit, or to amend a permit where statutes allow, of an unsatisfactory performer. The commission considered other evaluation periods and determined that evaluations more frequent than bi-annually may require shortening the appeal window to ensure appeal reviews could be completed before the next evaluation period begins.

The proposal amends §60.2(c) to change the methodology of grouping regulated entities from reliance on the North American Industry Classifications System (NAICS) to use of complexity points described in §60.2(e) as the commission has determined complexity to be a more accurate measurement criterion. In 2002, the commission determined Standard Industrial Classification (SIC) codes did not adequately capture the environmental complexity of the regulated community. In 2012, the commission listed NAICS codes as an option for grouping. However, over time, the commission found that the self-reported NAICS codes were frequently incorrect, inaccurate, or failed to fully describe the operations of the regulated site from an environmental impact standpoint. Therefore, the commission has not been able to effectively use NAICS codes for complexity determinations. The commission proposes to use the complexity formula to establish groupings to improve accuracy and provide certainty to the regulated public as they are already familiar with the formula and its impact on a site.

The proposal amends §60.2(f) to reflect changes to the way in which the commission evaluates repeat violators as required by SB 1397. Previously, in determining whether an entity was a repeat violator, the commission evaluated only major violations of the same nature and the same environmental media that occurred during the five-year compliance period. Under the proposed rule, in accordance with SB 1397, the commission will evaluate major, moderate, and minor violations of the same nature and environmental media that occurred during the five-year compliance period.

The new formula considers "repeat violation points" for each violation of the same nature and the same environmental media documented in any final enforcement orders, court judgments, and criminal convictions that occurred at least three times during the five-year compliance period. The number of "repeat violation points" varies by classification of the violation with each minor violation receiving 2 repeat violation points, each moderate violation receiving 10 points, and each major violation receiving 50 points. The total of all repeat violation points assessed to a regulated entity is used to determine whether the regulated entity has exceeded the repeat violation point thresholds to be classified as a repeat violator. The commission has established repeat violation point thresholds based on complexity points. Regulated entities with 15 or more complexity points and 150 or more "repeat violation points" will be classified as a repeat violator, while regulated entities with less than 15 complexity points and 100 or more "repeat violation points" will also be classified as a repeat violator.

The commission proposes changing §60.2(f)(1) and (2) and adding §60.2(f)(3). Proposed §60.2(f)(1) adds moderate and minor violations to repeat violator consideration and removes the requirement that violations be documented on separate occasions. Currently, multiple violations of the same type may be consolidated into a single enforcement action. Historically, the commission has considered "separate occasion" to mean individual orders or enforcement actions. For example, if a regulated entity had two unauthorized discharges within one compliance year and the entity signed a single agreed order that contained both major violations, the commission treated it as a single major violation for purposes of the repeat violator criteria. The legislative directive of SB 1397 to include all minor, moderate, and major violations requires the removal of the "separate occasion" language to ensure all violations are considered. The change allows the commission to consider all repeat occurrences of similar violations documented during the five-year evaluation period rather than the number of orders or enforcement actions that contained similar violations.

Proposed §60.2(f)(2)(A) - (C) establishes "repeat violation point" values based on the classification of the violation. Each violation of the same nature and the same environmental media documented in any final enforcement orders, court judgments, and criminal convictions that occurred at least three times during the five-year compliance period is assessed repeat violation points based on the classification of the violation. Each minor violation receives 2 repeat violation points, each moderate violation receives 10 points, and each major violation receives 50 points. This methodology allows the commission to clearly differentiate between repeat violators with significant actual or potential environmental harm from those entities that have repeat violations with minimal actual or potential environmental harm. For example, repeating a minor violation five times during a five-year period would be equally weighted with a single moderate violation, and repeating the same moderate violation five times during a five-year period would be weighted equally to one major violation.

Proposed §60.2(f)(3) establishes repeat violation point thresholds, based on complexity points, to determine repeat violator classifications. Under the proposal, a regulated entity is a repeat violator when: the site has less than a total of 15 complexity points and 100 or more repeat violation points; or the site has 15 or more complexity points and 150 or more repeat violation points. This approach continues to use 15 complexity points as the threshold and expands the criteria for repeat violators from three major violations for higher complex entities (150 points) to a combination of minor, moderate, and major violations (total 150 points) and two major violations for less complex entities (100 points) to a combination of minor, moderate and major violations (total 100 points). These thresholds ensure that the commission continues to hold repeat violators accountable without reducing environmental protections or standards. For example, higher complex regulated entities may reach the threshold by repeating the same moderate violation fifteen times within a five-year period, repeating the same minor violation seventy-five times within a five-year period, or some combination of violation points to reach the 150-point threshold.

The proposal moves "Repeat Violator Exemption" from existing §60.2(f)(2) to proposed §60.2(f)(4).

Proposed §60.2(g)(1)(L) changes the language referencing the Texas Environmental, Health, and Safety Audit Privilege Act. The Act was amended by the 85th Legislature in 2017 and the proposed language recognizes this change.

Proposed §60.2(g)(2) changes the site rating ranges for regulated entities. Currently, there is a common set of ranges for entities of all complexities. The commission proposes creating separate classification groups based on complexity points to address the Sunset Advisory Commission's management recommendation to compare entities of similar complexity to one another. The proposed rule establishes separate ranges for higher complex entities and less complex entities. Proposed §60.2(g)(2)(A) establishes the classification rating ranges for regulated entities with a complexity point total less than 15. For a regulated entity classified as less complex, a high performer is defined as having less than 0.10 points. A satisfactory performer is defined as having 0.10 points to 60 points. An unsatisfactory performer is defined as having more than 60 points.

Proposed §60.2(g)(2)(B) establishes the classification rating ranges for regulated entities with a complexity point total of 15 or more. A high performer is defined as having less than 0.10 points. A satisfactory performer is defined as having 0.10 points to 55 points. An unsatisfactory performer is defined as having more than 55 points.

As noted by the Sunset Advisory Commission, the compliance history rule calculation methodology disproportionately impacts less complex entities. The commission recognizes that, in general, less complex entities have fewer resources and face different challenges than their higher complexity counterparts. While the higher complexity entities are generally much larger in size, they tend to have more resources, represent a much smaller group of the regulated community, and typically have a potentially larger environmental footprint. The proposed rule allows for different classification thresholds for each complexity grouping, thereby accounting for their differences.

Proposed §60.2(g)(3)(A), (B)(i) and (ii) removes the specific point value that a regulated entity will receive following the application of a mitigating factor. Should a mitigating factor be granted to a regulated entity, the entity's rating will be adjusted to the maximum rating within the satisfactory classification for the entity's complexity point group. For regulated entities with less than 15 complexity points, the rating will be adjusted to 60. For regulated entities with 15 or more complexity points, the rating will be adjusted to 55.

Proposed §60.2(i) revises how a regulated entity can review their pending compliance history rating to match current practice by removing the submission of a Compliance History Review Form and replacing it with the registration for the Advanced Review of Compliance History (ARCH).

Fiscal Note: Costs to State and Local Government

Kyle Girten, analyst in the Budget and Planning Division, has determined that for the first five-year period the proposed rules are in effect, fiscal implications are anticipated for TCEQ and fiscal implications may result for units of local government as a result of implementation of the proposed rule. No fiscal implications are anticipated for other units of state government.

The General Appropriations Act (HB 1, 88th Legislature) authorized six full time equivalent (FTE) employees and $315,000 in funding to implement statutory changes to TWC §5.754 in SB 1397, 88th Legislature, 2023 and directives from the Sunset Advisory Commission that relate to this rulemaking. The proposed rulemaking would require TCEQ to update its compliance history twice annually instead of once per year (§60.2), and the rulemaking would also result in the agency needing to modify its compliance history application. The agency and Advanced Review of Compliance History website would need to be updated.

Local governmental entities which are permittees that are subject to the requirements of Chapter 60 could have indirect fiscal impacts from this rulemaking. This rule applies to approximately 400,000 entities, and this number includes businesses as well as local government entities. Compliance history information must be used by TCEQ when making decisions regarding permitting, enforcement, announced investigations, and participation in innovative programs (§60.3). Should the proposed rulemaking result in a change to whether an entity is classified as a satisfactory/unsatisfactory performer or repeat violator (§60.2), such an entity may have increased or decreased costs associated with permitting or administrative penalties. Ultimately, the fiscal impact on a regulated entity is dependent on compliance or non-compliance with the applicable environmental rules and regulations.

Public Benefits and Costs

Mr. Girten determined that for each year of the first five years the proposed rules are in effect, the public will benefit from having rules that are consistent with state law, specifically SB 1397 from the 88th Regular Legislative Session (2023) and directives from the Sunset Advisory Commission. The public will also benefit from having a more regularly updated record of regulated entities compliance status because the proposed rulemaking would require TCEQ to update compliance history information twice annually instead of once per year (§60.2).

Businesses which are permittees that are subject to the requirements of Chapter 60 could have indirect fiscal impacts from this rulemaking. Compliance history information must be used by TCEQ when making decisions regarding permitting, enforcement, announced investigations, and participation in innovative programs (§60.3). Should the proposed rulemaking result in a change to whether an entity is classified as a satisfactory/unsatisfactory performer or repeat violator (§60.2), such an entity may have increased or decreased costs associated with permitting or administrative penalties. Ultimately, the fiscal impact on a regulated entity is dependent on compliance or non-compliance with the applicable environmental rules and regulations.

Local Employment Impact Statement

The commission reviewed this proposed rulemaking and determined that a Local Employment Impact Statement is not required because the proposed rulemaking does not adversely affect a local economy in a material way for the first five years that the proposed rule is in effect.

Rural Community Impact Statement

The commission reviewed this proposed rulemaking and determined that the proposed rulemaking does not adversely affect rural communities in a material way for the first five years that the proposed rules are in effect. The amendments would apply statewide and have the same effect in rural communities as in urban communities.

Small Business and Micro-Business Assessment

No adverse fiscal implications are anticipated for small or micro-businesses due to the implementation or administration of the proposed rule for the first five-year period the proposed rules are in effect. Based on directives from the Sunset Advisory Commission, the proposed rulemaking is designed to address inequities between small and large entities. With the changes proposed in this rulemaking and the creation of separate groups based on complexity points, less complex entities will be separated from larger, higher complexity entities and compared to similarly complex sites when determining satisfactory rating classification and repeat violator status. This will allow each of the two groups to be held to separate standards which account for the unique opportunities and challenges faced by each group.

Small Business Regulatory Flexibility Analysis

The commission reviewed this proposed rulemaking and determined that a Small Business Regulatory Flexibility Analysis is not required because the proposed rule does not adversely affect a small or micro-business in a material way for the first five years the proposed rules are in effect.

Government Growth Impact Statement

The commission prepared a Government Growth Impact Statement assessment for this proposed rulemaking. The proposed rulemaking does not create or eliminate a government program and will not require an increase or decrease in future legislative appropriations to the agency. The proposed rulemaking does not require the creation of new employee positions, eliminate current employee positions, nor require an increase or decrease in fees paid to the agency. The proposed rulemaking amends an existing regulation, and it does not create, expand, repeal, or limit this regulation. The proposed rulemaking does not increase or decrease the number of individuals subject to its applicability. During the first five years, the proposed rule should not impact positively or negatively the state's economy.

Draft Regulatory Impact Analysis

The commission has reviewed the proposed rulemaking in light of the regulatory analysis requirements of Texas Government Code §2001.0225, and determined that the rulemaking is not subject to §2001.0225 because the proposed rule changes do not meet the definition of a "Major environmental rule" as defined in that statute. Although the intent of the proposed rule modifications are to protect the environment and reduce the risk to human health from environmental exposure, they do not adversely affect, in a material way, the economy, a sector of the economy, productivity, competition, jobs, the environment, or the public health and safety of the state or a sector of the state. Instead, the proposed rule changes merely modify the standards for the classification of a person's compliance history by setting the number of major, moderate, and minor violations needed to be classified as a repeat violator, to review and update the agency's compliance history rating formula to ensure it accurately reflects a regulated entity's record of violations, and to update compliance history ratings more often than once per fiscal year. The requirements for establishing standards for the classification of a person's compliance history are contained in TWC, §5.754.

The proposed rule modifications are designed to protect the environment, the public health, and the public safety of the state and all sectors of the state. Furthermore, the proposed rule modifications do not meet any of the four applicability requirements listed in §2001.0225(a). They do not exceed a standard set by federal law, because there is no comparable federal law. They do not exceed an express requirement of state law, because they are consistent with the requirements of TWC, §5.754. The proposed rule modifications do not exceed the requirements of a delegation agreement because there is no applicable delegation agreement. They are not proposed to be adopted solely under the general powers of the agency but will be adopted under the express requirements of TWC §5.754 and management recommendations adopted by the Sunset Advisory Commission.

The commission invites public comment on the draft regulatory impact analysis determination.

Takings Impact Assessment

The commission evaluated the proposed rules and performed an assessment of whether the proposed rules constitute a taking under TGC, Chapter 2007. The specific purpose of the proposed rules is to implement certain requirements of Senate Bill (SB) 1397 and other legislative directives, regarding compliance history. The proposed rules will substantially advance this stated purpose by modifying the standards for the classification of a person's compliance history by setting the number of major, moderate, and minor violations needed to be classified as a repeat violator, to review and update the agency's compliance history rating formula to ensure it accurately reflects a regulated entity's record of violations, and to update compliance history ratings more often than once per fiscal year.

Promulgation and enforcement of these proposed rules will be neither a statutory nor a constitutional taking of private real property. Specifically, the subject proposed regulations do not affect a landowner's rights in private real property because this rulemaking does not burden (constitutionally); nor restrict or limit the owner's right to property and reduce its value by 25% or more beyond that which would otherwise exist in the absence of the regulations. In other words, the proposed rules will not burden private real property because they modify the standards for the classification of a person's compliance history by setting the number of major, moderate, and minor violations needed to be classified as a repeat violator, to review and update the agency's compliance history rating formula to ensure it accurately reflects a regulated entity's record of violations, and to update compliance history ratings more often than once per fiscal year. The subject proposed rules do not affect a landowner's rights in private real property.

Consistency with the Coastal Management Program

The commission reviewed the proposed rulemaking and found that the proposal is subject to the Texas Coastal Management Program (CMP) in accordance with the Coastal Coordination Act, Texas Natural Resources Code, §§33.201 et seq., and therefore must be consistent with all applicable CMP goals and policies. The commission conducted a consistency determination for the proposed rules in accordance with Coastal Coordination Act Implementation Rules, 31 TAC §29.22, and found the proposed rulemaking consistent with the applicable CMP goals and policies.

CMP goals applicable to the proposed rule include: 31 TAC §26.12(1), to protect, preserve, restore, and enhance the diversity, quality, quantity, functions, and values of coastal natural resource areas (CNRAs); 31 TAC §26.12(2), to ensure sound management of all coastal resources by allowing for compatible economic development and multiple human uses of the coastal zone; 31 TAC §26.12(3), to minimize loss of human life and property due to the impairment and loss of protective features of CNRAs; 31 TAC §26.12(5), to balance the benefits from economic development and multiple human uses of the coastal zone, the benefits from protecting, preserving, restoring, and enhancing CNRAs, the benefits from minimizing loss of human life and property, and the benefits from public access to and enjoyment of the coastal zone; 31 TAC §26.12(6), to coordinate agency and subdivision decision-making affecting CNRAs by establishing clear, objective policies for the management of CNRAs; 31 TAC §26.12(7), to make agency and subdivision decision-making affecting CNRAs efficient by identifying and addressing duplication and conflicts among local, state, and federal regulatory and other programs for the management of CNRAs; and 31 TAC §26.12(8), to make agency and subdivision decision-making affecting CNRAs more effective by employing the most comprehensive, accurate, and reliable information and scientific data available and by developing, distributing for public comment, and maintaining a coordinated, publicly accessible geographic information system of maps of the coastal zone and CNRAs at the earliest possible date. The commission has reviewed the proposed rule for consistency with applicable goals of the CMP and determined that the proposed rule is consistent with the intent of the applicable goals and will not result in any significant adverse effect to CNRAs.

CMP policies applicable to the proposed rule include: 31 TAC §26.19, Construction and Operation of Solid Waste Treatment, Storage, and Disposal Facilities; 31 TAC §26.20, Prevention, Response, and Remediation of Oil Spills; 31 TAC §26.21, Discharge of Municipal and Industrial Wastewater to Coastal Waters; 31 TAC §26.22, Nonpoint Source (NPS) Water Pollution; 31 TAC §26.23, Development in Critical Areas; 31 TAC §26.25, Dredging and Dredged Material Disposal and Placement; 31 TAC §26.28, Development Within Coastal Barrier Resource System Units and Otherwise Protected Areas on Coastal Barriers; and 31 TAC §26.32, Emission of Air Pollutants. This rulemaking does not relax existing standards for issuing permits related to the construction and operation of solid waste treatment, storage, and disposal facilities in the coastal zone or for governing the prevention of, response to, and remediation of coastal oil spills. This rulemaking does not relax existing commission rules and regulations governing the discharge of municipal and industrial wastewater to coastal waters, nor does it affect the requirement that the agency consult with the Department of State Health Services regarding wastewater discharges that could significantly adversely affect oyster reefs. This rulemaking does not relax the existing requirements that state agencies and subdivisions with the authority to manage NPS pollution cooperate in the development and implementation of a coordinated program to reduce NPS pollution in order to restore and protect coastal waters. Further, it does not relax existing requirements applicable to: areas with the potential to develop agricultural or silvicultural NPS water quality problems; on-site disposal systems; underground storage tanks; or Texas Pollutant Discharge Elimination System permits for stormwater discharges. This rulemaking does not relax the standards related to dredging; the discharge, disposal, and placement of dredge material; compensatory mitigation; and authorization of development in critical areas. This rulemaking does not relax existing standards for issuing permits related to development of infrastructure within Coastal Barrier Resource System Units and Otherwise Protected Areas. Rather, the intent of the rulemaking is to increase compliance with existing standards and rule requirements.

Promulgation and enforcement of this rule will not violate or exceed any standards identified in the applicable CMP goals and policies because the proposed rule is consistent with these CMP goals and policies and because this rule does not create or have a direct or significant adverse effect on any coastal natural resource areas.

Written comments on the consistency of this rulemaking may be submitted to the contact person at the address listed under the Submittal of Comments section of this preamble.

Announcement of Hearing

The commission will hold a hold a hybrid virtual and in-person public hearing on this proposal in Austin on August 18, 2025, at 10:00 a.m. in Building D, Room 191, located at 12100 Park 35 Circle. The hearing is structured for the receipt of oral or written comments by interested persons. Individuals may present oral statements when called upon in order of registration. Open discussion will not be permitted during the hearing; however, commission staff members will be available to discuss the proposal 30 minutes prior to the hearing at 9:30 a.m.

Individuals who plan to attend the hearing virtually and want to provide oral comments and/or want their attendance on record must register by August 14, 2025. To register for the hearing, please email Rules@tceq.texas.gov and provide the following information: your name, your affiliation, your email address, your phone number, and whether or not you plan to provide oral comments during the hearing. Instructions for participating in the hearing will be sent on August 15, 2025, to those who register for the hearing.

For the public who do not wish to provide oral comments but would like to view the hearing may do so at no cost at:

https://events.teams.microsoft.com/event/d758c7a2-3f27-4605-bfe6-99749d686a8a@871a83a4-a1ce-4b7a-8156-3bcd93a08fba

Persons who have special communication or other accommodation needs who are planning to attend the hearing should contact Sandy Wong, Office of Legal Services at (512) 239-1802 or 1-800-RELAY-TX (TDD). Requests should be made as far in advance as possible.

Submittal of Comments

Written comments may be submitted to Gwen Ricco, MC 205, Office of Legal Services, Texas Commission on Environmental Quality, P.O. Box 13087, Austin, Texas 78711-3087, or faxed to fax4808@tceq.texas.gov. Electronic comments may be submitted at:

https://tceq.commentinput.com/comment/search. File size restrictions may apply to comments being submitted via the TCEQ Public Comments system. All comments should reference Rule Project Number 2024-043-060-CE. The comment period closes on August 25, 2025. Please choose one of the methods provided to submit your written comments.

Copies of the proposed rulemaking can be obtained from the commission's website at

https://www.tceq.texas.gov/rules/propose_adopt.html . For further information, please contact Krista Clement, Office of Compliance and Enforcement, (512) 239-1234.

Statutory Authority

The rule amendments are proposed under the authority of Texas Water Code (TWC) §5.753, concerning Standards for Evaluating and Using Compliance History, and TWC, §5.754, as amended by Senate Bill 1397, 88th Legislature, 2023, Section 13, concerning Classification and Use of Compliance History, which authorize rulemaking to establish compliance history standards, call upon the compliance history program to ensure consistency, and establish criteria for classifying a repeat violator. These provisions do not restrict the application of such classifications to be at specific intervals. Additional authority exists under TWC, §5.102, concerning General Powers, which provides the commission with the general powers to carry out its duties under the TWC; and TWC, §5.103, concerning Rules, which provides the commission the authority to adopt any rules necessary to carry out its powers and duties under the provisions of the TWC and other laws of this state.

The proposed rule amendments implements TWC, §§5.102, 5.103, 5.753, and 5.754.

§60.1. Compliance History.

(a) Applicability. The provisions of this chapter are applicable to all persons subject to the requirements of Texas Water Code (TWC), Chapters 26, 27, and 32 and Texas Health and Safety Code (THSC), Chapters 361, 375, 382, and 401.

(1) Specifically, the agency will utilize compliance history when making decisions regarding:

(A) the issuance, renewal, amendment, modification, denial, suspension, or revocation of a permit;

(B) enforcement;

(C) the use of announced investigations; and

(D) participation in innovative programs.

(2) For purposes of this chapter, the term "permit" means licenses, certificates, registrations, approvals, permits by rule, standard permits, or other forms of authorization.

(3) With respect to authorizations, this chapter only applies to forms of authorization, including temporary authorizations, that require some level of notification to the agency, and which, after receipt by the agency, requires the agency to make a substantive review of and approval or disapproval of the authorization required in the notification or submittal. For the purposes of this rule, "substantive review of and approval or disapproval" means action by the agency to determine, prior to issuance of the requested authorization, and based on the notification or other submittal, whether the person making the notification has satisfied statutory or regulatory criteria that are prerequisites to issuance of such authorization. The term "substantive review or response" does not include confirmation of receipt of a submittal.

(4) Notwithstanding [Regardless of the applicability of] paragraphs (2) and (3) of this subsection, this chapter does not apply to certain permit actions such as:

(A) voluntary permit revocations;

(B) minor amendments and nonsubstantive corrections to permits;

(C) Texas pollutant discharge elimination system and underground injection control minor permit modifications;

(D) Class 1 solid waste modifications, except for changes in ownership;

(E) municipal solid waste Class I modifications, except for temporary authorizations and municipal solid waste Class I modifications requiring public notice;

(F) permit alterations;

(G) administrative revisions; and

(H) air quality new source review permit amendments which meet the criteria of §39.402(a)(3)(A) - (C) and (5)(A) - (C) of this title (relating to Applicability to Air Quality Permits and Permit Amendments) and minor permit revisions under Chapter 122 of this title (relating to Federal Operating Permits Program).

(5) Further, this chapter does not apply to occupational licensing programs under the jurisdiction of the commission.

(6) Not later than March [September] 1, 2026 [2012], the executive director shall develop compliance histories with the components specified in this chapter. Prior to March [September] 1, 2026 [ 2012], the executive director shall continue in effect the standards and use of compliance history for any action (permitting, enforcement, or otherwise) that were in effect before March [September ] 1, 2026 [2012].

(7) Effective March [September] 1, 2026 [2012], this chapter shall apply to the use of compliance history in agency decisions relating to:

(A) applications submitted on or after this date for the issuance, amendment, modification, or renewal of permits;

(B) inspections and flexible permitting;

(C) a proceeding that is initiated or an action that is brought on or after this date for the suspension or revocation of a permit or the imposition of a penalty in a matter under the jurisdiction of the commission; and

(D) applications submitted on or after this date for other forms of authorization, or participation in an innovative program, except for flexible permitting.

(8) If a motion for reconsideration or a motion to overturn is filed under §50.39 or §50.139 of this title (relating to Motion for Reconsideration; and Motion to Overturn Executive Director's Decision) with respect to any of the actions listed in paragraph (4) of this subsection, and is set for commission agenda, a compliance history shall be prepared by the executive director and filed with the Office of the Chief Clerk no later than six days before the Motion is considered on the commission agenda.

(b) Compliance period. The compliance history period includes the five years prior to the date the permit application is received by the executive director; the five-year period preceding the date of the initial enforcement screening [initiating an enforcement action with an initial enforcement settlement offer or the filing date of an Executive Director's Preliminary Report, whichever occurs first]; for purposes of determining whether an announced investigation is appropriate, the five-year period preceding an investigation; or the five years prior to the date the application for participation in an innovative program is received by the executive director. The compliance history period may be extended beyond the date the application for the permit or participation in an innovative program is received by the executive director, up through completion of review of the application. Notices [Except as used in §60.2(f) of this title (relating to Classification) for determination of repeat violator, notices] of violation may only be used as a component of compliance history for a period not to exceed one year from the date of issuance.

(c) Components. The compliance history shall include multimedia compliance-related information about a person, specific to the site which is under review, as well as other sites which are owned or operated by the same person. The components are:

(1) any final enforcement orders, court judgments, and criminal convictions of this state relating to compliance with applicable legal requirements under the jurisdiction of the commission. "Applicable legal requirement" means an environmental law, regulation, permit, order, consent decree, or other requirement;

(2) notwithstanding [regardless of] any other provision of the TWC, orders developed under TWC, §7.070 and approved by the commission on or after February 1, 2002;

(3) to the extent readily available to the executive director, final enforcement orders, court judgments, consent decrees, and criminal convictions relating to violations of environmental rules of the United States Environmental Protection Agency;

(4) chronic excessive emissions events. For purposes of this chapter, the term "emissions event" is the same as defined in THSC, §382.0215(a);

(5) any information required by law or any compliance-related requirement necessary to maintain federal program authorization;

(6) the dates of investigations;

(7) all written notices of violation for a period not to exceed one year from the date of issuance of each notice of violation, including written notification of a violation from a regulated person, issued on or after September 1, 1999, except for those administratively determined to be without merit;

(8) the date of letters notifying the executive director of an intended audit conducted and any violations disclosed and having received immunity under the Texas Environmental, Health, and Safety Audit Privilege Act (Audit Act), 85th Legislature, 2017, TEX. HEALTH AND SAFETY CODE ch. 1101 [75th Legislature, 1997, TEX. REV. CIV. STAT. ANN. art. 4447cc (Vernon's)];

(9) an environmental management system approved under Chapter 90 of this title (relating to Innovative Programs), if any, used for environmental compliance;

(10) any voluntary on-site compliance assessments conducted by the executive director under a special assistance program;

(11) participation in a voluntary pollution reduction program; and

(12) a description of early compliance with or offer of a product that meets future state or federal government environmental requirements.

(d) Change in ownership. In addition to the requirements in subsections (b) and (c) of this section, if ownership of the site changed during the five-year compliance period, a distinction of compliance history of the site under each owner during that five-year period shall be made. Specifically, for any part of the compliance period that involves a previous owner, the compliance history will include only the site under review. For the purposes of this rule, a change in operator shall be considered a change in ownership if the operator is a co-permittee.

§60.2. Classification.

(a) Classifications. Effective March 1, 2026 [ Beginning September 1, 2002], the executive director shall evaluate the compliance history of each site and classify each site and person as needed for the actions listed in §60.1(a)(1) of this title (relating to Compliance History). On September 1, 2026 [2003 ], and semi-annually thereafter, the executive director shall evaluate the compliance history of each site, and classify each site and person. For the purposes of classification in this chapter, and except with regard to portable units, "site" means all regulated units, facilities, equipment, structures, or sources at one street address or location that are owned or operated by the same person. Site includes any property identified in the permit or used in connection with the regulated activity at the same street address or location. A "site" for a portable regulated unit or facility is any location where the unit or facility is or has operated. Each site and person shall be classified as:

(1) a high performer, which has an above-satisfactory compliance record;

(2) a satisfactory performer, which generally complies with environmental regulations; or

(3) an unsatisfactory performer, which performs below minimal acceptable performance standards established by the commission.

(b) Inadequate information. For purposes of this rule, "inadequate information" shall be defined as no compliance information. If there is no compliance information about the site at the time the executive director develops the compliance history classification, then the classification shall be designated as "unclassified." The executive director may conduct an investigation to develop a compliance history.

(c) Groupings. Sites will be divided into groupings based on complexity [North American Industry Classifications Systems (NAICS) codes] or other information available to the executive director. The complexity calculation is described in subsection (e) of this section (relating to Classification).

(d) Major, moderate, and minor violations. In classifying a site's compliance history, the executive director shall determine whether a documented violation of an applicable legal requirement is of major, moderate, or minor significance.

(1) Major violations are:

(A) a violation of a commission enforcement order, court order, or consent decree;

(B) operating without required authorization or using a facility that does not possess required authorization;

(C) an unauthorized release, emission, or discharge of pollutants that caused, or occurred at levels or volumes sufficient to cause, adverse effects on human health, safety, or the environment;

(D) falsification of data, documents, or reports; and

(E) any violation included in a criminal conviction, which required the prosecutor to prove a culpable mental state or a level of intent to secure the conviction.

(2) Moderate violations are:

(A) complete or substantial failure to monitor, analyze, or test a release, emission, or discharge, as required by a commission rule or permit;

(B) complete or substantial failure to submit or maintain records, as required by a commission rule or permit;

(C) not having an operator whose level of license, certification, or other authorization is adequate to meet applicable rule requirements;

(D) any unauthorized release, emission, or discharge of pollutants that is not classified as a major violation;

(E) complete or substantial failure to conduct a unit or facility inspection, as required by a commission rule or permit;

(F) any violation included in a criminal conviction, for a strict liability offense, in which the statute plainly dispenses with any intent element needed to be proven to secure the conviction; and

(G) maintaining or operating regulated units, facilities, equipment, structures, or sources in a manner that could cause an unauthorized or noncompliant release, emission, or discharge of pollutants.

(3) Minor violations are:

(A) performing most, but not all, of a monitoring or testing requirement, including required unit or facility inspections;

(B) performing most, but not all, of an analysis or waste characterization requirement;

(C) performing most, but not all, of a requirement addressing the submittal or maintenance of required data, documents, notifications, plans, or reports; and

(D) maintaining or operating regulated units, facilities, equipment, structures, or sources in a manner not otherwise classified as moderate.

(e) Complexity Points. All sites classified shall have complexity points as follows:

(1) Program Participation Points. A site shall be assigned Program Participation Points based upon its types of authorizations, as follows:

(A) four points for each permit type listed in clauses (i) - (viii) of this subparagraph issued to a person at a site:

(i) Radioactive Waste Disposal;

(ii) Hazardous or Industrial Non-Hazardous Storage Processing or Disposal;

(iii) Municipal Solid Waste Type I;

(iv) Prevention of Significant Deterioration;

(v) Phase I--Municipal Separate Storm Sewer System;

(vi) Texas Pollutant Discharge Elimination System (TPDES) or National Pollutant Discharge Elimination System (NPDES) Industrial or Municipal Major;

(vii) Nonattainment New Source Review; and

(viii) Underground Injection Control Class I/III;

(B) three points for each type of authorization listed in clauses (i) - (iv) of this subparagraph issued to a person at a site:

(i) Municipal Solid Waste Type I AE;

(ii) Municipal Solid Waste Type IV, V, or VI;

(iii) Municipal Solid Waste Type IV AE; and

(iv) TPDES or NPDES Industrial or Municipal Minor;

(C) two points for each permit type listed in clauses (i) - (iii) of this subparagraph issued to a person at a site or utilized by a person at a site:

(i) Title V Federal Operating Permit;

(ii) New Source Review individual permit; and

(iii) any other individual site-specific water quality permit not referenced in subparagraph (A) or (B) of this paragraph or any water quality general permit;

(D) one point for each type of authorization listed in clauses (i) - (xiii) of this subparagraph issued to a person at a site or utilized by a person at a site:

(i) Edwards Aquifer authorization;

(ii) Enclosed Structure permit or registration relating to the use of land over a closed Municipal Solid Waste landfill;

(iii) Industrial Hazardous Waste registration;

(iv) Municipal Solid Waste Tire Registrations;

(v) Other types of Municipal Solid Waste permits or registrations not listed in subparagraphs (A) - (C) of this paragraph;

(vi) Petroleum Storage Tank registration;

(vii) Radioactive Waste Storage or Processing license;

(viii) Sludge registration or permit;

(ix) Stage II Vapor Recovery registration;

(x) Municipal Solid Waste Type IX;

(xi) Permit by Rule requiring submission of an application under Chapter 106 of this title (relating to Permits by Rule);

(xii) Uranium license; and

(xiii) Air Quality Standard Permits.

(2) Size. Every site shall be assigned points based upon size as determined by the following:

(A) Facility Identification Numbers (FINs): The total number of FINS at a site will be multiplied by 0.02 and rounded up to the nearest whole number.

(B) Water Quality external outfalls:

(i) 10 points for a site with ten or more external outfalls;

(ii) 5 points for a site with at least five, but fewer than ten, external outfalls;

(iii) 3 points for sites with at least two, but fewer than five, external outfalls; and

(iv) 1 point for sites with one external outfall;

(C) Active Hazardous Waste Management Units (AHWMUs):

(i) 10 points for sites with 50 or more AHWMUs;

(ii) 5 points for sites with at least 20, but fewer than 50, AHWMUs;

(iii) 3 points for sites with at least ten, but fewer than 20, AHWMUs; and

(iv) 1 point for sites with at least one but fewer than ten AHWMUs.

(D) Small Entities shall receive 3 points. A small entity is defined as: a city with a population of less than 5,000; a county with a population of less than 25,000; or a small business. A small business is defined as any person, firm, or business which employs, by direct payroll and/or through contract, fewer than 100 full-time employees. A business that is a wholly owned subsidiary of a corporation shall not qualify as a small business if the parent organization does not qualify as a small business.

(E) Underground Storage Tanks (USTs) and Aboveground Storage Tanks (ASTs):

(i) 4 points for sites with 11 or more USTs;

(ii) 3 points for sites with five to ten USTs;

(iii) 3 points for sites with more than 11 ASTs;

(iv) 2 points for sites with three to four USTs;

(v) 2 points for sites with three to ten, ASTs;

(vi) 1 point for sites with one to two USTs; and

(vii) 1 point for sites with one to two ASTs.

(3) Nonattainment area points. Every site located in a nonattainment area shall be assigned 1 point.

(4) The subtotals from paragraphs (1) - (3) of this subsection shall be summed.

(f) Repeat violator.

(1) Repeat violator criteria. A person may be classified as a repeat violator at a site when[, on] multiple[, separate occasions,] major, moderate, or minor violations of the same nature and the same environmental media occurs during the preceding five-year compliance period [as provided in subparagraphs (A) and (B) of this paragraph]. Same nature is defined as violations that have the same root citation at the subsection level. For example, all rules under §334.50 of this title (relating to Release Detection) (e.g. §334.50(a) or (b)(2) of this title) would be considered same nature. The total complexity points for a site equals the sum of points assigned to a specific site in subsection (e) of this section. [A person is a repeat violator at a site when:]

[(A) the site has had a major violation(s) documented on at least two occasions and has less than a total of 15 complexity points; or]

[(B) the site has had a major violation(s) documented on at least three occasions.]

(2) Repeat violation points. Each repeat violation will be:

(A) Assigned 2 points for each minor violation as documented in any final enforcement orders, court judgments, and criminal convictions;

(B) Assigned 10 points for each moderate violation as documented in any final enforcement orders, court judgments, and criminal convictions; and

(C) Assigned 50 points for each major violation as documented in any final enforcement orders, court judgments, and criminal convictions.

(3) A person is a repeat violator at a site when the number of repeat violation points is:

(A) Equal to or greater than 150 for sites with 15 or more complexity points; or,

(B) Equal to or greater than 100 for sites with less than 15 complexity points.

(4) [(2)] Repeat violator exemption. The executive director shall designate a person as a repeat violator as provided in this subsection, unless the executive director determines the nature of the violations and the conditions leading to the violations do not warrant the designation.

(g) Formula. The executive director shall determine a site rating based upon the following method.

(1) Site rating. For the time period reviewed, the following calculations shall be performed based upon the compliance history at the site.

(A) The number of major violations contained in:

(i) any adjudicated final court judgments and default judgments, shall be multiplied by 160;

(ii) any non-adjudicated final court judgments or consent decrees without a denial of liability shall be multiplied by 140;

(iii) any non-adjudicated final court judgments or consent decrees containing a denial of liability, adjudicated final enforcement orders, and default orders, shall be multiplied by 120;

(iv) any final prohibitory emergency orders issued by the commission shall be multiplied by 120;

(v) any agreed final enforcement orders without a denial of liability shall be multiplied by 100; and

(vi) any agreed final enforcement orders containing a denial of liability shall be multiplied by 80.

(B) The number of moderate violations contained in:

(i) any adjudicated final court judgments and default judgments shall be multiplied by 115;

(ii) any non-adjudicated final court judgments or consent decrees without a denial of liability shall be multiplied by 95;

(iii) any non-adjudicated final court judgments or consent decrees containing a denial of liability, adjudicated final enforcement orders, and default orders, shall be multiplied by 75;

(iv) any agreed final enforcement orders without a denial of liability shall be multiplied by 60; and

(v) any agreed final enforcement orders containing a denial of liability shall be multiplied by 45.

(C) The number of minor violations contained in:

(i) any adjudicated final court judgments and default judgments shall be multiplied by 45;

(ii) any non-adjudicated final court judgments or consent decrees without a denial of liability shall be multiplied by 35;

(iii) any non-adjudicated final court judgments or consent decrees containing a denial of liability, adjudicated final enforcement orders, and default orders, shall be multiplied by 25;

(iv) any agreed final enforcement orders without a denial of liability shall be multiplied by 20; and

(v) any agreed final enforcement orders containing a denial of liability shall be multiplied by 15.

(D) The total number of points assigned for all resolved violations in subparagraphs (A) - (C) of this paragraph will be reduced based on achievement of compliance with all ordering provisions. For the first two years after the effective date of the enforcement order(s), court judgment(s), consent decree(s), and criminal conviction(s), the site will receive the total number of points assigned for violations in subparagraphs (A) - (C) of this paragraph. If all violations in subparagraphs (A) - (C) of this paragraph are resolved and compliance with all ordering provisions is achieved, for each enforcement order(s), court judgment(s), consent decree(s), and criminal conviction(s) :

(i) under two years old, the points associated with the violations in subparagraphs (A) - (C) of this paragraph will be multiplied by 1.0;

(ii) over two years old, the points associated with the violations in subparagraphs (A) - (C) of this paragraph will be multiplied by 0.75;

(iii) over three years old, the points associated with the violations in subparagraphs (A) - (C) of this paragraph will be multiplied by 0.50; and

(iv) over four years old, the points associated with the violations in subparagraphs (A) - (C) of this paragraph will be multiplied by 0.25.

(E) The number of major violations contained in any notices of violation shall be multiplied by 10.

(F) The number of moderate violations contained in any notices of violation shall be multiplied by 4.

(G) The number of minor violations contained in any notices of violation shall be multiplied by 1.

(H) The number of counts in all criminal convictions:

(i) under Texas Water Code (TWC), §§7.145, 7.152, 7.153, 7.162(a)(1) - (5), 7.163(a)(1) - (3), 7.164, 7.168 - 7.170, 7.176, 7.182, 7.183, and all felony convictions under the Texas Penal Code, TWC, Texas Health and Safety Code (THSC), or the United States Code (USC) shall be multiplied by 500; and

(ii) under TWC, §§7.147 - 7.151, 7.154, 7.157, 7.159, 7.160, 7.162(a)(6) - (8), 7.163(a)(4), 7.165 - 7.167, 7.171, 7.177 - 7.181, and all misdemeanor convictions under the Texas Penal Code, TWC, THSC, or the USC shall be multiplied by 250.

(I) The number of chronic excessive emissions events shall be multiplied by 100.

(J) The subtotals from subparagraphs (A) - (I) of this paragraph shall be summed.

(K) If the person is a repeat violator as determined under subsection (f) of this section, then 500 points shall be added to the total in subparagraph (J) of this paragraph. If the person is not a repeat violator as determined under subsection (f) of this section, then zero points shall be added to the total in subparagraph (J) of this paragraph.

(L) If the total in subparagraph (K) of this paragraph is greater than zero, then:

(i) subtract 1 point from the total in subparagraph (K) of this paragraph for each notice of an intended audit conducted under the Audit Act submitted to the agency during the compliance period; or

(ii) if a violation(s) was disclosed as a result of an audit conducted under the Audit Act [Texas Environmental, Health, and Safety Audit Privilege Act, (Audit Act), 75th Legislature, 1997, TEX. REV. CIV. STAT. ANN. art.4447cc (Vernon's)]; as amended, and the site received immunity from an administrative or civil penalty for that violation(s) by the agency, then the following number(s) shall be subtracted from the total in subparagraph (K) of this paragraph:

(I) the number of major violations multiplied by 10;

(II) the number of moderate violations multiplied by 4; and

(III) the number of minor violations multiplied by 1.

(M) The result of the calculations in subparagraphs (J) - (L) of this paragraph shall be divided by the number of investigations conducted during the compliance period multiplied by 0.1 plus the number of complexity points in subsection (e) of this section. If a site does not have any investigation points and the subtotal from subsection (e)(1) - (3) of this section equals zero, then one default point shall be used. Investigations that do not document any violations will be the only ones counted in the compliance history formula. The number of investigations multiplied by 0.1 shall be rounded up to the nearest whole number. If the value is less than zero, then the site rating shall be assigned a value of zero. For the purposes of this chapter, an investigation is a review or evaluation of information by the executive director or executive director's staff or agent regarding the compliance status of a site, excluding those investigations initiated by citizen complaints. An investigation, for the purposes of this chapter, may take the form of a site assessment, file or record review, compliance investigation, or other review or evaluation of information.

(N) If the person receives certification of an environmental management system (EMS) under Chapter 90 of this title (relating to Innovative Programs) and has implemented the EMS at the site for more than one year, then multiply the result in subparagraph (M) of this paragraph by 0.90, which is (1 - 0.10) and this is the maximum reduction that can be received for an EMS. If the person receives credit for a voluntary pollution reduction program or for early compliance, then multiply the result in subparagraph (M) of this paragraph by 0.95, which is (1 - 0.05). The maximum reduction that a site's compliance history may be reduced through voluntary pollution reduction programs in this subparagraph is 0.85, which is (1 - 0.15). If site participates in both EMS and voluntary pollution reduction programs then the maximum reduction that a site's compliance history may be reduced through EMS and voluntary programs in this subparagraph is 0.75, which is (1 - 0.10 - 0.15).

(2) Point ranges. The executive director shall assign the site a classification based upon the compliance history and application of the formula in paragraph (1) of this subsection to determine a site rating, utilizing the following site rating ranges for each classification:

(A) For entities with less than 15 complexity points:

(i) [(A)] fewer than 0.10 points--high performer;

(ii) 0.10 points to 60 points--satisfactory performer; and

(iii) more than 60 points--unsatisfactory performer.

(B) For entities with 15 or more complexity points:

(i) fewer than 0.10 points--high performer;

(ii) [(B)] 0.10 points to 55 points--satisfactory performer; and

(iii) [(C)] more than 55 points--unsatisfactory performer.

(3) Mitigating factors. The executive director shall evaluate mitigating factors for a site classified as an unsatisfactory performer.

(A) The executive director may reclassify the site from unsatisfactory to satisfactory performer [with 55 points] based upon the following mitigating factors:

(i) other compliance history components included in §60.1(c)(10) - (12) of this title;

(ii) implementation of an EMS not certified under Chapter 90 of this title at a site for more than one year;

(iii) a person, all of whose other sites have a high or satisfactory performer classification, purchased a site with an unsatisfactory performer classification or became permitted to operate a site with an unsatisfactory performer classification if the person entered into a compliance agreement with the executive director regarding actions to be taken to bring the site into compliance prior to the effective date of this rule; and

(iv) voluntarily reporting a violation to the executive director that is not otherwise required to be reported and that is not reported under the Audit Act, or that is reported under the Audit Act but is not granted immunity from an administrative or civil penalty for that violation(s) by the agency.

(B) When a person, all of whose other sites have a high or satisfactory performer classification, purchased a site with an unsatisfactory performer classification or became permitted to operate a site with an unsatisfactory performer classification and the person contemporaneously entered into a compliance agreement with the executive director regarding actions to be taken to bring the site into compliance, the executive director:

(i) shall reclassify the site from unsatisfactory performer to satisfactory performer [with 55 points] until such time as the next annual compliance history classification is performed; and

(ii) may, at the time of subsequent compliance history classifications, reclassify the site from unsatisfactory performer to satisfactory performer [with 55 points] based upon the executive director's evaluation of the person's compliance with the terms of the compliance agreement.

(h) Person classification. The executive director shall assign a classification to a person by adding the complexity weighted site ratings of all the sites owned and/or operated by that person in the State of Texas. Each site that a person is affiliated to will receive a point value based on the compliance history rating at the site multiplied by the percentage of complexity points that site represents of the person's total complexity points for all sites. Each of these calculated amounts will be added together to determine the person's compliance history rating.

(i) Notice of classifications. Notice of person and site classifications shall be posted on the commission's website after 30 days from the completion of the classification. The notice of classification shall undergo a quality assurance, quality control review period. An owner or operator of a site may review the pending compliance history rating upon request by registering for the Advanced Review of Compliance History. [submitting a Compliance History Review Form to the commission by August 15 each year.]

The agency certifies that legal counsel has reviewed the proposal and found it to be within the state agency's legal authority to adopt.

Filed with the Office of the Secretary of State on July 11, 2025.

TRD-202502364

Gitanjali Yadav

Deputy Director, Litigation Division

Texas Commission on Environmental Quality

Earliest possible date of adoption: August 24, 2025

For further information, please call: (512) 239-2678


CHAPTER 115. CONTROL OF AIR POLLUTION FROM VOLATILE ORGANIC COMPOUNDS

The Texas Commission on Environmental Quality (TCEQ, agency, or commission) proposes new §§115.260, 115.262, 115.264, 115.265, 115.266, and 115.269; and amended §§115.111, 115.112, 115.119, 115.122, 115.129, 115.411, 115.412, 115.415, 115.416, 115.419, 115.420, 115.421, 15.425, 115.427, 115.429, 115.440, 115.441, 115.449, 115.450, 115.451, 115.453, 115.455, 115.458-115.461, 115.463, 115.465, 115.468, and 115.469.

If adopted, these rules would be submitted to the U.S. Environmental Protection Agency (EPA) as a state implementation plan (SIP) revision.

Background and Summary of the Factual Basis for the Proposed Rules

On June 20, 2024, EPA published the reclassification of the Bexar County area, consisting of Bexar County, from moderate to serious nonattainment for the 2015 eight-hour ozone National Ambient Air Quality Standard (NAAQS) of 0.070 parts per million (ppm), effective July 22, 2024 (89 Federal Register (FR) 51829). The deadline for the Bexar County area to achieve attainment under the serious classification is September 24, 2027, with a 2026 attainment year. Federal Clean Air Act (FCAA), §182(b)(2) requires the commission to implement reasonably available control technology (RACT) provisions for all major sources of nitrogen oxides (NOX) and volatile organic compounds (VOC) in the Bexar County area. FCAA, §172(c) and §182(c) require the commission to submit serious classification attainment demonstration (AD) and reasonable further progress (RFP) SIP revisions to EPA. The required serious classification SIP revisions (Non-Rule Project Nos. 2024-040-SIP-NR and 2024-041-SIP-NR), along with the two concurrently proposed rulemakings (Rule Project Nos. 2025-006-115-AI and 2025-007-117-AI) needed for implementation of required NOX and VOC control measures, are due to EPA by January 1, 2026. This proposed rulemaking would address FCAA RACT requirements for major sources of VOC in the Bexar County area under the serious classification for the 2015 eight-hour ozone NAAQS. The proposed rulemaking also contains rule revisions to achieve sufficient VOC emissions reductions to demonstrate that the Bexar County area is making progress towards attainment and would achieve the mandated RFP reduction target for VOC.

In the Bexar County area, the emission profile presents unique challenges for reduction efforts. The county's VOC emissions are predominantly generated by nonpoint area sources, which constitute over 70% of the total emissions inventory (EI). In contrast, RACT is typically applied to point sources, which are fewer in number in Bexar County and contribute a relatively small fraction of overall VOC emissions. Nonpoint area sources offer the greatest potential for achieving significant VOC reductions in the Bexar County area. Accordingly, control strategies used to meet the RFP VOC emissions reduction requirement in this proposed rulemaking emphasize controlling area sources.

Attainment Demonstration Rulemaking Requirements

FCAA, §172(c) mandates that the commission submit an AD SIP revision to demonstrate that the Bexar County area will meet the NAAQS by its attainment date. Photochemical modeling for future years indicates that the Bexar County area will meet the 2015 ozone NAAQS by the mandated deadline using existing control strategies. The commission is neither required to propose nor is it proposing any rulemaking amendments to demonstrate attainment for the Bexar County area in this rulemaking because the modeling demonstrates attainment without the need for additional measures. A reasonably available control measures (RACM) analysis to identify additional potential control measures that could expedite attainment of the NAAQS earlier than the area's attainment date is provided in the concurrently proposed Bexar County 2015 Ozone NAAQS Serious AD SIP Revision (Non-Rule Project No. 2024-041-SIP-NR). The RACM analysis determined that no potential control measures met the criteria to be considered RACM. As a result, no rule revisions are proposed as RACM.

RACT Implementation Requirements

FCAA, §182(b)(2) requires the commission to implement RACT provisions for all major sources of VOC in the Bexar County area. EPA defines RACT as the lowest emission limitation that a particular source is capable of meeting by the application of control technology that is reasonably available considering technological and economic feasibility (44 FR 53761, September 17, 1979). RACT requirements for moderate and higher classification ozone nonattainment areas are included in the FCAA to ensure that significant source categories at major sources of ozone precursor emissions are controlled to a reasonable extent, but not necessarily to best available control technology levels expected of new sources or to maximum achievable control technology levels required for major sources of hazardous air pollutants. Although the FCAA requires the state to implement RACT, EPA guidance provides states with the flexibility to determine the most technologically and economically feasible RACT requirements for a nonattainment area. This rulemaking proposes to implement RACT requirements for the Bexar County serious nonattainment area, targeting sources that emit 50 tons per year (tpy) or more of VOCs. The proposed rules would specifically apply to offset lithographic printing operations, bakery ovens, and VOC storage tanks. While the proposed RACT rules are intended to fulfill SIP obligations resulting from the Bexar County area's reclassification from moderate to serious nonattainment, the rules are not expected to yield further reductions in VOC emissions. This is because RACT measures for moderate nonattainment are in effect in the area and already address all known point source emission sites. Since most non-mobile VOC emissions in the Bexar County area originate from nonpoint area sources in sectors associated with solvent utilization, such as smaller surface coating operations, RACT control strategies for major sources in this proposed rulemaking may have reduced impact and limited effectiveness. The proposed compliance date for these changes, March 1, 2026, is the start of the ozone season in Bexar County for the serious classification attainment year.

RFP Reduction Requirements

FCAA, §182(b)(1) requires the commission to demonstrate that the Bexar County area will achieve at least a 15% VOC emission reduction (15.85 tons per day (tpd)) from the 2017 baseline year. The concurrently proposed Bexar County 2015 Ozone NAAQS Serious RFP SIP Revision (Non-Rule Project No. 2024-040-SIP-NR) demonstrates that the Bexar County area will satisfy the 15% reduction requirement by using a combination of recently implemented measures and new rule changes. Recently implemented measures (Bexar County area moderate RACT Rules, Rule Project No. 2023-116-115-AI, adopted April 24, 2024) will achieve 3.75 tpd in VOC reductions. New rule changes in this proposed Bexar County area rulemaking are expected to achieve 12.13 tpd in VOC reductions. Collectively, these measures slightly exceed the 15% VOC RFP reduction requirement of 15.85 tpd. The proposed rule changes encompass several sections of Chapter 115. First, amendments are proposed to existing rules for degreasing processes within Subchapter E, Division 1 and are anticipated to result in 0.49 tpd of VOC emission reductions in the Bexar County area. Second, proposed revisions for fabric coating provisions outlined in Subchapter E, Division 2 are expected to result in 1.06 tpd of VOC emission reductions in the Bexar County area. Third, proposed revisions to coating of metal parts and products, architectural coatings, and industrial maintenance coatings provisions in Subchapter E, Division 5 are expected to result in 8.46 tpd of VOC emission reductions; along with revisions to industrial cleaning solvent provisions in Subchapter E, Division 6, which would result in 1.48 tpd of VOC emission reductions. Finally, proposed new rules in Subchapter C, Division 6, for gasoline dispensing nozzles and low permeation hoses from motor vehicle fuel dispensing facilities would result in an estimated 0.64 tpd in VOC emission reductions in the Bexar County area. The proposed compliance date for all these changes, March 1, 2026, is the start of the ozone season in Bexar County for the serious classification attainment year.

Section by Section Discussion

The commission proposes grammatical, stylistic, and other non-substantive changes to update the rules in accordance with current Texas Register style and format requirements, improve readability, establish consistency in the rules, and conform to the standards in the Texas Legislative Council Drafting Manual, September 2020. These non-substantive changes are not intended to alter the existing rule requirements in any way and are not specifically discussed in this preamble.

Among these non-substantive changes is removal of version identifiers for certain tests developed by the American Society of Testing and Materials (ASTM) in Subchapter E, Divisions 1, 2, and 5. Removal of the specific revision version will reference all test methods in these rule sections consistently. Sections affected by this change include §§115.415(1)(a), 115.420(c)(11)(S), 115.425(1)(B), 115.450(c)(9)(C) and (F), and 115.455(a)(1)(B).

SUBCHAPTER B: GENERAL VOLATILE ORGANIC COMPOUND SOURCES

DIVISION 1: STORAGE OF VOLATILE ORGANIC COMPOUNDS

Revisions in this division are proposed to fulfill major source RACT requirements.

§115.111. Exemptions

The commission proposes to establish exemption criteria in new §115.111(a)(17) for storage tanks and tank batteries storing condensate prior to custody transfer in Bexar County. To qualify for exemption from flashed gas control requirements, a storage tank or tank battery storing condensate must have a condensate throughput greater than 3,000 barrels (126,000 gallons) per year on a rolling 12-month basis, and owners or operators must be able to show, by the test methods specified, that uncontrolled VOC emissions are less than 50 tpy for individual tanks or aggregated tank batteries. This 50 tpy threshold aligns with the VOC RACT control requirements for major sources in Bexar County and effectively narrows the scope of tanks eligible for exemption to those with even lower emissions than what was allowed at the previous 100 tpy threshold. The exemption would become available beginning March 1, 2026. The commission proposes to remove a typographical error in language from §115.111(a)(15) that inadvertently repeated rule language.

§115.112. Control Requirements

The commission proposes to amend control requirements in §115.112(e)(4)(E) to clarify that fixed roof tanks in the Bexar County area storing condensate prior to custody transfer must continue to control flashed gases if the tank's throughput is greater than 6,000 barrels a year through February 28, 2026. This is considered equivalent to a 100 tpy VOC emission rate or greater. Beginning March 1, 2026, proposed control requirements in new §115.112(e)(5)(F) specify that owners or operators of fixed roof tanks storing condensate prior to custody transfer or at a pipeline breakout station must control flashed gases for tanks with VOC emissions greater than 50 tpy. The commission proposes to amend §115.112(e)(5)(E) to require that tanks at a tank battery or pipeline breakout station must route flashed gases to a vapor control system if they emit 50 or more tons of uncontrolled VOCs annually, rather than the previous threshold of 100 tons. This 50 tpy threshold aligns with the new VOC RACT major source limit.

§115.119. Compliance Schedules

The commission proposes to revise §115.119(g) to establish March 1, 2026, as the compliance date by which owners or operators of fixed roof storage tanks in the Bexar County area that store condensate prior to custody transfer must comply with the new requirements of §115.112(e)(4)(F) and §115.112(e)(5)(E) to control flashed gases.

DIVISION 2: VENT GAS CONTROL

Revisions in this division are proposed to fulfill major source RACT requirements.

§115.122 Control Requirements

The commission proposes to revise the rule text in §115.122(a)(3)(E) to require emission control requirements from vent gas from bakeries in the Bexar County area by lowering the applicability threshold from 100 tpy to 50 tpy for major source controls. Bakeries that emit 50 tpy or more of VOC emissions would be required to achieve an 80% reduction in VOC emissions through vent gas control from affected bakery ovens. By lowering the emission threshold and implementing stricter control requirements, this proposed rule revision seeks to address the area's ozone nonattainment classification of serious as well as ensure compliance with FCAA mandates for RACT implementation in Bexar County. Owners or operators of affected vent gas streams located in the Bexar County area must comply with the emission specifications in the subsection beginning March 1, 2026, the compliance date specified in proposed new §115.129(h).

The commission proposes revisions to §115.122(a)(3)(F)(iv), to prevent bakeries from claiming emission credits if they make emission reductions in the range of 30% to 90% associated with controlling VOC emissions from bakery oven vent gases in the Bexar County area. The current rule already prevents owners or operators in Bexar County with uncontrolled VOC emissions of 100 tpy or more from claiming emission credits under Chapter 101, Subchapter H, Division 1 to prevent double counting of reductions for the purposes of the SIP. This prohibition would apply for bakeries emitting VOC at the new, lower threshold of 50 tpy necessary for RACT implementation, beginning March 1, 2026.

§115.129 Counties and Compliance Schedules

The commission proposes to add new §115.129(h) to establish a compliance deadline of March 1, 2026, by which affected bakeries in the Bexar County area must meet updated RACT requirements for 90% vent gas controls from bakery ovens. Establishing this compliance date would ensure that RACT requirements are implemented as expeditiously as practicable and would also allow newly affected bakeries sufficient time to comply before the beginning of ozone season in the attainment year for the area.

SUBCHAPTER C: VOLATILE ORGANIC COMPOUND TRANSFER OPERATIONS

DIVISION 6: GASOLINE DISPENSING FACILITIES

Revisions in this division are proposed to result in VOC reductions necessary to meet RFP requirements.

The commission proposes to add a new Subchapter C, Division 6 to minimize Bexar County area gasoline dispensing facility (GDF) VOC spillage and associated gasoline transfer emissions from storage tanks into vehicles and containers. GDF sources would need to comply with the control requirements specified in §115.262, which include the installation of enhanced conventional (ECO) nozzles and low permeation hoses on gasoline dispensing pumps. Proposed Division 6 would also contain new sections with provisions for gasoline dispensing facility applicability and definitions, monitoring and inspection, testing and certification, recordkeeping, and compliance requirements.

Affected Bexar County area gasoline dispensing facilities would need to comply by March 1, 2026. Bexar County area gasoline dispensing facility equipment that becomes subject to Division 6 after March 1, 2026, would have 60 days to comply with its requirements.

§115.260 Applicability and Definitions

The commission proposes new §115.260 to establish new GDF rules and corresponding definitions in the Bexar County area. The rules only apply to gasoline dispenser equipment and not equipment that dispenses diesel or other fuels. Newly proposed §115.260 provisions are intended to assist owners and operators in identifying Division 6 applicability and clarifying regulatory definitions. Proposed §115.260(b) defines a GDF as one that includes retail, private, and commercial gasoline dispensing operations. It defines malfunctioning equipment as equipment that is not operating according to the manufacturer's design and specifications and requires remedial action to eliminate potential gasoline leakage. Proposed §115.260(b) also includes definitions for gasoline dispenser, conventional nozzle, ECO nozzle, low permeation hose, and gasoline dispensing spillage. Informing owners, operators, commission staff, and the public of the new §115.260 terminology would reduce confusion and inconsistent interpretations, which are crucial for compliance and enforcement.

§115.262 Control Requirements

The commission proposes new section §115.262 that would require ECO nozzle and low permeation hose controls on gasoline dispensing pumps in the Bexar County area. Only California Air Resources Board (CARB)-certified ECO nozzles and low permeation hoses that satisfy the proposed control requirements in §115.262 for reduced gasoline dispensing nozzle and reduced dispensing hose permeation rate gasoline emissions would be allowed. Retrofitting gasoline dispensing pumps with ECO nozzles and low permeation hoses required by proposed §115.262 reduces fuel drips or spills and vapor permeation, thereby significantly reducing VOC emissions from hundreds of GDFs in the county. Existing gasoline dispensing pumps would have until March 1, 2026, to install these items. Newly built gasoline dispensing pumps installed after March 1, 2026, would be required to install these items as soon as practicable and within 60 days of the pump's installation. Similar to other regulations, the commission would allow a 60-day period for new sites to come into compliance while anticipating that owners or operators of new sites will install the required hardware upon opening.

The commission also proposes work practice requirements in proposed §115.262. By implementing and enforcing spill prevention procedures, training, spill clean-up and other work practice requirements, GDFs can significantly minimize spills and associated VOC emissions. Proposed new §115.262 would require malfunctioning equipment to be repaired as soon as possible and before the next monthly inspection. The proposed regulation would require a GDF owner or operator to establish a policy to prohibit vehicle top-offs, require covers on open gasoline containers, mandate signs to inform customers and employees of proper filling practices and require spills to be cleaned up as soon as possible.

§115.264 Monitoring and Inspection Requirements

The commission proposes new §115.264 to establish monthly gasoline dispensing system monitoring and inspection requirements to identify leaking or malfunctioning equipment and facilitate timely repairs. ECO nozzles, low permeation hoses, and associated gasoline dispenser equipment would be inspected to ensure they were operating as intended and did not contain holes or tears that could allow gasoline leakage. The 0.64 tpd VOC emission reductions expected to be achieved from compliance with §115.264 requirements necessitates that GDF equipment remains in good condition, meets certification standards, and remains compliant with new rule requirements.

§115.265 Testing and Certification Requirements

The commission proposes new §115.265 to establish testing and certification provisions for the ECO nozzles and low permeation hoses that would be required at the affected gasoline dispensing facilities by proposed §115.262. Proposed §115.265 would require the use of UL 330 (7th ed) - Underwriters Laboratories' Standard for Hose and Hose Assemblies for Dispensing Flammable Liquids test methods to determine compliance with the proposed §115.262(a)(1) low permeation hose maximum permeation limit of 10.0 grams per square meters per day. ECO nozzles required to be installed by proposed §115.262(a)(3) would need to meet certification and test requirements in the California Air Resources Board Certification Procedure for Enhanced Conventional Nozzles and Low Permeation Conventional Hoses for Use at Gasoline Dispensing Facilities CP-207, dated July 12, 2021, including updates and revisions.

§115.266 Recordkeeping

The commission proposes new section §115.266 recordkeeping requirements to document compliance with newly proposed Chapter 115, Subchapter C, Division 6 rules. Proposed §115.266 would require owners and operators to keep GDF equipment monthly inspection records that include the inspector's name and inspection date; component inspected; inspection result and any corrective action; and the date corrective action was completed. GDFs would need to keep records of low permeation hose and ECO nozzle certifications as well as training records, described in §115.262(b)(6). The compliance records would need to be kept in a readily accessible format for a minimum of five years. Proposed §115.266 recordkeeping would include inspection, testing, certification, maintenance activity, and training documentation to confirm compliance with these rules. Tracking these activities documents compliance with the newly proposed Subchapter C, Division 6 rules.

§115.269 Compliance Schedules

The commission proposes a compliance deadline of March 1, 2026, for Bexar County area GDF equipment that meets applicability requirements on or before this initial compliance date. Bexar County area GDF equipment that becomes subject to Division 6 after the proposed March 1, 2026, compliance date would have 60 days after becoming subject to comply with its requirements. By establishing separate compliance dates in §115.269 for existing GDF equipment and similar components that may be installed in the future, the commission can ensure fair and consistent application of emission control requirements across all the intended sources, including newly constructed ones.

SUBCHAPTER E: SOLVENT-USING PROCESSES

DIVISION 1: DEGREASING PROCESSES

Revisions in this division are proposed to generate VOC reductions for RFP requirements.

§115.411 Exemptions

The commission proposes to revise §115.411(a) to remove the Bexar County area's applicability to exemptions currently available to degreasing operations under that subsection. On March 1, 2026, degreasing operations in Bexar County subject to §115.412(d) would no longer be eligible for exemptions under §115.411(a). This proposed amendment ensures that all degreasing operations, regardless of previous exemption status, adhere to lower VOC content limits. The commission proposes a new subsection, §115.411(c), with exemptions that would apply in the Bexar County area beginning March 1, 2026. Proposed new subsection §115.411(c) mirrors exemptions in current §115.411(b) for the Dallas-Fort Worth (DFW) and Houston-Galveston-Brazoria (HGB) areas, which would allow implementation of the same lower degreasing solvent VOC content limit in the Bexar County area.

§115.412 Control Requirements

The commission proposes to add a new subsection (d) to the control requirements in §115.412 to address VOC emissions from degreasing processes in the Bexar County area. This new subsection would establish specific VOC content limits for solvents used in cold solvent cleaning, open-top vapor degreasing, and conveyorized degreasing processes where there previously were none. The new degreasing limits require the use of solvents with a VOC content of no more than 25 grams/liter. The same limit is used as a contingency measure in the DFW and HGB areas in §§115.412(b) and (c), respectively, and it is necessary to implement in the Bexar County area to help achieve the VOC emissions reductions necessary for RFP requirements.

§115.415 Testing Requirements

The commission proposes to amend §115.415(3) to implement compliance testing requirements for the degreasing operations in the Bexar County area subject to §115.412(d). Under the existing rule, degreasing solvent VOC content limits are listed for the DFW and HGB areas in §115.412(b) and (c), respectively. The proposed inclusion of new §115.412(d) under §115.415(3) would specify the test method to determine VOC content for degreasing operations in the Bexar County area, bringing the requirements in line with other nonattainment areas. Accurate compliance testing, as outlined in methods specified in §115.415(3), is crucial for verifying that VOC limits are met so that intended VOC emission reduction targets are achieved from the implemented measures.

§115.416 Recordkeeping Requirements

The commission proposes new §115.416(5) to require degreasing operation facilities in the Bexar County area to maintain sufficient records to demonstrate compliance with the VOC content limits in §115.412(d) and applicable exemptions in §115.411.

§115.419 Counties and Compliance Schedules

The commission proposes to revise the compliance schedule in subsection §115.419(h) for degreasing operations to reflect new requirements. The schedule mandates that facilities subject to the provisions of proposed §115.412(d) in the Bexar County area comply with the updated control requirements by no later than March 1, 2026. This schedule provides facilities with sufficient time to adopt the necessary control measures and make operational adjustments while ensuring that the required VOC emission reductions needed from degreasing operations are achieved in a timely manner. In addition, the commission proposes a revision to §115.419(h) to remove a typographical error ‘by but' that was a remnant of the prior rulemaking and remove ‘Bexar' from the list of counties in §115.419(a). The commission should have deleted this in the prior rulemaking when existing §115.419(h) was added. Deleting it now provides a clear description of compliance requirements.

DIVISION 2: SURFACE COATING PROCESSES

Revisions in this division are proposed to generate VOC reductions for RFP requirements.

§115.420 Applicability and Definitions

The commission proposes to add the descriptor "Applicability" at the beginning of §115.420(a) to improve consistency with subsequent subsections §115.420(b) and §115.420(c) and parallel sections in other divisions of Chapter 115. The commission also proposes to add definitions under new §115.420(c)(4)(A) through §115.420(c)(4)(C) for "plasticizer, " "plastisol, " and "wash primer. " These new definitions would provide examples of fabric coatings that may be applied to protect or add new properties to a fabric substrate. The materials listed in §115.420(c)(4)(A) through §115.250(c)(4)(C), would help owners and operators, commission staff, and the public better understand what qualifies as a "fabric coating, "ensuring more consistent application, compliance, and enforcement of the rules. The commission proposes to update the reference in §115.420(c)(11)(S) from the outdated "Regulatory Guide 1.54" issued by the U.S. Atomic Energy Commission in June 1973 to the current Revision 3 of the guide, which was published in April 2017. The updated guide reflects the most recent requirements for protective coatings for nuclear power plants.

§115.421 Emission Specifications

The commission proposes to create new subparagraphs under existing §115.421(5) to differentiate proposed new requirements for fabric coating processes in the Bexar County area from existing requirements for other areas. Proposed subparagraph (A) would stipulate the existing requirements and areas subject to them, and proposed subparagraph (B) would require owners and operators of fabric coating processes in the Bexar County area to use coatings and wash primers containing 265 g/l (minus water and exempt solvent), which is a decrease from the existing limit of 350 g/l. The counties and areas listed under §115.421(5)(A), including Bexar County, would remain subject to the requirements in existing §115.421(5). Beginning March 1, 2026, the Bexar County area would then be subject to limits specified in §115.421(5)(B). Proposed new clauses §115.421(5)(B)(i) and §115.421(5)(B)(ii) would set limits for fabric coatings and wash primers at 265 g/l and for plastisol fabric coatings at 20 g/l (less water and exempt solvent), as applied at fabric coating operations in the Bexar County area. These proposed limits are based on South Coast Air Quality Management District (SCAQMD) Rule 1128, adopted on March 8, 1996, and approved by EPA on May 4, 1999, as documented in Federal Register at 64 FR 23774. The limits are proposed based on their potential to achieve greater VOC emission reductions from fabric coating operations. These reductions are necessary to meet RFP requirements in the Bexar County area.

§115.425 Testing Requirements

The commission proposes to make non-substantive changes to §115.425(1)(B) to remove version identifiers for certain tests developed by the American Society of Testing and Materials (ASTM). Removal of the specific revision version would reference all test methods in these rule sections consistently.

§115.427 Exemptions

Proposed new §115.427(3)(K) and amended §115.427(6) remove exemptions from rule requirements for low emitting fabric coating operations and aerosol coatings (spray paint), respectively, within the Bexar County area. Beginning March 1, 2026, owners or operators would be required to comply with the applicable emission specifications in §115.421 for fabric coatings. Proposed new §115.427(3)(K) and amended §115.427(6) exemptions allow for a wider range of VOC sources to be controlled to ensure that more fabric coating sources adhere to lower VOC content limits. The VOC reductions from these additional sources are necessary to help the Bexar County area meet RFP requirements. The commission also proposes to remove text in §115.427(3) in an example that references exemptions for architectural coatings. The proposed changes are intended to prevent confusion and to mirror text from a similar example in existing §115.451.

§115.429 Counties and Compliance Schedules

The commission proposes several changes in §115.429 to establish a binding deadline by which owners and operators of affected fabric coating operations must comply with particular rule provisions. Proposed amendments to §115.429(e) aim to clarify that compliance with fabric coating requirements of the division are required by the compliance date or within 60 days after becoming subject to the rule, if the compliance date has passed. The commission proposes adding new subsection §115.429(g) to establish compliance with the new fabric coating requirement in §115.421(5)(B) by March 1, 2026. The proposed amendment to §115.429(f) indicates that fabric coating operations in the Bexar County area currently subject to this division do not have to comply with the new requirement set in §115.421(5)(B) until the compliance date set in newly proposed §115.429(g).

DIVISION 4: OFFSET LITHOGRAPHIC PRINTING

Revisions in this division are proposed to fulfill major source RACT requirements and to generate VOC reductions for RFP requirements.

§115.440 Applicability and Definitions

The commission proposes to lower the major source threshold for offset lithographic facilities in the Bexar County area to comply with FCAA §§182(b)(2) and 182(f) RACT requirements. The definitions in subparagraphs §115.440(b)(8)(D) and §115.440(b)(9)(D) for both major and minor printing sources would be amended. In the existing rules, offset lithographic facilities in the Bexar County area with uncontrolled VOC emissions of 100 tpy are classified as major sources, while those below this threshold are considered minor. The proposed amendments would reduce the major source threshold to 50 tpy beginning March 1, 2026, for the Bexar County area. The definition for minor source would be revised similarly for the Bexar County area. Amendments to §115.440(b)(8)(D) and §115.440(b)(9)(D) would subject offset lithographic facilities to RACT requirements at lower thresholds of VOC and would ensure RACT requirements are implemented as required for offset lithographic printing facilities in the Bexar County area.

§115.441 Exemptions

The commission proposes changes to §115.441(b)(1) regarding the exemption for cleaning solutions used in offset lithographic printing operations in Bexar County for minor printing sources. In the existing rules, minor printing sources may exempt up to 110 gallons of cleaning solution per year from the VOC content limits in §115.442(c)(1). The proposed revision would remove this exemption for Bexar County beginning March 1, 2026. Removing the §115.441(b)(1) exemption for minor printing sources in Bexar County ensures that minor printing sources, regardless of previous exemption status, adhere to the lower VOC content limits proposed in Subchapter E, Division 6. The change is necessary to achieve the calculated VOC reductions associated with the proposed changes in Subchapter E, Division 6, which are necessary for RFP purposes in Bexar County. This change only affects sources in Bexar County, not the DFW or HGB areas.

§115.449 Compliance Schedules

The commission proposes to add rule text in §115.449(j) to establish a compliance deadline of March 1, 2026, by which date, affected facilities in the Bexar County area must adhere to RACT requirements and comply with low VOC content limits for offset lithographic operations.

DIVISION 5: CONTROL REQUIREMENTS FOR SURFACE COATING PROCESSES

Revisions in this division are proposed to generate VOC reductions for RFP requirements.

§115.450 Applicability and Definitions

The commission proposes to broaden the scope of surface coating operations subject to Subchapter E, Division 5 rules in the Bexar County area by adding architectural coatings to the list of applicable surface coating processes in §115.450(a). Language would be added to clarify that the rule applies only to architectural coatings in a commercial context and would explicitly exclude consumer use from applicability by stating that the rule applies to coatings applied for compensation. The commission proposes to add relevant architectural coating related definitions to §115.450 to accompany the architectural coatings VOC content limits that are proposed in §115.453. To ensure that all definitions in §115.450 remain in alphabetical order when new definitions are added, existing definitions would be reordered and renumbered accordingly.

The commission proposes to add §115.450(a)(9) and §115.450(a)(10) to extend the requirements in Subchapter E, Division 5 to architectural coatings and industrial maintenance coatings in the Bexar County area.

The commission proposes new §115.450(c)(11), which would provide definitions for different types of architectural coatings with VOC limits proposed in §115.453(a)(5). These proposed definitions are based on South Coast Air Quality Management District (SCAQMD) Rule 1113, amended on February 5, 2016, and approved by EPA on December 31, 2018, as documented in Federal Register at 40 CFR Part 52. The added definitions include aluminum roof coatings, appurtenance, below ground wood preservatives, bituminous coating materials, bituminous roof primers, bond breakers, building envelope, building envelope coatings, colorant, concrete-curing compounds, concrete surface retarders, default coatings, driveway sealers, dry-fog coatings, faux finishing coatings, clear topcoats, decorative coatings, glazes, japans, trowel applied coatings, fire-resistive coatings, flat coatings, form release compounds, gonioapparent, graphic arts coatings, interior stains, lacquers, low-solids coatings, magnesite cement coatings, mastic coating, metallic pigmented coatings, multi-color coatings, nonflat coatings, pearlescent, pigmented, post-consumer coatings, pre-treatment wash primers, primers, reactive penetrating sealers, recycled coatings, restoration architect, roof coatings, rust preventative coatings, sacrificial anti-graffiti coatings, sanding sealers, sealers, shellacs, specialty primers, stains, stationary structures, stone consolidants, swimming pool coatings, tile and stone sealers, topcoat, tub and tile refinishing coatings, undercoaters, varnishes, waterproofing sealers, wood coatings, wood conditioners, and wood preservatives. Many of these coating variants have their own separate VOC limits in §115.453(a)(5). By providing definitions in this section, owners and operators can more easily find the appropriate VOC limit for the product they are using.

§115.451 Exemptions

The commission proposes new §115.451(a)(6) to indicate that exemptions currently provided in §115.451(a)(1)-(3) for low-emission architectural coating operations, industrial maintenance coating operations, and metal parts and products coating operations would no longer apply in the Bexar County area beginning March 1, 2026. As of that date, owners or operators would be required to comply with applicable control requirements of §115.453. These changes are necessary to achieve all the calculated VOC reductions for RFP purposes in Bexar County.

The commission proposes to create exemptions in new subsection §115.451(q) for owners or operators of architectural coating operations in the Bexar County area. This new subsection identifies specific architectural coatings by type and size that would be exempt from the VOC limits in §115.453(a)(1)(C) and (D). Exemptions would apply to emulsion type bituminous pavement sealers (regardless of container size) under the newly proposed §115.451(q)(1); specific architectural coatings in containers of one liter or less are outlined in §115.451(q)(2)(A); and specific architectural coatings in containers of eight fluid ounces or less, or those used solely for touch-up are outlined in §115.451(q)(2)(B). Small containers of coatings, which are assumed to be used to cover small areas, contribute minimally to overall VOC emissions compared to larger containers. These exemptions mirror those in SCAQMD Rule 1113 and are necessary to achieve all the calculated VOC reductions for RFP purposes.

§115.453 Control Requirements

The commission proposes to restructure existing §115.453(a)(1)(C) VOC content limit provisions for miscellaneous metal parts and products. The existing limits apply in the Bexar, DFW, and HGB areas, and new limits would be added for the Bexar County area. The existing provisions would be relocated under §115.453(a)(1)(C)(i), and would continue to apply in Bexar County until February 28, 2026. Compliance with proposed new §115.453(a)(1)(C)(ii) would be required beginning March 1, 2026, in the Bexar County area. Existing provisions for the Bexar, DFW, and HGB areas would be relocated, without changes, from existing Figure: 30 TAC §115.453(a)(1)(C) to proposed new Figure: 30 TAC §115.453(a)(1)(C)(i). Separate provisions applicable only in the Bexar County area would be added under new Figure: 30 TAC §115.453(a)(1)(C)(ii). The proposed VOC content limits in subparagraph §115.453(a)(1)(C)(ii) for the Bexar County area aim to reduce emissions from coatings used in metal parts and products operations in the Bexar County area. Existing Table 2 under Figure: 30 TAC §115.453(a)(1)(C) specifying the VOC content as "pounds of volatile organic compounds per gallon of solids" will not be included for Bexar County provisions because the limits in the existing Table 2 are considered equivalent to existing Table 1, and because coating manufacturers typically do not specify VOC content in this manner on their documentation.

The proposed new Bexar County provisions would establish VOC content limits mirroring the limits in DFW and HGB, except for several coating categories as follows: one-component prefabricated architectural coatings (air-dried) VOC content limit would be 2.3 lbs/gal; multi-component prefabricated architectural coatings (air-dried) VOC content limit would be 2.8 lbs/gal; high-performance architectural coatings (air-dried) VOC content limit 3.5 lbs/gal; high-performance architectural coatings (baked) VOC content limit would 3.5 lbs/gal; extreme high-gloss coatings (air-dried) VOC content limit would be 2.8 lbs/gal; and one-component general coatings (air-dried) VOC content limit would be 2.3 lbs/gal. The proposed metal parts and products coatings VOC content limits, in lbs/gal coating, are based on the SCAQMD Rule 1107, adopted on January 6, 2006, and approved by EPA on November 24, 2008, as documented in the Federal Register (73 FR 70883). This rule has been successfully used in California to reduce VOC emissions from metal parts and products, and emissions reductions achieved based on these limits in Bexar County are necessary to meet RFP requirements.

The commission proposes to add new VOC content limits for architectural coatings in the Bexar County area. The new VOC content limits are currently used in other states. The new limits are listed in proposed renumbered §115.453(a)(5). Emissions reductions achieved based on these limits in Bexar County are necessary to meet RFP requirements The commission currently has no VOC content limits for architectural coatings in the Bexar County area or other areas of Texas. Three new tables would be created in §115.453(a)(5) that would list VOC content limits for various categories of architectural coatings, including bond breakers, building envelope coatings, concrete-curing compounds for roadways and bridges, concrete surface retarder, default coatings, driveway sealer, dry-fog coatings, faux finishing coatings, fire-resistive coatings, flat and nonflat coatings, floor coatings, form release compound, graphic arts (sign) coatings, magnesite cement coatings, mastic coatings, metallic pigmented coatings, multi-color coatings, pre-treatment wash primers, primers, sealers, and undercoaters, reactive penetrating sealers, recycled coatings, roof coatings, bituminous roof primers, rust preventative coatings, sacrificial, anti-graffiti coatings, shellacs, specialty primers, stains, stone consolidants, swimming pool coatings, tile and stone sealers, tub and tile refinishing coatings, waterproofing concrete/masonry sealers, wood coatings, conditioners, and preservatives, low-solids coatings, and certain colorants added to architectural coatings. Compliance would be achieved through the application of low VOC coatings. Applicable requirements for coating systems outlined in existing §115.453(c) and applicable work practice requirements detailed in existing §115.453(d) would apply and are not proposed for revision. The provision and equation in existing §115.453(a)(5) would be renumbered as §115.453(a)(6), with no additional proposed changes.

The commission proposes to add new subsection §115.453(j) to implement control measures for industrial maintenance coatings in the Bexar County area. The new §115.453(j) industrial maintenance coatings control requirement would set a VOC content limit of 2.1 lbs/gal or 250 (g/l) of coating, excluding water and exempt solvents to be met by applying low-VOC coatings. The limits of 2.1 lbs/gal and 250 g/l are considered equivalent. There is currently no VOC content limit control requirement for industrial maintenance coatings in the Bexar County area. This measure would establish control requirements for industrial maintenance coatings in the Bexar County area similar to contingency measures that exist in §115.453(f) and §115.453(g) for the DFW and HGB areas, respectively. This measure is necessary in the Bexar County area to meet RFP requirements.

§115.455 Approved Test Methods and Testing Requirements

The commission proposes to update approved test methods and testing requirements in §115.455 for architectural coating operations in the Bexar County area. Inclusion of these updates in the proposed rule is necessary because new architectural coatings definitions make references to them. The commission proposes to add American National Standards Institute (ANSI) A137.1 Standard Specifications for Ceramic Tiles, a test method for applicable tile and stone penetrative sealers, and is referenced in proposed §115.450(c)(11)(VV)(i)(II). The commission proposes to reference The National Cooperative Highway Research Report 244 (1981) "Concrete Sealers for the Protection of Bridge Structures" test method for applicable surface chloride screening applications, and would be referenced in proposed §115.450(c)(11)(HH)(vi). The commission proposes to update the existing ASTM test methods list in §115.455(a)(1)(B) to include references to test methods C67, C97/97M, C140, C309 Class B, C373, C642, D523, D714, D3359, D3363, D4060, D4214, D4585, D6490, E96/E96M, E284, E331, E2167, and E2178 since they are included in various proposed definitions throughout §115.450. Proposed §115.450(c)(4)(A), §115.450(c)(5)(A), and §115.450(c)(6)(H), would require use of test method ASTM D523, that extreme high-gloss coatings have a reflectance of 75% or more on a 60 degree meter. Proposed §115.450(c)(9)(F) would require test method ASTM D523 to show a reflectance of at least 85% on a 60 degree meter for high gloss coatings. Test method ASTM E2178 outlines the testing methodology for building envelope coatings to have air barriers with a permeance not exceeding 0.004 cubic feet per minute per square foot under a pressure differential of 1.57 pounds per square foot and is referenced in proposed §115.450(c)(11)(H)(i). Test method ASTM E331 is used to measure water resistance of building envelope coatings with water resistive barriers and is referenced in proposed §115.450(c)(11)(H)(ii)(I). The commission proposes to add the definition of "gonioapparent" in §115.450(c)(11)(S). Gonioapparent is a term that is used to describe decorative coatings, for which VOC content limits are proposed. Test method ASTM E284 is used to measure the change in appearance with the change in the angle of illumination or angle of view of gonioapparent coatings. Test methods ASTM C67, C97/97M, or C140 would be used to verify an improvement in water repellency of at least 80% after application for reactive penetrating sealers and is referenced in proposed §115.450(c)(11)(HH)(iv). Test methods ASTM E96/E96M and ASTM D6490 are used to verify the ability of reactive penetrating sealers to provide a breathable waterproof barrier for concrete or masonry surfaces that does not prevent or substantially retard water vapor transmission and are referenced in proposed §115.450(c)(11)(HH)(v). Test method ASTM D4214 defines an excessively chalky surface for the application of proposed specialty primers to condition such surfaces and is referenced in proposed §115.450(c)(11)(QQ). Test method ASTM E2167 specifies the proper use and specifications for proposed stone consolidants, and is referenced in proposed 115.450(c)(11)(TT)(iii). Test methods ASTM C373, C97/97M, or C642 are used to demonstrate absorption as low as 0.10% for penetrating tile and stone sealers and are referenced in proposed §115.450(c)(11)(VV)(i)(I). Test method ASTM D4060 is used to demonstrate that a proposed tub and tile refinishing coating has a weight loss of 20 milligrams or less after 1,000 cycles as determined with CS-17 wheels on bonderite 1,000, as referenced in proposed §115.450(c)(11)(XX)(ii). Test methods ASTM D4585 and D714 are used to demonstrate a tub and tile refinishing coatings' ability to withstand 1,000 hours or more of exposure with few or no #8 blisters, determined on unscribed bonderite and are referenced in proposed §115.450(c)(11)(XX)(iii). Test methods ASTM D3359 and D4585 are used to show a tube and tile refinishing coatings' adhesion rating as 4B or better after 24 hours of recovery as determined on unscribed bonderite, as referenced in proposed §115.450(c)(11)(XX)(iv). Test method ASTM D3363 is used to demonstrate a scratch hardness of 3H or harder and a gouge hardness of 4H or harder as determined on bonderite 1000, as referenced in proposed §115.450(c)(11)(XX)(i).

§115.458 Monitoring and Recordkeeping Requirements

The commission proposes to add recordkeeping requirements for the newly proposed architectural coating and industrial maintenance coating provisions for the Bexar County area. The commission is proposing to add a recordkeeping requirement for the newly proposed §115.453(j) industrial maintenance coating VOC limits and replace "or" with "and" in the last sentence of existing §115.458(b)(1), clarifying that records must be kept documenting compliance with all applicable §115.453 surface coating VOC control limits. By adding proposed new VOC content limits in §115.453(j) applicable in Bexar County, the "or" must be changed to "and" since applicable requirements would exist in §115.453(a) and (j) for some owners or operators in Bexar County. Owners or operators of architectural coating and industrial maintenance operations in the Bexar County area would be required to maintain records of solvent information such as VOC content, composition, solids content, and solvent density. Because the rule language requires records for all applicable VOC content limits, no owners or operators in the DFW or HGB areas would be required to maintain records of the industrial maintenance coating VOC content specified in proposed §115.453(j) since these coating limits would not be applicable in these areas. If, however, the contingency measures for industrial maintenance coating VOC content limits in existing §115.453(f) or (g) are triggered according to §115.459(e) or (g), respectively, affected owners or operators would be required to maintain such records because the industrial maintenance coating contingency VOC content limits would be applicable to them. Maintaining records of this information provides evidence that coatings and solvents comply with VOC content limits.

§115.459 Compliance Schedules

To provide owners and operators of metal parts and products coatings operations, architectural coating operations, and industrial maintenance surface coating operations in the Bexar County area with sufficient time to comply with new rule requirements, the commission is proposing to establish a compliance date of March 1, 2026, under §115.459(c). This deadline ensures that facilities can adjust operations and implement necessary changes while ensuring that the required VOC emission reductions needed for RFP are achieved during the attainment year.

DIVISION 6: INDUSTRIAL CLEANING SOLVENTS

Revisions in this division are proposed to generate VOC reductions for RFP requirements.

§115.460 Applicability and Definitions

The commission proposes to amend the definition of "electrical and electronic components" in §115.460(b)(7) for purposes of clarifying the Bexar County §115.461(f) exemption and §115.463(f) control requirements for the Bexar County area. The definition is different in the context of different rule provisions, and this amendment would ensure that the proper definition applies in the context of §115.461(f) and §115.463(f) requirements. The commission also proposes to amend the definition of "solvent cleaning operation" in §115.460(b)(42) for the Bexar County area §115.461(f) exemption and §115.463(f) control requirement.

§115.461 Exemptions

The commission proposes to relocate the existing §115.461(f) exemption to §115.461(g) and insert newly proposed §115.461(f) language that would prohibit the use of existing exemptions §115.461(a) through (d) in Bexar County beginning March 1, 2026. The proposed language would also update references to include the proposed renumbered §115.461(g). If adopted, newly proposed §115.461(f) would limit industrial solvent cleaning exemptions in Bexar County to the following twelve categories: 1) cleaning of solar cells, laser hardware, scientific instruments, and high-precision optics; 2) cleaning conducted with performance laboratory tests, coatings, adhesives, or inks; research and development programs; and laboratory tests in quality assurance laboratories; 3) cleaning of paper-based gaskets, and clutch assemblies where rubber is bonded to metal by means of an adhesive; 4) cleaning of cotton swabs to remove cottonseed oil before cleaning of high-precision optics; 5) medical device and pharmaceutical facilities using up to 1.5 gallons per day of solvents; 6) the cleaning of photocurable resins from stereolithography equipment and models; 7) cleaning of adhesive application equipment used for thin metal laminating operations provided the clean-up solvent used contains no more than 950 grams of VOC per liter; 8) cleaning of electronic or electrical cables provided the clean-up solvent used contains no more than 400 grams of VOC per liter; 9) touch up cleaning performed on printed circuit boards where surface mounted devices have already been attached provided that the solvent used contains no more than 800 grams of VOC per liter; 10) cleaning carried out in batch loaded cold cleaners, vapor degreasers, conveyorized degreasers, or motion picture film cleaning equipment; 11) janitorial cleaning, including graffiti removal; and 12) stripping of cured coatings, cured ink, or cured adhesives. The commission also proposes to add " and (g)" at the end of §115.461(a) to clarify that both industrial solvent activities listed in (f) and cleaning solvents in aerosol cans referenced in (g) of this section are exempt and not required to be quantified. The list of exemptions proposed for Bexar County mirror those in §115.461(e) available in the DFW and HGB areas if the industrial cleaning solvent contingency measures are triggered in those areas.

§115.463 Control Requirements

The commission proposes to add new VOC content limits for industrial cleaning solvent operations in §115.463(f) for the Bexar County area. The industrial cleaning solvent categories that would be subject include product cleaning during manufacturing processes or surface preparations for coating, adhesives, or ink applications; repair and maintenance cleaning; cleaning of coatings or adhesives application equipment; cleaning of ink application equipment; and cleaning of polyester resin application equipment. This measure is projected to reduce VOC emissions from industrial cleaning solvent operations in the Bexar County area and would align control requirements with the contingency measures in DFW and HGB by mirroring the requirements in §115.463(e). The commission also proposes to update the first sentence of §115.463(a) to clarify that sources in the DFW and HGB areas are not subject to §115.463(f), which only apply in the Bexar County area.

§115.465 Approved Test Methods and Testing Requirements

The commission proposes to amend §115.465(1) to specify testing requirements that could be used to verify the new VOC content limits proposed in §115.463(f). Existing testing methods, specified in §115.465(1)(A) through (D), could be used to verify the proposed limits in §115.463(f).

§115.468 Monitoring and Recordkeeping Requirements

The commission proposes to amend §115.468(b)(1) to add recordkeeping requirements for the newly proposed solvent cleaning provisions in the Bexar County area. The proposed amendment to §115.468(b)(1) would require owners and operators of solvent cleaning operations to maintain records documenting compliance with newly proposed §115.463(f) VOC limits. Records demonstrating compliance include testing data, MSDSs, or documentation of the standard reference texts used to determine the true vapor pressure of each VOC component.

§115.469 Compliance Schedules

The commission proposes an update to §115.469(b) to clarify that sources in the Bexar County area subject to the new Subchapter E, Division 6 industrial cleaning solvent requirements must be in compliance no later than March 1, 2026. This provides sufficient time for affected entities to implement compliant cleaning options while reducing VOC emissions prior to the ozone season of the attainment year.

Fiscal Note: Costs to State and Local Government

Kyle Girten, Analyst in the Budget and Planning Division, has determined that for the first five-year period the proposed rules are in effect, no significant fiscal implications are anticipated for TCEQ or other state government entities during implementation of the proposed rule.

Fiscal implications are anticipated for one city government entity during implementation of the proposed rule. It is estimated that new gasoline dispensing nozzles and low permeability hoses would need to be installed at 11 city refueling stations to comply with the proposed addition of Subchapter C, Division 6. Total costs as needed to replace all gasoline nozzles and gasoline dispensing hoses with low permeability hoses is estimated at $70,000 in year one. It is estimated that there would be savings of approximately $4,000 each year in years two through five because gasoline leakage would reduce with the new hoses.

Public Benefits and Costs

Mr. Girten determined that for each year of the first five years the proposed rules are in effect, the public benefit anticipated will be compliance with federal law and continued protection of the environment and public health and safety combined with efficient and fair administration of VOC emission standards for Bexar County. Corrections of errors and other non-substantive changes within the rule would also benefit the public.

Costs would be incurred for affected businesses operating in Bexar County for implementation of requirements appliable to RACT. This rulemaking would lower the major source threshold from 100 tpy to 50 tpy VOC for lithographic printing operations (Subchapter E, Division 4), bakery ovens (Subchapter B, Division 2), and VOC storage tanks (Subchapter B, Division 1). Additionally, to meet the required RFP reduction target, revisions would be made as needed to implement stricter VOC limits for degreasing processes (Subchapter E, Division 1), fabric coating (Subchapter E, Division 2), coating of metal parts, architectural coatings, and industrial maintenance coatings (Subchapter E, Division 5), industrial cleaning solvent provisions (Subchapter E, Division 6), and gasoline dispensing nozzles and low permeation hoses from motor vehicle dispensing facilities (Subchapter C, Division 6). Any impacted business may be required to update their permit with TCEQ to update processes that are approved for use at their facilities, and some costs may be incurred to meet these permitting requirements. Costs specific to affected businesses are discussed below.

It is estimated that there are 37 commercial bakeries, 61 lithographic printing facilities, and 25 facilities with VOC storage tanks that would be affected by this rulemaking. Because the individuals who are responsible for the sources should have implemented RACT measures after the updates to this Chapter were made on April 24, 2024 (Rule Project No. 2023-116-115-AI), it is not anticipated that any additional costs would be incurred for these businesses. Should any commercial bakeries need to implement RACT measures, the cost per bakery is estimated at $492,000 in year one and $74,000 in years two through five, and this includes costs related to incinerator control, monitoring, testing, and recordkeeping. Should any lithographic printing facilities need to implement RACT measures, the cost per facility is estimated at $22,000 each year as needed to meet control and recordkeeping requirements. Should RACT measures need implemented for VOC storage tanks, the cost per tanks is estimated at $150,280 in the year one and $22,100 in years two through five as needed to meet control, monitoring, testing, seal inspection, and recordkeeping requirements.

The remaining businesses that would be affected are nonpoint area sources. It is estimated that there are eight facilities with degreasing processes, 25 facilities with fabric coating processes, 23 facilities with metal parts and products, five facilities with architectural coating processes, 98 facilities that use industrial maintenance coatings, 98 facilities that use industrial cleaning solvents, and up to 1,181 retail gas stations that would incur costs.

Degreasing requirements (Subchapter E, Division 1) would apply to owners or operators of cold solvent cleaning, open-top vapor degreasing, and conveyorized decreasing processes. Total costs, as needed to meet lower VOC content requirements for degreasing materials, and associated recordkeeping, reporting, monitoring, or testing requirements is estimated to total approximately $270,000 in year one and $50,000 in years two through five.

Fabric coating requirements (Subchapter E, Division 2) would apply to fabric coating and wash primers. Total costs, as needed to meet lower VOC content requirements, and associated recordkeeping, reporting, monitoring, or testing requirements is estimated to total approximately $1.3 million each year of the first five years the proposed rules are in effect.

Metal parts, architectural coatings, and industrial maintenance coatings (Subchapter E, Division 5) would apply to coating processes. For metal parts, total costs as needed to meet lower VOC content requirements, and associated recordkeeping, reporting, monitoring, or testing requirements is $3.9 million each year of the first five years the proposed rules are in effect. For architectural coatings, costs to meet lower VOC content requirements, and associated recordkeeping, reporting, monitoring, or testing requirements similarly totals $3.9 million each year. No additional expenses are anticipated for businesses that use industrial maintenance coatings because recordkeeping for current materials is assumed to be done already. For the same reason, businesses that use industrial cleaning solvents (Subchapter E, Division 6) are not anticipated to incur any additional expenses.

Requirements related to gas stations (Subchapter C, Division 6) would apply to all retail gas stations in Bexar County. Assuming 670 gas stations are impacted, the total costs as needed to replace all gasoline nozzles and replace gasoline dispensing hoses with low permeability hoses is $4.3 million in year one. It is estimated that there would be savings of over $230,000 each year in years two through five because gasoline leakage would reduce with the new hoses.

Local Employment Impact Statement

The commission reviewed this proposed rulemaking and determined that a Local Employment Impact Statement is not required because the proposed rulemaking is not anticipated to adversely affect a local economy in a significant way for the first five years that the proposed rule is in effect.

Rural Communities Impact Assessment

The commission reviewed this proposed rulemaking and determined that the proposed rulemaking does not adversely affect rural communities in a material way for the first five years that the proposed rules are in effect. This rulemaking applies to Bexar County, which has a large population; therefore, rural communities are not significantly impacted. Some commercial bakeries, VOC storage tanks, degreasing operations, surface coating operations, and gasoline stations in rural communities would be impacted, but no adverse impacts to these communities are anticipated.

Small Business and Micro-Business Assessment

No significant adverse fiscal implications are anticipated for small or micro-businesses due to the implementation or administration of the proposed rule for the first five-year period the proposed rules are in effect. It is estimated there are seven commercial bakeries that are small businesses (four of which are micro-businesses), 61 lithographic printing facilities (53 of which are micro-businesses), 18 VOC storage tanks (all of which are micro-businesses), 11 small businesses that use fabric coating processes (all of which are micro-businesses), eight small businesses that use metal parts and product coatings (all of which are micro-businesses), 98 small businesses that use industrial maintenance coatings (88 of which are micro-businesses), and 590 gasoline stations (541 of which are micro-businesses).

Small Business Regulatory Flexibility Analysis

The commission reviewed this proposed rulemaking and determined that a Small Business Regulatory Flexibility Analysis is not required because the proposed rule does not adversely affect a small or micro-business in a material way for the first five years the proposed rules are in effect. The proposed rules are required to represent RACT requirements that are technologically and economically feasible for regulated sources. The same compliance and reporting requirements are necessary and apply to all businesses regardless of size.

Government Growth Impact Statement

The commission prepared a Government Growth Impact Statement assessment for this proposed rulemaking. The proposed rulemaking does not create or eliminate a government program and will not require an increase or decrease in future legislative appropriations to the agency. The proposed rulemaking does not require the creation of new employee positions, eliminate current employee positions, nor require an increase or decrease in fees paid to the agency. The proposed rulemaking amends an existing regulation, and it does not increase or decrease the number of individuals subject to its applicability. During the first five years, the proposed rule should not impact positively or negatively the state's economy.

Draft Regulatory Impact Analysis Determination

The commission reviewed the proposed rulemaking in light of the regulatory impact analysis requirements of Texas Government Code, §2001.0225, and determined that the proposed rulemaking does not meet the definition of a major environmental rule as defined in that statute, and in addition, if it did meet the definition, would not be subject to the requirement to prepare a regulatory impact analysis. A major environmental rule means a rule, the specific intent of which is to protect the environment or reduce risks to human health from environmental exposure, and that may adversely affect in a material way the economy, a sector of the economy, productivity, competition, jobs, the environment, or the public health and safety of the state or a sector of the state. Additionally, the proposed rulemaking does not meet any of the four applicability criteria for requiring a regulatory impact analysis for a major environmental rule, which are listed in Tex. Gov't Code Ann., §2001.0225(a). Section 2001.0225 of the Texas Government Code applies only to a major environmental rule, the result of which is to: 1) exceed a standard set by federal law, unless the rule is specifically required by state law; 2) exceed an express requirement of state law, unless the rule is specifically required by federal law; 3) exceed a requirement of a delegation agreement or contract between the state and an agency or representative of the federal government to implement a state and federal program; or 4) adopt a rule solely under the general powers of the agency instead of under a specific state law.

The specific intent of these proposed rules is to comply with federal requirements for the implementation of control strategies necessary to attain and maintain the NAAQS for ozone mandated by 42 United States Code (USC), 7410, FCAA, §110, and required to be included in operating permits by 42 USC, §7661a, FCAA, §502, as specified elsewhere in this preamble. The proposed rulemaking addresses RACT and RFP requirements for the Bexar County 2015 eight-hour ozone nonattainment area as discussed elsewhere in this preamble. States are required to adopt SIPs with enforceable emission limitations and other control measures, means, or techniques, as well as schedules and timetables for compliance, as may be necessary or appropriate to meet the applicable requirements of the FCAA. As discussed in the FISCAL NOTE portion of this preamble, the proposed rules are not anticipated to add any significant additional costs to affected individuals or businesses beyond what is necessary to attain the ozone NAAQS on the economy, a sector of the economy, productivity, competition, jobs, the environment, or the public health and safety of the state or a sector of the state.

If a state does not comply with its obligations under 42 USC, §7410, FCAA, §110 to submit SIPs, states are subject to discretionary sanctions under 42 USC, §7410(m) or mandatory sanctions under 42 USC, §7509, FCAA, §179; as well as the imposition of a federal implementation plan (FIP) under 42 USC, §7410, FCAA, §110(c). Under 42 USC, §7661a, FCAA, §502, states are required to have federal operating permit programs that provide authority to issue permits and assure compliance with each applicable standard, regulation, or requirement under the FCAA, including enforceable emission limitations and other control measures, means, or techniques, which are required under 42 USC, §7410, FCAA, §110. Similar to requirements in 42 USC, §7410, FCAA, §110, states are not free to ignore requirements in 42 USC, §7661a, FCAA, §502 and must develop and submit programs to provide for operating permits for major sources that include all applicable requirements of the FCAA. Lastly, states are also subject to the imposition of sanctions under 42 USC, §7661a(d) and (i), FCAA, §502(d) and (i) for failure to submit an operating permits program, the disapproval of any operating permits program, or failure to adequately administer and enforce the approved operating permits program.

The requirement to provide a fiscal analysis of regulations in the Texas Government Code was amended by Senate Bill (SB) 633 during the 75th legislative session in 1997. The intent of SB 633 was to require agencies to conduct a regulatory impact analysis of extraordinary rules. These are identified in the statutory language as major environmental rules that will have a material adverse impact and will exceed a requirement of state law, federal law, or a delegated federal program, or are adopted solely under the general powers of the agency. With the understanding that this requirement would seldom apply, the commission provided a cost estimate for SB 633 that concluded "based on an assessment of rules adopted by the agency in the past, it is not anticipated that the bill will have significant fiscal implications for the agency due to its limited application." The commission also noted that the number of rules that would require assessment under the provisions of the bill was not large. This conclusion was based, in part, on the criteria set forth in the bill that exempted rules from the full analysis unless the rule was a major environmental rule that exceeds a federal law. Because of the ongoing need to meet federal requirements, the commission routinely proposes and adopts rules incorporating or designed to satisfy specific federal requirements. The legislature is presumed to understand this federal scheme. If each rule proposed by the commission to meet a federal requirement was considered to be a major environmental rule that exceeds federal law, then each of those rules would require the full regulatory impact analysis (RIA) contemplated by SB 633. Requiring a full RIA for all federally required rules is inconsistent with the conclusions reached by the commission in its cost estimate and by the Legislative Budget Board (LBB) in its fiscal notes. Since the legislature is presumed to understand the fiscal impacts of the bills it passes, and that presumption is based on information provided by state agencies and the LBB, the that the intent of SB 633 was only to require the full RIA for rules that are extraordinary in nature. While the proposed rules may have a broad impact, that impact is no greater than is necessary or appropriate to meet the requirements of the FCAA, and in fact creates no additional impacts since the proposed rules do not impose burdens greater than required to demonstrate attainment of the ozone NAAQS as discussed elsewhere in this preamble. For these reasons, the proposed rules fall under the exception in Texas Government Code, §2001.0225(a), because they are required by, and do not exceed, federal law.

The commission has consistently applied this construction to its rules since this statute was enacted in 1997. Since that time, the legislature has revised the Texas Government Code, but left this provision substantially unamended. It is presumed that "when an agency interpretation is in effect at the time the legislature amends the laws without making substantial change in the statute, the legislature is deemed to have accepted the agency's interpretation." (Central Power & Light Co. v. Sharp, 919 S.W.2d 485, 489 (Tex. App. Austin 1995), writ denied with per curiam opinion respecting another issue, 960 S.W.2d 617 (Tex. 1997); Bullock v. Marathon Oil Co., 798 S.W.2d 353, 357 (Tex. App. Austin 1990, no writ). Cf. Humble Oil & Refining Co. v. Calvert, 414 S.W.2d 172 (Tex. 1967); Dudney v. State Farm Mut. Auto Ins. Co., 9 S.W.3d 884, 893 (Tex. App. Austin 2000); Southwestern Life Ins. Co. v. Montemayor, 24 S.W.3d 581 (Tex. App. Austin 2000, pet. denied); and Coastal Indust. Water Auth. v. Trinity Portland Cement Div., 563 S.W.2d 916 (Tex. 1978).) The commission's interpretation of the RIA requirements is also supported by a change made to the Texas Administrative Procedure Act (APA) by the legislature in 1999. In an attempt to limit the number of rule challenges based upon APA requirements, the legislature clarified that state agencies are required to meet these sections of the APA against the standard of "substantial compliance" (Texas Government Code, §2001.035). The legislature specifically identified Texas Government Code, §2001.0225 as falling under this standard.

As discussed in this analysis and elsewhere in this preamble, the commission has substantially complied with the requirements of Texas Government Code, §2001.0225. The proposed rulemaking implements the requirements of the FCAA as discussed in this analysis and elsewhere in this preamble. The proposed rules were determined to be necessary to attain the ozone NAAQS and are required to be included in permits under 42 USC, §7661a, FCAA, §502 and will not exceed any standard set by state or federal law. These proposed rules are not an express requirement of state law. The proposed rules do not exceed a requirement of a delegation agreement or a contract between state and federal government, as the proposed rules, if adopted by the commission and approved by EPA, will become federal law as part of the approved SIP required by 42 U.S.C. §7410, FCAA, §110. The proposed rules were not developed solely under the general powers of the agency but are authorized by specific sections of Texas Health and Safety Code, Chapter 382 (also known as the Texas Clean Air Act), and the Texas Water Code, which are cited in the Statutory Authority section of this preamble, including Texas Health and Safety Code, §§382.011, 382.012, and 382.017. Therefore, this proposed rulemaking action is not subject to the regulatory analysis provisions of Texas Government Code, §2001.0225(b).

The commission invites public comment regarding the Draft RIA Determination during the public comment period. Written comments on the Draft RIA Determination may be submitted to the contact person at the address listed under the Submittal of Comments section of this preamble.

Takings Impact Assessment

Under Texas Government Code, §2007.002(5), taking means a governmental action that affects private real property, in whole or in part or temporarily or permanently, in a manner that requires the governmental entity to compensate the private real property owner as provided by the Fifth and Fourteenth Amendments to the United States Constitution or §17 or §19, Article I, Texas Constitution; or a governmental action that affects an owner's private real property that is the subject of the governmental action, in whole or in part or temporarily or permanently, in a manner that restricts or limits the owner's right to the property that would otherwise exist in the absence of the governmental action; and is the producing cause of a reduction of at least 25% in the market value of the affected private real property, determined by comparing the market value of the property as if the governmental action is not in effect and the market value of the property determined as if the governmental action is in effect. The commission completed a takings impact analysis for the proposed rulemaking action under the Texas Government Code, §2007.043.

The primary purpose of this proposed rulemaking action, as discussed elsewhere in this preamble, is to meet federal requirements for the implementation of control strategies necessary to attain and maintain the NAAQS for ozone mandated by 42 United States Code (USC), 7410, FCAA, §110, and required to be included in operating permits by 42 USC, §7661a, FCAA, §502. The proposed rulemaking addresses VOC RACT and RFP requirements for the Bexar County 2015 eight-hour ozone nonattainment area as discussed elsewhere in this preamble.

States are required to adopt SIPs with enforceable emission limitations and other control measures, means, or techniques, as well as schedules and timetables for compliance, as may be necessary or appropriate to meet the applicable requirements of the FCAA. If a state does not comply with its obligations under 42 USC, §7410, FCAA, §110 to submit SIPs, states are subject to discretionary sanctions under 42 USC, §7410(m) or mandatory sanctions under 42 USC, §7509, FCAA, §179; as well as the imposition of a FIP under 42 USC, §7410, FCAA, §110(c). Under 42 USC, §7661a, FCAA, §502, states are required to have federal operating permit programs that provide authority to issue permits and assure compliance with each applicable standard, regulation, or requirement under the FCAA, including enforceable emission limitations and other control measures, means, or techniques, which are required under 42 USC, §7410, FCAA, §110. Similar to requirements in 42 USC, §7410, FCAA, §110, regarding the requirement to adopt and implement plans to attain and maintain the national ambient air quality standards, states are not free to ignore requirements in 42 USC, §7661a, FCAA, §502 and must develop and submit programs to provide for operating permits for major sources that include all applicable requirements of the FCAA. Lastly, states are also subject to the imposition of sanctions under 42 USC, §7661a(d) and (i), FCAA, §502(d) and (i) for failure to submit an operating permits program, the disapproval of any operating permits program, or failure to adequately administer and enforce the approved operating permits program.

The proposed rules will not create any additional burden on private real property beyond what is required under federal law, as the proposed rules, if adopted by the commission and approved by EPA, will become federal law as part of the approved SIP required by 42 U.S.C. §7410, FCAA, §110. The proposed rules will not affect private real property in a manner that would require compensation to private real property owners under the United States Constitution or the Texas Constitution. The proposal also will not affect private real property in a manner that restricts or limits an owner's right to the property that would otherwise exist in the absence of the governmental action. Therefore, the proposed rulemaking will not cause a taking under Texas Government Code, Chapter 2007.

Consistency with the Coastal Management Program

The commission reviewed the proposed rulemaking and found the proposal is a rulemaking identified in the Coastal Coordination Act Implementation Rules, 31 TAC §29.11(b)(2), relating to rules subject to the Coastal Management Program, and will, therefore, require that goals and policies of the Texas Coastal Management Program (CMP) be considered during the rulemaking process.

The commission reviewed this rulemaking for consistency with the CMP goals and policies in accordance with the regulations of the Coastal Coordination Advisory Committee and determined that the rulemaking will not affect any coastal natural resource areas because the rules only affect counties outside the CMP area and is, therefore, consistent with CMP goals and policies.

Written comments on the consistency of this rulemaking may be submitted to the contact person at the address listed under the Submittal of Comments section of this preamble.

Effect on Sites Subject to the Federal Operating Permits Program

Chapter 115 is an applicable requirement under 30 TAC Chapter 122, Federal Operating Permits Program. Once adopted, owners or operators of affected sites subject to the federal operating permit program must, consistent with the revision process in Chapter 122, upon the effective date of the rulemaking, revise their operating permit to include the new Chapter 115 requirements.

Announcement of Hearing

The commission will offer a public hearing on this proposal in San Antonio on August 19, 2025, at 7:00 p.m. Central Daylight Time at the Alamo Area Council of Governments (AACOG) at 2700 NE Loop 410, Suite 101. The hearing is structured for the receipt of oral or written comments by interested persons. Individuals may present oral statements when called upon in order of registration. Open discussion will not be permitted during the hearing; however, commission staff members will be available to discuss the proposal 30 minutes prior to the hearing.

Persons who have special communication or other accommodation needs who are planning to attend the hearing should contact Sandy Wong, Office of Legal Services at (512) 239-1802 or 1-800-RELAY-TX (TDD). Requests should be made as far in advance as possible.

Submittal of Comments

Written comments may be submitted to Gwen Ricco, MC 205, Office of Legal Services, Texas Commission on Environmental Quality, P.O. Box 13087, Austin, Texas 78711-3087, or faxed to fax4808@tceq.texas.gov. Electronic comments may be submitted at: https://tceq.commentinput.com/comment/search. File size restrictions may apply to comments being submitted via the TCEQ Public Comments system. All comments should reference Rule Project Number 2025-006-115-AI. The comment period closes on August 25, 2025. Please choose one of the methods provided to submit your written comments.

Copies of the proposed rulemaking can be obtained from the commission's website at https://www.tceq.texas.gov/rules/propose_adopt.html . For further information, please contact Julia Segura, Air Quality Planning Section, and julia.segura@tceq.texas.gov.

SUBCHAPTER B. GENERAL VOLATILE ORGANIC COMPOUND SOURCES

DIVISION 1. STORAGE OF VOLATILE ORGANIC COMPOUNDS

30 TAC §§115.111, 115.112, 115.119

Statutory Authority

The amendments are proposed under Texas Water Code (TWC), §5.102, concerning general powers; §5.103, concerning Rules; TWC, §5.105, concerning General Policy, which authorize the commission to adopt rules necessary to carry out its powers and duties under the TWC; TWC, §7.002, concerning Enforcement Authority, which authorizes the commission to enforce the provisions of the Water Code and the Health and Safety Code within the commission's jurisdiction; and under Texas Health and Safety Code (THSC), §382.017, concerning Rules, which authorizes the commission to adopt rules consistent with the policy and purpose of the Texas Clean Air Act.

The amendments are also proposed under THSC, §382.002, concerning Policy and Purpose, which establishes the commission's purpose to safeguard the state's air resources, consistent with the protection of public health, general welfare, and physical property; THSC, §382.011, concerning General Powers and Duties, which authorizes the commission to control the quality of the state's air; THSC, §382.012, concerning the State Air Control Plan, which authorizes the commission to prepare and develop a general, comprehensive plan for the proper control of the state's air; THSC, §382.016, concerning Monitoring Requirements; Examination of Records, which authorizes the commission to prescribe reasonable requirements for measuring and monitoring the emissions of air contaminants; and THSC, §382.021, concerning Sampling Methods and Procedures.

The proposed amendments implement TWC, §§5.102, 5.103, and 7.002; and THSC, §§382.002, 382.011, 382.012, 382.016, 382.017, and 382.021.

§115.111. Exemptions.

(a) The following exemptions apply in the Beaumont-Port Arthur, Bexar County, Dallas-Fort Worth, El Paso, and Houston-Galveston-Brazoria areas as defined in §115.10 of this title (relating to Definitions), except as noted in paragraphs (2), (4), (6), (7), and (9) - (11) of this subsection.

(1) Except as provided in §115.118 of this title (relating to Recordkeeping Requirements), a storage tank storing volatile organic compounds (VOC) with a true vapor pressure less than 1.5 pounds per square inch absolute (psia) is exempt from the requirements of this division.

(2) A storage tank with storage capacity less than 210,000 gallons storing crude oil or condensate prior to custody transfer in the Beaumont-Port Arthur, Bexar County, or El Paso areas, is exempt from the requirements of this division. This exemption no longer applies in the Dallas-Fort Worth area beginning March 1, 2013.

(3) A storage tank with a storage capacity less than 25,000 gallons located at a motor vehicle fuel dispensing facility is exempt from the requirements of this division.

(4) A welded storage tank in the Beaumont-Port Arthur, Bexar County, El Paso, and Houston-Galveston-Brazoria areas with a mechanical shoe primary seal that has a secondary seal from the top of the shoe seal to the tank wall (a shoe-mounted secondary seal) is exempt from the requirement for retrofitting with a rim-mounted secondary seal if the shoe-mounted secondary seal was installed or scheduled for installation before August 22, 1980.

(5) An external floating roof storage tank storing waxy, high pour point crude oils is exempt from any secondary seal requirements of §115.112(a), (d), and (e) of this title (relating to Control Requirements).

(6) A welded storage tank in the Beaumont-Port Arthur, Bexar County, El Paso, and Houston-Galveston-Brazoria areas storing VOC with a true vapor pressure less than 4.0 psia is exempt from any external floating roof secondary seal requirement if any of the following types of primary seals were installed before August 22, 1980:

(A) a mechanical shoe seal;

(B) a liquid-mounted foam seal; or

(C) a liquid-mounted liquid filled type seal.

(7) A welded storage tank in the Beaumont-Port Arthur, Bexar County, El Paso, and Houston-Galveston-Brazoria areas storing crude oil with a true vapor pressure equal to or greater than 4.0 psia and less than 6.0 psia is exempt from any external floating roof secondary seal requirement if any of the following types of primary seals were installed before December 10, 1982:

(A) a mechanical shoe seal;

(B) a liquid-mounted foam seal; or

(C) a liquid-mounted liquid filled type seal.

(8) A storage tank with storage capacity less than or equal to 1,000 gallons is exempt from the requirements of this division.

(9) In the Houston-Galveston-Brazoria area, a storage tank or tank battery storing condensate, as defined in §101.1 of this title (relating to Definitions), prior to custody transfer with a condensate throughput exceeding 1,500 barrels (63,000 gallons) per year on a rolling 12-month basis is exempt from the requirement in §115.112(d)(4) or (e)(4)(A) of this title, to control flashed gases if the owner or operator demonstrates, using the test methods specified in §115.117 of this title (relating to Approved Test Methods), that uncontrolled VOC emissions from the individual storage tank, or from the aggregate of storage tanks in a tank battery, are less than 25 tons per year on a rolling 12-month basis.

(10) In the Dallas-Fort Worth area, except Wise County, a storage tank or tank battery storing condensate prior to custody transfer with a condensate throughput exceeding 3,000 barrels (126,000 gallons) per year on a rolling 12-month basis is exempt from the requirement in §115.112(e)(4)(B) of this title, to control flashed gases if the owner or operator demonstrates, using the test methods specified in §115.117 of this title, that uncontrolled VOC emissions from the individual storage tank, or from the aggregate of storage tanks in a tank battery, are less than 50 tons per year on a rolling 12-month basis. This exemption no longer applies on November 7, 2025.

(11) In the Dallas-Fort Worth area, except in Wise County, on or after November 7, 2025, a storage tank or tank battery storing condensate prior to custody transfer with a condensate throughput exceeding 1,500 barrels (63,000 gallons) per year on a rolling 12-month basis is exempt from the requirement in §115.112(e)(4)(B) of this title, to control flashed gases if the owner or operator demonstrates, using the test methods specified in §115.117 of this title, that uncontrolled VOC emissions from the individual storage tank, or from the aggregate of storage tanks in a tank battery, are less than 25 tons per year on a rolling 12-month basis.

(12) In Wise County, prior to July 20, 2021, a storage tank or tank battery storing condensate prior to custody transfer with a condensate throughput exceeding 6,000 barrels (252,000 gallons) per year on a rolling 12-month basis is exempt from the requirement in §115.112(e)(4)(C)(i) of this title, to control flashed gases if the owner or operator demonstrates, using the test methods specified in §115.117 of this title, that uncontrolled VOC emissions from the individual storage tank, or from the aggregate of storage tanks in a tank battery, are less than 100 tons per year on a rolling 12-month basis.

(13) In Wise County until November 7, 2025, [,] a storage tank or tank battery storing condensate prior to custody transfer with a condensate throughput exceeding 3,000 barrels (126,000 gallons) per year on a rolling 12-month basis is exempt from the requirement in §115.112(e)(4)(C)(ii) of this title, to control flashed gases if the owner or operator demonstrates, using the test methods specified in §115.117 of this title, that uncontrolled VOC emissions from the individual storage tank, or from the aggregate of storage tanks in a tank battery, are less than 50 tons per year on a rolling 12-month basis.

(14) In Wise County beginning November 7, 2025, a storage tank or tank battery storing condensate prior to custody transfer with a condensate throughput exceeding 1,500 barrels (63,000 gallons) per year on a rolling 12-month basis is exempt from the requirement in §115.112(e)(4)(D) of this title, to control flashed gases if the owner or operator demonstrates, using the test methods specified in §115.117 of this title, that uncontrolled VOC emissions from the individual storage tank, or from the aggregate of storage tanks in a tank battery, are less than 25 tons per year on a rolling 12-month basis.

(15) In the Bexar County area beginning January 1, 2025, a storage tank or tank battery storing condensate prior to custody transfer with a condensate throughput exceeding 6,000 barrels (252,000 gallons) per year on a rolling 12-month basis is exempt from the requirement in §115.112(e)(4)(E) of this title, to control flashed gases if the owner or operator demonstrates, using the test methods specified in §115.117 of this title, that uncontrolled VOC emissions from the individual storage tank, or from the aggregate of storage tanks in a tank battery, are less than 100 tons per year on a rolling 12-month basis [of this title, to control flashed gases if the owner or operator demonstrates, using the test methods specified in §115.117 of this title, that uncontrolled VOC emissions from the individual storage tank, or from the aggregate of storage tanks in a tank battery, are less than 100 tons per year on a rolling 12-month basis].

(16) In the Bexar County, Dallas-Fort Worth, and Houston-Galveston-Brazoria areas, beginning when compliance is achieved with Division 7 of this subchapter (relating to Oil and Natural Gas Service in Ozone Nonattainment Areas) but no later than its initial §115.183 compliance deadline, a storage tank storing crude oil or condensate that is subject to the compliance requirements of Division 7 of this subchapter is exempt from all requirements in this division.

(17) In the Bexar County area beginning March 1, 2026, a storage tank or tank battery storing condensate prior to custody transfer with a condensate throughput exceeding 3,000 barrels (126,000 gallons) per year on a rolling 12-month basis is exempt from the requirement in §115.112(e)(4)(E) of this title, to control flashed gases, if the owner or operator demonstrates, using the test methods specified in §115.117 of this title, that uncontrolled VOC emissions from the individual storage tank, or from the aggregate of storage tanks in a tank battery, are less than 50 tons per year on a rolling 12-month basis.

(b) The following exemptions apply in Gregg, Nueces, and Victoria Counties.

(1) Except as provided in §115.118 of this title, a storage tank storing VOC with a true vapor pressure less than 1.5 psia is exempt from the requirements of this division.

(2) A storage tank with storage capacity less than 210,000 gallons storing crude oil or condensate prior to custody transfer is exempt from the requirements of this division.

(3) A storage tank with storage capacity less than 25,000 gallons located at a motor vehicle fuel dispensing facility is exempt from the requirements of this division.

(4) A welded storage tank with a mechanical shoe primary seal that has a secondary seal from the top of the shoe seal to the tank wall (a shoe-mounted secondary seal) is exempt from the requirement for retrofitting with a rim-mounted secondary seal if the shoe-mounted secondary seal was installed or scheduled for installation before August 22, 1980.

(5) An external floating roof storage tank storing waxy, high pour point crude oils is exempt from any secondary seal requirements of §115.112(b) of this title.

(6) A welded storage tank storing VOC with a true vapor pressure less than 4.0 psia is exempt from any external secondary seal requirement if any of the following types of primary seals were installed before August 22, 1980:

(A) a mechanical shoe seal;

(B) a liquid-mounted foam seal; or

(C) a liquid-mounted liquid filled type seal.

(7) A welded storage tank storing crude oil with a true vapor pressure equal to or greater than 4.0 psia and less than 6.0 psia is exempt from any external secondary seal requirement if any of the following types of primary seals were installed before December 10, 1982:

(A) a mechanical shoe seal;

(B) a liquid-mounted foam seal; or

(C) a liquid-mounted liquid filled type seal.

(8) A storage tank with storage capacity less than or equal to 1,000 gallons is exempt from the requirements of this division.

(c) The following exemptions apply in Aransas, Bexar, Calhoun, Matagorda, San Patricio, and Travis Counties. The exemptions in this subsection no longer apply in Bexar County beginning January 1, 2025.

(1) A storage tank storing VOC with a true vapor pressure less than 1.5 psia is exempt from the requirements of this division.

(2) Slotted guidepoles installed in a floating roof storage tank are exempt from the provisions of §115.112(c) of this title.

(3) A storage tank with storage capacity between 1,000 gallons and 25,000 gallons is exempt from the requirements of §115.112(c)(1) of this title if construction began before May 12, 1973.

(4) A storage tank with storage capacity less than or equal to 420,000 gallons is exempt from the requirements of §115.112(c)(3) of this title.

(5) A storage tank with storage capacity less than or equal to 1,000 gallons is exempt from the requirements of this division.

§115.112. Control Requirements.

(a) The following requirements apply in the Beaumont-Port Arthur, Dallas-Fort Worth, and El Paso areas, as defined in §115.10 of this title (relating to Definitions). The control requirements in this subsection no longer apply in the Dallas-Fort Worth area beginning March 1, 2013.

(1) No person shall place, store, or hold in any storage tank any volatile organic compounds (VOC) unless the storage tank is capable of maintaining working pressure sufficient at all times to prevent any vapor or gas loss to the atmosphere or is in compliance with the control requirements specified in Table I(a) of this paragraph for VOC other than crude oil and condensate or Table II(a) of this paragraph for crude oil and condensate.

Figure: 30 TAC §115.112(a)(1) (No change.)

(2) For an external floating roof or internal floating roof storage tank subject to the provisions of paragraph (1) of this subsection, the following requirements apply.

(A) All openings in an internal floating roof or external floating roof except for automatic bleeder vents (vacuum breaker vents) and rim space vents must provide a projection below the liquid surface or be equipped with a cover, seal, or lid. Any cover, seal, or lid must be in a closed (i.e., no visible gap) position at all times except when the device is in actual use.

(B) Automatic bleeder vents (vacuum breaker vents) must be closed at all times except when the roof is being floated off or landed on the roof leg supports.

(C) Rim vents, if provided, must be set to open only when the roof is being floated off the roof leg supports or at the manufacturer's recommended setting.

(D) Any roof drain that empties into the stored liquid must be equipped with a slotted membrane fabric cover that covers at least 90% of the area of the opening.

(E) There must be no visible holes, tears, or other openings in any seal or seal fabric.

(F) For an external floating roof storage tank, secondary seals must be the rim-mounted type (the seal must be continuous from the floating roof to the tank wall). The accumulated area of gaps that exceed 1/8 inch in width between the secondary seal and storage tank wall may not be greater than 1.0 square inch per foot of tank diameter.

(3) Vapor control systems, as defined in §115.10 of this title, used as a control device on any storage tank must maintain a minimum control efficiency of 90%. If a flare is used, it must be designed and operated in accordance with 40 Code of Federal Regulations §60.18(b) - (f) (as amended through December 22, 2008 (73 FR 78209)) and be lit at all times when VOC vapors are routed to the flare.

(b) The following requirements apply in Gregg, Nueces, and Victoria Counties.

(1) No person shall place, store, or hold in any storage tank any VOC, unless the storage tank is capable of maintaining working pressure sufficient at all times to prevent any vapor or gas loss to the atmosphere or is in compliance with the control requirements specified in Table I(a) in subsection (a)(1) of this section for VOC other than crude oil and condensate or Table II(a) in subsection (a)(1) of this section for crude oil and condensate. If a flare is used as a vapor recovery system, as defined in §115.10 of this title, it must be designed and operated in accordance with 40 Code of Federal Regulations §60.18(b) - (f) (as amended through December 22, 2008 (73 FR 78209)) and be lit at all times when VOC vapors are routed to the flare.

(2) For an external floating roof or internal floating roof storage tank subject to the provisions of paragraph (1) of this subsection, the following requirements apply.

(A) All openings in an internal floating roof or external floating roof, except for automatic bleeder vents (vacuum breaker vents) and rim space vents, must provide a projection below the liquid surface or be equipped with a cover, seal, or lid. Any cover, seal, or lid must be in a closed (i.e., no visible gap) position at all times, except when the device is in actual use.

(B) Automatic bleeder vents (vacuum breaker vents) must be closed at all times except when the roof is being floated off or landed on the roof leg supports.

(C) Rim vents, if provided, must be set to open only when the roof is being floated off the roof leg supports or at the manufacturer's recommended setting.

(D) Any roof drain that empties into the stored liquid must be equipped with a slotted membrane fabric cover that covers at least 90% of the area of the opening.

(E) There must be no visible holes, tears, or other openings in any seal or seal fabric.

(F) For an external floating roof storage tank, secondary seals must be the rim-mounted type (the seal shall be continuous from the floating roof to the tank wall). The accumulated area of gaps that exceed 1/8 inch in width between the secondary seal and tank wall may not be greater than 1.0 square inch per foot of tank diameter.

(c) The following requirements apply in Aransas, Bexar, Calhoun, Matagorda, San Patricio, and Travis Counties. The control requirements of this subsection no longer apply for sources located in Bexar County beginning January 1, 2025.

(1) No person may place, store, or hold in any storage tank any VOC, other than crude oil or condensate, unless the storage tank is capable of maintaining working pressure sufficient at all times to prevent any vapor or gas loss to the atmosphere or is in compliance with the control requirements specified in Table I(b) of this paragraph for VOC other than crude oil and condensate.

Figure: 30 TAC §115.112(c)(1) (No change.)

(2) For an external floating roof or internal floating roof storage tank subject to the provisions of paragraph (1) of this subsection, the following requirements apply.

(A) There must be no visible holes, tears, or other openings in any seal or seal fabric.

(B) All tank gauging and sampling devices must be vapor-tight except when gauging and sampling is taking place.

(3) No person in Matagorda or San Patricio Counties shall place, store, or hold crude oil or condensate in any storage tank unless the storage tank is a pressure tank capable of maintaining working pressures sufficient at all times to prevent vapor or gas loss to the atmosphere or is equipped with one of the following control devices, properly maintained and operated:

(A) an internal floating roof or external floating roof, as defined in §115.10 of this title. These control devices will not be allowed if the VOC has a true vapor pressure of 11.0 pounds per square inch absolute (psia) or greater. All tank-gauging and tank-sampling devices must be vapor-tight, except when gauging or sampling is taking place; or

(B) a vapor control system as defined in §115.10 of this title.

(d) The following requirements apply in the Houston-Galveston-Brazoria area, as defined in §115.10 of this title. The requirements in this subsection no longer apply beginning March 1, 2013.

(1) No person shall place, store, or hold in any storage tank any VOC unless the storage tank is capable of maintaining working pressure sufficient at all times to prevent any vapor or gas loss to the atmosphere or is in compliance with the control requirements specified in either Table I(a) of subsection (a)(1) of this section for VOC other than crude oil and condensate or Table II(a) of subsection (a)(1) of this section for crude oil and condensate.

(2) For an external floating roof or internal floating roof storage tank subject to the provisions of paragraph (1) of this subsection, the following requirements apply.

(A) All openings in an internal floating roof or external floating roof as defined in §115.10 of this title except for automatic bleeder vents (vacuum breaker vents), and rim space vents must provide a projection below the liquid surface. All openings in an internal floating roof or external floating roof except for automatic bleeder vents (vacuum breaker vents), rim space vents, leg sleeves, and roof drains must be equipped with a deck cover. The deck cover must be equipped with a gasket in good operating condition between the cover and the deck. The deck cover must be closed (i.e., no gap of more than 1/8 inch) at all times, except when the cover must be open for access.

(B) Automatic bleeder vents (vacuum breaker vents) and rim space vents must be equipped with a gasketed lid, pallet, flapper, or other closure device and must be closed (i.e., no gap of more than 1/8 inch) at all times except when required to be open to relieve excess pressure or vacuum in accordance with the manufacturer's design.

(C) Each opening into the internal floating roof for a fixed roof support column may be equipped with a flexible fabric sleeve seal instead of a deck cover.

(D) Any external floating roof drain that empties into the stored liquid must be equipped with a slotted membrane fabric cover that covers at least 90% of the area of the opening or an equivalent control that must be kept in a closed (i.e., no gap of more than 1/8 inch) position at all times except when the drain is in actual use. Stub drains on an internal floating roof storage tank are not subject to this requirement.

(E) There must be no visible holes, tears, or other openings in any seal or seal fabric.

(F) For an external floating roof storage tank, secondary seals must be the rim-mounted type (the seal must be continuous from the floating roof to the tank wall with the exception of gaps that do not exceed the following specification). The accumulated area of gaps that exceed 1/8 inch in width between the secondary seal and storage tank wall may not be greater than 1.0 square inch per foot of storage tank diameter.

(G) Each opening for a slotted guidepole in an external floating roof storage tank must be equipped with one of the following control device configurations:

(i) a pole wiper and pole float that has a seal or wiper at or above the height of the pole wiper;

(ii) a pole wiper and a pole sleeve;

(iii) an internal sleeve emission control system;

(iv) a retrofit to a solid guidepole system;

(v) a flexible enclosure system; or

(vi) a cover on an external floating roof tank.

(H) The external floating roof or internal floating roof must be floating on the liquid surface at all times except as specified in this subparagraph. The external floating roof or internal floating roof may be supported by the leg supports or other support devices, such as hangers from the fixed roof, during the initial fill or refill after the storage tank has been cleaned or as allowed under the following circumstances:

(i) when necessary for maintenance or inspection;

(ii) when necessary for supporting a change in service to an incompatible liquid;

(iii) when the storage tank has a storage capacity less than 25,000 gallons or the vapor pressure of the material stored is less than 1.5 psia;

(iv) when the vapors are routed to a control device from the time the floating roof is landed until the floating roof is within ten percent by volume of being refloated;

(v) when all VOC emissions from the tank, including emissions from roof landings, have been included in a floating roof storage tank emissions limit or cap approved under Chapter 116 of this title (relating to Control of Air Pollution by Permits for New Construction or Modification); or

(vi) when all VOC emissions from floating roof landings at the regulated entity, as defined in §101.1 of this title (relating to Definitions), are less than 25 tons per year.

(3) Vapor control systems, as defined in §115.10 of this title, used as a control device on any storage tank must maintain a minimum control efficiency of 90%.

(4) For a storage tank storing condensate, as defined in §101.1 of this title, prior to custody transfer, flashed gases must be routed to a vapor control system if the liquid throughput through an individual tank or the aggregate of tanks in a tank battery exceeds 1,500 barrels (63,000 gallons) per year.

(5) For a storage tank storing crude oil or condensate prior to custody transfer or at a pipeline breakout station, flashed gases must be routed to a vapor control system if the uncontrolled VOC emissions from an individual storage tank, or from the aggregate of storage tanks in a tank battery, equal or exceed 25 tons per year on a rolling 12-month basis. Uncontrolled emissions must be estimated by one of the following methods; however, if emissions determined using direct measurements or other methods approved by the executive director under subparagraph (A) or (D) of this paragraph are higher than emissions estimated using the default factors or charts in subparagraph (B) or (C) of this paragraph, the higher values must be used.

(A) The owner or operator may make direct measurements using the measuring instruments and methods specified in §115.117 of this title (relating to Approved Test Methods).

(B) The owner or operator may use a factor of 33.3 pounds of VOC per barrel (42 gallons) of condensate produced or 1.6 pounds of VOC per barrel (42 gallons) of oil produced.

(C) For crude oil storage only, the owner or operator may use the chart in Exhibit 2 of the United States Environmental Protection Agency publication Lessons Learned from Natural Gas Star Partners: Installing Vapor Recovery Units on Crude Oil Storage Tanks, October 2003, and assuming that the hydrocarbon vapors have a molecular weight of 34 pounds per pound mole and are 48% by weight VOC.

(D) Other test methods or computer simulations may be allowed if approved by the executive director.

(e) The control requirements in this subsection apply in the Bexar County, Houston-Galveston-Brazoria, and Dallas-Fort Worth areas, except as specified in §115.119 of this title (relating to Compliance Schedules) and in paragraph (3) of this subsection. Beginning on the applicable compliance date specified in §115.183 of this title (relating to Compliance Schedules), the requirements in this subsection no longer apply to storage tanks storing crude oil or condensate that are subject to Division 7 of this subchapter (relating to Oil and Natural Gas Service in Ozone Nonattainment Areas).

(1) No person shall place, store, or hold VOC in any storage tank unless the storage tank is capable of maintaining working pressure sufficient at all times to prevent any vapor or gas loss to the atmosphere or is in compliance with the control requirements specified in Table 1 of this paragraph for VOC other than crude oil and condensate or Table 2 of this paragraph for crude oil and condensate.

Figure: 30 TAC §115.112(e)(1) (No change.)

(2) For an external floating roof or internal floating roof storage tank subject to the provisions of paragraph (1) of this subsection, the following requirements apply.

(A) All openings in an internal floating roof or external floating roof must provide a projection below the liquid surface. Automatic bleeder vents (vacuum breaker vents) and rim space vents are not subject to this requirement.

(B) All openings in an internal floating roof or external floating roof must be equipped with a deck cover. The deck cover must be equipped with a gasket in good operating condition between the cover and the deck. The deck cover must be closed (i.e., no gap of more than 1/8 inch) at all times, except when the cover must be open for access. Automatic bleeder vents (vacuum breaker vents), rim space vents, leg sleeves, and roof drains are not subject to this requirement.

(C) Automatic bleeder vents (vacuum breaker vents) and rim space vents must be equipped with a gasketed lid, pallet, flapper, or other closure device and must be closed (i.e., no gap of more than 1/8 inch) at all times except when required to be open to relieve excess pressure or vacuum in accordance with the manufacturer's design.

(D) Each opening into the internal floating roof for a fixed roof support column may be equipped with a flexible fabric sleeve seal instead of a deck cover.

(E) Any external floating roof drain that empties into the stored liquid must be equipped with a slotted membrane fabric cover that covers at least 90% of the area of the opening or an equivalent control that must be kept in a closed (i.e., no gap of more than 1/8 inch) position at all times except when the drain is in actual use. Stub drains on an internal floating roof storage tank are not subject to this requirement.

(F) There must be no visible holes, tears, or other openings in any seal or seal fabric.

(G) For an external floating roof storage tank, secondary seals must be the rim-mounted type. The seal must be continuous from the floating roof to the tank wall with the exception of gaps that do not exceed the following specification. The accumulated area of gaps that exceed 1/8 inch in width between the secondary seal and storage tank wall may not be greater than 1.0 square inch per foot of storage tank diameter.

(H) Each opening for a slotted guidepole in an external floating roof storage tank must be equipped with one of the following control device configurations:

(i) a pole wiper and pole float that has a seal or wiper at or above the height of the pole wiper;

(ii) a pole wiper and a pole sleeve;

(iii) an internal sleeve emission control system;

(iv) a retrofit to a solid guidepole system;

(v) a flexible enclosure system; or

(vi) a cover on an external floating roof tank.

(I) The external floating roof or internal floating roof must be floating on the liquid surface at all times except as allowed under the following circumstances:

(i) during the initial fill or refill after the storage tank has been cleaned;

(ii) when necessary for preventive maintenance, roof repair, primary seal inspection, or removal and installation of a secondary seal, if product is not transferred into or out of the storage tank, emissions are minimized, and the repair is completed within seven calendar days;

(iii) when necessary for supporting a change in service to an incompatible liquid;

(iv) when the storage tank has a storage capacity less than 25,000 gallons;

(v) when the vapors are routed to a control device from the time the storage tank has been emptied to the extent practical or the drain pump loses suction until the floating roof is within 10% by volume of being refloated;

(vi) when all VOC emissions from the storage tank, including emissions from floating roof landings, have been included in an emissions limit or cap approved under Chapter 116 of this title prior to March 1, 2013; or

(vii) when all VOC emissions from floating roof landings at the regulated entity are less than 25 tons per year.

(3) A control device used to comply with this subsection must meet one of the following conditions at all times when VOC vapors are routed to the device.

(A) A control device, other than a vapor recovery unit or a flare, must maintain the following minimum control efficiency:

(i) 90% in the Houston-Galveston-Brazoria area until the date specified in clause (ii) of this subparagraph;

(ii) 95% in the Houston-Galveston-Brazoria area beginning July 20, 2018;

(iii) 95% in the Dallas-Fort Worth area; and

(iv) 95% in the Bexar County area.

(B) A vapor recovery unit must be designed to process all vapor generated by the maximum liquid throughput of the storage tank or the aggregate of storage tanks in a tank battery and must transfer recovered vapors to a pipe or container that is vapor-tight, as defined in §115.10 of this title.

(C) A flare must be designed and operated in accordance with 40 Code of Federal Regulations §60.18(b) - (f) (as amended through December 22, 2008 (73 FR 78209)) and be lit at all times when VOC vapors are routed to the flare.

(4) For a fixed roof storage tank storing condensate prior to custody transfer, flashed gases must be routed to a vapor control system if the condensate throughput of an individual tank or the aggregate of tanks in a tank battery exceeds;

(A) in the Houston-Galveston-Brazoria area, 1,500 barrels (63,000 gallons) per year on a rolling 12-month basis;

(B) in the Dallas-Fort Worth area, except Wise County, 3,000 barrels (126,000 gallons) per year on a rolling 12-month basis until November 7, 2025, upon which date, the requirements in subparagraph (D) of this paragraph apply;

(C) in Wise County:

(i) 6,000 barrels (252,000 gallons) per year on a rolling 12-month basis, until July 20, 2021; and

(ii) 3,000 barrels (126,000 gallons) per year on a rolling 12-month basis until November 7, 2025, upon which date, the requirements in subparagraph (D) of this paragraph apply;

(D) in the Dallas-Fort Worth area, 1,500 barrels (63,000 gallons) per year on a rolling 12-month basis beginning November 7, 2025, as specified in §115.119(f) of this title; and

(E) in the Bexar County area beginning January 1, 2025, through February 28, 2026, 6,000 barrels (252,000 gallons) per year on a rolling 12-month basis.

(F) in the Bexar County area beginning March 1, 2026, 3,000 barrels (126,000 gallons) per year on a rolling 12-month basis.

(5) For a fixed roof storage tank storing crude oil or condensate prior to custody transfer or at a pipeline breakout station, flashed gases must be routed to a vapor control system if the uncontrolled VOC emissions from an individual storage tank, or from the aggregate of storage tanks in a tank battery, or from the aggregate of storage tanks at a pipeline breakout station, equal or exceed:

(A) in the Houston-Galveston-Brazoria area, 25 tons per year on a rolling 12-month basis;

(B) in the Dallas-Fort Worth area, except Wise County: 50 tons per year on a rolling 12-month basis until November 7, 2025, upon which date, the requirements in subparagraph (D) of this paragraph apply;

(C) in Wise County:

(i) 100 tons per year on a rolling 12-month basis, until July 20, 2021;

(ii) 50 tons per year on a rolling 12-month basis beginning July 20, 2021, as specified in §115.119(f) of this title, until November 7, 2025, upon which date, the requirements in subparagraph (D) of this paragraph apply;

(D) in the Dallas-Fort Worth area, 25 tons per year on a rolling 12-month basis beginning November 7, 2025 as specified in §115.119(f) of this title; and

(E) in the Bexar County area 100 tons per year on a rolling 12-month basis prior to March 1, 2026, and 50 tons per year beginning March 1, 2026.

(6) Uncontrolled emissions from a fixed roof storage tank or fixed roof storage tank battery storing crude oil or condensate prior to custody transfer or at a pipeline breakout station must be estimated by one of the following methods. However, if emissions determined using direct measurements or other methods approved by the executive director under subparagraph (A) or (B) of this paragraph are higher than emissions estimated using the default factors or charts in subparagraph (C) or (D) of this paragraph, the higher values must be used.

(A) The owner or operator may make direct measurements using the measuring instruments and methods specified in §115.117 of this title.

(B) The owner or operator may use other test methods or computer simulations approved by the executive director.

(C) The owner or operator may use a factor of 33.3 pounds of VOC per barrel (42 gallons) of condensate produced or 1.6 pounds of VOC per barrel (42 gallons) of oil produced.

(D) For crude oil storage only, the owner or operator may use the chart in Exhibit 2 of the United States Environmental Protection Agency publication Lessons Learned from Natural Gas Star Partners: Installing Vapor Recovery Units on Crude Oil Storage Tanks, October 2003, and assuming that the hydrocarbon vapors have a molecular weight of 34 pounds per pound mole and are 48% by weight VOC.

(7) Fixed roof storage tanks in the Bexar County area, Dallas-Fort Worth area, and Houston-Galveston-Brazoria area storing crude oil or condensate prior to custody transfer or at a pipeline breakout station for which the owner or operator is required by this subsection to control flashed gases must be maintained in accordance with manufacturer instructions. All openings in the fixed roof storage tank through which vapors are not routed to a vapor recovery unit or other vapor control device must be equipped with a closure device maintained according to the manufacturer's instructions and operated according to this paragraph. If manufacturer instructions are unavailable, industry standards consistent with good engineering practice can be substituted.

(A) Each closure device must be closed at all times except when normally actuated or required to be open for temporary access or to relieve excess pressure or vacuum in accordance with the manufacturer's design and consistent with good air pollution control practices. Such opening, actuation, or use must be limited to minimize vapor loss.

(B) Each closure device must be properly sealed to minimize vapor loss when closed.

(C) Each closure device must either be latched closed or, if designed to relieve pressure, set to automatically open at a pressure that will ensure all vapors are routed to the vapor recovery unit or other vapor control device under normal operating conditions other than gauging the tank or taking a sample through an open thief hatch.

(D) No closure device may be allowed to have a VOC leak for more than 15 calendar days after the leak is found unless delay of repair is allowed. For the purposes of this subparagraph, a leak is the exuding of process gasses from a closed device based on sight, smell, or sound. If parts are unavailable, repair may be delayed. Parts must be ordered promptly and the repair must be completed within five days of receipt of required parts. Repair may be delayed until the next shutdown if the repair of the component would require a shutdown that would create more emissions than the repair would eliminate. Repair must be completed by the end of the next shutdown.

§115.119. Compliance Schedules.

(a) In Brazoria, Chambers, Fort Bend, Galveston, Harris, Liberty, Montgomery, and Waller Counties, the compliance date has passed and the owner or operator of each storage tank in which any volatile organic compounds (VOC) are placed, stored, or held shall continue to comply with this division except as follows.

(1) The affected owner or operator shall comply with the requirements of §§115.112(d); 115.115(a)(1), (2), (3)(A), and (4); 115.117; and 115.118(a) of this title (relating to Control Requirements; Monitoring Requirements; Approved Test Methods; and Recordkeeping Requirements, respectively) no later than January 1, 2009. Section 115.112(d) of this title no longer applies in the Houston-Galveston-Brazoria area beginning March 1, 2013. Prior to March 1, 2013, the owner or operator of a storage tank subject to §115.112(d) of this title shall continue to comply with §115.112(d) of this title until compliance has been demonstrated with the requirements of §115.112(e)(1) - (6) of this title. Section 115.112(e)(3)(A)(i) of this title no longer applies beginning July 20, 2018.

(A) If compliance with these requirements would require emptying and degassing of the storage tank, compliance is not required until the next time the storage tank is emptied and degassed but no later than January 1, 2017.

(B) The owner or operator of each storage tank with a storage capacity less than 210,000 gallons storing crude oil and condensate prior to custody transfer shall comply with the requirements of this division no later than January 1, 2009, regardless if compliance with these requirements would require emptying and degassing of the storage tank.

(2) The affected owner or operator shall comply with §§115.112(e)(1) - (6), 115.115(a)(3)(B), (5), and (6), and 115.116 of this title (relating to Testing Requirements) no later than March 1, 2013. Section 115.112(e)(3)(A)(i) of this title no longer applies beginning July 20, 2018. Prior to July 20, 2018, the owner or operator of a storage tank subject to §115.112(e)(3)(A)(i) of this title shall continue to comply with §115.112(e)(3)(A)(i) of this title until compliance has been demonstrated with the requirements of §115.112(e)(3)(A)(ii) of this title. After July 20, 2018, the owner or operator of a storage tank is subject to §115.112(e)(3)(A)(ii) of this title.

(A) If compliance with these requirements would require emptying and degassing of the storage tank, compliance is not required until the next time the storage tank is emptied and degassed but no later than January 1, 2017.

(B) The owner or operator of each storage tank with a storage capacity less than 210,000 gallons storing crude oil and condensate prior to custody transfer shall comply with these requirements no later than March 1, 2013, regardless if compliance with these requirements would require emptying and degassing of the storage tank.

(3) The affected owner or operator shall comply with §§115.112(e)(3)(A)(ii), 115.112(e)(7), 115.118(a)(6)(D) and (E), and 115.114(a)(5) of this title (relating to Inspection and Repair Requirements) as soon as practicable, but no later than July 20, 2018.

(b) In Collin, Dallas, Denton, Ellis, Johnson, Kaufman, Parker, Rockwall, and Tarrant Counties, the owner or operator of each storage tank in which any VOC is placed, stored, or held was required to be in compliance with this division on or before March 1, 2009, and shall continue to comply with this division, except as follows.

(1) The affected owner or operator shall comply with §§115.112(e), 115.115(a)(3)(B), (5), and (6), 115.116, and 115.118(a)(6) of this title as soon as practicable, but no later than March 1, 2013.

(A) If compliance with §115.112(e) of this title would require emptying and degassing of the storage tank, compliance is not required until the next time the storage tank is emptied and degassed but no later than December 1, 2021.

(B) The owner or operator of a storage tank with a storage capacity less than 210,000 gallons storing crude oil and condensate prior to custody transfer shall comply with these requirements no later than March 1, 2013, regardless if compliance with these requirements would require emptying and degassing of the storage tank.

(2) The affected owner or operator in Collin, Dallas, Denton, Ellis, Johnson, Kaufman, Parker, Rockwall, and Tarrant Counties shall comply with §§115.112(e)(7), 115.114(a)(5), and 115.118(a)(6)(D) and (E) of this title no later than January 1, 2017.

(c) In Hardin, Jefferson, and Orange Counties, the owner or operator of each storage tank in which any VOC is placed, stored, or held was required to be in compliance with this division by March 7, 1997, and shall continue to comply with this division, except that compliance with §115.115(a)(3)(B), (5), and (6), and §115.116 of this title is required no later than March 1, 2013.

(d) In El Paso County, the owner or operator of each storage tank in which any VOC is placed, stored, or held was required to be in compliance with this division by January 1, 1996, and shall continue to comply with this division, except that compliance with §115.115(a)(3)(B), (5), and (6), and §115.116 of this title is required no later than March 1, 2013.

(e) Except as specified in subsection (g) of this section, in Aransas, Bexar, Calhoun, Gregg, Matagorda, Nueces, San Patricio, Travis, and Victoria Counties, the owner or operator of each storage tank in which any VOC is placed, stored, or held was required to be in compliance with this division by July 31, 1993, and shall continue to comply with this division, except that compliance with §115.116(b) of this title is required as soon as practicable, but no later than March 1, 2013.

(f) In Wise County, the owner or operator of each storage tank in which any VOC is placed, stored, or held was required to be in compliance with this division by January 1, 2017, and shall continue to comply with this division, except that compliance with §115.112(e)(4)(D) and (5)(D) by no later than November 7, 2025.

(g) The owner or operator of each storage tank in the Bexar County area subject to the requirements of this division shall comply with the requirements of §115.112(c) and §115.114(c) of this title through December 31, 2024, and all other applicable requirements of this division no later than January 1, 2025. Beginning March 1, 2026, the owner or operator of each storage tank in the Bexar County area subject to the requirements of this division shall comply with the requirements of §115.112(e)(4)(F), §115.112(e)(5)(E), and all other applicable requirements of this division.

(h) The owner or operator of each storage tank in which any VOC is placed, stored, or held that becomes subject to this division on or after the date specified in subsections (a) - (f) of this section, shall comply with the requirements in this division no later than 60 days after becoming subject. In Brazoria, Chambers, Collin, Dallas, Denton, Ellis, Fort Bend, Galveston, Harris, Johnson, Kaufman, Liberty, Montgomery, Parker, Rockwall, Tarrant, Waller, and Wise Counties, the owner or operator of a storage tank storing crude oil or condensate shall continue to comply with the requirements in this division until compliance with the requirements in Division 7 of this subchapter (relating to Oil and Natural Gas Service in Ozone Nonattainment Areas) is achieved or until December 31, 2022, whichever is sooner.

The agency certifies that legal counsel has reviewed the proposal and found it to be within the state agency's legal authority to adopt.

Filed with the Office of the Secretary of State on July 11, 2025.

TRD-202502435

Charmaine Backens

Deputy Director, Environmental Law Division

Texas Commission on Environmental Quality

Earliest possible date of adoption: August 24, 2025

For further information, please call: (512) 239-2678


DIVISION 2. VENT GAS CONTROL

30 TAC §115.122, §115.129

Statutory Authority

The amendments are proposed under Texas Water Code (TWC), §5.102, concerning general powers; §5.103, concerning Rules; TWC, §5.105, concerning General Policy, which authorize the commission to adopt rules necessary to carry out its powers and duties under the TWC; TWC, §7.002, concerning Enforcement Authority, which authorizes the commission to enforce the provisions of the Water Code and the Health and Safety Code within the commission's jurisdiction; and under Texas Health and Safety Code (THSC), §382.017, concerning Rules, which authorizes the commission to adopt rules consistent with the policy and purpose of the Texas Clean Air Act.

The amendments are also proposed under THSC, §382.002, concerning Policy and Purpose, which establishes the commission's purpose to safeguard the state's air resources, consistent with the protection of public health, general welfare, and physical property; THSC, §382.011, concerning General Powers and Duties, which authorizes the commission to control the quality of the state's air; THSC, §382.012, concerning the State Air Control Plan, which authorizes the commission to prepare and develop a general, comprehensive plan for the proper control of the state's air; THSC, §382.016, concerning Monitoring Requirements; Examination of Records, which authorizes the commission to prescribe reasonable requirements for measuring and monitoring the emissions of air contaminants; and THSC, §382.021, concerning Sampling Methods and Procedures.

The proposed amendments implement TWC, §§5.102, 5.103, and 7.002; and THSC, §§382.002, 382.011, 382.012, 382.016, 382.017, and 382.021.

§115.122. Control Requirements.

(a) For all persons in the Beaumont-Port Arthur, Bexar County, Dallas-Fort Worth, El Paso, and Houston-Galveston-Brazoria areas, the following control requirements shall apply.

(1) Any vent gas streams affected by §115.121(a)(1) of this title (relating to Emission Specifications) must be controlled properly with a control efficiency of at least 90% or to a volatile organic compound (VOC) concentration of no more than 20 parts per million by volume (ppmv) (on a dry basis corrected to 3.0% oxygen for combustion devices):

(A) in a direct-flame incinerator at a temperature equal to or greater than 1,300 degrees Fahrenheit;

(B) in a smokeless flare that is lit at all times when VOC vapors are routed to the flare; or

(C) by any other vapor control system, as defined in §115.10 of this title (relating to Definitions). A glycol dehydrator reboiler burning the vent stream from the still vent is a vapor control system.

(2) Any vent gas streams affected by §115.121(a)(2) of this title must be controlled properly with a control efficiency of at least 98% or to a VOC concentration of no more than 20 ppmv (on a dry basis corrected to 3.0% oxygen for combustion devices):

(A) in a smokeless flare that is lit at all times when VOC vapors are routed to the flare; or

(B) by any other vapor control system, as defined in §115.10 of this title.

(3) For the Bexar County, Dallas-Fort Worth, El Paso, and Houston-Galveston-Brazoria areas, VOC emissions from each bakery with a bakery oven vent gas stream(s) affected by §115.121(a)(3) of this title shall be reduced as follows.

(A) Each bakery in the Houston-Galveston-Brazoria area with a total weight of VOC emitted from all bakery ovens on the property, when uncontrolled, equal to or greater than 25 tons per calendar year shall ensure that the overall emission reduction from the uncontrolled VOC emission rate of the oven(s) is at least 80%.

(B) Through November 6, 2025, each bakery in the Dallas-Fort Worth area, except in Wise County, with a total weight of VOC emitted from all bakery ovens on the property, when uncontrolled, equal to or greater than 50 tons per calendar year, shall ensure that the overall emission reduction from the uncontrolled VOC emission rate of the oven(s) is at least 80%. Beginning November 7, 2025, each bakery in the Dallas-Fort Worth area, including Wise County, with a total weight of VOC emitted from all bakery ovens on the property, when uncontrolled, equal to or greater than 25 tons per calendar year, shall ensure that the overall emission reduction from the uncontrolled VOC emission rate of the oven(s) is at least 80%.

(C) Each bakery in the Dallas-Fort Worth with a total weight of VOC emitted from all bakery ovens on the property, when uncontrolled, equal to or greater than 25 tons per calendar year, but less than 50 tons per calendar year, shall reduce total VOC emissions by at least 30% from the bakery's 1990 emissions inventory in accordance with the schedule specified in §115.129(d) of this title (relating to Counties and Compliance Schedules). The requirements of this subparagraph no longer apply beginning November 7, 2025.

(D) Each bakery in the El Paso area with a total weight of VOC emitted from all bakery ovens on the property, when uncontrolled, equal to or greater than 25 tons per calendar year shall reduce total VOC emissions by at least 30% from the bakery's 1990 emissions inventory in accordance with the schedule specified in §115.129(e) of this title.

(E) Each bakery in the Bexar County area with a total weight of VOC emitted from all bakery ovens on the property, when uncontrolled, equal to or greater than 100 tons per calendar year, shall ensure that the overall emission reduction from the uncontrolled VOC emission rate of the oven(s) is at least 80%. Beginning March 1, 2026, each bakery in the Bexar County area with a total weight of VOC emitted from all bakery ovens on the property, when uncontrolled, equal to or greater than 50 tons per calendar year, shall ensure that the overall emission reduction from the uncontrolled VOC emission rate of the oven(s) is at least 80%.

(F) Emission reductions in the 30% to 90% range are not creditable under Chapter 101, Subchapter H, Division 1 of this title (relating to Emission Credit Program) for the following bakeries:

(i) each bakery in the Houston-Galveston-Brazoria area with a total weight of VOC emitted from all bakery ovens on the property, when uncontrolled, equal to or greater than 25 tons per calendar year;

(ii) each bakery in the Dallas-Fort Worth area with a total weight of VOC emitted from all bakery ovens on the property, when uncontrolled, equal to or greater than 50 tons per calendar year through November 6, 2025, and 25 tons per calendar year beginning November 7, 2025;

(iii) each bakery in the El Paso area with a total weight of VOC emitted from all bakery ovens on the property, when uncontrolled, equal to or greater than 50 tons per calendar year; and

(iv) each bakery in the Bexar County area with a total weight of VOC emitted from all bakery ovens on the property, when uncontrolled, equal to or greater than 100 tons per calendar year through February 28, 2026, and 50 tons per calendar year beginning March 1, 2026.

(4) Any vent gas stream that becomes subject to the provisions of paragraphs (1), (2), or (3) of this subsection by exceeding provisions of §115.127(a) of this title (relating to Exemptions) shall remain subject to the provisions of this subsection, even if throughput or emissions later fall below the exemption limits unless and until emissions are reduced to no more than the controlled emissions level existing before implementation of the project by which throughput or emission rate was reduced to less than the applicable exemption limits in §115.127(a) of this title; and:

(A) the project by which throughput or emission rate was reduced is authorized by any permit or permit amendment or standard permit or permit by rule required by Chapter 116 or Chapter 106 of this title (relating to Control of Air Pollution by Permits for New Construction or Modification; and Permits by Rule). If a permit by rule is available for the project, compliance with this subsection must be maintained for 30 days after the filing of documentation of compliance with that permit by rule; or

(B) if authorization by permit, permit amendment, standard permit, or permit by rule is not required for the project, the owner or operator has given the executive director 30 days' notice of the project in writing.

(b) For all persons in Nueces and Victoria Counties, any vent gas streams affected by §115.121(b) of this title must be controlled properly with a control efficiency of at least 90% or to a VOC concentration of no more than 20 ppmv (on a dry basis corrected to 3.0% oxygen for combustion devices):

(1) in a direct-flame incinerator at a temperature equal to or greater than 1,300 degrees Fahrenheit;

(2) in a smokeless flare that is lit at all times when VOC vapors are routed to the flare; or

(3) by any other vapor control system, as defined in §115.10 of this title.

(c) For all persons in Aransas, Bexar, Calhoun, Matagorda, San Patricio, and Travis Counties, the following control requirements shall apply. The control requirements of the subsection no longer apply for sources located in Bexar County beginning January 1, 2025.

(1) Any vent gas streams affected by §115.121(c)(1) of this title must be controlled properly:

(A) in a direct-flame incinerator at a temperature equal to or greater than 1,300 degrees Fahrenheit;

(B) in a smokeless flare that is lit at all times when VOC vapors are routed to the flare; or

(C) by any other vapor control system, as defined in §115.10 of this title, with a control efficiency of at least 90% or to a VOC concentration of no more than 20 ppmv (on a dry basis corrected to 3.0% oxygen for combustion devices).

(2) Any vent gas streams affected by §115.121(c)(2) of this title must be controlled properly:

(A) in a direct-flame incinerator or boiler at a temperature equal to or greater than 1,300 degrees Fahrenheit; or

(B) by any other vapor control system, as defined in §115.10 of this title, with a control efficiency of at least 90% or to a VOC concentration of no more than 20 ppmv (on a dry basis corrected to 3.0% oxygen for combustion devices).

(3) Any vent gas streams affected by §115.121(c)(3) of this title must be controlled properly:

(A) at a temperature equal to or greater than 1,300 degrees Fahrenheit in an afterburner having a retention time of at least one-fourth of a second, and having a steady flame that is not affected by the cupola charge and relights automatically if extinguished; or

(B) by any other vapor control system, as defined in §115.10 of this title, with a control efficiency of at least 90% or to a VOC concentration of no more than 20 ppmv (on a dry basis corrected to 3.0% oxygen for combustion devices).

(4) Any vent gas streams affected by §115.121(c)(4) of this title must be controlled properly:

(A) in a smokeless flare that is lit at all times when VOC vapors are routed to the flare or in a combustion device used in a heating process associated with the operation of a blast furnace; or

(B) by any other vapor control system, as defined in §115.10 of this title, with a control efficiency of at least 90% or to a VOC concentration of no more than 20 ppmv (on a dry basis corrected to 3.0% oxygen for combustion devices).

§115.129. Counties and Compliance Schedules.

(a) Except as specified in subsections [subsection ] (g) and (h) of this section, in Aransas, Bexar, Brazoria, Calhoun, Chambers, Collin, Dallas, Denton, El Paso, Fort Bend, Galveston, Hardin, Harris, Jefferson, Liberty, Matagorda, Montgomery, Nueces, Orange, San Patricio, Travis, Victoria, and Waller Counties, the compliance date has passed and the owner or operator of each vent gas stream shall continue to comply with existing provisions in this division.

(b) The owner or operator of each bakery in Collin, Dallas, Denton, and Tarrant Counties subject to §115.122(a)(3)(C) of this title (relating to Control Requirements) shall comply with §§115.121(a)(3), 115.122(a)(3)(C), and 115.126(6) of this title (relating to Emission Specifications; Control Requirements; and Monitoring and Recordkeeping Requirements) as soon as practicable, but no later than one year, after the commission publishes notification in the Texas Register of its determination that this contingency rule is necessary as a result of failure to attain the national ambient air quality standard (NAAQS) for ozone by the attainment deadline or failure to demonstrate reasonable further progress as set forth in Federal Clean Air Act (FCAA), §172(c)(9).

(c) The owner or operator of each bakery in El Paso County subject to §115.122(a)(3)(D) of this title shall comply with §§115.121(a)(3), 115.122(a)(3)(D), and 115.126(6) of this title as soon as practicable, but no later than one year, after the commission publishes notification in the Texas Register of its determination that this contingency rule is necessary as a result of failure to attain the NAAQS for ozone by the attainment deadline or failure to demonstrate reasonable further progress as set forth in FCAA, §172(c)(9).

(d) The owner or operator of each vent gas stream in Ellis, Johnson, Kaufman, Parker, and Rockwall Counties shall comply with this division as soon as practicable, but no later than March 1, 2009.

(e) The owner or operator of each vent gas stream in Wise County shall comply with this division as soon as practicable, but no later than January 1, 2017.

(f) The owner or operator of a vent gas stream in Bexar, Collin, Dallas, Denton, Ellis, Johnson, Kaufman, Parker, Rockwall, Tarrant, and Wise Counties that becomes subject to a new requirement of this division on or after the applicable compliance date in this section shall comply with the requirements in this division as soon as practicable, but no later than 60 days after becoming subject.

(g) The owner or operator of each vent gas stream in the Bexar County area subject to the requirements of this division shall comply with the requirements of §115.121(c), §115.122(c), §115.123(c), and §115.127(c) through December 31, 2024, and all other applicable requirements of this division by no later than January 1, 2025.

(h) The owner or operator of each bakery in the Bexar County area subject to the requirements of this division shall comply with the requirements of §115.122(a)(3)(E) and §115.122(a)(3)(F)(iv) and all other applicable requirements of this division by no later than March 1, 2026.

The agency certifies that legal counsel has reviewed the proposal and found it to be within the state agency's legal authority to adopt.

Filed with the Office of the Secretary of State on July 11, 2025.

TRD-202502436

Charmaine Backens

Deputy Director, Environmental Law Division

Texas Commission on Environmental Quality

Earliest possible date of adoption: August 24, 2025

For further information, please call: (512) 239-2678


SUBCHAPTER C. VOLATILE ORGANIC COMPOUND TRANSFER OPERATIONS

DIVISION 6. GASOLINE DISPENSING FACILITY

30 TAC §§115.260, 115.262, 115.264 - 115.266, 115.269

Statutory Authority

The new rule sections are proposed under Texas Water Code (TWC), §5.102, concerning general powers; §5.103, concerning Rules; TWC, §5.105, concerning General Policy, which authorize the commission to adopt rules necessary to carry out its powers and duties under the TWC; TWC, §7.002, concerning Enforcement Authority, which authorizes the commission to enforce the provisions of the Water Code and the Health and Safety Code within the commission's jurisdiction; and under Texas Health and Safety Code (THSC), §382.017, concerning Rules, which authorizes the commission to adopt rules consistent with the policy and purpose of the Texas Clean Air Act.

The new rule sections are also proposed under THSC, §382.002, concerning Policy and Purpose, which establishes the commission's purpose to safeguard the state's air resources, consistent with the protection of public health, general welfare, and physical property; THSC, §382.011, concerning General Powers and Duties, which authorizes the commission to control the quality of the state's air; THSC, §382.012, concerning the State Air Control Plan, which authorizes the commission to prepare and develop a general, comprehensive plan for the proper control of the state's air; THSC, §382.016, concerning Monitoring Requirements; Examination of Records, which authorizes the commission to prescribe reasonable requirements for measuring and monitoring the emissions of air contaminants; and THSC, §382.021, concerning Sampling Methods and Procedures.

The proposed new sections implement TWC, §§5.102, 5.103, and 7.002; and THSC, §§382.002, 382.011, 382.012, 382.016, 382.017, and 382.021.

§115.260. Applicability and Definitions.

(a) Applicability. The requirements in this division apply to each gasoline dispensing facility in the Bexar County area. Both "gasoline dispensing facility" and "Bexar County area" are defined in §115.10 of this title (relating to Definitions).

(b) Definitions. Unless specifically defined in the Texas Clean Air Act (Texas Health and Safety Code, Chapter 382) or in §§3.2, 101.1, or 115.10 of this title (relating to Definitions, respectively), the terms in this division have the meanings commonly used in the field of air pollution control. The following meanings apply in this division unless the context clearly indicates otherwise.

(1) Conventional Nozzle--A gasoline dispensing facility pump nozzle that does not have a supplementary vapor recovery pathway and does not have features to control excess liquid releases such as spillage, post fueling drips, and liquid retention.

(2) Dispensing spillage--Spillage that occurs between the time when the dispensing nozzle is inserted into the tank receiving the dispensed liquid and the time when the dispensing nozzle is withdrawn from the tank or container receiving the dispensed liquid and reinserted into the gasoline pump nozzle housing bracket.

(3) Enhanced Conventional (ECO) Nozzle--A gasoline dispensing facility pump nozzle certified by California Air Resources Board (CARB) CP-207 dated July 12, 2021, (including updates and revisions) and listed on the CARB Executive Officer's Exhibit 1 "Component List" in CARB Executive Order NVR-1-F, "Relating to Certification of Non-Vapor Recovery Hoses and Enhanced Conventional Nozzles, For Use at Gasoline Dispensing Facilities with No Phase II Vapor Recovery Systems," executed February 18, 2021, including updates and revisions.

(4) Gasoline dispenser--Equipment at a gasoline dispensing facility, as defined in §115.10 of this title, that provides a connection and sufficient hydraulic force to transfer gasoline or a gasoline and ethanol mixture from a storage tank into motor vehicles.

(5) Low permeation hose--A hose used to dispense gasoline that is included by the CARB Executive Officer on the Exhibit 1 "Component List" in CARB Executive Order NVR-1-D, "Relating to Certification of Non-Vapor Recovery Hoses and Enhanced Conventional Nozzles, For Use at Gasoline Dispensing Facilities with No Phase II Vapor Recovery Systems, " executed March 1, 2019, and complies with the permeation performance standard in CARB CP-207 dated July 12, 2021, (including updates and revisions) as determined by UL 330 (seventh edition), including updates and revisions.

(6) Malfunctioning equipment--Equipment that is not operating according to the manufacturer's design or specifications.

§115.262. Control Requirements.

(a) Installation and use. The owner or operator of a gasoline dispenser equipment shall install low permeation hoses, as defined in §115.260(b) of this title (relating to Definitions), and enhanced conventional (ECO) nozzles, as defined in §115.260(b) of this title, on each affected gasoline dispenser as follows:

(1) All hoses dispensing gasoline or a gasoline and ethanol mixture must be low permeation hoses that permeate at a rate of no more than 10.0 grams per square meter per day (g/m2/day). This requirement exists for all hoses after the compliance date in §115.269(a) of this title (relating to Compliance Schedules).

(2) The owner or operator shall install ECO nozzles, as defined in §115.260(b) of this title, on each gasoline dispenser pump that becomes subject to this division by the compliance date in §115.269 of this title.

(b) Work Practices. The owner or operator of a gasoline dispensing facility shall not allow gasoline to be handled in a manner that would result in preventable vapor releases to the atmosphere for extended periods of time by implementing the following work practices:

(1) Implement and document spill prevention procedures.

(2) Prominently display the operating instructions for the gasoline dispensing system in the gasoline dispensing area and ensure instructions are clearly visible and legible to all customers. The operating instructions must include the following information:

(A) A clear, step by step description of how to correctly dispense gasoline with the nozzles used at the site using simple language and, if possible, visual aids; and

(B) An overfill warning to clearly state that continued attempts to dispense gasoline after the gasoline dispensing system indicates that the motor vehicle fuel tank is full may result in spillage and unnecessary air and water quality contamination.

(3) Establish and maintain a policy to not top off or overfill vehicle tanks or containers. Post sign(s) at the gasoline dispensing facility instructing a person filling up a motor vehicle to not top off the vehicle tank. A sign must be placed on each gasoline dispenser, or on a permanent fixture within six feet of the dispenser and be clearly visible to an individual using the hose and nozzle to dispense gasoline. Cover all gasoline storage tank fill-pipes with a gasketed seal when not in use.

(4) Clean up spills as expeditiously as practicable. The owner or operator must develop a written plan that describes how a spill will be cleaned up upon occurrence. The plan must include, but is not limited to, where spill materials are located, a brief description of how each is used, and an explanation of how the owner or operator is implementing the ‘as expeditiously as practicable' requirement.

(5) Minimize gasoline sent to open waste collection systems that collect and transport gasoline to reclamation and recycling devices, such as an oil/water separator.

(6) Provide adequate training and written instructions to gasoline dispensing facility operators and employees to ensure proper vehicle and container filling operations do not result in excessive or preventable gasoline spillage.

(7) Follow manufacturer's maintenance recommendations for all gasoline dispenser equipment to minimize gasoline spillage.

(c) Repair. Immediately remove from service and tag any gasoline dispensing system equipment identified during the inspection required by §115.264 of this title (relating to Monitoring and Inspection Requirements) as malfunctioning equipment until it is successfully repaired or replaced. Repair or replace any malfunctioning equipment identified as soon as possible before the next inspection required by §115.264 to minimize spillage.

(1) A component removed from service may not be returned to service until the malfunction is corrected.

(2) If the Executive Director or a designated representative finds during an inspection that a damaged or malfunctioning nozzle or other component of the gasoline dispensing system is not properly tagged, the component may not be returned to service until the defect is corrected.

§115.264. Monitoring and Inspection Requirements.

The owner or operator of gasoline dispenser equipment shall perform monthly inspections to check all of the following:

(1) Gasoline hoses are intact (no tears or holes).

(2) Gasoline nozzles function according to their design.

(3) Gasoline hoses are not touching the ground when the nozzle is resting on its holding bracket.

(4) Each gasoline nozzle fits securely in its holding bracket.

(5) Identify and document evidence of nozzle, hose, or other gasoline dispenser system leakage and the cause.

§115.265. Testing and Certification Requirements.

The following gasoline dispensing facility testing and certification requirements shall apply for the Bexar County area, as defined in §115.10 of this title (relating to Definitions).

(1) Test methods in UL 330 - Underwriters Laboratories' Standard for Hose and Hose Assemblies for Dispensing Flammable Liquids must be used to determine compliance with the low permeation hose limit in §115.262(a)(1) of this title (relating to Control Requirements).

(2) Each enhanced conventional nozzle subject to §115.262(b)(1) and (2) of this title must meet certification and test requirements in the California Air Resources Board (CARB) Certification Procedure for Enhanced Conventional (ECO) Nozzles and Low Permeation Conventional Hoses for Use at Gasoline Dispensing Facilities CP-207, dated July 12, 2021, including updates and revisions.

§115.266. Recordkeeping Requirements.

The owner or operator of gasoline dispensing facility equipment shall keep the following records.

(1) Records with the following information, as applicable, for each monitoring inspection conducted under subsection §115.264 of this title (relating to Monitoring and Inspection Requirements):

(A) The name of the person performing the inspection;

(B) The components inspected under subsection §115.264 of this title;

(C) The date the inspection was performed;

(D) The result of each inspection and repair of the components under §115.264 and §115.262(c) of this title (relating to Control Requirements), respectively;

(E) The name of the person making the correction or repair to the malfunctioning or failed component;

(F) The date the correction or repair was made to the malfunctioning or failed component; and

(G) The action taken to correct or repair the malfunctioning equipment.

(2) Records certifying the low permeation hoses and enhanced conventional nozzles.

(3) The owner or operator shall maintain on-site at the gasoline dispensing facility, or electronically stored allowing for on-site examination, a copy of the training schedule and written instructions required under §115.262(b) of this title.

(4) The owner or operator shall maintain all monitoring records for at least five years and make them available for review upon request by authorized representatives of the executive director, U.S. Environmental Protection Agency, or local air pollution control agencies with jurisdiction.

§115.269. Compliance Schedules.

(a) The owner or operator of gasoline dispenser equipment in Bexar County shall comply with the requirements of this division by no later than March 1, 2026.

(b) The owner or operator of gasoline dispenser equipment that becomes subject to this division after March 1, 2026, shall comply with the requirements of this division by no later than 60 days after becoming subject.

The agency certifies that legal counsel has reviewed the proposal and found it to be within the state agency's legal authority to adopt.

Filed with the Office of the Secretary of State on July 11, 2025.

TRD-202502437

Charmaine Backens

Deputy Director, Environmental Law Division

Texas Commission on Environmental Quality

Earliest possible date of adoption: August 24, 2025

For further information, please call: (512) 239-2678


SUBCHAPTER E. SOLVENT-USING PROCESSES

DIVISION 1. DEGREASING PROCESSES

30 TAC §§115.411, 115.412, 115.415, 115.416, 115.419

Statutory Authority

The amendments are proposed under Texas Water Code (TWC), §5.102, concerning general powers; §5.103, concerning Rules; TWC, §5.105, concerning General Policy, which authorize the commission to adopt rules necessary to carry out its powers and duties under the TWC; TWC, §7.002, concerning Enforcement Authority, which authorizes the commission to enforce the provisions of the Water Code and the Health and Safety Code within the commission's jurisdiction; and under Texas Health and Safety Code (THSC), §382.017, concerning Rules, which authorizes the commission to adopt rules consistent with the policy and purpose of the Texas Clean Air Act.

The amendments are also proposed under THSC, §382.002, concerning Policy and Purpose, which establishes the commission's purpose to safeguard the state's air resources, consistent with the protection of public health, general welfare, and physical property; THSC, §382.011, concerning General Powers and Duties, which authorizes the commission to control the quality of the state's air; THSC, §382.012, concerning the State Air Control Plan, which authorizes the commission to prepare and develop a general, comprehensive plan for the proper control of the state's air; THSC, §382.016, concerning Monitoring Requirements; Examination of Records, which authorizes the commission to prescribe reasonable requirements for measuring and monitoring the emissions of air contaminants; and THSC, §382.021, concerning Sampling Methods and Procedures.

The proposed amendments implement TWC, §§5.102, 5.103, and 7.002; and THSC, §§382.002, 382.011, 382.012, 382.016, 382.017, and 382.021.

§115.411. Exemptions.

(a) The following exemptions apply in the Beaumont-Port Arthur, Bexar County, Dallas-Fort Worth, El Paso, and Houston-Galveston-Brazoria areas and in Bastrop, Caldwell, Comal, Gregg, Guadalupe, Hays, Nueces, Travis, Victoria, Williamson, and Wilson Counties. The exemptions in this subsection are no longer available for an operation subject to §115.412(b) of this title (relating to Control Requirements) in the Dallas-Fort Worth area or §115.412(c) of this title in the Houston-Galveston-Brazoria area as of the compliance date specified in §115.419(f) or §115.419(g), respectively, of this title (relating to Counties and Compliance Schedules). Beginning March 1, 2026, the exemptions in this subsection are no longer available for an operation subject to §115.412(d) of this title in Bexar County.

(1) Any cold solvent cleaning system is exempt from the provisions of §115.412(a)(1)(B) of this title and may use an external drainage facility in place of an internal type drainage system, if the true vapor pressure of the solvent is less than or equal to 0.6 pounds per square inch absolute (psia) (4.1 kilo Pascals (kPa)) as measured at 100 degrees Fahrenheit (38 degrees Celsius) or if a cleaned part cannot fit into an internal drainage facility.

(2) The following are exempt from the requirements of §115.412(a)(1)(E) of this title:

(A) a cold solvent cleaning system for which the true vapor pressure of the solvent is less than or equal to 0.6 psia (4.1 kPa) as measured at 100 degrees Fahrenheit (38 degrees Celsius), provided that the solvent is not heated above 120 degrees Fahrenheit (49 degrees Celsius); and

(B) remote reservoir cold solvent cleaners.

(3) Any conveyorized degreaser with less than 20 square feet (ft2) (2 square meters (m2)) of air/vapor interface is exempt from the requirement of §115.412(a)(3)(A) of this title.

(4) An owner or operator who operates a remote reservoir cold solvent cleaner that uses solvent with a true vapor pressure equal to or less than 0.6 psia (4.1 kPa) measured at 100 degrees Fahrenheit (38 degrees Celsius) and that has a drain area less than 16 square inches (in2) (100 square centimeters (cm2)) and who properly disposes of waste solvent in enclosed containers is exempt from §115.412(a)(1) of this title.

(5) In Gregg, Nueces, and Victoria Counties, degreasing operations located on any property that can emit, when uncontrolled, a combined weight of volatile organic compounds (VOC) less than 550 pounds in any consecutive 24-hour period are exempt from the provisions of §115.412 of this title.

(b) If the commission publishes notice in the Texas Register, as provided in §115.419(f) of this title for the Dallas-Fort Worth area and/or §115.419(g) of this title for the Houston-Galveston-Brazoria area, to require compliance with the contingency measure control requirements of §115.412(b) of this title for the Dallas-Fort-Worth area and/or §115.412(c) of this title for the Houston-Galveston-Brazoria area, then the following exemptions apply in the applicable area as of the compliance date specified in §115.419(f) or (g) of this title.

(1) Any cold solvent cleaning system is exempt from the provisions of §115.412(a)(1)(B) of this title and may use an external drainage facility in place of an internal type drainage system if the VOC content of the solvent is less than or equal to 25 grams per liter (g/l) or if a cleaned part cannot fit into an internal drainage facility.

(2) The following are exempt from the requirements of §115.412(a)(1)(E) of this title:

(A) a cold solvent cleaning system for which the VOC content of the solvent is less than or equal to 25 g/l; and

(B) remote reservoir cold solvent cleaners.

(3) An owner or operator who operates a remote reservoir cold solvent cleaner that uses solvent with a VOC content that is less than or equal to 25 g/l and that has a drain area less than 16 (in2) (100 (cm2)) and who properly disposes of waste solvent in enclosed containers is exempt from §115.412(a)(1) of this title.

(c) Beginning March 1, 2026, the following exemptions apply in Bexar County.

(1) Any cold solvent cleaning system is exempt from the provisions of §115.412(a)(1)(B) of this title and may use an external drainage facility in place of an internal type drainage system if the VOC content of the solvent is less than or equal to 25 g/l or if a cleaned part cannot fit into an internal drainage facility.

(2) The following are exempt from the requirements of §115.412(a)(1)(E) of this title:

(A) a cold solvent cleaning system for which the VOC content of the solvent is less than or equal to 25 g/l; and

(B) remote reservoir cold solvent cleaners.

(3) An owner or operator who operates a remote reservoir cold solvent cleaner that uses solvent with a VOC content that is less than or equal to 25 g/l and that has a drain area less than 16 square inches (in2) (100 square centimeters (cm2)) and who properly disposes of waste solvent in enclosed containers is exempt from §115.412(a)(1) of this title.

§115.412. Control Requirements.

(a) In the Beaumont-Port Arthur, Bexar County, Dallas-Fort Worth, El Paso, and Houston-Galveston-Brazoria areas as defined in §115.10 of this title (relating to Definitions) and in Gregg, Nueces, Victoria, Comal, Guadalupe, Wilson, Bastrop, Caldwell, Hays, Travis, and Williamson Counties, the following control requirements shall apply.

(1) Cold solvent cleaning. No person shall own or operate a system utilizing a volatile organic compound (VOC) for the cold solvent cleaning of objects without the following controls.

(A) A cover shall be provided for each cleaner which shall be kept closed whenever parts are not being handled in the cleaner. The cover shall be designed for easy one-handed operation if any of the following exists:

(i) the true vapor pressure of the solvent is greater than 0.3 psia (2 kPa) as measured at 100 degrees Fahrenheit (38 degrees Celsius);

(ii) the solvent is agitated; or

(iii) the solvent is heated.

(B) An internal cleaned-parts drainage facility, for enclosed draining under a cover, shall be provided for all cold solvent cleaners.

(C) A permanent label summarizing the operating requirements in subparagraph (F) of this paragraph shall be attached to the cleaner in a conspicuous location near the operator.

(D) If a solvent spray is used, it must be a solid fluid stream (not a fine, atomized, or shower-type spray) and at an operating pressure of 10 [ten] psig or less as necessary to prevent splashing above the acceptable freeboard.

(E) The system shall be equipped with a freeboard that provides a ratio equal to or greater than 0.7, or a water cover (solvent must be insoluble in and heavier than water). To determine the freeboard ratio, the freeboard height measurement is taken from the top of the degreaser to the top of the air/solvent level. This number is then divided by the smallest width measurement. The width measurement is taken at the smallest interior dimension. This dimension could be located at any point, from the top or opening of the unit to the air/solvent level.

(F) The operating procedures shall be as follows.

(i) Waste solvent shall not be disposed of or transferred to another party such that the waste solvent can evaporate into the atmosphere. Waste solvents shall be stored only in covered containers.

(ii) The degreaser cover shall be kept closed whenever parts are not being handled in the cleaner.

(iii) Parts shall be drained for at least 15 seconds or until dripping ceases.

(iv) Porous or absorbent materials, such as cloth, leather, wood, or rope, shall not be degreased.

(2) Open-top vapor degreasing. No person shall own or operate a system utilizing a VOC for the open-top vapor degreasing of objects without the following controls:

(A) a cover that can be opened and closed easily without disturbing the vapor zone;

(B) the following devices which will automatically shut off the sump heat:

(i) a condenser coolant flow sensor and thermostat which will detect if the condenser coolant is not circulating or if the condenser coolant temperature exceeds the solvent manufacturer's recommendations;

(ii) a solvent level sensor which will detect if the solvent level drops below acceptable design limits; and

(iii) a vapor level sensor which will detect if the vapor level rises above acceptable design limits;

(C) a spray safety switch which will shut off the spray pump to prevent spraying above the vapor level;

(D) one of the following controls:

(i) a freeboard that provides a ratio equal to or greater than 0.75 and, if the degreaser opening is greater than 10 ft2 (1m2 [ 2]), a powered cover. To determine the freeboard ratio, the freeboard height measurement is taken from the top of the degreaser to the top of the air/vapor level. This number is then divided by the smallest width measurement. The width measurement is taken at the smallest interior dimension. This dimension could be located at any point, from the top or opening of the unit to the air/vapor level;

(ii) a properly sized refrigerated chiller capable of achieving 85% or greater control of VOC emissions;

(iii) an enclosed design where the cover or door opens only when the dry part is actually entering or exiting the degreaser; or

(iv) a carbon adsorption system with ventilation equal to or greater than 50 cfm/ft2 (15m3 [3]/min per m2) of air/vapor area (with the cover open) and exhausting less than 25 ppm of solvent by volume averaged over one complete adsorption cycle;

(E) a permanent, conspicuous, label summarizing the operating procedures listed in subparagraph (F) of this paragraph; and

(F) the following operating procedures:

(i) the cover shall be closed at all times except when processing work loads through the degreaser;

(ii) parts shall be positioned so that complete drainage is obtained;

(iii) parts shall be moved in and out of the degreaser at less than 11 ft/min (3.3 m/min);

(iv) the work load shall be retained in the vapor zone at least 30 seconds or until condensation ceases;

(v) any pools of solvent on the cleaned parts shall be removed by tipping the part before withdrawing it from the vapor zone;

(vi) parts shall be allowed to dry within the degreaser freeboard area for at least 15 seconds or until visually dry;

(vii) porous or absorbent materials, such as cloth, leather, wood, or rope, shall not be degreased;

(viii) work loads shall not occupy more than half of the degreaser open top surface area;

(ix) solvent shall not be sprayed above the vapor level;

(x) solvent leaks shall be repaired immediately, or the degreaser shall be shut down until repairs are made;

(xi) waste solvent shall not be disposed of or transferred to another party such that the waste solvent will evaporate into the atmosphere. Waste solvent shall be stored only in covered containers;

(xii) exhaust ventilation for systems other than those which vent to a major control device shall not exceed 65 cfm per ft2 [2] (20 m3/min per m2) of degreaser open area, unless necessary to meet Occupational Safety and Health Administration (OSHA) requirements or unless a carbon adsorption system is installed as a major control device. Ventilation fans or other sources of air agitation shall not be used near the degreaser opening; and

(xiii) water shall not be visibly detectable in the solvent exiting the water separator.

(3) Conveyorized degreasing. No person shall own or operate a system utilizing a VOC for the conveyorized cleaning of objects without the following controls:

(A) one of the following major control devices:

(i) a properly sized refrigerated chiller capable of achieving 85% or greater control of VOC emissions; or

(ii) a carbon adsorption system with ventilation equal to or greater than 50 cfm/ft2 (15 m3 [3]/min/m2 [ 2]) of air/vapor area (when downtime covers are open) and exhausting less than 25 ppm of solvent by volume averaged over one complete adsorption cycle;

(B) a drying tunnel or other means, such as rotating (tumbling) basket if space is available, to prevent solvent liquid or vapor carry-out;

(C) a condenser flow switch and thermostat which will shut off sump heat if the condenser coolant is not circulating or if the condenser coolant discharge temperature exceeds the solvent manufacturer's recommendation;

(D) a spray safety switch which will shut off the spray pump if the vapor level drops more than four inches (10 [ ten] cm);

(E) a vapor level control thermostat which will shut off the sump heat when the vapor level rises above the designed operating level;

(F) entrances and exits which silhouette work loads so that the average clearance (between parts and edge of the degreaser opening) is either less than four inches (10 [ten] cm) or less than 10% of the width of the opening;

(G) downtime covers which close off the entrance and exit during nonoperating hours;

(H) a permanent, conspicuous label near the operator summarizing the operating requirements in subparagraph (I) of this paragraph; and

(I) the following operating procedures:

(i) exhaust ventilation for systems other than those which vent to a major control device shall not exceed 65 cfm/ft2 (20 m3/min/m2) of degreaser opening, unless necessary to meet OSHA requirements or unless a carbon adsorption system is installed as a major control device. Ventilation fans shall not be used near the degreaser opening;

(ii) parts shall be positioned so that complete drainage is obtained;

(iii) vertical conveyor speed shall be maintained at less than 11 ft/min (3.3 m/min);

(iv) waste solvent shall not be disposed of, or transferred to another party, such that the waste solvent can evaporate into the atmosphere. Waste solvent shall be stored only in covered containers;

(v) leaks shall be repaired immediately or the degreaser shall be shut down until repairs are made;

(vi) water shall not be visibly detectable in the solvent exiting the water separator;

(vii) downtime covers shall be placed over entrances and exits of conveyorized degreasers immediately after the conveyor and exhaust are shut down and removed just before they are started up; and

(viii) porous or absorbent materials, such as cloth, leather, wood, or rope, shall not be degreased.

(b) In accordance with the compliance schedule for contingency requirements in §115.419(f) of this title (relating to Counties and Compliance Schedules), and in addition to the requirements of subsection (a) of this section, no person in the Dallas-Fort Worth area shall own or operate a system for the cold solvent cleaning, open-top vapor degreasing, or conveyorized degreasing of objects using a solvent with a VOC content greater than 25 grams per liter (g/l).

(c) In accordance with the compliance schedule for contingency requirements in §115.419(g) of this title, and in addition to the requirements of subsection (a) of this section, no person in the Houston-Galveston-Brazoria area shall own or operate a system for the cold solvent cleaning, open-top vapor degreasing, or conveyorized degreasing of objects using a solvent with a VOC content greater than 25 g/l.

(d) In addition to the requirements of subsection (a) of this section, beginning March 1, 2026, no person in the Bexar County area shall own or operate a system for cold solvent cleaning, open-top vapor degreasing, or conveyorized degreasing of objects using a solvent with a VOC content greater than 25 g/l.

§115.415. Testing Requirements.

The testing requirements for degreasing processes in the Beaumont-Port Arthur, Bexar County, Dallas-Fort Worth, El Paso, and Houston-Galveston-Brazoria areas and in Bastrop, Caldwell, Comal, Gregg, Guadalupe, Hays, Nueces, Travis, Victoria, Williamson, and Wilson Counties are as follows.

(1) Compliance with §115.412(a)(1) of this title (relating to Control Requirements) must be determined by applying the following test methods, as applicable:

(A) determination of true vapor pressure using ASTM International Test Method D323 [D323-89], ASTM Test Method D2879, ASTM Test Method D4953, ASTM Test Method D5190, or ASTM Test Method D5191 for the measurement of Reid vapor pressure, adjusted for actual storage temperature in accordance with American Petroleum Institute Publication 2517, Third Edition, 1989;

(B) minor modifications to the test methods and procedures listed in subparagraph (A) of this paragraph that are approved by the executive director.;

(C) using standard reference materials for the true vapor pressure of each volatile organic compound component; or

(D) using analytical data from the solvent supplier or manufacturer's material safety data sheet.

(2) Compliance with §115.412(a)(2)(D)(iv) and (a)(3)(A)(ii) of this title and §115.413(3) of this title (relating to Alternate Control Requirements) must be determined by applying the following test methods, as appropriate:

(A) Test Methods 1-4 (40 Code of Federal Regulations (CFR) Part 60, Appendix A) for determining flow rates, as necessary;

(B) Test Method 18 (40 CFR Part 60, Appendix A) for determining gaseous organic compound emissions by gas chromatography;

(C) Test Method 25 (40 CFR Part 60, Appendix A) for determining total gaseous nonmethane organic emissions as carbon;

(D) Test Methods 25A or 25B (40 CFR Part 60, Appendix A) for determining total gaseous organic concentrations using flame ionization or nondispersive infrared analysis; or

(E) minor modifications to these test methods and procedures approved by the executive director.

(3) Compliance with §115.412(b), [and ] (c), and (d) of this title must be determined by applying the following test methods, as applicable:

(A) Method 24 (40 CFR Part 60, Appendix A); or

(B) additional test procedures described in 40 CFR §60.446 (as amended through October 17, 2000 (65 Federal Register 61761)).

(4) Test methods other than those specified in paragraphs (1) - (3) of this section may be used if validated by 40 CFR Part 63, Appendix A, Test Method 301. For the purposes of this paragraph, substitute "executive director" each place that Test Method 301 references "administrator."

§115.416. Recordkeeping Requirements.

The owner or operator of each degreasing process in Beaumont-Port Arthur, Bexar County, Dallas-Fort Worth, El Paso, and Houston-Galveston-Brazoria areas and in Bastrop, Caldwell, Comal, Gregg, Guadalupe, Hays, Nueces, Travis, Victoria, Williamson, and Wilson Counties shall maintain the following records at the facility for at least two years and shall make such records available upon request to representatives of the executive director, the United States Environmental Protection Agency, or the local air pollution control agency having jurisdiction in the area:

(1) a record of control equipment maintenance, such as replacement of the carbon in a carbon adsorption unit;

(2) the results of all tests conducted at the facility in accordance with the requirements described in §115.415(2) and (3) of this title (relating to Testing Requirements);

(3) for each degreasing process in Gregg, Nueces, and Victoria Counties which is exempt under §115.411(a)(5) of this title (relating to Exemptions), records of solvent usage in sufficient detail to document continuous compliance with this exemption;

(4) for each degreasing process in the Dallas-Fort Worth area, records sufficient to demonstrate continuous compliance with:

(A) the vapor pressure testing described in §115.415(1)(A) - (D) of this title; and

(B) the applicable exemptions in §115.411 of this title

(5) for each degreasing process in the Bexar County area, records sufficient to demonstrate continuous compliance with:

(A) the volatile organic compound testing described in §115.415(3) of this title; and

(B) the applicable exemptions in §115.411 of this title.

§115.419. Counties and Compliance Schedules.

(a) In [Bexar,] Brazoria, Chambers, Collin, Dallas, Denton, El Paso, Fort Bend, Galveston, Gregg, Hardin, Harris, Jefferson, Liberty, Montgomery, Nueces, Orange, Tarrant, Victoria, and Waller, Counties, the compliance date has passed and all affected persons shall continue to comply with this division.

(b) All affected persons in Bastrop, Caldwell, Comal, Guadalupe, Hays, Travis, Williamson, and Wilson Counties shall comply with this division as soon as practicable, but no later than December 31, 2005.

(c) All affected persons in Ellis, Johnson, Kaufman, Parker, and Rockwall Counties shall comply with this division as soon as practicable, but no later than March 1, 2009.

(d) All affected persons of a degreasing process in Wise County shall comply with this division as soon as practicable, but no later than January 1, 2017.

(e) All affected persons of a degreasing process in Collin, Dallas, Denton, Ellis, Johnson, Kaufman, Parker, Rockwall, Tarrant, and Wise Counties that becomes subject to this division on or after the applicable compliance date in subsection (a), (c), or (d) of this section shall comply with the requirements in this division as soon as practicable, but no later than 60 days after becoming subject.

(f) All affected owners or operators of a degreasing process in Collin, Dallas, Denton, Ellis, Johnson, Kaufman, Parker, Rockwall, Tarrant, and Wise Counties shall be in compliance with §115.412(b) of this title (relating to Control Requirements) by no later than 270 days after the commission publishes notification in the Texas Register of its determination that this contingency rule is necessary as a result of EPA publication of a notice in the Federal Register that the specified area failed to attain the applicable National Ambient Air Quality Standard for ozone by the attainment deadline or failed to demonstrate reasonable further progress as set forth in the 1990 Amendments to the Federal Clean Air Act, §172(c)(9).

(g) All affected owners or operators of a degreasing process in Brazoria, Chambers, Fort Bend, Galveston, Harris, Liberty, Montgomery, and Waller Counties shall be in compliance with §115.412(c) of this title by no later than 270 days after the commission publishes notification in the Texas Register of its determination that this contingency rule is necessary as a result of EPA publication of a notice in the Federal Register that the specified area failed to attain the applicable National Ambient Air Quality Standard for ozone by the attainment deadline or failed to demonstrate reasonable further progress as set forth in the 1990 Amendments to the Federal Clean Air Act, §172(c)(9).

(h) The owner or operator of a degreasing process or operation in the Bexar County area subject to the requirements of this division shall comply with the requirements of this division, except §115.412(d) of this title, by no later than January 1, 2025. Beginning March 1, 2026, the owner or operator of a degreasing process or operation in the Bexar County area subject to the requirements of this division shall comply with §115.412(d). All affected persons of a degreasing process or operation in the Bexar County area that becomes subject to this division on or after the applicable compliance date in this subsection shall comply with the requirements of this division [by but] no later than 60 days after becoming subject.

The agency certifies that legal counsel has reviewed the proposal and found it to be within the state agency's legal authority to adopt.

Filed with the Office of the Secretary of State on July 11, 2025.

TRD-202502438

Charmaine Backens

Deputy Director, Environmental Law Division

Texas Commission on Environmental Quality

Earliest possible date of adoption: August 24, 2025

For further information, please call: (512) 239-2678


DIVISION 2. SURFACE COATING PROCESSES

30 TAC §§115.420, 115.421, 115.425, 115.427, 115.429

Statutory Authority

The amendments are proposed under Texas Water Code (TWC), §5.102, concerning general powers; §5.103, concerning Rules; TWC, §5.105, concerning General Policy, which authorize the commission to adopt rules necessary to carry out its powers and duties under the TWC; TWC, §7.002, concerning Enforcement Authority, which authorizes the commission to enforce the provisions of the Water Code and the Health and Safety Code within the commission's jurisdiction; and under Texas Health and Safety Code (THSC), §382.017, concerning Rules, which authorizes the commission to adopt rules consistent with the policy and purpose of the Texas Clean Air Act.

The amendments are also proposed under THSC, §382.002, concerning Policy and Purpose, which establishes the commission's purpose to safeguard the state's air resources, consistent with the protection of public health, general welfare, and physical property; THSC, §382.011, concerning General Powers and Duties, which authorizes the commission to control the quality of the state's air; THSC, §382.012, concerning the State Air Control Plan, which authorizes the commission to prepare and develop a general, comprehensive plan for the proper control of the state's air; THSC, §382.016, concerning Monitoring Requirements; Examination of Records, which authorizes the commission to prescribe reasonable requirements for measuring and monitoring the emissions of air contaminants; and THSC, §382.021, concerning Sampling Methods and Procedures.

The proposed amendments implement TWC, §§5.102, 5.103, and 7.002; and THSC, §§382.002, 382.011, 382.012, 382.016, 382.017, and 382.021.

§115.420. Applicability and Definitions.

(a) Applicability. The owner or operator of a surface coating process in the Beaumont-Port Arthur, Bexar County, Dallas-Fort Worth, El Paso, and Houston-Galveston-Brazoria areas, as defined in §115.10 of this title (relating to Definitions), and in Gregg, Nueces, and Victoria Counties, as specified in each paragraph below, is subject to this division. All owners and operators shall be in compliance with this division in accordance with the compliance schedules listed in §115.429 of this title (relating to Counties and Compliance Schedules).

(1) Large appliance coating. The requirements in this division apply in the Beaumont-Port Arthur and El Paso areas and in Gregg, Nueces, and Victoria Counties.

(2) Metal furniture coating. The requirements in this division apply in the Beaumont-Port Arthur and El Paso areas and in Gregg, Nueces, and Victoria Counties.

(3) Coil coating. The requirements in this division apply in the Beaumont-Port Arthur, Bexar County, Dallas-Fort Worth, El Paso, and Houston-Galveston-Brazoria areas and in Gregg, Nueces, and Victoria Counties.

(4) Paper coating. The requirements in this division apply in the Beaumont-Port Arthur, Dallas-Fort Worth, El Paso, and Houston-Galveston-Brazoria areas and in Gregg, Nueces, and Victoria Counties. In the Dallas-Fort Worth and Houston-Galveston-Brazoria areas, applicability is determined by the volatile organic compound (VOC) emissions from each individual paper coating line.

(A) Each paper coating line in the Dallas-Fort Worth and Houston-Galveston-Brazoria areas that has the potential to emit less than 25 tons per year (tpy) of VOC is subject to this division.

(B) Each paper coating line in the Dallas-Fort Worth and Houston-Galveston-Brazoria areas that has the potential to emit equal to or greater than 25 tpy of VOC is subject to the requirements in Division 5 of this Subchapter (relating to Control Requirements for Surface Coating Processes).

(5) Fabric coating. The requirements in this division apply in the Beaumont-Port Arthur, Bexar County, Dallas-Fort Worth, El Paso, and Houston-Galveston-Brazoria areas and in Gregg, Nueces, and Victoria Counties.

(6) Vinyl coating. The requirements in this division apply in the Beaumont-Port Arthur, Bexar County, Dallas-Fort Worth, El Paso, and Houston-Galveston-Brazoria areas, and in Gregg, Nueces, and Victoria Counties.

(7) Can coating. The requirements in this division apply in the Beaumont-Port Arthur, Bexar County, Dallas-Fort Worth, El Paso, and Houston-Galveston-Brazoria areas, and in Gregg, Nueces, and Victoria Counties.

(8) Automobile and light-duty truck coating. The requirements in this division apply in the Beaumont-Port Arthur, El Paso, and Houston-Galveston-Brazoria areas.

(9) Vehicle refinishing coating (body shops). The requirements in this division apply in the Bexar County, Dallas-Fort Worth, El Paso, and Houston-Galveston-Brazoria areas.

(10) Miscellaneous metal parts and products coating. The requirements in this division apply in the Beaumont-Port Arthur and El Paso areas and in Gregg, Nueces, and Victoria Counties. In the Dallas-Fort Worth and Houston-Galveston-Brazoria areas, the requirements in this division apply only to designated on-site maintenance shops as specified in §115.427(8) of this title (relating to Exemptions).

(11) Factory surface coating of flat wood paneling. The requirements in this division apply in the Beaumont-Port Arthur, Bexar County, Dallas-Fort Worth, El Paso, and Houston-Galveston-Brazoria areas and in Gregg, Nueces, and Victoria Counties.

(12) Aerospace coating. The requirements in this division apply in the Beaumont-Port Arthur, Bexar County, Dallas-Fort Worth, El Paso, and Houston-Galveston-Brazoria areas and in Gregg, Nueces, and Victoria Counties.

(13) Mirror backing coating. The requirements in this division apply in the Beaumont-Port Arthur, Bexar County, Dallas-Fort Worth El Paso, and Houston-Galveston-Brazoria areas.

(14) Wood parts and products coating. The requirements in this division apply in the Bexar County, Dallas-Fort Worth El Paso, and Houston-Galveston-Brazoria areas.

(15) Wood furniture manufacturing coatings. The requirements in this division apply in the Beaumont-Port Arthur, Bexar County, Dallas-Fort Worth, El Paso, and Houston-Galveston-Brazoria areas.

(16) Marine coatings. The requirements in this division apply in the Beaumont-Port Arthur and Houston-Galveston-Brazoria areas.

(b) General surface coating definitions. The following terms, when used in this division have the following meanings, unless the context clearly indicates otherwise. Additional definitions for terms used in this division are found in §§3.2, 101.1, and 115.10 of this title (relating to Definitions).

(1) Aerosol coating (spray paint)--A hand-held, pressurized, nonrefillable container that expels an adhesive or a coating in a finely divided spray when a valve on the container is depressed.

(2) Coating--A material applied onto or impregnated into a substrate for protective, decorative, or functional purposes. Such materials include, but are not limited to, paints, varnishes, sealants, adhesives, thinners, diluents, inks, maskants, and temporary protective coatings.

(3) Coating application system--Devices or equipment designed for the purpose of applying a coating material to a surface. The devices may include, but are not be limited to, brushes, sprayers, flow coaters, dip tanks, rollers, knife coaters, and extrusion coaters.

(4) Coating line--An operation consisting of a series of one or more coating application systems and including associated flashoff area(s), drying area(s), and oven(s) wherein a surface coating is applied, dried, or cured.

(5) Coating solids (or solids)--The part of a coating that remains after the coating is dried or cured.

(6) Daily weighted average--The total weight of volatile organic compound (VOC) emissions from all coatings subject to the same emission standard in §115.421 of this title (relating to Emission Specifications), divided by the total volume of those coatings (minus water and exempt solvent) delivered to the application system each day. Coatings subject to different emission standards in §115.421 of this title must not be combined for purposes of calculating the daily weighted average. In addition, determination of compliance is based on each individual coating line.

(7) High-volume low-pressure spray guns--Equipment used to apply coatings by means of a spray gun which operates between 0.1 and 10.0 pounds per square inch gauge air pressure at the air cap.

(8) Normally closed container--A container that is closed unless an operator is actively engaged in activities such as adding or removing material.

(9) Pounds of VOC per gallon of coating (minus water and exempt solvents)--Basis for emission limits for surface coating processes. Can be calculated by the following equation:

Figure: 30 TAC §115.420(b)(9) (No change.)

(10) Pounds of VOC per gallon of solids--Basis for emission limits for surface coating process. Can be calculated by the following equation:

Figure: 30 TAC §115.420(b)(10) (No change.)

(11) Spray gun--A device that atomizes a coating or other material and projects the particulates or other material onto a substrate.

(12) Surface coating processes--Operations which utilize a coating application system.

(13) Transfer efficiency--The amount of coating solids deposited onto the surface of a part or product divided by the total amount of coating solids delivered to the coating application system.

(c) Specific surface coating definitions. The following terms, when used in this division, shall have the following meanings, unless the context clearly indicates otherwise.

(1) Aerospace coating.

(A) Ablative coating--A coating that chars when exposed to open flame or extreme temperatures, as would occur during the failure of an engine casing or during aerodynamic heating. The ablative char surface serves as an insulative barrier, protecting adjacent components from the heat or open flame.

(B) Adhesion promoter--A very thin coating applied to a substrate to promote wetting and form a chemical bond with the subsequently applied material.

(C) Adhesive bonding primer--A primer applied in a thin film to aerospace components for the purpose of corrosion inhibition and increased adhesive bond strength by attachment. There are two categories of adhesive bonding primers: primers with a design cure at 250 degrees Fahrenheit or below and primers with a design cure above 250 degrees Fahrenheit.

(D) Aerospace vehicle or component--Any fabricated part, processed part, assembly of parts, or completed unit, with the exception of electronic components, of any aircraft including but not limited to airplanes, helicopters, missiles, rockets, and space vehicles.

(E) Aircraft fluid systems--Those systems that handle hydraulic fluids, fuel, cooling fluids, or oils.

(F) Aircraft transparency--The aircraft windshield, canopy, passenger windows, lenses, and other components which are constructed of transparent materials.

(G) Antichafe coating--A coating applied to areas of moving aerospace components that may rub during normal operations or installation.

(H) Antique aerospace vehicle or component--An aerospace vehicle or component thereof that was built at least 30 years ago. An antique aerospace vehicle would not routinely be in commercial or military service in the capacity for which it was designed.

(I) Aqueous cleaning solvent--A solvent in which water is at least 80% by volume of the solvent as applied.

(J) Bearing coating--A coating applied to an antifriction bearing, a bearing housing, or the area adjacent to such a bearing in order to facilitate bearing function or to protect base material from excessive wear. A material shall not be classified as a bearing coating if it can also be classified as a dry lubricative material or a solid film lubricant.

(K) Bonding maskant--A temporary coating used to protect selected areas of aerospace parts from strong acid or alkaline solutions during processing for bonding.

(L) Caulking and smoothing compounds--Semi-solid materials which are applied by hand application methods and are used to aerodynamically smooth exterior vehicle surfaces or fill cavities such as bolt hole accesses. A material shall not be classified as a caulking and smoothing compound if it can also be classified as a sealant.

(M) Chemical agent-resistant coating--An exterior topcoat designed to withstand exposure to chemical warfare agents or the decontaminants used on these agents.

(N) Chemical milling maskant--A coating that is applied directly to aluminum components to protect surface areas when chemically milling the component with a Type I or II etchant. Type I chemical milling maskants are used with a Type I etchant and Type II chemical milling maskants are used with a Type II etchant. This definition does not include bonding maskants, critical use and line sealer maskants, and seal coat maskants. Additionally, maskants that must be used with a combination of Type I or II etchants and any of the above types of maskants (i.e., bonding, critical use and line sealer, and seal coat) are not included. Maskants that are defined as specialty coatings are not included under this definition.

(O) Cleaning operation--Spray-gun, hand-wipe, and flush cleaning operations.

(P) Cleaning solvent--A liquid material used for hand-wipe, spray gun, or flush cleaning. This definition does not include solutions that contain no VOC.

(Q) Clear coating--A transparent coating usually applied over a colored opaque coating, metallic substrate, or placard to give improved gloss and protection to the color coat.

(R) Closed-cycle depainting system--A dust free, automated process that removes permanent coating in small sections at a time, and maintains a continuous vacuum around the area(s) being depainted to capture emissions.

(S) Coating operation--Using a spray booth, tank, or other enclosure or any area (such as a hangar) for applying a single type of coating (e.g., primer); using the same spray booth for applying another type of coating (e.g., topcoat) constitutes a separate coating operation for which compliance determinations are performed separately.

(T) Coating unit--A series of one or more coating applicators and any associated drying area and/or oven wherein a coating is applied, dried, and/or cured. A coating unit ends at the point where the coating is dried or cured, or prior to any subsequent application of a different coating.

(U) Commercial exterior aerodynamic structure primer--A primer used on aerodynamic components and structures that protrude from the fuselage, such as wings and attached components, control surfaces, horizontal stabilizers, vertical fins, wing-to-body fairings, antennae, and landing gear and doors, for the purpose of extended corrosion protection and enhanced adhesion.

(V) Commercial interior adhesive--Materials used in the bonding of passenger cabin interior components. These components must meet the Federal Aviation Administration (FAA) fireworthiness requirements.

(W) Compatible substrate primer--Either compatible epoxy primer or adhesive primer. Compatible epoxy primer is primer that is compatible with the filled elastomeric coating and is epoxy based. The compatible substrate primer is an epoxy-polyamide primer used to promote adhesion of elastomeric coatings such as impact-resistant coatings. Adhesive primer is a coating that:

(i) inhibits corrosion and serves as a primer applied to bare metal surfaces or prior to adhesive application; or

(ii) is applied to surfaces that can be expected to contain fuel. Fuel tank coatings are excluded from this category.

(X) Confined space--A space that:

(i) is large enough and so configured that a person can bodily enter and perform assigned work;

(ii) has limited or restricted means for entry or exit (for example, fuel tanks, fuel vessels, and other spaces that have limited means of entry); and

(iii) is not suitable for continuous occupancy.

(Y) Corrosion prevention compound--A coating system or compound that provides corrosion protection by displacing water and penetrating mating surfaces, forming a protective barrier between the metal surface and moisture. Coatings containing oils or waxes are excluded from this category.

(Z) Critical use and line sealer maskant--A temporary coating, not covered under other maskant categories, used to protect selected areas of aerospace parts from strong acid or alkaline solutions such as those used in anodizing, plating, chemical milling and processing of magnesium, titanium, or high-strength steel, high-precision aluminum chemical milling of deep cuts, and aluminum chemical milling of complex shapes. Materials used for repairs or to bridge gaps left by scribing operations (i.e., line sealer) are also included in this category.

(AA) Cryogenic flexible primer--A primer designed to provide corrosion resistance, flexibility, and adhesion of subsequent coating systems when exposed to loads up to and surpassing the yield point of the substrate at cryogenic temperatures (-275 degrees Fahrenheit and below).

(BB) Cryoprotective coating--A coating that insulates cryogenic or subcooled surfaces to limit propellant boil-off, maintain structural integrity of metallic structures during ascent or re-entry, and prevent ice formation.

(CC) Cyanoacrylate adhesive--A fast-setting, single component adhesive that cures at room temperature. Also known as "super glue."

(DD) Dry lubricative material--A coating consisting of lauric acid, cetyl alcohol, waxes, or other noncross linked or resin-bound materials that act as a dry lubricant.

(EE) Electric or radiation-effect coating--A coating or coating system engineered to interact, through absorption or reflection, with specific regions of the electromagnetic energy spectrum, such as the ultraviolet, visible, infrared, or microwave regions. Uses include, but are not limited to, lightning strike protection, electromagnetic pulse (EMP) protection, and radar avoidance. Coatings that have been designated as "classified" by the Department of Defense are excluded.

(FF) Electrostatic discharge and electromagnetic interference coating--A coating applied to space vehicles, missiles, aircraft radomes, and helicopter blades to disperse static energy or reduce electromagnetic interference.

(GG) Elevated-temperature Skydrol-resistant commercial primer--A primer applied primarily to commercial aircraft (or commercial aircraft adapted for military use) that must withstand immersion in phosphate-ester hydraulic fluid (Skydrol 500b or equivalent) at the elevated temperature of 150 degrees Fahrenheit for 1,000 hours.

(HH) Epoxy polyamide topcoat--A coating used where harder films are required or in some areas where engraving is accomplished in camouflage colors.

(II) Fire-resistant (interior) coating--For civilian aircraft, fire-resistant interior coatings are used on passenger cabin interior parts that are subject to the FAA fireworthiness requirements. For military aircraft, fire-resistant interior coatings are used on parts that are subject to the flammability requirements of MIL-STD-1630A and MIL-A-87721. For space applications, these coatings are used on parts that are subject to the flammability requirements of SE-R-0006 and SSP 30233.

(JJ) Flexible primer--A primer that meets flexibility requirements such as those needed for adhesive bond primed fastener heads or on surfaces expected to contain fuel. The flexible coating is required because it provides a compatible, flexible substrate over bonded sheet rubber and rubber-type coatings as well as a flexible bridge between the fasteners, skin, and skin-to-skin joints on outer aircraft skins. This flexible bridge allows more topcoat flexibility around fasteners and decreases the chance of the topcoat cracking around the fasteners. The result is better corrosion resistance.

(KK) Flight test coating--A coating applied to aircraft other than missiles or single-use aircraft prior to flight testing to protect the aircraft from corrosion and to provide required marking during flight test evaluation.

(LL) Flush cleaning--Removal of contaminants such as dirt, grease, oil, and coatings from an aerospace vehicle or component or coating equipment by passing solvent over, into, or through the item being cleaned. The solvent may simply be poured into the item being cleaned and then drained, or assisted by air or hydraulic pressure, or by pumping. Hand-wipe cleaning operations where wiping, scrubbing, mopping, or other hand action are used are not included.

(MM) Fuel tank adhesive--An adhesive used to bond components exposed to fuel and must be compatible with fuel tank coatings.

(NN) Fuel tank coating--A coating applied to fuel tank components for the purpose of corrosion and/or bacterial growth inhibition and to assure sealant adhesion in extreme environmental conditions.

(OO) Grams of VOC per liter of coating (less water and less exempt solvent)--The weight of VOC per combined volume of total volatiles and coating solids, less water and exempt compounds. Can be calculated by the following equation:

Figure: 30 TAC §115.420(c)(1)(OO) (No change.)

(PP) Hand-wipe cleaning operation--Removing contaminants such as dirt, grease, oil, and coatings from an aerospace vehicle or component by physically rubbing it with a material such as a rag, paper, or cotton swab that has been moistened with a cleaning solvent.

(QQ) High temperature coating--A coating designed to withstand temperatures of more than 350 degrees Fahrenheit.

(RR) Hydrocarbon-based cleaning solvent--A solvent which is composed of VOC (photochemically reactive hydrocarbons) and/or oxygenated hydrocarbons, has a maximum vapor pressure of seven millimeters of mercury (mm Hg) at 20 degrees Celsius (68 degrees Fahrenheit), and contains no hazardous air pollutant (HAP) identified in the 1990 Amendments to the Federal Clean Air Act (FCAA), §112(b).

(SS) Insulation covering--Material that is applied to foam insulation to protect the insulation from mechanical or environmental damage.

(TT) Intermediate release coating--A thin coating applied beneath topcoats to assist in removing the topcoat in depainting operations and generally to allow the use of less hazardous depainting methods.

(UU) Lacquer--A clear or pigmented coating formulated with a nitrocellulose or synthetic resin to dry by evaporation without a chemical reaction. Lacquers are resoluble in their original solvent.

(VV) Limited access space--Internal surfaces or passages of an aerospace vehicle or component that cannot be reached without the aid of an airbrush or a spray gun extension for the application of coatings.

(WW) Metalized epoxy coating--A coating that contains relatively large quantities of metallic pigmentation for appearance and/or added protection.

(XX) Mold release--A coating applied to a mold surface to prevent the molded piece from sticking to the mold as it is removed.

(YY) Monthly weighted average--The total weight of VOC emission from all coatings divided by the total volume of those coatings (minus water and exempt solvents) delivered to the application system each calendar month. Coatings shall not be combined for purposes of calculating the monthly weighted average. In addition, determination of compliance is based on each individual coating operation.

(ZZ) Nonstructural adhesive--An adhesive that bonds nonload bearing aerospace components in noncritical applications and is not covered in any other specialty adhesive categories.

(AAA) Operating parameter value--A minimum or maximum value established for a control equipment or process parameter that, if achieved by itself or in combination with one or more other operating parameter values, determines that an owner or operator has continued to comply with an applicable emission limitation.

(BBB) Optical antireflection coating--A coating with a low reflectance in the infrared and visible wavelength ranges that is used for antireflection on or near optical and laser hardware.

(CCC) Part marking coating--Coatings or inks used to make identifying markings on materials, components, and/or assemblies of aerospace vehicles. These markings may be either permanent or temporary.

(DDD) Pretreatment coating--An organic coating that contains at least 0.5% acids by weight and is applied directly to metal or composite surfaces to provide surface etching, corrosion resistance, adhesion, and ease of stripping.

(EEE) Primer--The first layer and any subsequent layers of identically formulated coating applied to the surface of an aerospace vehicle or component. Primers are typically used for corrosion prevention, protection from the environment, functional fluid resistance, and adhesion of subsequent coatings. Primers that are defined as specialty coatings are not included under this definition.

(FFF) Radome--The nonmetallic protective housing for electromagnetic transmitters and receivers (e.g., radar, electronic countermeasures, etc.).

(GGG) Rain erosion-resistant coating--A coating or coating system used to protect the leading edges of parts such as flaps, stabilizers, radomes, engine inlet nacelles, etc. against erosion caused by rain impact during flight.

(HHH) Research and development--An operation whose primary purpose is for research and development of new processes and products and that is conducted under the close supervision of technically trained personnel and is not involved in the manufacture of final or intermediate products for commercial purposes, except in a de minimis manner.

(III) Rocket motor bonding adhesive--An adhesive used in rocket motor bonding applications.

(JJJ) Rocket motor nozzle coating--A catalyzed epoxy coating system used in elevated temperature applications on rocket motor nozzles.

(KKK) Rubber-based adhesive--A quick setting contact cement that provides a strong, yet flexible bond between two mating surfaces that may be of dissimilar materials.

(LLL) Scale inhibitor--A coating that is applied to the surface of a part prior to thermal processing to inhibit the formation of scale.

(MMM) Screen print ink--An ink used in screen printing processes during fabrication of decorative laminates and decals.

(NNN) Sealant--A material used to prevent the intrusion of water, fuel, air, or other liquids or solids from certain areas of aerospace vehicles or components. There are two categories of sealants: extrudable/rollable/brushable sealants and sprayable sealants.

(OOO) Seal coat maskant--An overcoat applied over a maskant to improve abrasion and chemical resistance during production operations.

(PPP) Self-priming topcoat--A topcoat that is applied directly to an uncoated aerospace vehicle or component for purposes of corrosion prevention, environmental protection, and functional fluid resistance. More than one layer of identical coating formulation may be applied to the vehicle or component.

(QQQ) Semiaqueous cleaning solvent--A solution in which water is a primary ingredient. More than 60% by volume of the solvent solution as applied must be water.

(RRR) Silicone insulation material--An insulating material applied to exterior metal surfaces for protection from high temperatures caused by atmospheric friction or engine exhaust. These materials differ from ablative coatings in that they are not "sacrificial."

(SSS) Solid film lubricant--A very thin coating consisting of a binder system containing as its chief pigment material one or more of the following: molybdenum, graphite, polytetrafluoroethylene, or other solids that act as a dry lubricant between faying (i.e., closely or tightly fitting) surfaces.

(TTT) Space vehicle--A man-made device, either manned or unmanned, designed for operation beyond earth's atmosphere. This definition includes integral equipment such as models, mock-ups, prototypes, molds, jigs, tooling, hardware jackets, and test coupons. Also included is auxiliary equipment associated with test, transport, and storage, that through contamination can compromise the space vehicle performance.

(UUU) Specialty coating--A coating that, even though it meets the definition of a primer, topcoat, or self-priming topcoat, has additional performance criteria beyond those of primers, topcoats, and self-priming topcoats for specific applications. These performance criteria may include, but are not limited to, temperature or fire resistance, substrate compatibility, antireflection, temporary protection or marking, sealing, adhesively joining substrates, or enhanced corrosion protection.

(VVV) Specialized function coating--A coating that fulfills extremely specific engineering requirements that are limited in application and are characterized by low volume usage. This category excludes coatings covered in other specialty coating categories.

(WWW) Structural autoclavable adhesive--An adhesive used to bond load-carrying aerospace components that is cured by heat and pressure in an autoclave.

(XXX) Structural nonautoclavable adhesive--An adhesive cured under ambient conditions that is used to bond load-carrying aerospace components or other critical functions, such as nonstructural bonding in the proximity of engines.

(YYY) Surface preparation--The removal of contaminants from the surface of an aerospace vehicle or component or the activation or reactivation of the surface in preparation for the application of a coating.

(ZZZ) Temporary protective coating--A coating applied to provide scratch or corrosion protection during manufacturing, storage, or transportation. Two types include peelable protective coatings and alkaline removable coatings. These materials are not intended to protect against strong acid or alkaline solutions. Coatings that provide this type of protection from chemical processing are not included in this category.

(AAAA) Thermal control coating--A coating formulated with specific thermal conductive or radiative properties to permit temperature control of the substrate.

(BBBB) Topcoat--A coating that is applied over a primer on an aerospace vehicle or component for appearance, identification, camouflage, or protection. Topcoats that are defined as specialty coatings are not included under this definition.

(CCCC) Touch-up and repair coating--A coating used to cover minor coating imperfections appearing after the main coating operation.

(DDDD) Touch-up and repair operation--That portion of the coating operation that is the incidental application of coating used to cover minor imperfections in the coating finish or to achieve complete coverage. This definition includes out-of-sequence or out-of-cycle coating.

(EEEE) Volatile organic compound (VOC) composite vapor pressure--The sum of the partial pressures of the compounds defined as VOCs, determined by the following calculation:

Figure: 30 TAC §115.420(c)(1)(EEEE) (No change.)

(FFFF) Waterborne (water-reducible) coating--A coating which contains more than 5.0% water by weight as applied in its volatile fraction.

(GGGG) Wet fastener installation coating--A primer or sealant applied by dipping, brushing, or daubing to fasteners that are installed before the coating is cured.

(HHHH) Wing coating--A corrosion-resistant topcoat that is resilient enough to withstand the flexing of the wings.

(2) Can coating--The coating of cans for beverages (including beer), edible products (including meats, fruit, vegetables, and others), tennis balls, motor oil, paints, and other mass-produced cans.

(3) Coil coating--The coating of any flat metal sheet or strip supplied in rolls or coils.

(4) Fabric coating--The application of coatings to fabric, which includes rubber application (rainwear, tents, and industrial products such as gaskets and diaphragms). The following definitions apply to fabric coatings.

(A) Plasticizer--A material used to keep plastic material soft and viscous.

(B) Plastisol--A coating that is a liquid dispersion of small particles of resins and plasticizers that are fused to become a plastic.

(C) Wash Primer--A material used to clean and/or activate surfaces of fabric, and may contain no more than 5.0 percent, by weight, solid materials.

(5) Factory surface coating of flat wood paneling--Coating of flat wood paneling products, including hardboard, hardwood plywood, particle board, printed interior paneling, and tile board.

(6) Large appliance coating--The coating of doors, cases, lids, panels, and interior support parts of residential and commercial washers, dryers, ranges, refrigerators, freezers, water heaters, dishwashers, trash compactors, air conditioners, and other large appliances.

(7) Metal furniture coating--The coating of metal furniture (tables, chairs, wastebaskets, beds, desks, lockers, benches, shelves, file cabinets, lamps, and other metal furniture products) or the coating of any metal part which will be a part of a nonmetal furniture product.

(8) Mirror backing coating--The application of coatings to the silvered surface of a mirror.

(9) Miscellaneous metal parts and products coating.

(A) Clear coat--A coating which lacks opacity or which is transparent and which may or may not have an undercoat that is used as a reflectant base or undertone color.

(B) Drum (metal)--Any cylindrical metal shipping container with a nominal capacity equal to or greater than 12 gallons (45.4 liters) but equal to or less than 110 gallons (416 liters).

(C) Extreme performance coating--A coating intended for exposure to extreme environmental conditions, such as continuous outdoor exposure; temperatures frequently above 95 degrees Celsius (203 degrees Fahrenheit); detergents; abrasive and scouring agents; solvents; and corrosive solutions, chemicals, or atmospheres.

(D) High-bake coatings--Coatings designed to cure at temperatures above 194 degrees Fahrenheit.

(E) Low-bake coatings--Coatings designed to cure at temperatures of 194 degrees Fahrenheit or less.

(F) Miscellaneous metal parts and products (MMPP) coating--The coating of MMPP in the following categories at original equipment manufacturing operations; designated on-site maintenance shops which recoat used parts and products; and off-site job shops which coat new parts and products or which recoat used parts and products:

(i) large farm machinery (harvesting, fertilizing, and planting machines, tractors, combines, etc.);

(ii) small farm machinery (lawn and garden tractors, lawn mowers, rototillers, etc.);

(iii) small appliances (fans, mixers, blenders, crock pots, dehumidifiers, vacuum cleaners, etc.);

(iv) commercial machinery (computers and auxiliary equipment, typewriters, calculators, vending machines, etc.);

(v) industrial machinery (pumps, compressors, conveyor components, fans, blowers, transformers, etc.);

(vi) fabricated metal products (metal-covered doors, frames, etc.); and

(vii) any other category of coated metal products, including, but not limited to, those which are included in the Standard Industrial Classification Code major group 33 (primary metal industries), major group 34 (fabricated metal products), major group 35 (nonelectrical machinery), major group 36 (electrical machinery), major group 37 (transportation equipment), major group 38 (miscellaneous instruments), and major group 39 (miscellaneous manufacturing industries). Excluded are those surface coating processes specified in paragraphs (1) - (8) and (10) - (14) of this subsection.

(G) Pail (metal)--Any cylindrical metal shipping container with a nominal capacity equal to or greater than 1 gallon (3.8 liters) but less than 12 gallons (45.4 liters) and constructed of 29 gauge or heavier material.

(10) Paper coating--The coating of paper and pressure-sensitive tapes (regardless of substrate and including paper, fabric, and plastic film) and related web coating processes on plastic film (including typewriter ribbons, photographic film, and magnetic tape) and metal foil (including decorative, gift wrap, and packaging).

(11) Marine coatings.

(A) Air flask specialty coating--Any special composition coating applied to interior surfaces of high pressure breathing air flasks to provide corrosion resistance and that is certified safe for use with breathing air supplies.

(B) Antenna specialty coating--Any coating applied to equipment through which electromagnetic signals must pass for reception or transmission.

(C) Antifoulant specialty coating--Any coating that is applied to the underwater portion of a vessel to prevent or reduce the attachment of biological organisms and that is registered with the EPA as a pesticide under the Federal Insecticide, Fungicide, and Rodenticide Act.

(D) Batch--The product of an individual production run of a coating manufacturer's process. (A batch may vary in composition from other batches of the same product.)

(E) Bitumens--Black or brown materials that are soluble in carbon disulfide, which consist mainly of hydrocarbons.

(F) Bituminous resin coating--Any coating that incorporates bitumens as a principal component and is formulated primarily to be applied to a substrate or surface to resist ultraviolet radiation and/or water.

(G) Epoxy--Any thermoset coating formed by reaction of an epoxy resin (i.e., a resin containing a reactive epoxide with a curing agent).

(H) General use coating--Any coating that is not a specialty coating.

(I) Heat resistant specialty coating--Any coating that during normal use must withstand a temperature of at least 204 degrees Celsius (400 degrees Fahrenheit).

(J) High-gloss specialty coating--Any coating that achieves at least 85% reflectance on a 60 degree meter when tested by the American Society for Testing and Materials (ASTM) Method D523 [D-523].

(K) High-temperature specialty coating--Any coating that during normal use must withstand a temperature of at least 426 degrees Celsius (800 degrees Fahrenheit).

(L) Inorganic zinc (high-build) specialty coating--A coating that contains 960 grams per liter (eight pounds per gallon) or more elemental zinc incorporated into an inorganic silicate binder that is applied to steel to provide galvanic corrosion resistance. (These coatings are typically applied at more than two mil dry film thickness.)

(M) Maximum allowable thinning ratio--The maximum volume of thinner that can be added per volume of coating without exceeding the applicable VOC limit of §115.421(15) of this title.

(N) Military exterior specialty coating--Any exterior topcoat applied to military or United States Coast Guard vessels that are subject to specific chemical, biological, and radiological washdown requirements.

(O) Mist specialty coating--Any low viscosity, thin film, epoxy coating applied to an inorganic zinc primer that penetrates the porous zinc primer and allows the occluded air to escape through the paint film prior to curing.

(P) Navigational aids specialty coating--Any coating applied to Coast Guard buoys or other Coast Guard waterway markers when they are recoated aboard ship at their usage site and immediately returned to the water.

(Q) Nonskid specialty coating--Any coating applied to the horizontal surfaces of a marine vessel for the specific purpose of providing slip resistance for personnel, vehicles, or aircraft.

(R) Nonvolatiles (or volume solids)--Substances that do not evaporate readily. This term refers to the film-forming material of a coating.

(S) Nuclear specialty coating--Any protective coating used to seal porous surfaces such as steel (or concrete) that otherwise would be subject to intrusion by radioactive materials. These coatings must be resistant to long-term (service life) cumulative radiation exposure (ASTM D4082 [D4082-83]), relatively easy to decontaminate (ASTM D4256[-83]), and resistant to various chemicals to which the coatings are likely to be exposed (ASTM 3912 [3912-80]). (For nuclear coatings, see the general protective requirements outlined by the Nuclear Regulatory Commission ["U.S. Atomic Energy Commission in a report entitled "U.S. Atomic Energy Commission] Regulatory Guide 1.54, "Service Level I, II, III, and In-Scope License Renewal Protective Coatings Applied to Nuclear Power Plants" Revision 3, [ "] dated April 2017 [June 1973], available in 82 Federal Register 19113, [ through the Government Printing Office at (202) 512-2249] as document number 2017-08363. [A74062-00001.)]

(T) Organic zinc specialty coating--Any coating derived from zinc dust incorporated into an organic binder that contains more than 960 grams of elemental zinc per liter (eight pounds per gallon) of coating, as applied, and that is used for the expressed purpose of corrosion protection.

(U) Pleasure craft--Any marine or fresh-water vessel used by individuals for noncommercial, nonmilitary, and recreational purposes that is less than 20 meters (65.6 feet) in length. A vessel rented exclusively to, or chartered for, individuals for such purposes shall be considered a pleasure craft.

(V) Pretreatment wash primer specialty coating--Any coating that contains a minimum of 0.5% acid by weight that is applied only to bare metal surfaces to etch the metal surface for corrosion resistance and adhesion of subsequent coatings.

(W) Repair and maintenance of thermoplastic coating of commercial vessels (specialty coating)--Any vinyl, chlorinated rubber, or bituminous resin coating that is applied over the same type of existing coating to perform the partial recoating of any in-use commercial vessel. (This definition does not include coal tar epoxy coatings, which are considered "general use" coatings.)

(X) Rubber camouflage specialty coating--Any specially formulated epoxy coating used as a camouflage topcoat for exterior submarine hulls and sonar domes.

(Y) Sealant for thermal spray aluminum--Any epoxy coating applied to thermal spray aluminum surfaces at a maximum thickness of one dry mil.

(Z) Ship--Any marine or fresh-water vessel, including self-propelled vessels, those propelled by other craft (barges), and navigational aids (buoys). This definition includes, but is not limited to, all military and Coast Guard vessels, commercial cargo and passenger (cruise) ships, ferries, barges, tankers, container ships, patrol and pilot boats, and dredges. Pleasure craft and offshore oil or gas drilling platforms are not considered ships.

(AA) Shipbuilding and ship repair operations--Any building, repair, repainting, converting, or alteration of ships or offshore oil or gas drilling platforms.

(BB) Special marking specialty coating--Any coating that is used for safety or identification applications, such as ship numbers and markings on flight decks.

(CC) Specialty interior coating--Any coating used on interior surfaces aboard United States military vessels pursuant to a coating specification that requires the coating to meet specified fire retardant and low toxicity requirements, in addition to the other applicable military physical and performance requirements.

(DD) Tack coat specialty coating--Any thin film epoxy coating applied at a maximum thickness of two dry mils to prepare an epoxy coating that has dried beyond the time limit specified by the manufacturer for the application of the next coat.

(EE) Undersea weapons systems specialty coating--Any coating applied to any component of a weapons system intended to be launched or fired from under the sea.

(FF) Weld-through preconstruction primer (specialty coating)--A coating that provides corrosion protection for steel during inventory, is typically applied at less than one mil dry film thickness, does not require removal prior to welding, is temperature resistant (burn back from a weld is less than 1.25 centimeters (0.5 inches)), and does not normally require removal before applying film-building coatings, including inorganic zinc high-build coatings. When constructing new vessels, there may be a need to remove areas of weld-through preconstruction primer due to surface damage or contamination prior to application of film-building coatings.

(12) Automobile and light-duty truck manufacturing.

(A) Automobile coating--The assembly-line coating of passenger cars, or passenger car derivatives, capable of seating 12 or fewer passengers.

(B) Light-duty truck coating--The assembly-line coating of motor vehicles rated at 8,500 pounds (3,855.5 kg) gross vehicle weight or less and designed primarily for the transportation of property, or derivatives such as pickups, vans, and window vans.

(13) Vehicle refinishing (body shops).

(A) Basecoat/clearcoat system--A topcoat system composed of a pigmented basecoat portion and a transparent clearcoat portion. The VOC content of a basecoat (BCCA-AG)/clearcoat (cc) system shall be calculated according to the following formula.

Figure: 30 TAC §115.420(c)(13)(A) (No change.)

(B) Precoat--Any coating that is applied to bare metal to deactivate the metal surface for corrosion resistance to a subsequent water-based primer. This coating is applied to bare metal solely for the prevention of flash rusting.

(C) Pretreatment--Any coating which contains a minimum of 0.5% acid by weight that is applied directly to bare metal surfaces to etch the metal surface for corrosion resistance and adhesion of subsequent coatings.

(D) Primer or primer surfacers--Any base coat, sealer, or intermediate coat which is applied prior to colorant or aesthetic coats.

(E) Sealers--Coatings that are formulated with resins which, when dried, are not readily soluble in typical solvents. These coatings act as a shield for surfaces over which they are sprayed by resisting the penetration of solvents which are in the final topcoat.

(F) Specialty coatings--Coatings or additives which are necessary due to unusual job performance requirements. These coatings or additives prevent the occurrence of surface defects and impart or improve desirable coating properties. These products include, but are not limited to, uniform finish blenders, elastomeric materials for coating of flexible plastic parts, coatings for non-metallic parts, jambing clear coatings, gloss flatteners, and anti-glare/safety coatings.

(G) Three-stage system--A topcoat system composed of a pigmented basecoat portion, a semitransparent midcoat portion, and a transparent clearcoat portion. The VOC content of a three-stage system shall be calculated according to the following formula:

Figure: 30 TAC §115.420(c)(13)(G) (No change.)

(H) Vehicle refinishing (body shops)--The coating of motor vehicles, as defined in §114.620 of this title (relating to Definitions), including, but not limited to, motorcycles, passenger cars, vans, light-duty trucks, medium-duty trucks, heavy-duty trucks, buses, and other vehicle body parts, bodies, and cabs by an operation other than the original manufacturer. The coating of non-road vehicles and non-road equipment, as these terms are defined in §114.3 and §114.6 of this title (relating to Low Emission Vehicle Fleet Definitions; and Low Emission Fuel Definitions), and trailers is not included.

(I) Wipe-down solutions--Any solution used for cleaning and surface preparation.

(14) Vinyl coating--The use of printing or any decorative or protective topcoat applied over vinyl sheets or vinyl-coated fabric.

(15) Wood parts and products. The following terms apply to wood parts and products coating facilities subject to §115.421(14) of this title.

(A) Clear coat--A coating which lacks opacity or which is transparent and uses the undercoat as a reflectant base or undertone color.

(B) Clear sealers--Liquids applied over stains, toners, and other coatings to protect these coatings from marring during handling and to limit absorption of succeeding coatings.

(C) Final repair coat--Liquids applied to correct imperfections or damage to the topcoat.

(D) Opaque ground coats and enamels--Colored, opaque liquids applied to wood or wood composition substrates which completely hide the color of the substrate in a single coat.

(E) Semitransparent spray stains and toners--Colored liquids applied to wood to change or enhance the surface without concealing the surface, including but not limited to, toners and nongrain-raising stains.

(F) Semitransparent wiping and glazing stains--Colored liquids applied to wood that require multiple wiping steps to enhance the grain character and to partially fill the porous surface of the wood.

(G) Shellacs--Coatings formulated solely with the resinous secretions of the lac beetle (laccifer lacca), thinned with alcohol, and formulated to dry by evaporation without a chemical reaction.

(H) Topcoat--A coating which provides the final protective and aesthetic properties to wood finishes.

(I) Varnishes--Clear wood finishes formulated with various resins to dry by chemical reaction on exposure to air.

(J) Wash coat--A low-solids clear liquid applied over semitransparent stains and toners to protect the color coats and to set the fibers for subsequent sanding or to separate spray stains from wiping stains to enhance color depth.

(K) Wood parts and products coating--The coating of wood parts and products, excluding factory surface coating of flat wood paneling.

(16) Wood furniture manufacturing facilities. The following terms apply to wood furniture manufacturing facilities subject to §115.421(15) of this title.

(A) Adhesive--Any chemical substance that is applied for the purpose of bonding two surfaces together other than by mechanical means. Adhesives are not considered to be coatings or finishing materials for wood furniture manufacturing facilities subject to §115.421(15) of this title.

(B) Basecoat--A coat of colored material, usually opaque, that is applied before graining inks, glazing coats, or other opaque finishing materials and is usually topcoated for protection.

(C) Cleaning operations--Operations in which organic solvent is used to remove coating materials from equipment used in wood furniture manufacturing operations.

(D) Continuous coater--A finishing system that continuously applies finishing materials onto furniture parts moving along a conveyor system. Finishing materials that are not transferred to the part are recycled to the finishing material reservoir. Several types of application methods can be used with a continuous coater, including spraying, curtain coating, roll coating, dip coating, and flow coating.

(E) Conventional air spray--A spray coating method in which the coating is atomized by mixing it with compressed air at an air pressure greater than 10 pounds per square inch gauge (psig) at the point of atomization. Airless and air-assisted airless spray technologies are not conventional air spray because the coating is not atomized by mixing it with compressed air. Electrostatic spray technology is also not conventional air spray because an electrostatic charge is employed to attract the coating to the workpiece. In addition, high-volume low-pressure (HVLP) spray technology is not conventional air spray because its pressure is less than 10 psig.

(F) Finishing application station--The part of a finishing operation where the finishing material is applied (for example, a spray booth).

(G) Finishing material--A coating used in the wood furniture industry. For the wood furniture manufacturing industry, such materials include, but are not limited to, basecoats, stains, washcoats, sealers, and topcoats.

(H) Finishing operation--Those activities in which a finishing material is applied to a substrate and is subsequently air-dried, cured in an oven, or cured by radiation.

(I) Organic solvent--A liquid containing VOCs that is used for dissolving or dispersing constituents in a coating; adjusting the viscosity of a coating; cleaning; or washoff. When used in a coating, the organic solvent evaporates during drying and does not become a part of the dried film.

(J) Sealer--A finishing material used to seal the pores of a wood substrate before additional coats of finishing material are applied. Washcoats, which are used in some finishing systems to optimize aesthetics, are not sealers.

(K) Stain--Any color coat having a solids content of no more than 8.0% by weight that is applied in single or multiple coats directly to the substrate. Includes, but is not limited to, nongrain raising stains, equalizer stains, sap stains, body stains, no-wipe stains, penetrating stains, and toners.

(L) Strippable booth coating--A coating that is applied to a booth wall to provide a protective film to receive overspray during finishing operations; is subsequently peeled off and disposed; and reduces or eliminates the need to use organic solvents to clean booth walls.

(M) Topcoat--The last film-building finishing material applied in a finishing system. A material such as a wax, polish, nonoxidizing oil, or similar substance that must be periodically reapplied to a surface over its lifetime to maintain or restore the reapplied material's intended effect is not considered to be a topcoat.

(N) Touch-up and repair--The application of finishing materials to cover minor finishing imperfections.

(O) Washcoat--A transparent special purpose coating having a solids content of 12% by weight or less. Washcoats are applied over initial stains to protect and control color and to stiffen the wood fibers in order to aid sanding.

(P) Washoff operations--Those operations in which organic solvent is used to remove coating from a substrate.

(Q) Wood furniture--Any product made of wood, a wood product such as rattan or wicker, or an engineered wood product such as particleboard that is manufactured under any of the following standard industrial classification codes: 2434 (wood kitchen cabinets), 2511 (wood household furniture, except upholstered), 2512 (wood household furniture, upholstered), 2517 (wood television, radios, phonograph and sewing machine cabinets), 2519 (household furniture not elsewhere classified), 2521 (wood office furniture), 2531 (public building and related furniture), 2541 (wood office and store fixtures, partitions, shelving and lockers), 2599 (furniture and fixtures not elsewhere classified), or 5712 (custom kitchen cabinets).

(R) Wood furniture component--Any part that is used in the manufacture of wood furniture. Examples include, but are not limited to, drawer sides, cabinet doors, seat cushions, and laminated tops. However, foam seat cushions manufactured and fabricated at a facility that does not engage in any other wood furniture or wood furniture component manufacturing operation are excluded from this definition.

(S) Wood furniture manufacturing operations--The finishing, cleaning, and washoff operations associated with the production of wood furniture or wood furniture components.

§115.421. Emission Specification.

The owner or operator of the surface coating processes specified in §115.420(a) of this title (relating to Applicability and Definitions) shall not cause, suffer, allow, or permit volatile organic compound (VOC) emissions to exceed the specified emission limits in paragraphs (1) - (16) of this subsection. These limitations are based on the daily weighted average of all coatings delivered to each coating line, except for those in paragraph (9) of this subsection which are based on paneling surface area, and those in paragraph (15) of this subsection which, if using an averaging approach, must use one of the daily averaging equations within that paragraph. The owner or operator of a surface coating operation subject to paragraph (10) of the subsection may choose to comply by using the monthly weighted average option as defined in §115.420(c)(1)(YY) of this title.

(1) Large appliance coating. VOC emissions from the application, flashoff, and oven areas during the coating of large appliances (prime and topcoat, or single coat) must not exceed 2.8 pounds per gallon of coating (minus water and exempt solvent) delivered to the application system (0.34 kilogram/liter (kg/liter)).

(2) Metal furniture coating. VOC emissions from metal furniture coating lines (prime and topcoat, or single coat) must not exceed 3.0 pounds per gallon of coating (minus water and exempt solvent) delivered to the application system (0.36 kg/liter).

(3) Coil coating. VOC emissions from the coating (prime and topcoat, or single coat) of metal coils must not exceed 2.6 pounds per gallon of coating (minus water and exempt solvent) delivered to the application system (0.31 kg/liter).

(4) Paper coating. VOC emissions from the coating of paper (or specified tapes or films) must not exceed 2.9 pounds per gallon of coating (minus water and exempt solvent) delivered to the application system (0.35 kg/liter).

(5) Fabric coating. [VOC emissions from the coating of fabric must not exceed 2.9 pounds per gallon of coating (minus water and exempt solvent) delivered to the application system (0.35 kg/liter).]

(A) In the Beaumont-Port Arthur, Dallas-Fort Worth, El Paso, and Houston-Galveston-Brazoria areas, in Gregg, Nueces, and Victoria Counties, and in Bexar County until March 1, 2026, VOC emissions from the coating of fabric must not exceed 350 grams per liter of coating (minus water and exempt solvent) delivered to the application system (2.9 pounds per gallon).

(B) In the Bexar County area, the following limits apply.

(i) VOC emissions from the application of coating or wash primer to fabric substrates must not exceed 265 grams per liter of coating (minus water and exempt solvent) delivered to the application system (2.2 pounds per gallon).

(ii) VOC emissions from the application of plastisol to fabric substrates must not exceed 20 grams per liter of coating (minus water and exempt solvent) delivered to the application system (0.167 pounds per gallon).

(6) Vinyl coating. VOC emissions from the coating of vinyl fabrics or sheets must not exceed 3.8 pounds per gallon of coating (minus water and exempt solvent) delivered to the application system (0.45 kg/liter). Plastisol coatings should not be included in calculations.

(7) Can coating. The following VOC emission limits must be achieved, on the basis of VOC solvent content per unit of volume of coating (minus water and exempt solvent) delivered to the application system:

Figure: 30 TAC §115.421(7) (No change.)

(8) Miscellaneous metal parts and products (MMPP) coating.

(A) VOC emissions from the coating of MMPP must not exceed the following limits for each surface coating type:

Figure: 30 TAC §115.421(8) (No change.)

(B) If more than one emission limitation in subparagraph (A) of this paragraph applies to a specific coating, then the least stringent emission limitation applies.

(C) All VOC emissions from non-exempt solvent washings must be included in determination of compliance with the emission limitations in subparagraph (A) of this paragraph unless the solvent is directed into containers that prevent evaporation into the atmosphere.

(9) Factory surface coating of flat wood paneling. The following emission limits apply to each product category of factory-finished paneling (regardless of the number of coats applied):

Figure: 30 TAC §115.421(9) (No change.)

(10) Aerospace coatings. The VOC content of coatings, including any VOC-containing materials added to the original coating supplied by the manufacturer, that are applied to aerospace vehicles or components must not exceed the following limits (in grams of VOC per liter of coating, less water and exempt solvent). The following applications are exempt from the VOC content limits of this paragraph: manufacturing or re-work of space vehicles or antique aerospace vehicles or components of each; touchup; United States Department of Defense classified coatings; and separate coating formulations in volumes less than 50 gallons per year to a maximum of 200 gallons per year for all such formulations at an account.

(A) For the broad categories of primers, topcoats, and chemical milling maskants (Type I/II) which are not specialty coatings as listed in subparagraph (B) of this paragraph:

(i) primer, 350;

(ii) topcoats (including self-priming topcoats), 420; and

(iii) chemical milling maskants:

(I) Type I, 622; and

(II) Type II, 160.

(B) For specialty coatings:

Figure: 30 TAC §115.421(10)(B) (No change.)

(11) Automobile and light-duty truck manufacturing coating. The following VOC emission limits must be achieved, on the basis of solvent content per unit volume of coating (minus water and exempt solvents) delivered to the application system or for primer surfacer and top coat application, compliance may be demonstrated on the basis of VOC emissions per unit volume of solids deposited as determined by §115.425(3) of this title (relating to Testing Requirements).

Figure: 30 TAC §115.421(11) (No change.)

(12) Vehicle refinishing coating (body shops). VOC emissions from coatings or solvents must not exceed the following limits, as delivered to the application system. Additional control requirements for vehicle refinishing (body shops) are referenced in §115.422 of this title (relating to Control Requirements).

Figure: 30 TAC §115.421(12) (No change.)

(13) Surface coating of mirror backing.

(A) VOC emissions from the coating of mirror backing must not exceed the following limits for each surface coating application method:

(i) 4.2 pounds per gallon (0.50 kg/liter) of coating (minus water and exempt solvent) delivered to a curtain coating application system; and

(ii) 3.6 pounds per gallon (0.43 kg/liter) of coating (minus water and exempt solvent) delivered to a roll coating application system.

(B) All VOC emissions from solvent washings must be included in determination of compliance with the emission limitations in subparagraph (A) of this paragraph, unless the solvent is directed into containers that prevent evaporation into the atmosphere.

(14) Surface coating of wood parts and products. VOC emissions from the coating of wood parts and products must not exceed the following limits, as delivered to the application system, for each surface coating type. All VOC emissions from solvent washings must be included in determination of compliance with the emission limitations in this paragraph, unless the solvent is directed into containers that prevent evaporation into the atmosphere.

Figure: 30 TAC §115.421(14) (No change.)

(15) Surface coating at wood furniture manufacturing facilities. For facilities which are subject to this paragraph, adhesives are not considered to be coatings or finishing materials.

(A) VOC emissions from finishing operations must be limited by:

(i) using topcoats with a VOC content no greater than 0.8 kilogram of VOC per kilogram of solids (0.8 pound of VOC per pound of solids), as delivered to the application system; or

(ii) using a finishing system of sealers with a VOC content no greater than 1.9 kilograms of VOC per kilogram of solids (1.9 pounds of VOC per pound of solids), as applied, and topcoats with a VOC content no greater than 1.8 kilograms of VOC per kilogram of solids (1.8 pounds of VOC per pound of solids), as delivered to the application system; or

(iii) for wood furniture manufacturing facilities using acid-cured alkyd amino vinyl sealers or acid-cured alkyd amino conversion varnish topcoats, using sealers and topcoats that meet the following criteria:

(I) if the wood furniture manufacturing facility uses acid-cured alkyd amino vinyl sealers and acid-cured alkyd amino conversion varnish topcoats, the sealer must contain no more than 2.3 kilograms of VOC per kilogram of solids (2.3 pounds of VOC per pound of solids), as applied, and the topcoat must contain no more than 2.0 kilograms of VOC per kilogram of solids (2.0 pounds of VOC per pound of solids), as delivered to the application system; or

(II) if the wood furniture manufacturing facility uses a sealer other than an acid-cured alkyd amino vinyl sealer and acid-cured alkyd amino conversion varnish topcoats, the sealer must contain no more than 1.9 kilograms of VOC per kilogram of solids (1.9 pounds of VOC per pound of solids), as applied, and the topcoat must contain no more than 2.0 kilograms of VOC per kilogram of solids (2.0 pounds of VOC per pound of solids), as delivered to the application system; or

(III) if the wood furniture manufacturing facility uses an acid-cured alkyd amino vinyl sealer and a topcoat other than an acid-cured alkyd amino conversion varnish topcoat, the sealer must contain no more than 2.3 kilograms of VOC per kilogram of solids (2.3 pounds of VOC per pound of solids), as applied, and the topcoat must contain no more than 1.8 kilograms of VOC per kilogram of solids (1.8 pounds of VOC per pound of solids), as delivered to the application system; or

(iv) using an averaging approach and demonstrating that actual daily emissions from the wood furniture manufacturing facility are less than or equal to the lower of the actual versus allowable emissions using one of the following inequalities:

Figure: 30 TAC §115.421(15)(A)(iv) (No change.)

(v) using a vapor control system that will achieve an equivalent reduction in emissions as the requirements of clauses (i) or (ii) of this subparagraph. If this option is used, the requirements of §115.423(3) of this title do not apply; or

(vi) using a combination of the methods presented in clauses (i) - (v) of this subparagraph.

(B) Strippable booth coatings used in cleaning operations must not contain more than 0.8 kilogram of VOC per kilogram of solids (0.8 pound of VOC per pound of solids), as delivered to the application system.

(16) Marine coatings.

(A) The following VOC emission limits apply to the surface coating of ships and offshore oil or gas drilling platforms at shipbuilding and ship repair operations, and are based upon the VOC content of the coatings as delivered to the application system.

Figure: 30 TAC §115.421(16)(A) (No change.)

(B) For a coating to which thinning solvent is routinely or sometimes added, the owner or operator shall determine the VOC content as follows.

(i) Prior to the first application of each batch, designate a single thinner for the coating and calculate the maximum allowable thinning ratio (or ratios, if the shipbuilding and ship repair operation complies with the cold-weather limits in addition to the other limits specified in subparagraph (A) of this paragraph) for each batch as follows.

Figure: 30 TAC §115.421(16)(B)(i) (No change.)

(ii) If the volume fraction of solids in the batch as supplied Vs is not supplied directly by the coating manufacturer, the owner or operator shall determine Vs as follows.

Figure: 30 TAC §115.421(16)(B)(ii) (No change.)

§115.425. Testing Requirements.

The testing requirements for surface coating processes in the Beaumont-Port Arthur, Bexar County, Dallas-Fort Worth, El Paso, and Houston-Galveston-Brazoria areas and in Gregg, Nueces, and Victoria Counties are as follows.

(1) The owner or operator shall determine compliance with §115.421 of this title (relating to Emission Specifications) by applying the following test methods, as appropriate, except as specified in paragraph (5) of this section. Where a test method also inadvertently measures compounds that are exempt solvent, an owner or operator may exclude these exempt solvents when determining compliance with an emission standard:

(A) Test Method 24 (40 Code of Federal Regulations (CFR) Part 60, Appendix A) with a one-hour bake;

(B) ASTM International Test Methods D1186, D1200, D1644, D2832, D3794, and D3960 [D 1186-06.01, D 1200-06.01, D 3794-06.01, D 2832-69, D 1644-75, and D 3960-81];

(C) The United States Environmental Protection Agency (EPA) guidelines series document "Procedures for Certifying Quantity of Volatile Organic Compounds (VOC) Emitted by Paint, Ink, and Other Coatings (EPA-450/3-84-019)," as in effect December, 1984;

(D) additional test procedures described in 40 Code of Federal Regulations (CFR) §60.446; or

(E) minor modifications to these test methods approved by the executive director

(2) Compliance with §115.423(3) of this title (relating to Alternate Control Requirements) must be determined by applying the following test methods, as appropriate:

(A) Test Methods 1-4 (40 CFR Part 60, Appendix A) for determining flow rates, as necessary;

(B) Test Method 25 (40 CFR Part 60, Appendix A) for determining total gaseous nonmethane organic emissions as carbon;

(C) Test Method 25A or 25B (40 CFR Part 60, Appendix A) for determining total gaseous organic concentrations using flame ionization or nondispersive infrared analysis;

(D) additional performance test procedures described in 40 CFR §60.044; or

(E) minor modifications to these test methods approved by the executive director.

(3) Compliance with the alternative emission limits in §115.421(11) of this title must be determined by applying the following test methods, as appropriate:

(A) Protocol for Determining the Daily VOC Emission Rate of Automobile and Light-Duty Truck Topcoat Operations (EPA 450/3-88-018); or

(B) The procedure contained in this paragraph for determining daily compliance with the alternative emission limitation in §115.421(11) of this title for final repair. Calculation of occurrence weighted average for each combination of repair coatings (primer, specific basecoat, clearcoat) must be determined by the following procedure.

(i) The characteristics identified below, which are represented in the following equations by the variables shown, are established for each repair material as sprayed:

Figure: 30 TAC §115.425(3)(B)(i) (No change.)

(ii) The relative occurrence weighted usage is calculated as follows:

Figure: 30 TAC §115.425(3)(B)(ii) (No change.)

(iii) The occurrence weighted average (Q) in pounds of VOC per gallon of coating (minus water and exempt solvents) as applied for each potential combination of repair coatings is calculated according to paragraph (4) of this section.

Figure: 30 TAC §115.425(3)(B)(iii) (No change.)

(4) In the Beaumont-Port Arthur, Bexar County, Dallas-Fort Worth, El Paso, and Houston-Galveston-Brazoria areas, the owner or operator of surface coating processes subject to §115.423(3) of this title shall measure the capture efficiency using applicable procedures outlined in 40 CFR §52.741, Subpart O, Appendix B. These procedures are: Procedure T-Criteria for and Verification of a Permanent or Temporary Total Enclosure; Procedure L-VOC Input; Procedure G.2-Captured VOC Emissions (Dilution Technique); Procedure F.1-Fugitive VOC Emissions from Temporary Enclosures; and Procedure F.2-Fugitive VOC Emissions from Building Enclosures.

(A) Exemptions to capture efficiency testing requirements:

(i) If a source installs a permanent total enclosure (PTE) that meets the specifications of Procedure T and directs all VOC to a control device, then the capture efficiency is assumed to be 100%, and the source is exempted from capture efficiency testing requirements. This does not exempt the source from performance of any control device efficiency testing that may be required. In addition, a source must demonstrate all criteria for a PTE are met during testing for control efficiency.

(ii) If a source uses a control device designed to collect and recover VOC (e.g., carbon adsorption system), an explicit measurement of capture efficiency is not necessary if the following conditions are met. The overall control of the system can be determined by directly comparing the input liquid VOC to the recovered liquid VOC. The general procedure for use in this situation is given in 40 CFR §60.433, with the following additional restrictions.

(I) The source must be able to equate solvent usage with solvent recovery on a 24-hour (daily) basis, rather than a 30-day weighted average. This must be done within 72 hours following each 24-hour period of the 30-day period.

(II) The solvent recovery system (i.e., capture and control system) must be dedicated to a single process line (e.g., one process line venting to a carbon adsorber system); or if the solvent recovery system controls multiple process lines, the source must be able to demonstrate that the overall control (i.e., the total recovered solvent VOC divided by the sum of liquid VOC input to all process lines venting to the control system) meets or exceeds the most stringent standard applicable for any process line venting to the control system.

(B) The capture efficiency must be calculated using one of the following four protocols referenced. Any affected source must use one of these protocols, unless a suitable alternative protocol is approved by the executive director and the EPA.

(i) Gas/gas method using Temporary Total Enclosure (TTE). The EPA specifications to determine whether a temporary enclosure is considered a TTE are given in Procedure T. The capture efficiency equation to be used for this protocol is:

Figure: 30 TAC §115.425(4)(B)(i) (No change.)

(ii) Liquid/gas method using TTE. The EPA specifications to determine whether a temporary enclosure is considered a TTE are given in Procedure T. The capture efficiency equation to be used for this protocol is:

Figure: 30 TAC §115.425(4)(B)(ii) (No change.)

(iii) Gas/gas method using the building or room in which the affected source is located as the enclosure (BE) and in which G and F are measured while operating only the affected facility. All fans and blowers in the BE must be operating as they would under normal production. The capture efficiency equation to be used for this protocol is:

Figure: 30 TAC §115.425(4)(B)(iii) (No change.)

(iv) Liquid/gas method using a BE in which L and F are measured while operating only the affected facility. All fans and blowers in the building or room must be operated as they would under normal production. The capture efficiency equation to be used for this protocol is:

Figure: 30 TAC §115.425(4)(B)(iv) (No change.)

(C) The following conditions must be met in measuring capture efficiency:

(i) Any error margin associated with a test protocol may not be incorporated into the results of a capture efficiency test.

(ii) All affected facilities must accomplish the initial capture efficiency testing by July 31, 1992, in Brazoria, Dallas, El Paso, Galveston, Harris, Jefferson, Orange, and Tarrant Counties, and by July 31, 1993, in Chambers, Collin, Denton, Fort Bend, Hardin, Liberty, Montgomery, and Waller Counties, except that all mirror backing coating facilities must accomplish the initial capture efficiency testing by July 31, 1994. Affected sources in the Bexar County area must conduct initial capture efficiency testing by no later than July 1, 2024.

(iii) During an initial pretest meeting, the executive director and the source owner or operator shall identify those operating parameters that must be monitored to ensure that capture efficiency does not change significantly over time. These parameters must be monitored and recorded initially during the capture efficiency testing and thereafter during facility operation. The executive director may require a new capture efficiency test if the operating parameter values change significantly from those recorded during the initial capture efficiency test.

(5) The following additional testing requirements apply to each aerospace vehicle or component coating facility subject to §115.421(10) of this title.

(A) For coatings which are not waterborne (water-reducible), determine the VOC content of each formulation (less water and less exempt solvents) as applied using manufacturer's supplied data or Method 24 of 40 CFR Part 60, Appendix A. If there is a discrepancy between the manufacturer's formulation data and the results of the Method 24 analysis, compliance must be based on the results from the Method 24 analysis. For water-borne (water-reducible) coatings, manufacturer's supplied data alone can be used to determine the VOC content of each formulation.

(B) For aqueous and semiaqueous cleaning solvents, manufacturers' supplied data must be used to determine the water content.

(C) For hand-wipe cleaning solvents, manufacturers' supplied data or standard engineering reference texts or other equivalent methods shall be used to determine the vapor pressure or VOC composite vapor pressure for blended cleaning solvents.

(D) Except for specialty coatings, compliance with the test method requirements of 40 CFR §63.750, (National Emission Standards for Aerospace Manufacturing and Rework Facilities), is considered to represent compliance with the requirements of this section.

(6) Test methods other than those specified in paragraphs (1) - (5) of this section may be used if validated by 40 CFR Part 63, Appendix A, Test Method 301. For the purposes of this paragraph, substitute "executive director" each place that Test Method 301 references "administrator."

§115.427. Exemptions.

In the Beaumont-Port Arthur, Bexar County, Dallas-Fort Worth, El Paso, and Houston-Galveston-Brazoria areas, as defined in §115.10 of this title (relating to Definitions) and in Gregg, Nueces, and Victoria Counties the following exemptions apply.

(1) The following coating operations are exempt from the miscellaneous metal parts and products surface coating emission specifications in §115.421(8) of this title (relating to Emission Specifications):

(A) aerospace vehicles and components;

(B) in the Bexar County, Dallas-Fort Worth, El Paso, and Houston-Galveston-Brazoria areas, vehicle refinishing (body shops); and

(C) in the Beaumont-Port Arthur and Houston-Galveston-Brazoria areas, ships and offshore oil or gas drilling platforms.

(2) The following coating operations are exempt from the factory surface coating of flat wood paneling emission specifications in §115.421(9) of this title:

(A) the manufacture of exterior siding;

(B) tile board; or

(C) particle board used as a furniture component.

(3) In the Beaumont-Port Arthur, Bexar County, Dallas-Fort Worth, El Paso, and Houston-Galveston-Brazoria areas, the following exemptions apply to surface coating processes, except as specified in paragraphs (3)(K) and (6) of this section, and except for vehicle refinishing (body shops) controlled by §115.421(12) of this title. Excluded from the volatile organic compounds (VOC) emission calculations are coatings and solvents used in surface coating activities that are not addressed by the surface coating categories of §115.421(1) - (16) or §115.453 of this title (relating to Control Requirements). For example, architectural coatings [(i.e., coatings that are] applied in the field to stationary structures and their appurtenances, [to] portable buildings, [to] pavements, or [to] curbs[)] at a property would not be included in the calculations.

(A) Surface coating operations on a property that, when uncontrolled, will emit a combined weight of VOC of less than 3.0 pounds per hour and 15 pounds in any consecutive 24-hour period are exempt from §115.421 of this title and §115.423 of this title (relating to Alternate Control Requirements).

(B) Surface coating operations on a property that, when uncontrolled, will emit a combined weight of VOC of less than 100 pounds in any consecutive 24-hour period are exempt from §115.421 and §115.423 of this title if documentation is provided to and approved by both the executive director and the United States Environmental Protection Agency to demonstrate that necessary coating performance criteria cannot be achieved with coatings that satisfy applicable emission specifications and that control equipment is not technically or economically feasible.

(C) Surface coating operations on a property for which total coating and solvent usage does not exceed 150 gallons in any consecutive 12-month period are exempt from §115.421 and §115.423 of this title.

(D) Mirror backing coating operations located on a property that, when uncontrolled, emit a combined weight of VOC less than 25 tons in one year (based on historical coating and solvent usage) are exempt from this division.

(E) Wood furniture manufacturing facilities that are subject to and are complying with §115.421(15) of this title and §115.422(3) of this title (relating to Control Requirements) are exempt from §115.421(14) of this title. These wood furniture manufacturing facilities must continue to comply with §115.421(14) of this title until these facilities are in compliance with §115.421(15) and §115.422(3) of this title.

(F) Wood furniture manufacturing facilities that, when uncontrolled, emit a combined weight of VOC from wood furniture manufacturing operations less than 25 tons per year (tpy) are exempt from §115.421(15) and §115.422(3) of this title.

(G) In Hardin, Jefferson, and Orange Counties, wood parts and products coating facilities are exempt from §115.421(14) of this title.

(H) In Hardin, Jefferson, and Orange Counties, shipbuilding and ship repair operations that, when uncontrolled, emit a combined weight of VOC from ship and offshore oil or gas drilling platform surface coating operations less than 50 tpy are exempt from §115.421(16) and §115.422(4) of this title.

(I) In Brazoria, Chambers, Fort Bend, Galveston, Harris, Liberty, Montgomery, and Waller Counties, shipbuilding and ship repair operations that, when uncontrolled, emit a combined weight of VOC from ship and offshore oil or gas drilling platform surface coating operations less than 25 tpy are exempt from §115.421(16) and §115.422(4) of this title.

(J) The following activities where cleaning and coating of aerospace vehicles or components may take place are exempt from this division: research and development, quality control, laboratory testing, and electronic parts and assemblies, except for cleaning and coating of completed assemblies.

(K) Beginning March 1, 2026, fabric coating operations in the Bexar County area are no longer eligible for the exemptions in subparagraphs (3)(A) - (C) of this subsection.

(4) Vehicle refinishing (body shops) in Hardin, Jefferson, and Orange Counties are exempt from §115.421(12) and §115.422(1) and (2) of this title.

(5) The coating of vehicles at in-house (fleet) vehicle refinishing operations and the coating of vehicles by private individuals are exempt from §115.421(11)(B) and §115.422(1) and (2) of this title. This exemption is not applicable if the coating of a vehicle by a private individual occurs at a commercial operation.

(6) Aerosol coatings (spray paint) are exempt from this division. However, in the Bexar County area, aerosol coatings, commonly known as spray paint, are no longer exempt from the requirements for fabric coating operations as of the compliance date specified in §115.429(g) of this title.

(7) In Gregg, Nueces, and Victoria Counties, surface coating operations located at any property that, when uncontrolled, will emit a combined weight of VOC less than 550 pounds (249.5 kilograms) in any continuous 24-hour period are exempt from §115.421 of this title. Excluded from this calculation are coatings and solvents used in surface coating activities that are not addressed by the surface coating categories of §115.421(1) - (10) of this title. For example, architectural coatings (i.e., coatings that are applied in the field to stationary structures and their appurtenances, to portable buildings, to pavements, or to curbs) at a property would not be included in the calculation.

(8) In the Dallas-Fort Worth and Houston-Galveston-Brazoria areas, the following surface coating categories that are subject to the requirements of Chapter 115, Subchapter E, Division 5 of this title (relating to Control Requirements for Surface Coating Processes) are exempt from the requirements in this division:

(A) large appliance coating;

(B) metal furniture coating;

(C) miscellaneous metal parts and products coating;

(D) each paper coating line with the potential to emit equal to or greater than 25 tpy of VOC from all coatings applied; and

(E) automobile and light-duty truck manufacturing coating.

(9) In the Dallas-Fort Worth and the Houston-Galveston-Brazoria areas, the re-coating of used miscellaneous metal parts and products at a designated on-site maintenance shop that was exempt from §115.421(8) of this title prior to January 1, 2012, or that begins operation on or after January 1, 2012, is exempt from all requirements in this division. The re-coating of used miscellaneous metal parts and products at a designated on-site maintenance shop that was subject to §115.421(8) of this title prior to January 1, 2012, remains subject to this division. For purposes of this exemption, a designated on-site maintenance shop is an area at a site where used miscellaneous metal parts or products are re-coated on a routine basis. Miscellaneous metal parts and products coating processes in Wise County are not subject to this division.

§115.429. Counties and Compliance Schedules.

(a) In Brazoria, Chambers, Collin, Dallas, Denton, Ellis, El Paso, Fort Bend, Galveston, Gregg, Hardin, Harris, Jefferson, Johnson, Kaufman, Liberty, Montgomery, Nueces, Orange, Parker, Rockwall, Tarrant, Victoria, and Waller Counties, the compliance date has passed and the owner or operator of a surface coating process shall continue to comply with this division.

(b) In Hardin, Jefferson, and Orange Counties the compliance date has passed and the owner or operator of each shipbuilding and ship repair operation that, when uncontrolled, emits a combined weight of volatile organic compounds from ship and offshore oil or gas drilling platform surface coating operations equal to or greater than 50 tons per year and less than 100 tons per year shall continue to comply with this division.

(c) The owner or operator of a paper surface coating process located in the Dallas-Fort Worth area, except Wise County, and Houston-Galveston-Brazoria area, as defined in §115.10 of this title (relating to Definitions), shall comply with the requirements in §115.422(7) of this title (relating to Control Requirements), no later than March 1, 2013.

(d) The owner or operator of a surface coating process in Wise County shall comply with the requirements in this division as soon as practicable, but no later than January 1, 2017.

(e) The owner or operator of a surface coating process that becomes subject to this division on or after the applicable compliance date of this section shall comply with the requirements in this division no later than 60 days after becoming subject. [The owner or operator of a surface coating process in Collin, Dallas, Denton, Ellis, Johnson, Kaufman, Parker, Rockwall, Tarrant, and Wise Counties that becomes subject to this division on or after the applicable compliance date in this section shall comply with the requirements in this division as soon as practicable, but no later than 60 days after becoming subject.]

(f) The owner or operator of a surface coating process in the Bexar County area subject to the requirements of this division shall comply with the requirements of this division, with the exception of §115.421(5)(B) of this title (relating to Emission Specification), no later than January 1, 2025. [All affected persons of a surface coating process in the Bexar County area that becomes subject to this division on or after the applicable compliance date in this subsection shall comply with the requirements of this division as soon as practicable, but no later than 60 days after becoming subject.]

(g) The owner or operator of a fabric coating process in the Bexar County area subject to the requirements of §115.421 of this title shall comply with the requirements in §115.421(5)(B) of this title no later than March 1, 2026.

The agency certifies that legal counsel has reviewed the proposal and found it to be within the state agency's legal authority to adopt.

Filed with the Office of the Secretary of State on July 11, 2025.

TRD-202502440

Charmaine Backens

Deputy Director, Environmental Law Division

Texas Commission on Environmental Quality

Earliest possible date of adoption: August 24, 2025

For further information, please call: (512) 239-2678


DIVISION 4. OFFSET LITHOGRAPHIC PRINTING

30 TAC §§115.440, 115.441, 115.449

Statutory Authority

The amendments are proposed under Texas Water Code (TWC), §5.102, concerning general powers; §5.103, concerning Rules; TWC, §5.105, concerning General Policy, which authorize the commission to adopt rules necessary to carry out its powers and duties under the TWC; TWC, §7.002, concerning Enforcement Authority, which authorizes the commission to enforce the provisions of the Water Code and the Health and Safety Code within the commission's jurisdiction; and under Texas Health and Safety Code (THSC), §382.017, concerning Rules, which authorizes the commission to adopt rules consistent with the policy and purpose of the Texas Clean Air Act.

The amendments are also proposed under THSC, §382.002, concerning Policy and Purpose, which establishes the commission's purpose to safeguard the state's air resources, consistent with the protection of public health, general welfare, and physical property; THSC, §382.011, concerning General Powers and Duties, which authorizes the commission to control the quality of the state's air; THSC, §382.012, concerning the State Air Control Plan, which authorizes the commission to prepare and develop a general, comprehensive plan for the proper control of the state's air; THSC, §382.016, concerning Monitoring Requirements; Examination of Records, which authorizes the commission to prescribe reasonable requirements for measuring and monitoring the emissions of air contaminants; and THSC, §382.021, concerning Sampling Methods and Procedures.

The proposed amendments implement TWC, §§5.102, 5.103, and 7.002; and THSC, §§382.002, 382.011, 382.012, 382.016, 382.017, and 382.021.

§115.440. Applicability and Definitions.

(a) Applicability. The provisions in this division apply to offset lithographic printing lines located in the Bexar County, Dallas-Fort Worth, El Paso, and Houston-Galveston-Brazoria areas, as defined in §115.10 of this title (relating to Definitions).

(b) Definitions. Unless specifically defined in the Texas Clean Air Act (Texas Health and Safety Code, Chapter 382) or in §§3.2, 101.1, and 115.10 of this title (relating to Definitions), the terms in this division have the meanings commonly used in the field of air pollution control. In addition, the following meanings apply unless the context clearly indicates otherwise.

(1) Alcohol--Any of the hydroxyl-containing organic compounds with a molecular weight equal to or less than 74.12, which includes methanol, ethanol, propanol, and butanol.

(2) Alcohol substitutes--Nonalcohol additives that contain volatile organic compounds and are used in the fountain solution to reduce the surface tension of water or prevent ink piling.

(3) Batch--A supply of fountain solution or cleaning solution that is prepared and used without alteration until completely used or removed from the printing process.

(4) Cleaning solution--Liquids used to remove ink and debris from the operating surfaces of the printing press and its parts.

(5) Fountain solution--A mixture of water, nonvolatile printing chemicals, and a liquid additive that reduces the surface tension of the water so that it spreads easily across the printing plate surface. The fountain solution wets the non-image areas so that the ink is maintained within the image areas.

(6) Heatset--Any operation where heat is required to evaporate ink oil from the printing ink.

(7) Lithography--A plane-o-graphic printing process where the image and non-image areas are on the same plane of the printing plate. The image and non-image areas are chemically differentiated so the image area is oil receptive and the non-image area is water receptive.

(8) Major printing source--All offset lithographic printing lines located on a property with combined uncontrolled emissions of volatile organic compounds (VOC) greater than or equal to:

(A) 50 tons of VOC per calendar year before and 25 tons of VOC per calendar year on and after November 7, 2025, in the Dallas-Fort Worth area as defined in §115.10 of this title (relating to Definitions), except Wise County;

(B) 25 tons of VOC per calendar year in the Houston-Galveston-Brazoria area, as defined in §115.10 of this title;

(C) 100 tons of VOC per calendar year before and 25 tons of VOC per calendar year on and after November 7, 2025, in Wise County; or

(D) 100 tons of VOC per calendar year before and 50 tons of VOC per calendar year on and after March 1, 2026, [ on and after January 1, 2025] in the Bexar County area.

(9) Minor printing source--All offset lithographic printing lines located on a property with combined uncontrolled emissions of volatile organic compounds (VOC) less than:

(A) 50 tons of VOC per calendar year before and 25 tons of VOC per calendar year on and after November 7, 2025, in the Dallas-Fort Worth area, defined in §115.10 of this title (relating to Definitions), except Wise County;

(B) 25 tons of VOC per calendar year in the Houston-Galveston-Brazoria area, as defined in §115.10 of this title;

(C) 100 tons of VOC per calendar year before and 25 tons of VOC per calendar year on and after November 7, 2025, in Wise County; or

(D) 100 tons of VOC per calendar year before and 50 tons of VOC per calendar year on and after March 1, 2026, [ on and after January 1, 2025,] in the Bexar County area.

(10) Non-heatset--Any operation where the printing inks are set without the use of heat. For the purposes of this division, ultraviolet-cured and electron beam-cured inks are considered non-heatset.

(11) Offset lithography--A printing process that transfers the ink film from the lithographic plate to an intermediary surface (blanket) that, in turn, transfers the ink film to the substrate.

(12) Volatile organic compound (VOC) composite partial pressure--The sum of the partial pressures of the compounds that meet the definition of VOC in §101.1 of this title (relating to Definitions). The VOC composite partial pressure is calculated as follows.

Figure: 30 TAC §115.440(b)(12) (No change.)

§115.441. Exemptions.

(a) In the Bexar County, Dallas-Fort Worth, and Houston-Galveston-Brazoria areas, as defined in §115.10 of this title (relating to Definitions), the owner or operator of all offset lithographic printing lines located on a property with combined emissions of volatile organic compounds less than 3.0 tons per calendar year when uncontrolled, is exempt from the requirements in this division except as specified in subsection (b)(1) of this section and §115.446 of this title (relating to Monitoring and Recordkeeping Requirements).

(b) In the Bexar County, Dallas-Fort Worth and Houston-Galveston-Brazoria areas, the owner or operator of a minor printing source, as defined in §115.440 of this title (relating to Applicability and Definitions) and in Wise County, the owner or operator of a minor printing source or a major printing source, as defined in §115.440 of this title:

(1) may exempt up to 110 gallons of cleaning solution per calendar year from the content limits in §115.442(c)(1) of this title (relating to Control Requirements), though as of March 1, 2026, this exemption no longer applies in Bexar County;

(2) may exempt any press with a total fountain solution reservoir less than 1.0 gallons from the fountain solution content limits in §115.442(c)(2) - (4) of this title; and

(3) may exempt any sheet-fed press with a maximum sheet size of 11.0 inches by 17.0 inches or less from the fountain solution content limits in §115.442(c)(2) of this title.

§115.449. Compliance Schedules.

(a) In the El Paso area, the owner or operator of all offset lithographic printing presses must be in compliance with §§115.442, 115.443, 115.445, and 115.446 of this title (relating to Control Requirements; Alternate Control Requirements; Approved Test Methods; and Monitoring and Recordkeeping Requirements) as soon as practicable, but no later than November 15, 1996.

(b) In Collin, Dallas, Denton, and Tarrant Counties, the owner or operator of all offset lithographic printing presses on a property that, when uncontrolled, emit a combined weight of volatile organic compounds (VOC) equal to or greater than 50 tons per calendar year, must be in compliance with §§115.442(a), 115.443, 115.445, and 115.446(a) of this title as soon as practicable, but no later than December 31, 2000.

(c) In Brazoria, Chambers, Fort Bend, Galveston, Harris, Liberty, Montgomery, and Waller Counties, the owner or operator of all offset lithographic printing presses on a property that, when uncontrolled, emit a combined weight of VOC equal to or greater than 25 tons per calendar year, must be in compliance with §§115.442(a), 115.443, 115.445, and 115.446(a) of this title as soon as practicable, but no later than December 31, 2002.

(d) In Ellis, Johnson, Kaufman, Parker, and Rockwall Counties, the owner or operator of all offset lithographic printing presses on a property that, when uncontrolled, emit a combined weight of VOC equal to or greater than 50 tons per calendar year, shall comply with §§115.442(a), 115.443, 115.445, and 115.446(a) of this title as soon as practicable, but no later than March 1, 2009.

(e) The owner or operator of a major printing source, as defined in §115.440 of this title (relating to Applicability and Definitions), in Brazoria, Chambers, Collin, Dallas, Denton, Ellis, Fort Bend, Galveston, Harris, Johnson, Kaufman, Liberty, Montgomery, Parker, Rockwall, Tarrant, and Waller Counties, as defined in §115.10 of this title (relating to Definitions), shall comply with the requirements in this division no later than March 1, 2011, except as specified in subsections (b), (c), and (d) of this section.

(f) The owner or operator of a minor printing source, as defined in §115.440 of this title, in the Brazoria, Chambers, Collin, Dallas, Denton, Ellis, Fort Bend, Galveston, Harris, Johnson, Kaufman, Liberty, Montgomery, Parker, Rockwall, Tarrant, and Waller Counties, shall comply with the requirements in this division no later than March 1, 2012.

(g) The owner or operator of a major or minor printing source, as defined in §115.440 of this title, in Wise County, shall comply with the requirements in this division as soon as practicable, but no later than January 1, 2017.

(h) The owner or operator of a major or minor printing source, as defined in §115.440 of this title, in the Bexar County area subject to the requirements of this division shall comply with the requirements of this division no later than January 1, 2025.

(i) The owner or operator of an offset lithographic printing line in Brazoria, Bexar, Chambers, Collin, Dallas, Denton, Ellis, Fort Bend, Galveston, Harris, Johnson, Kaufman, Liberty, Montgomery, Parker, Rockwall, Tarrant, Waller, and Wise Counties that becomes subject to this division on or after the date specified in subsections (e) - (h) of this section, shall comply with the requirements in this division no later than 60 days after becoming subject.

(j) The owner or operator of a major or minor printing source, as defined in §115.440(b)(8)(D) and §115.440(b)(9)(D) of this title, in the Bexar County area subject to the requirements of this division shall comply with the requirements of this division no later than March 1, 2026.

The agency certifies that legal counsel has reviewed the proposal and found it to be within the state agency's legal authority to adopt.

Filed with the Office of the Secretary of State on July 11, 2025.

TRD-202502441

Charmaine Backens

Deputy Director, Environmental Law Division

Texas Commission on Environmental Quality

Earliest possible date of adoption: August 24, 2025

For further information, please call: (512) 239-2678


DIVISION 5. CONTROL REQUIREMENTS FOR SURFACE COATING PROCESSES

30 TAC §§115.450, 115.451, 115.453, 115.455, 115.458, 115.459

Statutory Authority

The amendments are proposed under Texas Water Code (TWC), §5.102, concerning general powers; §5.103, concerning Rules; TWC, §5.105, concerning General Policy, which authorize the commission to adopt rules necessary to carry out its powers and duties under the TWC; TWC, §7.002, concerning Enforcement Authority, which authorizes the commission to enforce the provisions of the Water Code and the Health and Safety Code within the commission's jurisdiction; and under Texas Health and Safety Code (THSC), §382.017, concerning Rules, which authorizes the commission to adopt rules consistent with the policy and purpose of the Texas Clean Air Act.

The amendments are also proposed under THSC, §382.002, concerning Policy and Purpose, which establishes the commission's purpose to safeguard the state's air resources, consistent with the protection of public health, general welfare, and physical property; THSC, §382.011, concerning General Powers and Duties, which authorizes the commission to control the quality of the state's air; THSC, §382.012, concerning the State Air Control Plan, which authorizes the commission to prepare and develop a general, comprehensive plan for the proper control of the state's air; THSC, §382.016, concerning Monitoring Requirements; Examination of Records, which authorizes the commission to prescribe reasonable requirements for measuring and monitoring the emissions of air contaminants; and THSC, §382.021, concerning Sampling Methods and Procedures.

The proposed amendments implement TWC, §§5.102, 5.103, and 7.002; and THSC, §§382.002, 382.011, 382.012, 382.016, 382.017, and 382.021.

§115.450. Applicability and Definitions.

(a) Applicability. In the Bexar County, Dallas-Fort Worth and Houston-Galveston-Brazoria areas, as defined in §115.10 of this title (relating to Definitions), the requirements in this division apply to the following surface coating processes, except as specified in paragraphs (6) through (10) [(8)] of this subsection:

(1) large appliance surface coating;

(2) metal furniture surface coating;

(3) miscellaneous metal parts and products surface coating, miscellaneous plastic parts and products surface coating, pleasure craft surface coating, and automotive/transportation and business machine plastic parts surface coating at the original equipment manufacturer and off-site job shops that coat new parts and products or that re-coat used parts and products;

(4) motor vehicle materials applied to miscellaneous metal and plastic parts specified in paragraph (3) of this subsection, at the original equipment manufacturer and off-site job shops that coat new metal and plastic parts or that re-coat used parts and products;

(5) paper, film, and foil surface coating lines with the potential to emit from all coatings greater than or equal to 25 tons per year of volatile organic compounds (VOC) when uncontrolled;

(6) in the Bexar County and Dallas-Fort Worth areas, automobile and light-duty truck assembly surface coating processes conducted by the original equipment manufacturer and operators that conduct automobile and light-duty truck surface coating processes under contract with the original equipment manufacturer;

(7) as of the compliance date specified in §115.459(e) or (g) of this title (relating to Compliance Schedules), industrial maintenance coatings in the Dallas-Fort Worth area and/or the Houston-Galveston-Brazoria area if the commission has published notice for the applicable area in the Texas Register, as provided in §115.459(e) or (g) of this title, to require compliance with the applicable contingency measure control requirements of §115.453(f) or (g) of this title (relating to Control Requirements); [and]

(8) as of the compliance date specified in §115.459(f) or (h) of this title, traffic marking coatings in the Dallas-Fort Worth area and/or the Houston-Galveston-Brazoria area if the commission has published notice for the applicable area in the Texas Register, as provided in §115.459(f) or (h) of this title, to require compliance with the applicable contingency measure control requirements of §115.453(h) or (i) of this title ; [.]

(9) in the Bexar County area beginning March 1, 2026, architectural coatings applied for compensation to stationary structures or their appurtenances; and

(10) in the Bexar County area beginning March 1, 2026, industrial maintenance coatings surface coating processes.

(b) General definitions. Unless specifically defined in the Texas Clean Air Act (Texas Health and Safety Code, Chapter 382) or in §§3.2, 101.1, or 115.10 of this title (relating to Definitions), the terms in this division have the meanings commonly used in the field of air pollution control. In addition, the following meanings apply in this division unless the context clearly indicates otherwise.

(1) Aerosol coating (spray paint)--A hand-held, pressurized, non-refillable container that expels an adhesive or a coating in a finely divided spray when a valve on the container is depressed.

(2) Air-dried coating--A coating that is cured at a temperature below 194 degrees Fahrenheit (90 degrees Celsius). These coatings may also be referred to as low-bake coatings.

(3) Baked Coating--A coating that is cured at a temperature at or above 194 degrees Fahrenheit (90 degrees Celsius). These coatings may also be referred to as high-bake coatings.

(4) Coating application system--Devices or equipment designed for the purpose of applying a coating material to a surface. The devices may include, but are not be limited to, brushes, sprayers, flow coaters, dip tanks, rollers, knife coaters, and extrusion coaters.

(5) Coating line--An operation consisting of a series of one or more coating application systems and associated flash-off area(s), drying area(s), and oven(s) wherein a surface coating is applied, dried, or cured. The coating line ends at the point the coating is dried or cured, or prior to any subsequent application of a different coating.

(6) Coating solids (or solids)--The part of a coating that remains on the substrate after the coating is dried or cured.

(7) Daily weighted average--The total weight of volatile organic compounds (VOC) emissions from all coatings subject to the same VOC limit in §115.453 of this title (relating to Control Requirements), divided by the total volume or weight of those coatings (minus water and exempt solvent), where applicable, or divided by the total volume or weight of solids, delivered to the application system on each coating line each day. Coatings subject to different VOC content limits in §115.453 of this title may not be combined for purposes of calculating the daily weighted average.

(8) Multi-component coating--A coating that requires the addition of a separate reactive resin, commonly known as a catalyst or hardener, before application to form an acceptable dry film. These coatings may also be referred to as two-component coatings.

(9) Normally closed container--A container that is closed unless an operator is actively engaged in activities such as adding or removing material.

(10) One-component coating--A coating that is ready for application as it comes out of its container to form an acceptable dry film. A thinner, necessary to reduce the viscosity, is not considered a component.

(11) Pounds of volatile organic compounds (VOC) per gallon of coating (minus water and exempt solvent)--The basis for content limits for surface coating processes that can be calculated by the following equation:

Figure: 30 TAC §115.450(b)(11) (No change.)

(12) Pounds of volatile organic compounds (VOC) per gallon of solids--The basis for emission limits for surface coating processes that can be calculated by the following equation:

Figure: 30 TAC §115.450(b)(12) (No change.)

(13) Spray gun--A device that atomizes a coating or other material and projects the particulates or other material onto a substrate.

(14) Surface coating processes--Operations that use a coating application system.

(c) Specific surface coating definitions. The following meanings apply in this division unless the context clearly indicates otherwise.

(1) Automobile and light-duty truck manufacturing--The following definitions apply to this surface coating category.

(A) Adhesive--Any chemical substance that is applied for the purpose of bonding two surfaces together other than by mechanical means.

(B) Automobile and light-duty truck adhesive--An adhesive, including glass-bonding adhesive, used in an automobile or light-duty truck assembly surface coating process and applied for the purpose of bonding two vehicle surfaces together without regard to the substrates involved.

(C) Automobile and light-duty truck bedliner--A multi-component coating used in an automobile or light-duty truck assembly surface coating process and applied to a cargo bed after the application of topcoat and outside of the topcoat operation to provide additional durability and chip resistance.

(D) Automobile and light-duty truck cavity wax--A coating, used in an automobile or light-duty truck assembly surface coating process, applied into the cavities of the vehicle primarily for the purpose of enhancing corrosion protection.

(E) Automobile and light-duty truck deadener--A coating used in an automobile or light-duty truck assembly surface coating process and applied to selected vehicle surfaces primarily for the purpose of reducing the sound of road noise in the passenger compartment.

(F) Automobile and light-duty truck gasket/gasket sealing material--A fluid used in an automobile or light-duty truck assembly surface coating process and applied to coat a gasket or replace and perform the same function as a gasket. Automobile and light-duty truck gasket/gasket sealing material includes room temperature vulcanization seal material.

(G) Automobile and light-duty truck glass-bonding primer--A primer, used in an automobile or light-duty truck assembly surface coating process, applied to windshield or other glass, or to body openings, to prepare the glass or body opening for the application of glass-bonding adhesives or the installation of adhesive-bonded glass. Automobile and light-duty truck glass-bonding primer includes glass-bonding/cleaning primers that perform both functions (cleaning and priming of the windshield or other glass, or body openings) prior to the application of an adhesive or the installation of adhesive-bonded glass.

(H) Automobile and light-duty truck lubricating wax/compound--A protective lubricating material used in an automobile or light-duty truck assembly surface coating process and applied to vehicle hubs and hinges.

(I) Automobile and light-duty truck sealer--A high viscosity material used in an automobile or light-duty truck assembly surface coating process and generally, but not always, applied in the paint shop after the body has received an electrodeposition primer coating and before the application of subsequent coatings (e.g., primer-surfacer). The primary purpose of automobile and light-duty truck sealer is to fill body joints completely so that there is no intrusion of water, gases, or corrosive materials into the passenger area of the body compartment. Such materials are also referred to as sealant, sealant primer, or caulk.

(J) Automobile and light-duty truck trunk interior coating--A coating used in an automobile or light-duty truck assembly surface coating process outside of the primer-surfacer and topcoat operations and applied to the trunk interior to provide chip protection.

(K) Automobile and light-duty truck underbody coating--A coating used in an automobile or light-duty truck assembly surface coating process and applied to the undercarriage or firewall to prevent corrosion or provide chip protection.

(L) Automobile and light-duty truck weather strip adhesive--An adhesive used in an automobile or light-duty truck assembly surface coating process and applied to weather-stripping materials for the purpose of bonding the weather-stripping material to the surface of the vehicle.

(M) Automobile assembly surface coating process--The assembly-line coating of new passenger cars, or passenger car derivatives, capable of seating 12 or fewer passengers.

(N) Electrodeposition primer--A process of applying a protective, corrosion-resistant waterborne primer on exterior and interior surfaces that provides thorough coverage of recessed areas. Electrodeposition primer is a dip-coating method that uses an electrical field to apply or deposit the conductive coating onto the part; the object being painted acts as an electrode that is oppositely charged from the particles of paint in the dip tank. Electrodeposition primer is also referred to as E-Coat, Uni-Prime, and ELPO Primer.

(O) Final repair--The operation(s) performed and coating(s) applied to completely assembled motor vehicles or to parts that are not yet on a completely assembled vehicle to correct damage or imperfections in the coating. The curing of the coatings applied in these operations is accomplished at a lower temperature than that used for curing primer-surfacer and topcoat. This lower temperature cure avoids the need to send parts that are not yet on a completely assembled vehicle through the same type of curing process used for primer-surfacer and topcoat and is necessary to protect heat-sensitive components on completely assembled vehicles.

(P) In-line repair--The operation(s) performed and coating(s) applied to correct damage or imperfections in the topcoat on parts that are not yet on a completely assembled vehicle. The curing of the coatings applied in these operations is accomplished at essentially the same temperature as that used for curing the previously applied topcoat. In-line repair is also referred to as high-bake repair or high-bake reprocess. In-line repair is considered part of the topcoat operation.

(Q) Light-duty truck assembly surface coating process--The assembly-line coating of new motor vehicles rated at 8,500 pounds gross vehicle weight or less and designed primarily for the transportation of property, or derivatives such as pickups, vans, and window vans.

(R) Primer-surfacer--An intermediate protective coating applied over the electrodeposition primer and under the topcoat. Primer-surfacer provides adhesion, protection, and appearance properties to the total finish. Primer-surfacer is also referred to as guide coat or surfacer. Primer-surfacer operations may include other coatings (e.g., anti-chip, lower-body anti-chip, chip-resistant edge primer, spot primer, blackout, deadener, interior color, basecoat replacement coating, etc.) that are applied in the same spray booth(s).

(S) Topcoat--The final coating system applied to provide the final color or a protective finish. The topcoat may be a monocoat color or basecoat/clearcoat system. In-line repair and two-tone are part of topcoat. Topcoat operations may include other coatings (e.g., blackout, interior color, etc.) that are applied in the same spray booth(s).

(T) Solids turnover ratio (RT')--The ratio of total volume of coating solids that is added to the electrodeposition primer system (EDP) in a calendar month divided by the total volume design capacity of the EDP system.

(2) Automotive/transportation and business machine plastic parts--The following definitions apply to this surface coating category.

(A) Adhesion prime--A coating that is applied to a polyolefin part to promote the adhesion of a subsequent coating. An adhesion prime is clearly identified as an adhesion prime or adhesion promoter on its accompanying material safety data sheet.

(B) Automotive/transportation plastic parts--Interior and exterior plastic components of automobiles, trucks, tractors, lawnmowers, and other mobile equipment.

(C) Black coating--A coating that has a maximum lightness of 23 units and a saturation less than 2.8, where saturation equals the square root of A2 + B2. These criteria are based on Cielab color space, 0/45 geometry. For spherical geometry, specular included, maximum lightness is 33 units.

(D) Business machine--A device that uses electronic or mechanical methods to process information, perform calculations, print or copy information, or convert sound into electrical impulses for transmission. This definition includes devices listed in Standard Industrial Classification codes 3572, 3573, 3574, 3579, and 3661 and photocopy machines, a subcategory of Standard Industrial Classification code 3861.

(E) Clear coating--A coating that lacks color and opacity or is transparent and that uses the undercoat as a reflectant base or undertone color.

(F) Coating of plastic parts of automobiles and trucks--The coating of any plastic part that is or will be assembled with other parts to form an automobile or truck.

(G) Coating of business machine plastic parts--The coating of any plastic part that is or will be assembled with other parts to form a business machine.

(H) Electrostatic prep coat--A coating that is applied to a plastic part solely to provide conductivity for the subsequent application of a prime, a topcoat, or other coating through the use of electrostatic application methods. An electrostatic prep coat is clearly identified as an electrostatic prep coat on its accompanying material safety data sheet.

(I) Flexible coating--A coating that is required to comply with engineering specifications for impact resistance, mandrel bend, or elongation as defined by the original equipment manufacturer.

(J) Fog coat--A coating that is applied to a plastic part for the purpose of color matching without masking a molded-in texture. A fog coat may not be applied at a thickness of more than 0.5 mil of coating solids.

(K) Gloss reducer--A coating that is applied to a plastic part solely to reduce the shine of the part. A gloss reducer may not be applied at a thickness of more than 0.5 mil of coating solids.

(L) Red coating--A coating that meets all of the following criteria:

(i) yellow limit: the hue of hostaperm scarlet;

(ii) blue limit: the hue of monastral red-violet;

(iii) lightness limit for metallics: 35% aluminum flake;

(iv) lightness limit for solids: 50% titanium dioxide white;

(v) solid reds: hue angle of -11 to 38 degrees and maximum lightness of 23 to 45 units; and

(vi) metallic reds: hue angle of -16 to 35 degrees and maximum lightness of 28 to 45 units. These criteria are based on Cielab color space, 0/45 geometry. For spherical geometry, specular included, the upper limit is 49 units. The maximum lightness varies as the hue moves from violet to orange. This is a natural consequence of the strength of the colorants, and real colors show this effect.

(M) Resist coat--A coating that is applied to a plastic part before metallic plating to prevent deposits of metal on portions of the plastic part.

(N) Stencil coat--A coating that is applied over a stencil to a plastic part at a thickness of 1.0 mil or less of coating solids. Stencil coats are most frequently letters, numbers, or decorative designs.

(O) Texture coat--A coating that is applied to a plastic part which, in its finished form, consists of discrete raised spots of the coating.

(P) Vacuum-metalizing coatings--Topcoats and basecoats that are used in the vacuum-metalizing process.

(3) Industrial maintenance coating--A high performance maintenance coating, including primers, sealers, undercoaters, intermediate coats, and topcoats, that is not applied to items meeting the definition for miscellaneous metal parts and products in §115.450(c)(6)(Q) of this section, and is formulated for application to stationary source substrates, including floors, exposed to one or more of the following extreme environmental conditions.

(A) Immersion in water, wastewater, or chemical solutions (aqueous and non-aqueous solutions), or chronic exposures of interior surfaces to moisture condensation; or

(B) Acute or chronic exposure to corrosive, caustic, or acidic agents, or to chemicals, chemical fumes, or chemical mixtures or solutions; or

(C) Frequent exposure to temperatures above 121°C (250°F); or

(D) Frequent heavy abrasion, including mechanical wear and frequent scrubbing with industrial solvents, cleansers, or scouring agents; or

(E) Exterior exposure of metal structures and structural components.

(4) Large appliance coating--The coating of doors, cases, lids, panels, and interior support parts of residential and commercial washers, dryers, ranges, refrigerators, freezers, water heaters, dishwashers, trash compactors, air conditioners, and other large appliances.

(A) Extreme high-gloss coating--A coating which, when tested by the American Society for Testing Material Test Method D523 adopted in 1980, shows a reflectance of 75% or more on a 60 degree meter.

(B) Extreme performance coating--A coating used on a metal surface where the coated surface is, in its intended use, subject to:

(i) chronic exposure to corrosive, caustic or acidic agents, chemicals, chemical fumes, chemical mixtures, or solutions;

(ii) repeated exposure to temperatures in excess of 250 degrees Fahrenheit (121 degrees Celsius);

(iii) repeated heavy abrasion, including mechanical wear and repeated scrubbing with industrial grade solvents, cleansers, or scouring agents; or

(iv) exposure to extreme environmental conditions, such as continuous outdoor exposure.

(C) Heat-resistant coating--A coating that must withstand a temperature of at least 400 degrees Fahrenheit (204 degrees Celsius) during normal use.

(D) Metallic coating--A coating that contains more than 0.042 pounds of metal particles per gallon of coating as applied. Metal particles are pieces of a pure elemental metal or a combination of elemental metals.

(E) Pretreatment coating--A coating that contains no more than 12% solids by weight and at least 0.50% acid by weight; is used to provide surface etching; and is applied directly to metal surfaces to provide corrosion resistance, adhesion, and ease of stripping.

(F) Solar-absorbent coating--A coating that has as its prime purpose the absorption of solar radiation.

(5) Metal furniture coating--The coating of metal furniture including, but not limited to, tables, chairs, wastebaskets, beds, desks, lockers, benches, shelves, file cabinets, lamps, and other metal furniture products or the coating of any metal part that will be a part of a nonmetal furniture product.

(A) Extreme high-gloss coating--A coating which, when tested by the American Society for Testing Material Test Method D523 adopted in 1980, shows a reflectance of 75% or more on a 60 degree meter.

(B) Extreme performance coating--A coating used on a metal surface where the coated surface is, in its intended use, subject to:

(i) chronic exposure to corrosive, caustic or acidic agents, chemicals, chemical fumes, chemical mixtures, or solutions;

(ii) repeated exposure to temperatures in excess of 250 degrees Fahrenheit (121 degrees Celsius);

(iii) repeated heavy abrasion, including mechanical wear and repeated scrubbing with industrial grade solvents, cleansers, or scouring agents; or

(iv) exposure to extreme environmental conditions, such as continuous outdoor exposure.

(C) Heat-resistant coating--A coating that must withstand a temperature of at least 400 degrees Fahrenheit (204 degrees Celsius) during normal use.

(D) Metallic coating--A coating containing more than 5.0 grams of metal particles per liter of coating as applied. Metal particles are pieces of a pure elemental metal or a combination of elemental metals.

(E) Pretreatment coating--A coating that contains no more than 12% solids by weight and at least 0.50% acid by weight; is used to provide surface etching; and is applied directly to metal surfaces to provide corrosion resistance, adhesion, and ease of stripping.

(F) Solar-absorbent coating--A coating that has as its primary purpose the absorption of solar radiation.

(6) Miscellaneous metal and plastic parts--The following definitions apply to this surface coating category.

(A) Camouflage coating--A coating used, principally by the military, to conceal equipment from detection.

(B) Clear coat--A coating that lacks opacity or is transparent and may or may not have an undercoat that is used as a reflectant base or undertone color.

(C) Drum (metal)--Any cylindrical metal shipping container with a capacity equal to or greater than 12 gallons but equal to or less than 110 gallons.

(D) Electric-dissipating coating--A coating that rapidly dissipates a high-voltage electric charge.

(E) Electric-insulting varnish--A non-convertible-type coating applied to electric motors, components of electric motors, or power transformers, to provide electrical, mechanical, and environmental protection or resistance.

(F) EMI/RFI shielding--A coating used on electrical or electronic equipment to provide shielding against electromagnetic interference (EMI), radio frequency interference (RFI), or static discharge.

(G) Etching filler--A coating that contains less than 23% solids by weight and at least 0.50% acid by weight and is used instead of applying a pretreatment coating followed by a primer.

(H) Extreme high-gloss coating--A coating which, when tested by the American Society for Testing and Materials Test Method D523 adopted in 1980, shows a reflectance of 75% or more on a 60 degree meter.

(I) Extreme performance coating--A coating used on a metal or plastic surface where the coated surface is, in its intended use, subject to one of the following conditions. Extreme performance coatings include, but are not limited to, coatings applied to locomotives, railroad cars, farm machinery, marine shipping containers, downhole drilling equipment, and heavy-duty trucks:

(i) chronic exposure to corrosive, caustic or acidic agents, chemicals, chemical fumes, chemical mixtures, or solutions;

(ii) repeated exposure to temperatures in excess of 250 degrees Fahrenheit (121 degrees Celsius);

(iii) repeated heavy abrasion, including mechanical wear and repeated scrubbing with industrial grade solvents, cleansers, or scouring agents; or

(iv) exposure to extreme environmental conditions, such as continuous outdoor exposure.

(J) Heat-resistant coating--A coating that must withstand a temperature of at least 400 degrees Fahrenheit (204 degrees Celsius) during normal use.

(K) High performance architectural coating--A coating used to protect architectural subsections and meets the requirements of the American Architectural Manufacturers Association's publication number AAMA 2604-05 (Voluntary Specification, Performance Requirements and Test Procedures for High Performance Organic Coatings on Aluminum Extrusions and Panels) or 2605-05 (Voluntary Specification, Performance Requirements and Test Procedures for Superior Performing Organic Coatings on Aluminum Extrusions and Panels).

(L) High temperature coating--A coating that is certified to withstand a temperature of 1000 degrees Fahrenheit (538 degrees Celsius) for 24 hours.

(M) Mask coating--A thin film coating applied through a template to coat a small portion of a substrate.

(N) Metallic coating--A coating containing more than 5.0 grams of metal particles per liter of coating as applied. Metal particles are pieces of a pure elemental metal or a combination of elemental metals.

(O) Military specification coating--A coating that has a formulation approved by a United States Military Agency for use on military equipment.

(P) Mold-seal coating--The initial coating applied to a new mold or a repaired mold to provide a smooth surface that when coated with a mold release coating, prevents products from sticking to the mold.

(Q) Miscellaneous metal parts and products--Parts and products considered miscellaneous metal parts and products include:

(i) large farm machinery (harvesting, fertilizing, and planting machines, tractors, combines, etc.);

(ii) small farm machinery (lawn and garden tractors, lawn mowers, rototillers, etc.);

(iii) small appliances (fans, mixers, blenders, crock pots, dehumidifiers, vacuum cleaners, etc.);

(iv) commercial machinery (computers and auxiliary equipment, typewriters, calculators, vending machines, etc.);

(v) industrial machinery (pumps, compressors, conveyor components, fans, blowers, transformers, etc.);

(vi) fabricated metal products (metal-covered doors, frames, etc.); and

(vii) any other category of coated metal products, including, but not limited to, those that are included in the Standard Industrial Classification Code major group 33 (primary metal industries), major group 34 (fabricated metal products), major group 35 (nonelectrical machinery), major group 36 (electrical machinery), major group 37 (transportation equipment), major group 38 (miscellaneous instruments), and major group 39 (miscellaneous manufacturing industries). Excluded are those surface coating processes specified in §115.420(c)(1) - (8) and (10) - (16) of this title (relating to Surface Coating Definitions) and paragraphs (1) - (4) and (6) - (8) of this subsection.

(R) Miscellaneous plastic parts and products--Parts and products considered miscellaneous plastic parts and products include, but are not limited to:

(i) molded plastic parts;

(ii) small and large farm machinery;

(iii) commercial and industrial machinery and equipment;

(iv) interior or exterior automotive parts;

(v) construction equipment;

(vi) motor vehicle accessories;

(vii) bicycles and sporting goods;

(viii) toys;

(ix) recreational vehicles;

(x) lawn and garden equipment;

(xi) laboratory and medical equipment;

(xii) electronic equipment; and

(xiii) other industrial and household products. Excluded are those surface coating processes specified in §115.420(c)(1) - (16) of this title and paragraphs (1) - (4) and (6) - (8) of this subsection.

(S) Multi-colored coating--A coating that exhibits more than one color when applied, is packaged in a single container, and applied in a single coat.

(T) Off-site job shop--A non-manufacturer of metal or plastic parts and products that applies coatings to such products at a site under contract with one or more parties that operate under separate ownership and control.

(U) Optical coating--A coating applied to an optical lens.

(V) Pail (metal)--Any cylindrical metal shipping container with a capacity equal to or greater than 1 gallon but less than 12 gallons and constructed of 29 gauge or heavier material.

(W) Pan-backing coating--A coating applied to the surface of pots, pans, or other cooking implements that are exposed directly to a flame or other heating elements.

(X) Prefabricated architectural component coating--A coating applied to metal parts and products that are to be used as an architectural structure.

(Y) Pretreatment coating--A coating that contains no more than 12% solids by weight and at least 0.50% acid by weight; is used to provide surface etching; and is applied directly to metal surfaces to provide corrosion resistance, adhesion, and ease of stripping.

(Z) Repair coating--A coating used to re-coat portions of a previously coated product that has sustained mechanical damage to the coating following normal surface coating processes.

(AA) Safety-indicating coating--A coating that changes physical characteristics, such as color, to indicate unsafe conditions.

(BB) Shock-free coating--A coating applied to electrical components to protect the user from electric shock. The coating has characteristics of being low-capacitance and high-resistance and having resistance to breaking down under high voltage.

(CC) Silicone-release coating--A coating that contains silicone resin and is intended to prevent food from sticking to metal surfaces such as baking pans.

(DD) Solar-absorbent coating--A coating that has as its primary purpose the absorption of solar radiation.

(EE) Stencil coating--A pigmented coating or ink that is rolled or brushed onto a template or stamp in order to add identifying letters, symbols, or numbers.

(FF) Touch-up coating--A coating used to cover minor coating imperfections appearing after the main surface coating process.

(GG) Translucent coating--A coating that contains binders and pigment and formulated to form a colored, but not opaque, film.

(HH) Vacuum-metalizing coating--The undercoat applied to the substrate on which the metal is deposited or the overcoat applied directly to the metal film. Vacuum metalizing or physical vapor deposition is the process whereby metal is vaporized and deposited on a substrate in a vacuum chamber.

(7) Motor vehicle materials--The following definitions apply to this surface coating category.

(A) Motor vehicle bedliner--A multi-component coating used in a process that is not an automobile or light-duty truck manufacturing coating process and is applied to a cargo bed after the application of topcoat to provide additional durability and chip resistance.

(B) Motor vehicle cavity wax--A coating used in a process that is not an automobile or light-duty truck manufacturing coating process and is applied into the cavities of the vehicle primarily for the purpose of enhancing corrosion protection.

(C) Motor vehicle deadener--A coating used in a process that is not an automobile or light-duty truck manufacturing coating process and is applied to selected vehicle surfaces primarily for the purpose of reducing the sound of road noise in the passenger compartment.

(D) Motor vehicle gasket/sealing material--A fluid used in a process that is not an automobile or light-duty truck manufacturing coating process and is applied to coat a gasket or replace and perform the same function as a gasket. Automobile and light-duty truck gasket/gasket sealing material includes room temperature vulcanization seal material.

(E) Motor vehicle lubricating wax/compound--A protective lubricating material used in a process that is not an automobile or light-duty truck manufacturing coating process and is applied to vehicle hubs and hinges.

(F) Motor vehicle sealer--A high viscosity material used in a process that is not an automobile or light-duty truck manufacturing coating process and is generally, but not always, applied in the paint shop after the body has received an electrodeposition primer coating and before the application of subsequent coatings (e.g., primer-surfacer). The primary purpose of motor vehicle sealer is to fill body joints completely so that there is no intrusion of water, gases, or corrosive materials into the passenger area of the body compartment. Such materials are also referred to as sealant, sealant primer, or caulk.

(G) Motor vehicle trunk interior coating--A coating used in a process that is not an automobile or light-duty truck manufacturing coating process and is applied to the trunk interior to provide chip protection.

(H) Motor vehicle underbody coating--A coating used in a process that is not an automobile or light-duty truck manufacturing coating process and is applied to the undercarriage or firewall to prevent corrosion or provide chip protection.

(8) Paper, film, and foil coating--The coating of paper and pressure-sensitive tapes (regardless of substrate and including paper, fabric, and plastic film), related web coating processes on plastic film (including typewriter ribbons, photographic film, and magnetic tape), metal foil (including decorative, gift wrap, and packaging), industrial and decorative laminates, abrasive products (including fabric coated for use in abrasive products), and flexible packaging.

(A) Paper, film, and foil coating includes the application of a continuous layer of a coating material across the entire width or any portion of the width of a paper, film, or foil web substrate to:

(i) provide a covering, finish, or functional or protective layer to the substrate;

(ii) saturate the substrate for lamination; or

(iii) provide adhesion between two substrates for lamination.

(B) Paper, film, and foil coating excludes coating performed on or in-line with any offset lithographic, screen, letterpress, flexographic, rotogravure, or digital printing press; or size presses and on-machine coaters that function as part of an in-line papermaking system.

(9) Pleasure craft--Any marine or fresh-water vessel used by individuals for noncommercial, nonmilitary, and recreational purposes that is less than 65.6 feet in length. A vessel rented exclusively to, or chartered for, individuals for such purposes is considered a pleasure craft.

(A) Antifoulant coating--A coating applied to the underwater portion of a pleasure craft to prevent or reduce the attachment of biological organisms, and registered with the United States Environmental Protection Agency as a pesticide under the Federal Insecticide, Fungicide, and Rodenticide Act (7 United States Code, §136).

(B) Antifoulant sealer/tie coating--A coating applied over an antifoulant coating to prevent the release of biocides into the environment or to promote adhesion between an antifoulant coating and a primer or other antifoulants.

(C) Extreme-90 high-gloss coating--A coating that achieves at least 90% reflectance on a 60 degree meter when tested by American Society for Testing and Materials Method D523 [ D523-89].

(D) Finish primer-surfacer--A coating applied with a wet film thickness less than 10 mils prior to the application of a topcoat for purposes of providing corrosion resistance, adhesion of subsequent coatings, a moisture barrier, or promotion of a uniform surface necessary for filling in surface imperfections.

(E) High-build primer-surfacer--A coating applied with a wet film thickness of 10 mils or more prior to the application of a topcoat for purposes of providing corrosion resistance, adhesion of subsequent coatings, or a moisture barrier, or promoting a uniform surface necessary for filling in surface imperfections.

(F) High-gloss coating--A coating that achieves at least 85% reflectance on a 60 degree meter when tested by American Society for Testing and Materials Test Method D523 [D523-89 ].

(G) Pleasure craft coating--A marine coating, except unsaturated polyester resin (fiberglass) coatings, applied by brush, spray, roller, or other means to a pleasure craft.

(H) Pretreatment wash primer--A coating that contains no more than 25% solids by weight and at least 0.10% acids by weight; used to provide surface etching; and applied directly to fiberglass and metal surfaces to provide corrosion resistance and adhesion of subsequent coatings.

(I) Repair coating--A coating used to re-coat portions of a previously coated product that has sustained mechanical damage to the coating following normal surface coating processes.

(J) Topcoat--A final coating applied to the interior or exterior of a pleasure craft.

(K) Touch-up coating--A coating used to cover minor coating imperfections appearing after the main surface coating process.

(10) Traffic marking coating--A coating labeled and formulated for marking and striping streets, highways, or other traffic surfaces including, but not limited to, curbs, berms, driveways, parking lots, sidewalks, and airport runways.

(11) Architectural Coatings--Any coatings applied to stationary structures or their appurtenances, or to fields and lawns.

(A) Aluminum Roof Coatings--Roof coatings containing at least 0.7 pounds per gallon (84 grams per liter) of coating as applied, of elemental aluminum pigment.

(B) Appurtenance--Accessories to a stationary structure including, but not limited to: hand railings, cabinets, bathroom and kitchen fixtures, fences, rain-gutters and down-spouts, window screens, lamp-posts, heating and air conditioning equipment, other mechanical equipment, large fixed stationary tools, signs, motion picture and television production sets, and concrete forms.

(C) Below Ground Wood Preservatives--Wood preservatives formulated to protect below-ground wood.

(D) Bituminous Coating Materials--Black or brownish coating materials, soluble in carbon disulfide, consisting mainly of hydrocarbons and which are obtained from natural deposits, or as residues from the distillation of crude petroleum oils, or of low grades of coal.

(E) Bituminous Roof Primers--Primers formulated for or applied to roofing that incorporate bituminous coating materials.

(F) Bond Breakers--Coatings formulated for or applied between layers of concrete to prevent the freshly poured top layer of concrete from bonding to the substrate over which it is poured.

(G) Building Envelope--The ensemble of exterior and demising partitions of a building that enclose conditioned space.

(H) Building Envelope Coatings--Fluid applied coatings applied to the building envelope to provide a continuous barrier to air or vapor leakage through the building envelope that separates conditioned from unconditioned spaces. Building Envelope Coatings are applied to diverse materials including, but not limited to, concrete masonry units (CMU), oriented stranded board (OSB), gypsum board, and wood substrates and must meet the following performance criteria:

(i) Air Barriers formulated to have an air permeance not exceeding 0.004 cubic feet per minute (cfm) per square foot (ft2) under a pressure differential of 1.57 pounds per square foot (0.004 cfm/ft2 at 1.57 psf), (0.02 liters per square meter per second under a pressure differential of 75 Pascals (Pa) (0.02 liter per second per square meter at 75 Pa) when tested in accordance with ASTM E2178; and/or

(ii) Water Resistive Barriers formulated to resist liquid water that has penetrated a cladding system from further intruding into the exterior wall assembly and is classified as follows:

(I) Passes water resistance testing according to ASTM E331, and

(II) Water vapor permeance is classified in accordance with ASTM E96/E96M.

(I) Colorant--Solutions of dyes or suspensions of pigments.

(J) Concrete-Curing Compounds--coatings labeled and formulated for application to freshly poured concrete to retard the evaporation of water, harden the surface of freshly poured concrete, or dustproof the surface of freshly poured concrete.

(K) Concrete Surface Retarders--Coatings containing one or more ingredients such as extender pigments, primary pigments, resins, and solvents that interact chemically with the cement to prevent hardening on the surface where the retarder is applied, allowing the mix of cement and sand at the surface to be washed away to create an exposed aggregate finish.

(L) Default Coatings--Specialty coatings (those other than flat or nonflat coatings) that are not defined in §115.450(c)(11) of this title as any other coating category.

(M) Driveway Sealers--Coatings that are applied to worn asphalt driveway surfaces in order to:

(i) Fill cracks;

(ii) Seal the surface to provide protection; or

(iii) Restore or preserve the surface appearance.

(N) Dry-Fog Coatings--Coatings which are formulated only for spray application so that when sprayed, overspray droplets dry before falling on floors and other surfaces.

(O) Faux Finishing Coatings--Coatings that meet one or more of the following subcategories:

(i) Clear Topcoats--Clear coatings used to enhance, seal, and protect a faux finishing coating that meets the requirements of §115.450(c)(11)(K)(ii), (iii), (iv) or (v) of this title. These clear topcoats must be sold and used solely as part of a faux finishing or graphic arts coating system.

(ii) Decorative Coatings--Coatings used to create a gonioapparent appearance, such as metallic, iridescent, or pearlescent appearance, that contain at least 48 grams of pearlescent mica pigment or other iridescent pigment per liter of coating as applied (at least 0.4 pounds per gallon).

(iii) Glazes--Coatings formulated and recommended to be used (or to be mixed with another coating) for:

(I) Wet-in-wet techniques, where a wet coating is applied over another wet coating to create artistic effects, including simulated marble or wood grain, or

(II) Wet-in-dry techniques, where a wet coating is applied over a pre-painted or a specially prepared substrate or base coat and is either applied or is treated during the drying period with various tools, such as a brush, rag, comb, or sponge to create artistic effects such as dirt, old age, smoke damage, simulated marble and wood grain finishes, decorative patterns, or color blending.

(iv) Japans--Pure concentrated pigments, finely ground in a slow drying vehicle used by motion picture and television production studios to create artistic effects including, but not limited to, dirt, old age, smoke damage, water damage, simulated marble, and wood grain.

(v) Trowel Applied Coatings--Coatings exclusively applied by trowel that are used to create aesthetic effects including, but not limited to, polished plaster, clay, suede and dimensional, tactile textures.

(P) Fire-Resistive Coatings--Opaque coatings formulated to protect the structural integrity of steel and other construction materials and listed by UL Solutions for the fire protection of steel.

(Q) Flat Coatings--Coatings that register a gloss of less than 15 on an 85-degree meter or less than five on a 60-degree meter according to ASTM Test method D523.

(R) Form Release Compounds--Coatings designed for or applied to a concrete form to prevent the freshly poured concrete from bonding to the form. The form may consist of metal, wood, or some material other than concrete.

(S) Gonioapparent--Change in appearance with a change in the angle of illumination or the angle of view, as defined according to ASTM E284.

(T) Graphic Arts Coatings (Sign Paints)--Coatings formulated for hand-application by artists using brush or roller techniques to indoor and outdoor signs (excluding structural components) and murals, including lettering enamels, poster colors, copy blockers, and bulletin enamels.

(U) Interior Stains--Stains labeled and formulated exclusively for use on interior surfaces.

(V) Lacquers--Clear or pigmented wood topcoats or clear lacquer sanding sealers, both formulated with nitrocellulose or synthetic resins to dry by evaporation without chemical reaction.

(W) Low-Solids Coatings--Coatings containing one pound or less of solids per gallon of material.

(X) Magnesite Cement Coatings--Coatings formulated for or applied to magnesite cement decking to protect the magnesite cement substrate from erosion by water.

(Y) Mastic Coating--Coatings formulated to cover holes and minor cracks and to conceal surface irregularities, excluding roof coatings, and applied in a thickness of at least 10 mils (dry, single coat).

(Z) Metallic Pigmented Coatings--Are decorative coatings, excluding industrial maintenance and roof coatings, containing at least 0.4 pounds per gallon (48 grams/liter) of coating, as applied, of elemental metallic pigment (excluding zinc).

(AA) Multi-Color Coatings--Coatings which exhibit more than one color when applied, are packaged in a single container and applied in a single coat.

(BB) Nonflat Coatings--Coatings that register a gloss of five or greater on a 60 degree meter and a gloss of 15 or greater on an 85 degree meter according to ASTM Test Method D523.

(CC) Pearlescent--Exhibiting various colors depending on the angles of illumination and viewing, as observed in mother-of-pearl.

(DD) Pigmented--Containing colorant or dry coloring matter, such as an insoluble powder, to impart color to a substrate.

(EE) Post-Consumer Coatings--Finished coatings that would have been disposed of in a landfill, having completed their usefulness to a consumer, and does not include manufacturing wastes.

(FF) Pre-Treatment Wash Primers--Coatings which contain a minimum of 0.5% acid, by weight, applied directly to bare metal surfaces to provide necessary surface etching.

(GG) Primers--Coatings applied to a surface to provide a firm bond between the substrate and subsequent coats.

(HH) Reactive Penetrating Sealers--Clear or pigmented coatings labeled and formulated for application to above-grade concrete and masonry substrates to provide protection from water and waterborne contaminants including, but not limited to, alkalis, acids, and salts. Reactive Penetrating Sealers must meet all of the following criteria:

(i) Used only for reinforced concrete bridge structures for transportation projects within five miles of the coast or for restoration and/or preservation projects on registered historical buildings that are under the purview of a restoration architect.

(ii) Penetrate into concrete and masonry substrates and chemically react to form covalent bonds with naturally occurring minerals in the substrate.

(iii) Line the pores of concrete and masonry substrates with a hydrophobic coating, but do not form a surface film.

(iv) Improve water repellency at least 80% after application on a concrete or masonry substrate. This performance must be verified on standardized test specimens, in accordance with one or more of the following standards: ASTM C67, or ASTM C97/C97M, or ASTM C140.

(v) Provide a breathable waterproof barrier for concrete or masonry surfaces that does not prevent or substantially retard water vapor transmission. This performance must be verified on standardized test specimens, in accordance with ASTM E96/E96M or ASTM D6490.

(vi) Meet the performance criteria listed in the National Cooperative Highway Research Report 244 (1981), surface chloride screening applications, for products labeled and formulated for vehicular traffic.

(II) Recycled Coatings--Coatings manufactured by a certified recycled paint manufacturer and formulated such that 50% or more of the total weight consists of secondary and post-consumer coatings and 10% or more of the total weight consists of post-consumer coatings.

(JJ) Restoration Architect--An architect that has a valid certificate of registration as an architect issued by the California State Board of Architectural Examiners or the National Council of Architectural Registration Boards and working on registered historical restoration and/or preservation projects.

(KK) Roof Coatings--Coatings formulated for application to exterior roofs for the primary purpose of preventing penetration of the substrate by water or reflecting heat and ultraviolet radiation.

(LL) Rust Preventative Coatings--Coatings formulated for use in preventing the corrosion of metal surfaces in residential and commercial situations.

(MM) Sacrificial Anti-Graffiti Coatings--Non-binding, clear coatings which are formulated and recommended for applications that allow for the removal of graffiti primarily by power washing.

(NN) Sanding Sealers--Clear wood coatings formulated for or applied to bare wood for sanding and to seal the wood for subsequent application(s) of coatings.

(OO) Sealers--Coatings applied to either block materials from penetrating into or leaching out of a substrate, to prevent subsequent coatings from being absorbed by the substrate, or to prevent harm to subsequent coatings by materials in the substrate.

(PP) Shellacs--Clear or pigmented coatings formulated solely with the resinous secretions of the lac insect (laccifer lacca). Shellacs are formulated to dry by evaporation without a chemical reaction providing a quick-drying, solid, protective film for priming and sealing stains and odors; and for wood finishing excluding floors.

(QQ) Specialty Primers--Coatings formulated for or applied to a substrate to seal fire, smoke or water damage, or to condition excessively chalky surfaces. An excessively chalky surface is one that is defined as having chalk rating of four or less as determined by ASTM D4214- Photographic Reference Standard No. 1 or the Federation of Societies for Coatings Technology "Pictorial Standards for Coatings Defects."

(RR) Stains--Opaque or semi-transparent coatings which are formulated to change the color but not conceal the grain pattern or texture.

(SS) Stationary Structures--include, but are not limited to, homes, office buildings, factories, mobile homes, pavements, curbs, roadways, racetracks, and bridges.

(TT) Stone Consolidants--Coatings that are labeled and formulated for application to stone substrates to repair historical structures that have been damaged by weathering or other decay mechanisms. Stone Consolidants must meet all of the following criteria:

(i) Used only for restoration and/or preservation projects on registered historical buildings that are under the purview of a restoration architect.

(ii) Penetrate into stone substrates to create bonds between particles and consolidate deteriorated material.

(iii) Specified and used in accordance with ASTM E2167.

(UU) Swimming Pool Coatings--Coatings specifically formulated for or applied to the interior of swimming pools including, but not limited to, water park attractions, ponds and fountains, to resist swimming pool chemicals.

(VV) Tile and Stone Sealers--Clear or pigmented sealers that are used for sealing tile, stone, or grout to provide resistance against water, alkalis, acids, ultraviolet light, or staining and which meet one of the following subcategories:

(i) Penetrating sealers are polymer solutions that cross-link in the substrate and must meet all of the following criteria:

(I) A fine particle structure to penetrate dense tile such as porcelain with absorption as low as 0.10% per ASTM C373, ASTM C97/C97M, or ASTM C642,

(II) Retain or increase static coefficient of friction per ANSI A137.1,

(III) Not create a topical surface film on the tile or stone, and

(IV) Allow vapor transmission per ASTM E96/96M.

(ii) Film forming sealers which leave a protective film on the surface.

(WW) Topcoat--Any final coating, applied in one or more coats, to the interior or exterior of a stationary structure or their appurtenances.

(XX) Tub and Tile Refinishing Coatings--Clear or opaque coatings that are used exclusively for refinishing the surface of a bathtub, shower, or sink and must meet all of the following criteria:

(i) Have a scratch hardness of 3H or harder and a gouge hardness of 4H or harder as determined on bonderite 1000 in accordance with ASTM D3363,

(ii) Have a weight loss of 20 milligrams or less after 1000 cycles as determined with CS-17 wheels on bonderite 1000 in accordance with ASTM D4060,

(iii) Must withstand 1,000 hours or more of exposure with few or no #8 blisters as determined on unscribed bonderite in accordance with ASTM D4585, and ASTM D714, and

(iv) Must have an adhesion rating of 4B or better after 24 hours of recovery as determined on unscribed bonderite in accordance with ASTM D4585 and ASTM D3359.

(YY) Undercoaters--Coatings formulated for or applied to substrates to provide a smooth surface for subsequent coats.

(ZZ) Varnishes--Clear or pigmented wood topcoats formulated with various resins to dry by chemical reaction.

(AAA) Waterproofing Sealers--Coatings which are formulated for the primary purpose of preventing penetration of porous substrates by water.

(BBB) Waterproofing Concrete/Masonry Sealers--Clear or pigmented sealers that are formulated for sealing concrete and masonry to provide resistance against water, alkalis, acids, ultraviolet light, or staining.

(CCC) Wood Coatings--Film forming coatings used for application to wood substrates only, which are applied to substrates including floors, decks, and porches. The Wood Coating category includes all lacquers, varnishes, and sanding sealers, regardless of whether they are clear, semi-transparent, or opaque.

(DDD) Wood Coatings, Other--The Wood Coating, Other category excludes all lacquers, varnishes, sanding sealers, wood coatings, and wood preservatives.

(EEE) Wood Conditioners--Coatings that are formulated for or applied to bare wood, prior to applying a stain, to provide uniform penetration of the stain.

(FFF) Wood Preservatives--Coatings formulated to protect wood from decay or insect attack by the addition of a wood preservative chemical registered by the United States Environmental Protection Agency.

§115.451. Exemptions.

(a) The volatile organic compounds (VOC) from coatings and solvents used in surface coating processes and associated cleaning operations not addressed by the surface coating categories in §115.421(3) - (7), (9), (10), and (13) - (16) of this title (relating to Emission Specifications) or §115.453 of this title (relating to Control Requirements) are excluded from the VOC emission calculations for the purposes of paragraphs (1) - (3) of this subsection. For example, architectural coatings applied in the field to stationary structures and their appurtenances, portable buildings, pavements, or curbs at a property would not be included in the calculations, except as specified in paragraphs (4) [and], (5), and (6) of this subsection.

(1) All surface coating processes on a property that, when uncontrolled, will emit a combined weight of VOC of less than 3.0 pounds per hour and 15 pounds in any consecutive 24-hour period are exempt from all of the requirements in §115.453 of this title except §115.453(f) - (i) of this title.

(2) Surface coating processes on a property that, when uncontrolled, will emit a combined weight of VOC of less than 100 pounds in any consecutive 24-hour period are exempt from §115.453(a) of this title if documentation is provided to and approved by both the executive director and the United States Environmental Protection Agency to demonstrate that necessary coating performance criteria cannot be achieved with coatings that satisfy applicable VOC limits and that control equipment is not technologically or economically feasible.

(3) Surface coating processes on a property where total coating and solvent usage does not exceed 150 gallons in any consecutive 12-month period are exempt from the VOC limits in §115.453(a) of this title.

(4) As of the applicable compliance date in §115.459(e) or (g) of this title, if the commission has published notice for the Dallas-Fort Worth and/or Houston-Galveston-Brazoria area in the Texas Register, as provided in §115.459(e) or (g) of this title, to require compliance for the applicable area with the industrial maintenance coatings contingency measure control requirements of §115.453(f) or (g) of this title, respectively, the exemptions in paragraphs (1) through (3) of this subsection no longer apply to industrial maintenance coatings. The owner or operator of a site may continue to exclude industrial maintenance coatings from the criteria in paragraphs (1) through (3) of this subsection for the purposes of determining applicability of this division for the purposes of coatings other than industrial maintenance coatings.

(5) As of the applicable compliance date in §115.459(f) or (h) of this title, if the commission has published notice for the Dallas-Fort Worth and/or Houston-Galveston-Brazoria area in the Texas Register, as provided in §115.459(f) or (h) of this title, to require compliance for the applicable area with the traffic marking coatings contingency measure control requirements of §115.453(h) or (i) of this title, respectively, the exemptions in paragraphs (1) through (3) of this subsection no longer apply to traffic marking coatings. The owner or operator of a site may continue to exclude traffic marking coatings from the criteria in paragraphs (1) through (3) of this subsection for the purposes of determining applicability of this division for the purposes of coatings other than traffic marking coatings.

(6) Beginning March 1, 2026, the exemptions in paragraphs (1) through (3) of this subsection no longer apply to industrial maintenance coatings, metal parts and products coatings, or architecture coatings in the Bexar County area. The owner or operator of a site may continue to exclude industrial maintenance coatings, metal parts and products coatings, and architectural coatings from the criteria in paragraphs (1) through (3) of this subsection to determine applicability of this division for the purposes of coatings other than industrial maintenance coatings, metal parts and products coatings, and architectural coatings.

(b) The following surface coating processes are exempt from the VOC limits for miscellaneous metal and plastic parts coatings in §115.453(a)(1)(C) - (F) of this title and motor vehicle materials in §115.453(a)(2) of this title:

(1) large appliance surface coating;

(2) metal furniture surface coating;

(3) automobile and light-duty truck assembly surface coating; and

(4) surface coating processes specified in §115.420(a)(1) - (9) and (11) - (16) of this title (relating to Applicability and Definitions).

(c) Paper, film, and foil surface coating processes are exempt from the coating application system requirements in §115.453(c) of this title and the coating use work practice requirements in §115.453(d)(1) of this title.

(d) Automobile and light-duty truck assembly surface coating processes are exempt from the coating application system requirements in §115.453(c) of this title and the cleaning-related work practice requirements in §115.453(d)(2) of this title.

(e) Automobile and light-duty truck assembly surface coating materials supplied in containers with a net volume of 16 ounces or less, or a net weight of 1.0 pound or less, are exempt from the VOC limits in Table 2 in §115.453(a)(3) of this title.

(f) The following miscellaneous metal part and product surface coatings and surface coating processes are exempt from the coating application system requirements in §115.453(c) of this title:

(1) touch-up coatings, repair coatings, and textured finishes;

(2) stencil coatings;

(3) safety-indicating coatings;

(4) solid-film lubricants;

(5) electric-insulating and thermal-conducting coatings;

(6) magnetic data storage disk coatings; and

(7) plastic extruded onto metal parts to form a coating.

(g) All miscellaneous plastic part airbrush surface coatings and surface coating processes where total coating usage is less than 5.0 gallons per year are exempt from the coating application system requirements in §115.453(c) of this title.

(h) The application of extreme high-gloss coatings to pleasure craft is exempt from the coating application system requirements in §115.453(c) of this title.

(i) The following miscellaneous plastic parts surface coatings and surface coating processes are exempt from the coating VOC limits in §115.453(a)(1)(D) of this title:

(1) touch-up and repair coatings;

(2) stencil coatings applied on clear or transparent substrates;

(3) clear or translucent coatings;

(4) any individual coating type used in volumes less than 50 gallons in any one year, if substitute compliant coatings are not available, provided that the total usage of all such coatings does not exceed 200 gallons per year, per property;

(5) reflective coating applied to highway cones;

(6) mask coatings that are less than 0.5 mil thick dried and the area coated is less than 25 square inches;

(7) electromagnetic interference/radio frequency interference (EMI/RFI) shielding coatings; and

(8) heparin-benzalkonium chloride-containing coatings applied to medical devices, if the total usage of all such coatings does not exceed 100 gallons per year, per property.

(j) The following automotive/transportation and business machine plastic part surface coatings and surface coating processes are exempt from the VOC limits in §115.453(a)(1)(E) of this title:

(1) texture coatings;

(2) vacuum-metalizing coatings;

(3) gloss reducers;

(4) texture topcoats;

(5) adhesion primers;

(6) electrostatic preparation coatings;

(7) resist coatings; and

(8) stencil coatings.

(k) Powder coatings and ultraviolet curable coatings applied during metal and plastic parts surface coating processes specified in §115.453(a)(1)(C) - (F) and (2) of this title are exempt from the requirements in this division, except as specified in §115.458(b)(5) of this title (relating to Monitoring and Recordkeeping Requirements).

(l) Aerosol coatings (spray paint) are exempt from the requirements in this division, except for §115.453(f) - (i) of this title.

(m) Coatings applied to test panels and coupons as part of research and development, quality control, or performance testing activities at paint research or manufacturing facilities are exempt from the requirements in this division.

(n) Pleasure craft touch-up and repair coatings supplied in containers less than or equal to 1.0 quart, are exempt from the VOC limits in §115.453(a)(1)(F) of this title provided that the total usage of all such coatings does not exceed 50 gallons per calendar year per property.

(o) Pleasure craft surface coating processes are exempt from the VOC limits in §115.453(a)(1)(C) and (D) of this title.

(p) Adhesives applied to miscellaneous metal and plastic parts listed in §115.453(a)(1)(C) - (F) and (2) of this title that meet a specific adhesive or adhesive primer application process definition in §115.470 of this title (relating to Applicability and Definitions) and are listed in Table 2 of §115.473(a) of this title (relating to Control Requirements) are not subject to the requirements in this division. Contact adhesives are not included in this exemption.

(q) In the Bexar County area, the following categories are exempt from the VOC limits in §115.453(a)(1)(C) and (D) of this title:

(1) Emulsion type bituminous pavement sealers; and

(2) Architectural coatings based on small container usage.

(A) One liter (1.057 quarts) or less:

(i) Bond Beakers;

(ii) Building Envelope Coatings;

(iii) Concrete-Curing Compounds;

(iv) Concrete Surface Retarders;

(v) Default Coatings;

(vi) Driveway Sealers;

(vii) Dry-Fog Coatings;

(viii) Faux Finishing Coatings (Clear, Topcoat, Decorative Coatings, Glazes, Japans, and Trowel Applied Coatings);

(ix) Fire-Resistive Coatings;

(x) Form Release Compound;

(xi) Graphic Arts (Sign) Coatings;

(xii) Mastic Coatings;

(xiii) Primers, Sealers, and Undercoaters;

(xiv) Recycled Coatings;

(xv) Roof Coatings;

(xvi) Roof Primer, Bituminous;

(xvii) Specialty Primers;

(xviii) Stains (Stains, Interior);

(xix) Tile and Stone Sealers;

(xx) Waterproofing Concrete/Masonry sealers; and

(xxi) Waterproofing Sealers.

(B) Eight fluid ounces or less or used for touch-up purpose only:

(i) Flat Coating;

(ii) Nonflat Coatings; and

(iii) Rust Preventive Coatings.

§115.453. Control Requirements.

(a) The following control requirements apply to surface coating processes subject to this division. Except as specified in paragraph (3) of this subsection, these limitations are based on the daily weighted average of all coatings, as defined in §101.1 of this title (relating to Definitions), as delivered to the application system. Upon the compliance date specified in §115.459(d) or (e) of this title (relating to Compliance Schedules), the requirements in subsection (f) or (h) of this section apply in the Dallas-Fort Worth area in addition to this subsection, and upon the compliance date specified in §115.459(g) or (h) of this title, the requirements in subsection (g) or (i) of this section apply in the Houston-Galveston-Brazoria area in addition to this subsection.

(1) The following limits must be met by applying low-volatile organic compound (VOC) coatings to meet the specified VOC content limits on a pound of VOC per gallon of coating basis (lb VOC/gal coating) (minus water and exempt solvent), or by applying coatings in combination with the operation of a vapor control system, as defined in §115.10 (relating to Definitions), to meet the specified VOC emission limits on a pound of VOC per gallon of solids basis (lb VOC/gal solids). If a coating meets more than one coating type definition, then the coating with the least stringent VOC limit applies.

(A) Large appliances. If a coating does not meet a specific coating type definition, then it can be assumed to be a general-use coating and the VOC limit for general coating applies.

Figure: 30 TAC §115.453(a)(1)(A) (No change.)

(B) Metal furniture. If a coating does not meet a specific coating type definition, then it can be assumed to be a general-use coating and the VOC limit for general coating applies.

Figure: 30 TAC §115.453(a)(1)(B) (No change.)

(C) Miscellaneous metal parts and products. If a coating does not meet a specific coating type definition, then it can be assumed to be a general-use coating and the VOC limit for general coating applies.

[Figure: 30 TAC §115.453(a)(1)(C)]

(i) The following VOC limits apply in the Dallas-Fort Worth and Houston-Galveston-Brazoria areas, as defined in §115.10 of this title (relating to Definitions) These limits also apply in the Bexar County area, as defined in §115.10 of this title (relating to Definitions), until March 1, 2026.

Figure: 30 TAC §115.453(a)(1)(C)(i)

(ii) The following VOC limits apply in the Bexar County area beginning March 1, 2026.

Figure: 30 TAC §115.453(a)(1)(C)(ii) (.pdf)

(D) Miscellaneous plastic parts and products. If a coating does not meet a specific coating category definition, then it can be assumed to be a general-use coating and the VOC limit for general coating applies.

Figure: 30 TAC §115.453(a)(1)(D) (No change.)

(E) Automotive/transportation and business machine plastic parts. For red, yellow, and black automotive/transportation coatings, except touch-up and repair coatings, the VOC limit is determined by multiplying the appropriate limit in Table 1 of this subparagraph by 1.15.

Figure: 30 TAC §115.453(a)(1)(E) (No change.)

(F) Pleasure craft. If a coating does not meet a specific coating category definition, then it can be assumed to be a general-use coating and the VOC limits for other coatings applies.

Figure: 30 TAC §115.453(a)(1)(F) (No change.)

(2) The coating VOC limits for motor vehicle materials applied to the metal and plastic parts in paragraph (1)(C) - (F) of this subsection, as delivered to the application system, must be met using low-VOC coatings (minus water and exempt solvent).

Figure: 30 TAC §115.453(a)(2) (No change.)

(3) The coating VOC limits for automobile and light-duty truck assembly surface coating processes must be met by applying low-VOC coatings.

Figure: 30 TAC §115.453(a)(3) (No change.)

(A) The owner or operator shall determine compliance with the VOC limits for electrodeposition primer operations on a monthly weighted average in accordance with §115.455(a)(2)(D) of this title (relating to Approved Test Methods and Testing Requirements).

(B) As an alternative to the VOC limit in Table 1 of this paragraph for final repair coatings, if an owner or operator does not compile records sufficient to enable determination of the daily weighted average, compliance may be demonstrated each day by meeting a standard of 4.8 lb VOC/gal coating (minus water and exempt solvent) on an occurrence weighted average basis. Compliance with the VOC limits on an occurrence weighted average basis must be determined in accordance with the procedure specified in §115.455(a)(2) of this title.

(C) The owner or operator shall determine compliance with the VOC limits in Table 2 of this paragraph in accordance with §115.455(a)(1) or (2)(C) of this title, as appropriate.

(4) The coating VOC limits for paper, film, and foil surface coating processes must be met by applying low-VOC coatings to meet the specified VOC content limits on a pound of VOC per pound of coating basis, as delivered to the application system, or by applying coatings in combination with the operation of a vapor control system to meet the specified VOC emission limits on a pound of VOC per pound of solids basis, as delivered to the application system.

Figure: 30 TAC §115.453(a)(4) (No change.)

(5) The coating VOC limits for an architectural coating surface coating process must be met by applying low-VOC coatings.

Figure: 30 TAC §115.453(a)(5) (.pdf)

[Figure: 30 TAC §115.453(a)(5)]

(6) [(5)] An owner or operator applying coatings in combination with the operation of a vapor control system to meet the VOC emission limits in paragraph (1) or (4) of this subsection shall use the following equation to determine the minimum overall control efficiency necessary to demonstrate equivalency. Control device and capture efficiency testing must be performed in accordance with the testing requirements in §115.455 (a)(3) and (4) of this title.

Figure: 30 TAC §115.453(a)(6) (.pdf)

[Figure: 30 TAC §115.453(a)(5)]

(b) Except for the surface coating process in subsection (a)(5) of this section, the owner or operator of a surface coating process may operate a vapor control system capable of achieving a 90% overall control efficiency as an alternative to subsection (a) of this section. Control device and capture efficiency testing must be performed in accordance with the testing requirements in §115.455(a)(3) and (4) of this title. If the owner or operator complies with the overall control efficiency option under this subsection, then the owner or operator is exempt from the application system requirements of subsection (c) of this section.

(c) The owner or operator of any surface coating process subject to this division shall not apply coatings unless one of the following coating application systems is used:

(1) electrostatic application;

(2) high-volume, low-pressure (HVLP) spray;

(3) flow coat;

(4) roller coat;

(5) dip coat;

(6) brush coat or hand-held paint rollers; or

(7) for metal and plastic parts surface coating processes specified in §115.450(a)(3) and (4) of this title (relating to Applicability and Definitions), airless spray or air-assisted airless spray; or

(8) other coating application system capable of achieving a transfer efficiency equivalent to or better than that achieved by HVLP spray. For the purpose of this requirement, the transfer efficiency of HVLP spray is assumed to be 65%. The owner or operator shall demonstrate that either the application system being used is equivalent to the transfer efficiency of an HVLP spray or that the application system being used has a transfer efficiency of at least 65%.

(d) The following work practices apply to the owner or operator of each surface coating process subject to this division.

(1) For all coating-related activities including, but not limited to, solvent storage, mixing operations, and handling operations for coatings and coating-related waste materials, the owner or operator shall:

(A) store all VOC-containing coatings and coating-related waste materials in closed containers;

(B) minimize spills of VOC-containing coatings;

(C) convey all coatings in closed containers or pipes;

(D) close mixing vessels and storage containers that contain VOC coatings and other materials except when specifically in use;

(E) clean up spills immediately; and

(F) for automobile and light-duty truck assembly coating processes, minimize VOC emissions from the cleaning of storage, mixing, and conveying equipment.

(2) For all cleaning-related activities including, but not limited to, waste storage, mixing, and handling operations for cleaning materials, the owner or operator shall:

(A) store all VOC-containing cleaning materials and used shop towels in closed containers;

(B) ensure that storage containers used for VOC-containing cleaning materials are kept closed at all times except when depositing or removing these materials;

(C) minimize spills of VOC-containing cleaning materials;

(D) convey VOC-containing cleaning materials from one location to another in closed containers or pipes;

(E) minimize VOC emissions from cleaning of storage, mixing, and conveying equipment;

(F) clean up spills immediately; and

(G) for metal and plastic parts surface coating processes specified in §115.450(a)(3) - (5) of this title (relating to Applicability and Definitions), minimize VOC emission from the cleaning of application, storage, mixing, and conveying equipment by ensuring that equipment cleaning is performed without atomizing the cleaning solvent and all spent solvent is captured in closed containers.

(3) The owner or operator of automobile and light-duty truck assembly surface coating processes shall implement a work practice plan containing procedures to minimize VOC emissions from cleaning activities and purging of coating application equipment. Properties with a work practice plan already in place to comply with requirements specified in 40 Code of Federal Regulations (CFR) §63.3094(b) (as amended through April 20, 2006 (71 FR 20464)), may incorporate procedures for minimizing non-hazardous air pollutant VOC emissions to comply with the work practice plan required by this paragraph.

(e) A surface coating process that becomes subject to subsection (a) of this section by exceeding the exemption limits in §115.451 of this title (relating to Exemptions) is subject to the provisions in subsection (a) of this section even if throughput or emissions later fall below exemption limits unless emissions are maintained at or below the controlled emissions level achieved while complying with subsection (a) of this section and one of the following conditions is met.

(1) The project that caused throughput or emission rate to fall below the exemption limits in §115.451 of this title must be authorized by a permit, permit amendment, standard permit, or permit by rule required by Chapters 106 or 116 of this title (relating to Permits by Rule; and Control of Air Pollution by Permits for New Construction or Modification, respectively). If a permit by rule is available for the project, the owner or operator shall continue to comply with subsection (a) of this section for 30 days after the filing of documentation of compliance with that permit by rule.

(2) If authorization by permit, permit amendment, standard permit, or permit by rule is not required for the project, the owner or operator shall provide the executive director 30 days notice of the project in writing.

(f) In the Dallas-Fort Worth area, in accordance with the schedule specified in 115.459(e) of this title, industrial maintenance coatings must meet a VOC limit of 2.1 pounds per gallon (250 grams per liter) of coating (minus water and exempt solvent), which must be met by applying low-VOC coatings.

(g) In the Houston-Galveston-Brazoria area, in accordance with the schedule specified in 115.459(g) of this title, industrial maintenance coatings must meet a VOC limit of 2.1 pounds per gallon (250 grams per liter) of coating (minus water and exempt solvent), which must be met by applying low-VOC coatings.

(h) In the Dallas-Fort Worth area, in accordance with the schedule specified in §115.459(f) of this title, traffic marking coatings must meet a VOC content limit of 100 grams of VOC per liter of coating (minus water and exempt solvent), which must be met by applying low-VOC coatings.

(i) In the Houston-Galveston-Brazoria area, in accordance with the schedule specified in §115.459(h) of this title, traffic marking coatings must meet a VOC content limit of 100 grams of VOC per liter of coating (minus water and exempt solvent), which must be met by applying low-VOC coatings.

(j) In the Bexar County area, industrial maintenance coatings must meet a VOC content limit of 2.1 pounds per gallon (250 grams per liter) of coating (minus water and exempt solvent), which must be met by applying low-VOC coatings.

§115.455. Approved Test Methods and Testing Requirements.

(a) Approved Test Methods and Testing Requirements. Compliance with the requirements in this division must be determined by applying one or more of the following test methods, as appropriate. As an alternative to the test methods in paragraph (1) of this subsection, the volatile organic compounds (VOC) content of coatings and, if necessary dilution solvent, may be determined by using analytical data from the material safety data sheet.

(1) The owner or operator shall demonstrate compliance with the VOC limits in §115.453 of this title (relating to Control Requirements), by applying the following test methods, as appropriate. Where a test method also inadvertently measures compounds that are exempt solvent an owner or operator may exclude the exempt solvent when determining compliance with a VOC limit. The methods include:

(A) Method 24 (40 Code of Federal Regulations (CFR) Part 60, Appendix A);

(B) American Society for Testing and Materials (ASTM) Test Methods C67, C97, C97M, C140, C309 Class B, C373, C642, D523, D714, D1186, D1200, D1644, D2832, D3359, D3363, D3794, D3960 [ D1186-06.01, D1200-06.01, D3794-06.01, D2832-69, D1644-75, and D3960-81] , D4060, D4214, D4585, D6490, E96/E96M, E284, E331, E2167, and E2178.

(C) the United States Environmental Protection Agency (EPA) guidelines series document "Procedures for Certifying Quantity of Volatile Organic Compounds Emitted by Paint, Ink, and Other Coatings," EPA-450/3-84-019, as in effect December, 1984;

(D) The American National Standards Institute (ANSI) A137.1 Standard Specifications for Ceramic Tiles;

(E) The National Cooperative Highway Research Report 244 (1981), "Concrete Sealers for the Protection of Bridge Structures";

(F) [(D)] additional test procedures described in 40 CFR §60.446 (as amended through October 17, 2000 (65 FR 61761)); and

(G) [(E)] minor modifications to these test methods approved by the executive director.

(2) The owner or operator shall determine compliance with the VOC limits for automobile and light-duty truck assembly coating processes in §115.453(a)(3) of this title by applying the following test methods in addition to paragraph (1) of this subsection, as appropriate. The methods include:

(A) Protocol for Determining the Daily VOC Emission Rate of Automobile and Light-Duty Truck Topcoat Operations (EPA-453/R-08-002);

(B) the procedure contained in subparagraph (A) of this paragraph for determining daily compliance with the alternative emission limitation in §115.453(a)(3) of this title for final repair. Calculation of occurrence weighted average for each combination of repair coatings (primer, specific basecoat, clearcoat) must be determined by the following procedure;

(i) the relative occurrence weighted usage calculated as follows for each repair coating:

Figure: 30 TAC §115.455(a)(2)(B)(i) (No change.)

(ii) the occurrence weighted average (Q) in pounds of VOC per gallon of coating (minus water and exempt solvents) as applied, for each potential combination of repair coatings calculated according to this subparagraph;

Figure: 30 TAC §115.455(a)(2)(B)(ii) (No change.)

(C) the procedure contained in 40 CFR Part 63, Subpart PPPP, Appendix A (as amended through April 24, 2007 (72 FR 20237)), for reactive adhesives; and

(D) the procedure contained in 40 CFR Part 60, Subpart MM (as amended October 17, 2000 (65 FR 61760)) for determining the monthly weighted average for electrodeposition primer.

(3) The owner or operator shall determine compliance with the vapor control system requirements in §115.453 of this title by applying the following test methods, as appropriate:

(A) Methods 1 - 4 (40 CFR Part 60, Appendix A) for determining flow rates, as necessary;

(B) Method 25 (40 CFR Part 60, Appendix A) for determining total gaseous nonmethane organic emissions as carbon;

(C) Method 25A or 25B (40 CFR Part 60, Appendix A) for determining total gaseous organic concentrations using flame ionization or nondispersive infrared analysis;

(D) additional performance test procedures described in 40 CFR §60.444 (as amended through October 18, 1983 (48 FR 48375)); or

(E) minor modifications to these test methods approved by the executive director.

(4) The owner or operator of a surface coating process subject to §115.453(a)(6) [§115.453(a)(5)] or (b) of this title shall measure the capture efficiency using applicable procedures outlined in 40 CFR §52.741, Subpart O, Appendix B (as amended through October 21, 1996 (61 FR 54559)). These procedures are: Procedure T - Criteria for and Verification of a Permanent or Temporary Total Enclosure; Procedure L - VOC Input; Procedure G.2 - Captured VOC Emissions (Dilution Technique); Procedure F.1 - Fugitive VOC Emissions from Temporary Enclosures; and Procedure F.2 - Fugitive VOC Emissions from Building Enclosures.

(A) The following exemptions apply to capture efficiency testing requirements.

(i) If a source installs a permanent total enclosure that meets the specifications of Procedure T and that directs all VOC to a control device, then the capture efficiency is assumed to be 100%, and the source is exempted from capture efficiency testing requirements. This does not exempt the source from performance of any control device efficiency testing that may be required. In addition, a source must demonstrate all criteria for a permanent total enclosure are met during testing for control efficiency.

(ii) If a source uses a vapor control system designed to collect and recover VOC (e.g., carbon adsorption system), an explicit measurement of capture efficiency is not necessary if the following conditions are met. The overall control of the system can be determined by directly comparing the input liquid VOC to the recovered liquid VOC. The general procedure for use in this situation is given in 40 CFR §60.433 (as amended through October 17, 2000 (65 FR 61761)), with the following additional restrictions.

(I) The source must be able to equate solvent usage with solvent recovery on a 24-hour (daily) basis, rather than a 30-day weighted average. This verification must be done within 72 hours following each 24-hour period of the 30-day period.

(II) The solvent recovery system (i.e., capture and control system) must be dedicated to a single process line (e.g., one process line venting to a carbon adsorber system); or if the solvent recovery system controls multiple process lines, the source must be able to demonstrate that the overall control (i.e., the total recovered solvent VOC divided by the sum of liquid VOC input to all process lines venting to the control system) meets or exceeds the most stringent standard applicable for any process line venting to the control system.

(B) The capture efficiency must be calculated using one of the following protocols referenced. Any affected source must use one of these protocols, unless a suitable alternative protocol is approved by the executive director and the EPA.

(i) Gas/gas method using temporary total enclosure (TTE). The EPA specifications to determine whether a temporary enclosure is considered a TTE are given in Procedure T. The capture efficiency equation to be used for this protocol is:

Figure: 30 TAC §115.455(a)(4)(B)(i) (No change.)

(ii) Liquid/gas method using TTE. The EPA specifications to determine whether a temporary enclosure is considered a TTE are given in Procedure T. The capture efficiency equation to be used for this protocol is:

Figure: 30 TAC §115.455(a)(4)(B)(ii) (No change.)

(iii) Gas/gas method using the building or room enclosure (BE) in which the affected source is located and in which the mass of VOC captured and delivered to a control device and the mass of fugitive VOC that escapes from BE are measured while operating only the affected facility. All fans and blowers in the BE must be operating as they would under normal production. The capture efficiency equation to be used for this protocol is:

Figure: 30 TAC §115.455(a)(4)(B)(iii) (No change.)

(iv) Liquid/gas method using a BE in which the mass of liquid VOC input to process and the mass of fugitive VOC that escapes from BE are measured while operating only the affected facility. All fans and blowers in the building or room must be operated as they would under normal production. The capture efficiency equation to be used for this protocol is:

Figure: 30 TAC §115.455(a)(4)(B)(iv) (No change.)

(C) The operating parameters selected for monitoring of the capture system for compliance with the requirements in §115.458(a) of this title (relating to Monitoring and Recordkeeping Requirements) must be monitored and recorded during the initial capture efficiency test and thereafter during facility operation. The executive director may require a new capture efficiency test if the operating parameter values change significantly from those recorded during the initial capture efficiency test.

(5) Test methods other than those specified in paragraphs (1) - (4) of this subsection may be used if approved by the executive director and validated by Method 301 (40 CFR Part 63, Appendix A). For the purposes of this paragraph, substitute "executive director" each place that Method 301 references "administrator."

(b) Inspection requirements. The owner or operator of each surface coating process subject to §115.453 of this title shall provide samples, without charge, upon request by authorized representatives of the executive director, the EPA, or any local air pollution agency with jurisdiction. The representative or inspector requesting the sample will determine the amount of coating needed to test the sample to determine compliance.

§115.458. Monitoring and Recordkeeping Requirements.

(a) Monitoring requirements. The following monitoring requirements apply to the owner or operator of a surface coating process subject to this division that uses a vapor control system in accordance with §115.453 of this title (relating to Control Requirements). The owner or operator shall install and maintain monitors to accurately measure and record operational parameters of all required control devices to ensure the proper functioning of those devices in accordance with design specifications, including:

(1) continuous monitoring of the exhaust gas temperature immediately downstream of direct-flame incinerators or the gas temperature immediately upstream and downstream of any catalyst bed;

(2) the total amount of volatile organic compounds (VOC) recovered by carbon adsorption or other solvent recovery systems during a calendar month;

(3) continuous monitoring of carbon adsorption bed exhaust; and

(4) appropriate operating parameters for capture systems and control devices other than those specified in paragraphs (1) - (3) of this subsection.

(b) Recordkeeping requirements. The following recordkeeping requirements apply to the owner or operator of a surface coating process subject to this division.

(1) The owner or operator shall maintain records of the testing data or the material safety data sheets (MSDS) in accordance with the requirements in §115.455(a) of this title (relating to Approved Test Methods and Testing Requirements). The MSDS must document relevant information regarding each coating and solvent available for use in the affected surface coating processes including the VOC content, composition, solids content, and solvent density. Records must be sufficient to demonstrate continuous compliance with the applicable VOC limits in §115.453(a) and [or] (f) - (j)[(i)] of this title.

(2) Records must be maintained of the quantity and type of each coating and solvent consumed during the specified averaging period if any of the coatings, as delivered to the coating application system, exceed the applicable VOC limits. Such records must be sufficient to calculate the applicable weighted average of VOC content for all coatings.

(3) As an alternative to the recordkeeping requirements of paragraph (2) of this subsection, the owner or operator that qualifies for exemption under §115.451(a)(3) of this title (relating to Exemptions) may maintain records of the total gallons of coating and solvent used in each month and total gallons of coating and solvent used in the previous 12 months.

(4) The owner or operator shall maintain, on file, the capture efficiency protocol submitted under §115.455(a)(4) of this title. The owner or operator shall submit all results of the test methods and capture efficiency protocols to the executive director within 60 days of the actual test date. The owner or operator shall maintain records of the capture efficiency operating parameter values on-site for a minimum of one year. If any changes are made to capture or control equipment, the owner or operator is required to notify the executive director in writing within 30 days of these changes and a new capture efficiency or control device destruction or removal efficiency test may be required.

(5) The owner or operator claiming an exemption in §115.451 of this title shall maintain records sufficient to demonstrate continuous compliance with the applicable exemption criteria.

(6) Records must be maintained of any testing conducted in accordance with the provisions specified in §115.455(a) of this title.

(7) Records must be maintained a minimum of two years and be made available upon request to authorized representatives of the executive director, the United States Environmental Protection Agency, or any local air pollution agency with jurisdiction.

§115.459. Compliance Schedules.

(a) The owner or operator of a surface coating process in Brazoria, Chambers, Collin, Dallas, Denton, Ellis, Fort Bend, Galveston, Harris, Johnson, Kaufman, Liberty, Montgomery, Parker, Rockwall, Tarrant, and Waller Counties subject to this division shall comply with the requirements of this division, except as specified in §115.453(f) - (i) of this title (relating to Control Requirements), no later than March 1, 2013.

(b) The owner or operator of a surface coating process in Wise County shall comply with the requirements in this division, except as specified in §115.453(f) - (i) of this title, no later than January 1, 2017.

(c) The owner or operator of a surface coating process in the Bexar County area subject to the requirements of this division shall comply with all applicable [the] requirements [in this division], except for §115.453(a)(1)(C)(ii) and §115.453(a)(5) of this title, [no later than] by January 1, 2025. Compliance with §115.453(a)(1)(C)(ii), §115.453(a)(5), and §115.453(j) of this title must be achieved no later than March 1, 2026.

(d) The owner or operator of a surface coating process that becomes subject to this division on or after the applicable compliance date of this section shall comply with the requirements in this division no later than 60 days after becoming subject.

(e) The owner or operator of a surface coating process in Collin, Dallas, Denton, Ellis, Johnson, Kaufman, Parker, Rockwall, Tarrant, and Wise Counties shall comply with §115.453(f) of this title by no later than 270 days after the commission publishes notification in the Texas Register of its determination that this industrial maintenance coating contingency rule is necessary as a result of EPA publication of a notice in the Federal Register that the specified area failed to attain the applicable National Ambient Air Quality Standard for ozone by the attainment deadline or failure to demonstrate reasonable further progress as set forth in the 1990 Amendments to the Federal Clean Air Act, §172(c)(9).

(f) The owner or operator of a surface coating process in Collin, Dallas, Denton, Ellis, Johnson, Kaufman, Parker, Rockwall, Tarrant, and Wise Counties shall comply with §115.453(h) of this title by no later than 270 days after the commission publishes notification in the Texas Register of its determination that this traffic marking coating contingency rule is necessary as a result of EPA publication of a notice in the Federal Register that the specified area failed to attain the applicable National Ambient Air Quality Standard for ozone by the attainment deadline or failure to demonstrate reasonable further progress as set forth in the 1990 Amendments to the Federal Clean Air Act, §172(c)(9).

(g) The owner or operator of a surface coating process in Brazoria, Chambers, Fort Bend, Galveston, Harris, Liberty, Montgomery, and Waller Counties shall be in compliance with §115.453(g) of this title by no later than 270 days after the commission publishes notification in the Texas Register of its determination that this industrial maintenance coating contingency rule is necessary as a result of EPA publication of a notice in the Federal Register that the specified area failed to attain the applicable National Ambient Air Quality Standard for ozone by the attainment deadline or failed to demonstrate reasonable further progress as set forth in the 1990 Amendments to the Federal Clean Air Act, §172(c)(9).

(h) The owner or operator of a surface coating process in Brazoria, Chambers, Fort Bend, Galveston, Harris, Liberty, Montgomery, and Waller Counties shall be in compliance with §115.453(i) of this title by no later than 270 days after the commission publishes notification in the Texas Register of its determination that this traffic marking coating contingency rule is necessary as a result of EPA publication of a notice in the Federal Register that the specified area failed to attain the applicable National Ambient Air Quality Standard for ozone by the attainment deadline or failure to demonstrate reasonable further progress as set forth in the 1990 Amendments to the Federal Clean Air Act, §172(c)(9).

The agency certifies that legal counsel has reviewed the proposal and found it to be within the state agency's legal authority to adopt.

Filed with the Office of the Secretary of State on July 11, 2025.

TRD-202502442

Charmaine Backens

Deputy Director, Environmental Law Division

Texas Commission on Environmental Quality

Earliest possible date of adoption: August 24, 2025

For further information, please call: (512) 239-2678


DIVISION 6. INDUSTRIAL CLEANING SOLVENTS

30 TAC §§115.460, 115.461, 115.463, 115.465, 115.468, 115.469

Statutory Authority

The amendments are proposed under Texas Water Code (TWC), §5.102, concerning general powers; §5.103, concerning Rules; TWC, §5.105, concerning General Policy, which authorize the commission to adopt rules necessary to carry out its powers and duties under the TWC; TWC, §7.002, concerning Enforcement Authority, which authorizes the commission to enforce the provisions of the Water Code and the Health and Safety Code within the commission's jurisdiction; and under Texas Health and Safety Code (THSC), §382.017, concerning Rules, which authorizes the commission to adopt rules consistent with the policy and purpose of the Texas Clean Air Act.

The amendments are also proposed under THSC, §382.002, concerning Policy and Purpose, which establishes the commission's purpose to safeguard the state's air resources, consistent with the protection of public health, general welfare, and physical property; THSC, §382.011, concerning General Powers and Duties, which authorizes the commission to control the quality of the state's air; THSC, §382.012, concerning the State Air Control Plan, which authorizes the commission to prepare and develop a general, comprehensive plan for the proper control of the state's air; THSC, §382.016, concerning Monitoring Requirements; Examination of Records, which authorizes the commission to prescribe reasonable requirements for measuring and monitoring the emissions of air contaminants; and THSC, §382.021, concerning Sampling Methods and Procedures.

The proposed amendments implement TWC, §§5.102, 5.103, and 7.002; and THSC, §§382.002, 382.011, 382.012, 382.016, 382.017, and 382.021.

§115.460. Applicability and Definitions.

(a) Applicability. Except as specified in §115.461 of this title (relating to Exemptions), the requirements in this division apply to solvent cleaning operations in the Bexar County, Dallas-Fort Worth and Houston-Galveston-Brazoria areas, as defined in §115.10 of this title (relating to Definitions). Residential cleaning and janitorial cleaning are not considered solvent cleaning operations.

(b) Definitions. Unless specifically defined in the Texas Clean Air Act (Texas Health and Safety Code, Chapter 382) or in §§3.2, 101.1, or 115.10 of this title (relating to Definitions), the terms in this division have the meanings commonly used in the field of air pollution control. In addition, the following meanings apply in this division unless the context clearly indicates otherwise indicates otherwise.

(1) Aerosol can--A hand-held, non-refillable container that expels pressurized product by means of a propellant-induced force.

(2) Application device--A device used to apply adhesive, coating, ink, or polyester resin materials.

(3) Application line--A portion of a motor vehicle assembly production line which applies surface and other coatings to motor vehicle bodies, hoods, fenders, cargo boxes, doors, and grill opening panels.

(4) Blanket--A synthetic rubber mat used in offset-lithography to transfer or offset an image from a planographic printing plate to the paper or other substrate.

(5) Blanket wash--A solvent used to remove ink from the blanket of a press.

(6) Cured coating, cured ink, or cured adhesive--A coating, ink, or adhesive, which is dry to the touch.

(7) Electrical and electronic components--Components and assemblies of components that generate, convert, transmit, or modify electrical energy. Electrical and electronic components include, but are not limited to, wires, windings, stators, rotors, magnets, contacts, relays, printed circuit boards, printed wire assemblies, wiring boards, integrated circuits, resistors, capacitors, and transistors. Cabinets that house electrical and electronic components are not considered electrical and electronic components. In the context of the provisions in §115.461(d), [and] (e), and (f) of this title (relating to Exemptions) and §115.463(e) and (f) of this title (relating to Control Requirements), Electronic component is defined as that portion of an assembly, including circuit card assemblies, printed wire assemblies, printed circuit boards, soldered joints, ground wires, bus bars, and other electrical fixtures, except for the actual cabinet in which the components are housed; and Electrical component is defined as an internal component such as wires, windings, stators, rotors, magnets, contacts, relays, energizers, and connections in an apparatus that generates or transmits electrical energy including, but not limited to: alternators, generators, transformers, electric motors, cables, and circuit breakers, except for the actual cabinet in which the components are housed. Electrical components of graphic arts application equipment and hot-line tools are also included in this category.

(8) Electron beam ink--An ink that dries by chemical reaction caused by high energy electrons.

(9) Facility--A business or businesses engaged in solvent cleaning operations which are owned or operated by the same person or persons and are located on the same or contiguous parcels.

(10) Grams of VOC per liter of material--The weight of VOC per volume of material and can be calculated by the following equation.

Figure: 30 TAC §115.460(b)(10) (No change.)

(11) Graphic arts--All gravure, letterpress, flexographic, and lithographic printing processes.

(12) Gravure printing-- An intaglio process in which the ink is carried in minute etched or engraved wells on a roll or cylinder. The excess ink is removed from the surface by a doctor blade.

(13) High precision optic--An optical element used in an electro-optical device and is designed to sense, detect, or transmit light energy, including specific wavelengths of light energy and changes in light energy levels.

(14) Hot-line tool--A specialized tool used primarily on the transmission systems, sub-transmission systems and distribution systems for replacing and repairing circuit components or for other types of work with electrically energized circuits.

(15) Janitorial cleaning--The cleaning of building or facility components including, but not limited to, floors, ceilings, walls, windows, doors, stairs, bathrooms, furnishings, and exterior surfaces of office equipment, and excludes the cleaning of work areas where manufacturing or repair activity is performed.

(16) Letterpress printing--The method in which the image area is raised relative to the non-image area and the ink is transferred to the paper directly from the image surface.

(17) Liquid-tight food container--A paperboard container that can hold liquid food and food products without leaking even when it is held upside-down.

(18) Lithographic printing--A plane-o-graphic method in which the image and non-image areas are on the same plane.

(19) Magnet wire--Wire used in electromagnetic field application in electrical machinery and equipment such as transformers, motors, generators, and magnetic tape recorders.

(20) Magnet wire coating operation--The process of applying insulation coatings such as varnish or enamel on magnet wire where wire is continuously drawn through a coating applicator.

(21) Maintenance cleaning--A solvent cleaning operation or activity carried out to keep clean general work areas where manufacturing or repair activity is performed, to clean tools, machinery, molds, forms, jigs, and equipment. This definition does not include the cleaning of coatings, adhesives, or ink application equipment.

(22) Manufacturing process--The process of making goods or articles by hand or by machinery.

(23) Medical device--An instrument, apparatus, implement, machine, contrivance, implant, in vitro reagent or other similar article, including any component or accessory, that meets one of the following conditions:

(A) it is intended for use in the diagnosis of disease or other conditions, or in the cure, mitigation, treatment, or prevention of disease; or

(B) it is intended to affect the structure or any function of the body; or

(C) it is defined in the National Formulary of the United States Pharmacopeia, or any supplement to them.

(24) Medical device and pharmaceutical preparation operations--Medical devices, pharmaceutical products, and associated manufacturing and product handling equipment and material, work surfaces, maintenance tools, and room surfaces that are subject to the United States Federal Drug Administration current Good Manufacturing/Laboratory Practice, or Center for Disease Control or National Institute of Health guidelines for biological disinfection of surfaces.

(25) Medical or pharmaceutical work surface--An area of a medical device or pharmaceutical facility where solvent cleaning is performed on work surfaces including, but not limited to, tables, countertops, and laboratory benches. Medical or pharmaceutical work surface shall not include items defined under janitorial cleaning.

(26) Non-absorbent container--A container made of nonporous material, which does not allow the migration of the liquid solvent through it.

(27) On-press component--A part, component, or accessory of a press that is cleaned while still being physically attached to the press.

(28) On-press screen cleaning--A solvent cleaning activity carried out during press runs in screen printing operation to remove excess inks and contaminants from a screen that is still attached to the press.

(29) Packaging printing--Any lithographic, flexographic, gravure, or letterpress printing that results in identifying or beautifying paper, paperboard, or cardboard products to be used as containers, enclosures, wrappings, or boxes.

(30) Pharmaceutical product--A preparation or compound of medicinal drugs including, but not limited to, a prescription drug, analgesic, decongestant, antihistamine, cough suppressant, vitamin, mineral and herb, and is used by humans or animals for consumption to enhance personal health.

(31) Photocurable resin--A chemical material that solidifies upon exposure to light.

(32) Polyester resin operation--The fabrication, rework, repair, or touch-up of composite products for commercial, military, or industrial uses by mixing, pouring, manual application, molding, impregnating, injecting, forming, spraying, pultrusion, filament winding, or centrifugally casting with polyester resins.

(33) Precision optics--The optical elements used in electro-optical devices that are designed to sense, detect, or transmit light energy, including specific wavelengths of light energy and changes of light energy levels.

(34) Printing--In the graphic arts, is any operation that imparts color, design, alphabet, or numerals on a substrate.

(35) Removable press component--A part, component, or accessory of a press that is physically attached to the press but is disassembled and removed from the press prior to being cleaned. Rollers, blankets, metering rollers, dampening rollers, ink trays, printing plates, fountains, impression cylinders and plates shall not be considered as removable press components.

(36) Repair cleaning--A solvent cleaning operation or activity carried out during a repair process.

(37) Repair process--The process of returning a damaged object or an object not operating properly to good condition.

(38) Roller wash--A solvent used to remove ink from the rollers of a press.

(39) Scientific instrument--An instrument (including the components, assemblies, and subassemblies used in their manufacture) and associated accessories and reagents that is used for the detection, measurement, analysis, separation, synthesis, or sequencing of various compounds.

(40) Screen printing--A process in which the printing ink passes through a web or a fabric to which a refined form of stencil has been applied. The stencil openings determine the form and dimensions of the imprint.

(41) Solvent--A volatile organic compound-containing liquid used to perform solvent cleaning operations.

(42) Solvent cleaning operation--The removal of uncured adhesives, inks, and coatings; and contaminants such as dirt, soil, oil, and grease from parts, products, tools, machinery, equipment, vessels, floors, walls, and other work production-related areas using a solvent. In the context of the provisions in §115.461(d), [ and] (e), and (f) this title and §115.463(e) and (f) of this title, each distinct method of cleaning in a cleaning process that consists of a series of cleaning methods shall constitute a separate solvent cleaning operation.

(43) Solvent flushing--The use of a solvent to remove uncured adhesives, uncured inks, uncured coatings, or contaminants from the internal surfaces and passages of the equipment by flushing solvent through the equipment.

(44) Specialty flexographic printing--Flexographic printing on polyethylene or polypropylene food packaging, fertilizer bags, or liquid-tight food containers.

(45) Stereolithography--A type of printing process that employs a system using a light to solidify photocurable resins in a desired configuration in order to produce a 3-dimensional object.

(46) Stripping--The removal of cured coatings, cured inks, or cured adhesives.

(47) Surface preparation--The removal of contaminants such as dust, soil, oil, grease, etc., prior to coating, adhesive, or ink applications.

(48) Ultraviolet ink--An ink that dries by polymerization reaction induced by ultraviolet energy.

(49) Volatile organic compound (VOC) composite partial pressure--The sum of the partial pressures of the compounds that meet the definition of VOC in §101.1 of this title (relating to Definitions). The VOC composite partial pressure is calculated as follows.

Figure: 30 TAC §115.460(b)(12) (No change.)

§115.461. Exemptions.

(a) Solvent cleaning operations located on a property with total actual volatile organic compounds (VOC) emissions of less than 3.0 tons per calendar year from all cleaning solvents, when uncontrolled, are exempt from the requirements of this division, except as specified in §115.468(b)(2) of this title (relating to Monitoring and Recordkeeping Requirements). When calculating the VOC emissions, solvents used for solvent cleaning operations that are exempt from this division under subsections (b) - (d), [and] (f), and (g) of this section are excluded.

(b) The owner or operator of any process or operation subject to another division of this chapter that specifies solvent cleaning operation requirements related to that process or operation is exempt from the requirements in this division.

(c) A solvent cleaning operation is exempt from this division if:

(1) the process or operation that the solvent cleaning operation is associated with is subject to another division in this chapter; and

(2) the VOC emissions from the solvent cleaning operation are controlled in accordance with an emission specification or control requirement of the division that the process or operation is subject to.

(d) The following are exempt from the VOC limits in §115.463(a) of this title (relating to Control Requirements:

(1) electrical and electronic components;

(2) precision optics;

(3) numisimatic dies;

(4) resin mixing, molding, and application equipment;

(5) coating, ink, and adhesive mixing, molding, and application equipment;

(6) stripping of cured inks, cured adhesives, and cured coatings;

(7) research and development laboratories;

(8) medical device or pharmaceutical preparation operations;

(9) performance or quality assurance testing of coatings, inks, or adhesives;

(10) architectural coating manufacturing and application operations;

(11) magnet wire coating operations;

(12) semiconductor wafer fabrication;

(13) coating, ink, resin, and adhesive manufacturing;

(14) polyester resin operations;

(15) flexographic and rotogravure printing processes;

(16) screen printing operations; and

(17) digital printing operations.

(e) If the commission publishes notice in the Texas Register, as provided in §115.469(d) of this title (relating to Compliance Schedules) for the Dallas-Fort Worth area, or §115.469(e) of this title for the Houston-Galveston-Brazoria area, or both areas, to require compliance with the contingency measure control requirements of §115.463(e) of this title, then the exemptions in subsections (a) - (d) of this section are no longer available, and the following exemptions apply in the applicable area as of the compliance date specified in §115.469(d) or (e) of this title.

(1) In the Dallas-Fort Worth area, in accordance with the schedule specified in §115.469(d) of this title, the following types of cleaning are exempt from the VOC content limits in §115.463(e)(1) of this title:

(A) Cleaning of solar cells, laser hardware, scientific instruments, and high-precision optics;

(B) Cleaning conducted with performance laboratory tests on coatings, adhesives, or inks; research and development programs; and laboratory tests in quality assurance laboratories;

(C) Cleaning of paper-based gaskets, and clutch assemblies where rubber is bonded to metal by means of an adhesive;

(D) Cleaning of cotton swabs to remove cottonseed oil before cleaning of high-precision optics;

(E) Medical device and pharmaceutical facilities using up to 1.5 gallons per day of solvents;

(F) The cleaning of photocurable resins from stereolithography equipment and models;

(G) Cleaning of adhesive application equipment used for thin metal laminating operations provided the clean-up solvent used contains no more than 950 grams of VOC per liter;

(H) Cleaning of electronic or electrical cables provided the clean-up solvent used contains no more than 400 grams of VOC per liter;

(I) Touch up cleaning performed on printed circuit boards where surface mounted devices have already been attached provided that the solvent used contains no more than 800 grams of VOC per liter;

(J) Cleaning carried out in batch loaded cold cleaners, vapor degreasers, conveyorized degreasers, or motion picture film cleaning equipment;

(K) Janitorial cleaning, including graffiti removal; and

(L) Stripping of cured coatings, cured ink, or cured adhesives.

(2) In the Houston-Galveston-Brazoria area, in accordance with the schedule specified in §115.469(e) of this title, the following types of cleaning are exempt from the VOC content limits in §115.463(e)(2) of this title:

(A) Cleaning of solar cells, laser hardware, scientific instruments, and high-precision optics;

(B) Cleaning conducted with performance laboratory tests on coatings, adhesives, or inks; research and development programs; and laboratory tests in quality assurance laboratories;

(C) Cleaning of paper-based gaskets, and clutch assemblies where rubber is bonded to metal by means of an adhesive;

(D) Cleaning of cotton swabs to remove cottonseed oil before cleaning of high-precision optics;

(E) Medical device and pharmaceutical facilities using up to 1.5 gallons per day of solvents;

(F) The cleaning of photocurable resins from stereolithography equipment and models;

(G) Cleaning of adhesive application equipment used for thin metal laminating operations provided the clean-up solvent used contains no more than 950 grams of VOC per liter;

(H) Cleaning of electronic or electrical cables provided the clean-up solvent used contains no more than 400 grams of VOC per liter;

(I) Touch up cleaning performed on printed circuit boards where surface mounted devices have already been attached provided that the solvent used contains no more than 800 grams of VOC per liter;

(J) Cleaning carried out in batch loaded cold cleaners, vapor degreasers, conveyorized degreasers, or motion picture film cleaning equipment;

(K) Janitorial cleaning, including graffiti removal; and

(L) Stripping of cured coatings, cured ink, or cured adhesives.

(f) In the Bexar County area, exemptions in §115.461(a) through (d) of this section do not apply after February 28, 2026. Beginning March 1, 2026, exemptions for industrial cleaning solvents from the VOC content limits specified in §115.463(f) of this title are limited to the following cleaning activities:

(1) Cleaning of solar cells, laser hardware, scientific instruments, and high-precision optics;

(2) Cleaning conducted with performance laboratory tests on coatings, adhesives, or inks; research and development programs; and laboratory tests in quality assurance laboratories;

(3) Cleaning of paper-based gaskets and clutch assemblies where rubber is bonded to metal by means of an adhesive;

(4) Cleaning of cotton swabs to remove cottonseed oil before cleaning of high-precision optics;

(5) Medical device and pharmaceutical facilities using up to 1.5 gallons per day of solvents;

(6) The cleaning of photocurable resins from stereolithography equipment and models;

(7) Cleaning of adhesive application equipment used for thin metal laminating operations provided the clean-up solvent used contains no more than 950 grams of VOC per liter;

(8) Cleaning of electronic or electrical cables provided the clean-up solvent used contains no more than 400 grams of VOC per liter;

(9) Touch up cleaning performed on printed circuit boards where surface mounted devices have already been attached provided that the solvent used contains no more than 800 grams of VOC per liter;

(10) Cleaning carried out in batch loaded cold cleaners, vapor degreasers, conveyorized degreasers, or motion picture film cleaning equipment;

(11) Janitorial cleaning, including graffiti removal; and

(12) Stripping of cured coatings, cured ink, or cured adhesives.

(g) [(f)] Cleaning solvents supplied in aerosol cans are exempt from the VOC limits in §115.463(a) of this title if total aerosol use for the property is less than 160 fluid ounces per day.

§115.463. Control Requirements.

(a) Except as specified in subsections [subsection ] (e) and (f) of this section, the owner or operator shall limit the volatile organic compounds (VOC) content of cleaning solutions to:

(1) 0.42 pound of VOC per gallon of solution (lb VOC/gal solution), as applied; or

(2) limit the composite partial vapor pressure of the cleaning solution to 8.0 millimeters of mercury at 20 degrees Celsius (68 degrees Fahrenheit).

(b) As an alternative to subsection (a) of this section, the owner or operator shall operate a vapor control system capable of achieving an overall control efficiency of 85% by mass. Control device and capture efficiency testing must be performed in accordance with the testing requirements in §115.465 of this title (relating to Approved Test Methods and Testing Requirements).

(c) The owner or operator of a solvent cleaning operation shall implement the following work practices during the handling, storage, and disposal of cleaning solvents and shop towels:

(1) cover open containers and used applicators;

(2) minimize air circulation around solvent cleaning operations;

(3) properly dispose of used solvent and shop towels; and

(4) implement equipment practices that minimize emissions (e.g. maintaining cleaning equipment to repair solvent leaks).

(d) A solvent cleaning operation that becomes subject to subsection (a) of this section by exceeding the exemption limits in §115.461 of this title (relating to Exemptions) is subject to the provisions in subsection (a) of this section even if throughput or emissions later fall below exemption limits unless emissions are maintained at or below the controlled emissions level achieved while complying with subsection (a) of this section and one of the following conditions is met.

(1) The project that caused throughput or emission rate to fall below the exemption limits in §115.461 of this title must be authorized by a permit, permit amendment, standard permit, or permit by rule required by Chapter 116 or Chapter 106 of this title (relating to Control of Air Pollution by Permits for New Construction or Modification; and Permits by Rule, respectively). If a permit by rule is available for the project, the owner or operator shall continue to comply with subsection (a) of this section for 30 days after the filing of documentation of compliance with that permit by rule.

(2) If authorization by permit, permit amendment, standard permit, or permit by rule is not required for the project, the owner or operator shall provide the executive director 30 days notice of the project in writing.

(e) If the commission has published notice in the Texas Register, as provided in §115.469(d) or (e) of this title (relating to Compliance Schedules), to require compliance with the contingency measure control requirements for the Dallas-Fort Worth area, the Houston-Galveston-Brazoria area, or both areas the following control requirements apply instead of subsection (a) of this section.

Figure: 30 TAC §115.463(e) (No change.)

(1) In the Dallas-Fort Worth area, in accordance with the schedule specified in §115.469(d) of this title, the limits in Table 1 of this subsection apply.

(2) In the Houston-Galveston-Brazoria area, in accordance with the schedule specified in §115.469(e) of this title, the limits in Table 1 of this subsection apply.

(f) In the Bexar County area, the following control requirements apply beginning March 1, 2026.

Figure: 30 TAC §115.463(f) (.pdf)

§115.465. Approved Test Methods and Testing Requirements.

The owner or operator shall demonstrate compliance with the control requirements in §115.463 of this title (relating to Control Requirements) by applying the following test methods, as appropriate.

(1) Compliance with the volatile organic compound (VOC) limits in §115.463(a), [or] (e), or (f) of this title must be determined by the following methods, as applicable:

(A) Method 24 (40 Code of Federal Regulations (CFR) Part 60, Appendix A);

(B) American Society for Testing and Materials Method D2879, Standard Test Method for Vapor Pressure-Temperature Relationship and Initial Decomposition Temperature of Liquids by Isoteniscope to demonstrate compliance with §115.463(a)(2) of this title;

(C) using standard reference texts for the true vapor pressure of each VOC component to demonstrate compliance with §115.463(a)(2) of this title; or

(D) using analytical data from the cleaning solvent supplier or manufacturer's material safety data sheet.

(2) The owner or operator subject to §115.463(b) of this title shall measure the capture efficiency using applicable procedures outlined in 40 CFR §52.741, Subpart O, Appendix B (as amended through October 21, 1996 (61 FR 54559)). These procedures are: Procedure T - Criteria for and Verification of a Permanent or Temporary Total Enclosure; Procedure L - VOC Input; Procedure G.2 - Captured VOC Emissions (Dilution Technique); Procedure F.1 - Fugitive VOC Emissions from Temporary Enclosures; and Procedure F.2 - Fugitive VOC Emissions from Building Enclosures.

(A) The following exemptions apply to capture efficiency testing requirements.

(i) If a source installs a permanent total enclosure that meets the specifications of Procedure T and that directs all VOC to a control device, then the capture efficiency is assumed to be 100%, and the source is exempted from capture efficiency testing requirements. This does not exempt the source from performance of any control device efficiency testing that may be required. In addition, a source must demonstrate all criteria for a permanent total enclosure are met during testing for control efficiency.

(ii) If a source uses a vapor control system designed to collect and recover VOC (e.g., carbon adsorption system), an explicit measurement of capture efficiency is not necessary if the following conditions are met. The overall control of the system can be determined by directly comparing the input liquid VOC to the recovered liquid VOC. The general procedure for use in this situation is given in 40 CFR §60.433 (as amended through October 17, 2000 (65 FR 61761)), with the following additional restrictions.

(I) The source must be able to equate solvent usage with solvent recovery on a 24-hour (daily) basis, rather than a 30-day weighted average. This verification must be done within 72 hours following each 24-hour period of the 30-day period.

(II) The solvent recovery system (i.e., capture and control system) must be dedicated to a single process line (e.g., one process line venting to a carbon adsorber system) or if the solvent recovery system controls multiple process lines, the source must be able to demonstrate that the overall control (i.e., the total recovered solvent VOC divided by the sum of liquid VOC input to all process lines venting to the control system) meets or exceeds the most stringent standard applicable for any process line venting to the control system.

(B) The capture efficiency must be calculated using one of the following protocols referenced. Any affected source must use one of these protocols, unless a suitable alternative protocol is approved by the executive director and the United States Environmental Protection Agency (EPA).

(i) Gas/gas method using temporary total enclosure (TTE). The EPA specifications to determine whether a temporary enclosure is considered a TTE are given in Procedure T. The capture efficiency equation to be used for this protocol is:

Figure: 30 TAC §115.465(2)(B)(i) (No change.)

(ii) Liquid/gas method using TTE. The EPA specifications to determine whether a temporary enclosure is considered a TTE are given in Procedure T. The capture efficiency equation to be used for this protocol is:

Figure: 30 TAC §115.465(2)(B)(ii) (No change.)

(iii) Gas/gas method using the building or room enclosure (BE) in which the affected source is located and in which the mass of VOC captured and delivered to a control device and the mass of fugitive VOC that escapes from the BE are measured while operating only the affected facility. All fans and blowers in the BE must be operating as they would under normal production. The capture efficiency equation to be used for this protocol is:

Figure: 30 TAC §115.465(2)(B)(iii) (No change.)

(iv) Liquid/gas method using a BE in which the mass of liquid VOC input to process and the mass of fugitive VOC that escapes from the BE are measured while operating only the affected facility. All fans and blowers in the BE must be operated as they would under normal production. The capture efficiency equation to be used for this protocol is:

Figure: 30 TAC §115.465(2)(B)(iv) (No change.)

(C) The operating parameters selected for monitoring of the capture system for compliance with the requirements in §115.468(a) of this title (relating to Monitoring and Recordkeeping Requirements) must be monitored and recorded during the initial capture efficiency testing and thereafter during facility operation. The executive director may require a new capture efficiency test if the operating parameter values change significantly from those recorded during the initial capture efficiency test.

(3) In addition to the requirements of paragraph (2) of this section, the owner or operator shall determine compliance with §115.463(b) of this title by applying the following test methods, as appropriate:

(A) Methods 1 - 4 (40 CFR Part 60, Appendix A) for determining flow rates, as necessary;

(B) Method 25 (40 CFR Part 60, Appendix A) for determining total gaseous nonmethane organic emissions as carbon;

(C) Method 25A or 25B (40 CFR Part 60, Appendix A) for determining total gaseous organic concentrations using flame ionization or nondispersive infrared analysis; and

(D) additional performance test procedures described in 40 CFR §60.444 (as amended through October 18, 1983 (48 FR 48375)).

(4) Minor modifications to the methods in paragraphs (1) - (3) of this section may be approved by the executive director. Methods other than those specified in paragraphs (1) - (3) of this section may be used if approved by the executive director and validated using Method 301 (40 CFR Part 63, Appendix A). For the purposes of this paragraph, substitute "executive director" each place that Method 301 references "administrator."

§115.468. Monitoring and Recordkeeping Requirements.

(a) Monitoring requirements. The following monitoring requirements apply to the owner or operator of a solvent cleaning operation subject to this division that uses a vapor control system in accordance with §115.463(b) of this title (relating to Control Requirements). The owner or operator shall install and maintain monitors to accurately measure and record operational parameters of all required control devices, as necessary, to ensure the proper functioning of those devices in accordance with design specifications, including:

(1) continuous monitoring of the exhaust gas temperature immediately downstream of direct-flame incinerators or the gas temperature immediately upstream and downstream of any catalyst bed;

(2) the total amount of volatile organic compounds (VOC) recovered by carbon adsorption or other solvent recovery systems during a calendar month;

(3) continuous monitoring of carbon adsorption bed exhaust; and

(4) appropriate operating parameters for vapor control systems other than those specified in paragraphs (1) - (3) of this subsection.

(b) Recordkeeping requirements. The following recordkeeping requirements apply to the owner or operator of a solvent cleaning operation subject to this division.

(1) The owner or operator shall maintain records of the testing data, the material safety data sheet,or documentation of the standard reference texts used to determine the true vapor pressure of each VOC component, in accordance with the requirements in §115.465(1) of this title (relating to Approved Test Methods and Testing Requirements). The concentration of all VOC used to prepare the cleaning solution and, if diluted prior to use, the proportions that each of these materials is used must be recorded. Records must be sufficient to demonstrate continuous compliance with the VOC limits in §115.463(a), [ and] (e), and (f) of this title.

(2) The owner or operator claiming an exemption in §115.461 of this title (relating to Exemptions) shall maintain records sufficient to demonstrate continuous compliance with the applicable exemption criteria.

(3) The owner or operator claiming exemption from this division in accordance with §115.461(c) of this title shall maintain records indicating the applicable division the process or operation is subject to as specified in §115.461(c)(1) of this title and the control requirements or emission specifications used to control the VOC emissions from the solvent cleaning operation as specified in §115.461(c)(2) of this title. The owner or operator shall also comply with the applicable recordkeeping requirements from the division the process or operation is subject to sufficient to demonstrate that the VOC emissions from the solvent cleaning operation are controlled in accordance with the control requirements or emission specifications of that division.

(4) The owner or operator shall maintain records of any testing conducted in accordance with the provisions specified in §115.465(2) - (4) of this title.

(5) Records must be maintained a minimum of two years and be made available upon request to authorized representatives of the executive director, the United States Environmental Protection Agency, or any local air pollution agency with jurisdiction.

§115.469. Compliance Schedules.

(a) In Brazoria, Chambers, Collin, Dallas, Denton, Ellis, Fort Bend, Galveston, Harris, Johnson, Kaufman, Liberty, Montgomery, Parker, Rockwall, Tarrant, Waller, and Wise Counties the compliance date has passed for control requirements in §115.463(a) - (d) of this title (relating to Control Requirements) and all associated requirements, and the owner or operator of a solvent cleaning operation shall continue to comply with the requirements in this division, except as specified in subsection (d) and (e) of this section.

(b) The owner or operator of a solvent cleaning operation in the Bexar County area subject to the requirements of this division shall comply with each applicable requirement [the requirements in this division no later than], except for §115.463(f) of this title, by January 1, 2025. Compliance with the control requirement in §115.463(f) of this title must be achieved no later than March 1, 2026.

(c) The owner or operator of a solvent cleaning operation that becomes subject to this division on or after the applicable compliance date in this section shall comply with the requirements in this division no later than 60 days after becoming subject.

(d) The owner or operator of a solvent cleaning operation in Collin, Dallas, Denton, Ellis, Johnson, Kaufman, Parker, Rockwall, Tarrant, and Wise Counties shall be in compliance with the requirements of §115.463(e) of this title (relating to Control Requirements) no later than 270 days after the commission publishes notification in the Texas Register of its determination that the industrial cleaning solvent contingency requirements are necessary as a result of EPA publication of a notice in the Federal Register that the specified area failed to attain the applicable National Ambient Air Quality Standard for ozone by the attainment deadline or failed to demonstrate reasonable further progress as set forth in the 1990 Amendments to the federal Clean Air Act, §172(c)(9).

(e) The owner or operator of a solvent cleaning operation in Brazoria, Chambers, Fort Bend, Galveston, Harris, Liberty, Montgomery, and Waller Counties shall be in compliance with the requirements of §115.463(e) of this title no later than 270 days after the commission publishes notification in the Texas Register of its determination that the contingency requirements are necessary as a result of EPA publication of a notice in the Federal Register that the specified area failed to attain the applicable National Ambient Air Quality Standard for ozone by the attainment deadline or failed to demonstrate reasonable further progress as set forth in the 1990 Amendments to the federal Clean Air Act.

The agency certifies that legal counsel has reviewed the proposal and found it to be within the state agency's legal authority to adopt.

Filed with the Office of the Secretary of State on July 11, 2025.

TRD-202502443

Charmaine Backens

Deputy Director, Environmental Law Division

Texas Commission on Environmental Quality

Earliest possible date of adoption: August 24, 2025

For further information, please call: (512) 239-2678


CHAPTER 117. CONTROL OF AIR POLLUTION FROM NITROGEN COMPOUNDS

The Texas Commission on Environmental Quality (TCEQ, agency, or commission) proposes amendments to §§117.10, 117.200, 117.203, 117.205, 117.230, 117.235, 117.240, 117.245 and 117.9010.

If adopted, these rules would be submitted to the U.S. Environmental Protection Agency (EPA) as a state implementation plan (SIP) revision.

Background and Summary of the Factual Basis for the Proposed Rules

On June 20, 2024, EPA published the final reclassification of the Bexar County 2015 eight-hour ozone National Ambient Air Quality Standards (NAAQS) nonattainment area from moderate to serious, effective July 22, 2024 (89 Federal Register (FR) 51829). The attainment date for Bexar County under the serious classification is September 24, 2027, with a 2026 attainment year. TCEQ is required to submit serious classification attainment demonstration (AD) and reasonable further progress (RFP) SIP revisions to EPA by January 1, 2026, to comply with the serious ozone nonattainment area requirements, as outlined in federal Clean Air Act (FCAA), §§172(c), 182(c), and 182(f) for the Bexar County 2015 eight-hour ozone nonattainment area.

Nonattainment areas classified as moderate and above, including serious, are required to meet the mandates of the FCAA in §172(c)(1) and §182(c) and (f). FCAA, §172(c)(1) requires that the SIP incorporate all reasonably available control measures (RACM), including reasonably available control technology (RACT), as expeditiously as practicable and to provide for attainment of the NAAQS. FCAA, §182(c) addresses the SIP requirements for demonstrating attainment and RFP for areas classified as serious.

FCAA, §172(c) mandates that the commission submit an AD SIP revision to demonstrate that the Bexar County area will meet the NAAQS by its attainment date. Photochemical modeling for future years indicates that the Bexar County area will meet the 2015 ozone NAAQS by the mandated deadline using existing control strategies. The commission is neither required to propose nor is it proposing any amendments to demonstrate attainment for the Bexar County area in this rulemaking because the AD modeling demonstrates attainment without the need for additional measures. A RACM analysis to identify additional potential control measures that could expedite attainment of the NAAQS earlier than the area's attainment date is provided in the concurrently proposed Bexar County 2015 Ozone NAAQS Serious AD SIP Revision (Non-Rule Project No. 2024-041-SIP-NR). The RACM analysis determined that no potential control measures met the criteria to be considered RACM. As a result, no rule revisions are proposed as RACM.

FCAA, §182(f) requires the state to submit a SIP revision that implements RACT for all major sources of nitrogen oxides (NOX). EPA defines RACT as the lowest emission limitation that a particular source is capable of meeting by the application of control technology that is reasonably available considering technological and economic feasibility (44 FR 53761, September 17, 1979). RACT requirements for moderate and higher classification ozone nonattainment areas are included in the FCAA to ensure that significant source categories at major sources of ozone precursor emissions are controlled to a reasonable extent, but not necessarily to best available control technology levels expected of new sources or to maximum achievable control technology levels required for major sources of hazardous air pollutants. Although the FCAA requires the state to implement RACT, EPA guidance provides states with the flexibility to determine the most technologically and economically feasible RACT requirements for a nonattainment area. As currently defined in 30 Texas Administrative Code (TAC) §117.10(29), a major source of NOx is any stationary source or group of sources located within a contiguous area and under common control that emits or has the potential to emit a specific amount of NOX emissions based on the area's ozone nonattainment classification. For the Bexar County serious ozone nonattainment area, a major source of NOX is any stationary source or group of sources located within a contiguous area and under common control that emits or has the potential to emit at least 50 tons per year (tpy) of NOX.

For the reclassification to serious ozone nonattainment, TCEQ reviewed the 2022 point source Emissions Inventory (EI) to identify all major sources of NOX emissions in the Bexar County ozone nonattainment area. Since the point source EI database reports actual emissions rather than potential to emit, TCEQ reviewed sources that reported actual emissions as low as 10 tpy of NOX to account for the difference between actual and potential emissions. TCEQ also reviewed air permits to further confirm which sites with low emissions in 2022 were major sources of NOX due to authorized emissions of 50 or more tpy. Sites from the point source EI database with emissions of 10 tpy or more of NOX that could not be verified as minor sources by other means were included in the RACT analysis. To evaluate what rules would be necessary to fulfill RACT requirements, TCEQ considered other Chapter 117 rules that address other ozone nonattainment areas, rules in other states, and federal rules for the unit categories identified at the major NOX sources in the serious ozone nonattainment area. As part of this proposed rulemaking, TCEQ determined that the proposed rule revisions for the affected major NOX sources located in the Bexar County ozone nonattainment area would fulfill RACT requirements for those sources and be consistent with or more stringent than controls implemented in other ozone nonattainment areas within the state and outside the state. Because the Bexar County 2015 eight-hour ozone NAAQS nonattainment area was previously classified as moderate, sources that emit or have the potential to emit at least 100 tpy NOX are already required to comply with Chapter 117 RACT rules. On April 24, 2024, the commission adopted NOX RACT rules for sources in Bexar County under the moderate classification in a Chapter 117 rulemaking (Rule Project No. 2023-117-117-AI) that was part of the Bexar County 2015 Eight-Hour Ozone Standard Moderate Nonattainment Area RACT SIP Revision (Non-Rule Project No. 2023-132-SIP-NR). This proposed rulemaking would extend implementation of RACT to all major sources of NOX in the area that emit or have the potential to emit at least 50 tpy of NOX.

As required by FCAA, §172(c)(1) and §182(f), the proposed rulemaking would ensure that all major sources of NOX in the Bexar County ozone nonattainment area are subject to RACT, either by being subject to requirements that meet or exceed the applicable RACT requirements, or by determining that further emission controls on the sources in the area are either not economically feasible or not technologically feasible. Federally approved state rules and rule approval dates can be found in 40 Code of Federal Regulations (CFR) §52.2270(c), EPA Approved Regulations in the Texas SIP.

The commission proposes to revise Chapter 117, Subchapter B, Division 2 to change the requirements for major industrial, commercial, or institutional (ICI) sources of NOX in the Bexar County ozone nonattainment area to address NOX RACT requirements for serious ozone nonattainment areas. Proposed revisions would require some owners or operators of major ICI sources of NOX in Bexar County to reduce NOX emissions from certain stationary sources and source categories for the serious ozone nonattainment area. The proposed rulemaking would extend rule applicability of Subchapter B, Division 2 to stationary gas-fired engines fired on landfill gas, stationary diesel engines, ICI process heaters, natural gas-fired ovens, and incinerators. The proposed rulemaking would also include new emission standards for stationary gas-fired engines fired on landfill gas. Proposed rule revisions would further include new emission standards and exemptions for stationary diesel engines, process heaters, and natural gas-fired ovens. Proposed rule revisions would also include new exemptions for incinerators. The proposed rulemaking would also extend applicability of existing monitoring, testing, recordkeeping, and reporting requirements associated with Division 2 to the newly affected major sources of NOX located in the Bexar County serious ozone nonattainment area. These monitoring, testing, recordkeeping, and reporting requirements would be necessary to ensure compliance with the new emission specifications, confirm eligibility for certain exemptions, and ensure that NOX emission reductions are achieved from the units that become subject to the requirements of Chapter 117, Subchapter B, Division 2.

Section by Section Discussion

In addition to the proposed amendments associated with implementing RACT for the Bexar County ozone nonattainment area and specific minor clarifications and corrections discussed in greater detail in this section, this proposed rulemaking also includes various stylistic, non-substantive changes to update rule language to current Texas Register style and format requirements. Such changes include appropriate and consistent use of acronyms, section references, rule structure, and certain terminology. These changes are non-substantive and generally are not specifically discussed in this preamble.

Subchapter A, Definitions

Section 117.10, Definitions

The proposal would revise the definition of major source in §117.10(29)(B) to lower the major source threshold from 100 tpy to 50 tpy for NOX for sources in the Bexar County ozone nonattainment area. The change is necessary to address the area's reclassification to serious nonattainment for the 2015 eight-hour ozone NAAQS. Major sources affected by the proposed rulemaking would be required to comply with all applicable Chapter 117 rules by March 1, 2026, as stated in the rule compliance schedule in proposed revised §117.9010.

The proposed rulemaking would also expand the definition of unit in §117.10(51)(G) to include the list of units that would be covered under §117.205 concerning RACT emissions specifications in Bexar County. The proposed changes to §117.10(51)(G) would add process heaters and any other stationary source of NOX at a major source, as defined in §117.10. The proposed changes to §117.10(51)(G) would also replace the term "gas-fired lean-burn stationary reciprocating internal combustion engine" with the proposed new term "stationary internal combustion engine." As with the existing definition for stationary internal combustion engine, the proposed changes to §117.10(51)(G) would specify that stationary gas-fired lean-burn engines remain subject to the requirements of Subchapter B, Division 2 and that stationary diesel engines and stationary gas-fired engines fired on landfill gas would also become subject to the requirements of Subchapter B, Division 2. Because the emission reductions required by the RACT provisions necessitate further reductions from additional unit categories not previously covered, the proposed revisions broaden the applicability of the definition of unit to include any other stationary source of NOX at a major source, including those units that may qualify for a proposed exemption.

Subchapter B, Combustion Control at Major Industrial, Commercial, and Institutional Sources in Ozone Nonattainment Areas

Division 2, Bexar County Ozone Nonattainment Area Major Sources

Section 117.200, Applicability

The proposed rulemaking would expand the applicability of Subchapter B, Division 2 to include additional unit categories under §117.200. Section 117.200 currently applies to stationary gas turbines, duct burners used in turbine exhaust ducts, and gas-fired lean-burn stationary reciprocating internal combustion engines located at a major source of NOX in the Bexar County ozone nonattainment area. Proposed changes would add ICI process heaters and natural gas-fired ovens, flares, and incinerators to the list of applicable units. The term "gas-fired lean-burn stationary reciprocating internal combustion engines" in §117.200(3) is proposed to be replaced with the new term, "stationary internal combustion engines." Considering that the existing definition of stationary internal combustion engines in §117.10(46) addresses any reciprocating engine that satisfies the time in residence requirement of the definition, revising §117.200(3) to apply to stationary internal combustion engines would cover not only gas-fired lean-burn stationary reciprocating internal combustion engines, but also stationary diesel engines and stationary gas-fired engines fired on landfill gas. All known diesel-fuel fired and gaseous-fuel fired stationary engines at major NOX sources in the Bexar County ozone nonattainment area that are not identified as stationary turbines are reciprocating internal combustion engines.

The commission proposes to add new paragraphs (4) through (7) in §117.200 to expand applicability of the rule provisions of Subchapter B, Division 2 to ICI process heaters and natural gas-fired ovens, flares, and incinerators. These unit categories were identified in the 2022 point source EI at NOX major sources in the Bexar County ozone nonattainment area.

Section 117.203, Exemptions

Existing §117.203 lists the units that are exempt from the provisions of Chapter 117, Subchapter B, Division 2. The commission notes that the existing rule provision reference to §117.245(f)(9) in §117.203 is an error. Section 117.245(f) currently does not contain a paragraph (9). Therefore, the existing reference to §117.245(f)(9) in §117.203 is proposed to be deleted. Because the commission proposes a new §117.245(f)(7) to specify recordkeeping requirements concerning diesel engines and operating restrictions, the commission proposes a new rule provision reference to proposed new §117.245(f)(7) in §117.203. Because the commission further proposes a new §117.205(e) to specify operating restrictions for owners or operators of stationary diesel engines, the commission proposes a new rule provision reference to proposed new §117.205(e) in §117.203.

Proposed revised paragraph (1) would replace the term gas-fired lean-burn stationary reciprocating internal combustion engines with the term stationary internal combustion engines. This proposed change would coincide with the proposed change to §117.200(3) to list stationary internal combustion engines as applicable units subject to the provisions of Subchapter B, Division 2. With this proposed change, owners or operators of gas-fired lean-burn stationary reciprocating internal combustion engines, stationary diesel engines, and stationary gas-fired engines fired on landfill gas would be able to claim an exemption based on dedicated use. The allowed dedicated uses eligible for an exemption are listed in subparagraphs (A) through (E) of paragraph (1).

Existing §117.203(1)(D) provides for an exemption for owners or operators of stationary gas turbines and gas-fired lean-burn stationary reciprocating internal combustion engines that are used exclusively in emergency situations, as defined in §117.10(15), except that operation of the unit for testing or maintenance purposes of the unit is allowed for up to 100 hours per year, on a rolling 12-month basis. For an owner or operator of a stationary diesel engine used exclusively in emergency situations, as defined in §117.10(15), to claim this exemption, proposed revisions to subparagraph (D) would specify that a stationary diesel engine would have to be placed into service before March 1, 2026. The proposed change would make clear that any new stationary diesel engine and any modified, reconstructed, or relocated existing stationary diesel engine placed into service on or after March 1, 2026, would be ineligible for the exemption under proposed revised subparagraph (D). For the purposes of this exemption, the terms "modification" and "reconstruction" have the meanings defined in 30 TAC §116.10 and 40 CFR §60.15 (December 16, 1975), respectively, and the term "relocated" means to newly install at an account, as defined in 30 TAC §101.1, a used engine from anywhere outside that account.

This proposed change would mirror similar provisions in other parts of Chapter 117 for other ozone nonattainment areas for owners or operators of stationary diesel engines claiming an exemption based on dedicated emergency use. The proposed change to subparagraph (D) provides owners or operators of existing stationary diesel engines that are used solely for emergency reasons the opportunity to continue to rely on such units without having to modify an engine, install post-combustion controls, or replace a unit to meet proposed NOX emission specifications so long as the existing unit is never modified or reconstructed, nor is an existing unit ever relocated from outside the area to a major source of NOX in the Bexar County ozone nonattainment area, on or after the proposed threshold date. These changes to the existing exemption are proposed due to the relatively small NOX emissions contribution in the area from these sources due to their limited, dedicated use or the impracticality of using NOX emissions controls during such limited operating times. A threshold date is proposed in §117.203(1)(D) to ensure the net effect is that existing stationary diesel engines, if used exclusively in emergency situations and placed into service before the proposed threshold date, would be exempt from the new emission specifications in proposed new §117.205(a)(3)(B), whereas new, modified, reconstructed, or relocated stationary diesel engines placed into service on or after March 1, 2026, would be required to be cleaner diesel engines. New, modified, reconstructed, or relocated stationary diesel engines placed into service on or after March 1, 2026, would be required to meet federal Tier 4 emission standards for non-road diesel engines in effect at the time of installation, modification, reconstruction, or relocation. These proposed measures would leverage the natural replacement cycle of equipment and ensure that as older stationary diesel engines reach the end of their operational life, and turnover of older, higher-emitting stationary diesel engines occurs, the replacement units would be cleaner diesel engines. The gradual modernization of stationary diesel engines in the Bexar County area would lead to consistent decreases in NOX emissions, helping the area comply with more stringent NAAQS.

The proposed changes to §117.203 would also add a new §117.203(2) to exempt existing stationary diesel engines located at major sources of NOX in the Bexar County ozone nonattainment area that are placed into service before March 1, 2026, and operate less than 100 hours per calendar year on a rolling 12-month basis. The proposed new §117.203(2) would not exempt any modified, reconstructed, or relocated stationary diesel engine placed into service on or after March 1, 2026. For the purposes of this exemption, the terms "modification" and "reconstruction" have the meanings defined in 30 TAC §116.10 and 40 CFR §60.15 (December 16, 1975), respectively, and the term "relocated" means to newly install at an account, as defined in 30 TAC §101.1, a used engine from anywhere outside that account. This exemption in proposed new §117.203(2) would be similar in effect to the proposed revisions to §117.203(1)(D) in that an owner or operator of an existing stationary diesel engine could continue to operate the unit provided the unit would not be altered on or after the rule compliance date. This would help to ensure that the same NOx emissions profile from the existing unit could be expected in the future. This would also help to ensure that all NOX emissions from any existing unit already located in the nonattainment area and any existing unit that may be moved into the area, thus considered new, are accounted for during SIP development. Based on reported information in the 2022 point source EI, the commission does not anticipate owners or operators of existing stationary diesel engines placed into service before the proposed threshold date of March 1, 2026, would be unable to meet the proposed operating hour requirement of less than 100 hours per calendar year based on a rolling 12-month basis.

The proposed changes to §117.203 would further add a new §117.203(3) to exempt new, modified, reconstructed, or relocated stationary diesel engines located at major sources of NOX in the Bexar County ozone nonattainment area if the new, modified, reconstructed, or relocated stationary diesel engine is placed into service on or after March 1, 2026, operates less than 100 hours per calendar year on a rolling 12-month basis and meets the corresponding NOX emission standard for non-road engines listed in 40 CFR §1039.101, Table 1 (effective July 29, 2021), and in effect at the time of installation, modification, reconstruction, or relocation. Operating time during emergency situations, as defined in §117.10(15), would be excluded from the limit on operating hours under proposed new §117.203(3). For the purposes of this exemption, the terms "modification" and "reconstruction" have the meanings defined in 30 TAC §116.10 and 40 CFR §60.15 (December 16, 1975), respectively, and the term "relocated" means to newly install at an account, as defined in 30 TAC §101.1, a used engine from anywhere outside that account. Similar to the proposed revisions to §117.203(1)(D) and proposed new §117.203(2), owners or operators of existing units could continue to operate their existing units as they previously had provided the units would not be altered on or after the proposed threshold date of March 1, 2026. Furthermore, these and the other proposed new requirements for stationary diesel engines would ensure that as turnover of older, higher-emitting stationary diesel engines occurs, the replacement units would be cleaner diesel engines.

Existing paragraphs (2) and (3) in §117.203 are proposed to be renumbered to paragraphs (4) and (5), respectively. Existing paragraph (2), renumbered as paragraph (4), concerning exempt units, continues to apply to gas-fired lean-burn stationary internal combustion engines rated less than 50 horsepower (hp) and fired on any type of gaseous fuel other than landfill gas. The commission also proposes to remove the word "reciprocating" from the term "gas-fired lean-burn stationary reciprocating internal combustion engines" in existing paragraph (2), renumbered as paragraph (4), because, for purposes of Chapter 117, the concept of a reciprocating engine is implied with stationary engines as opposed to rotary engines. For purposes of Chapter 117, rotary engines are considered stationary turbines, and the existing definition for stationary internal combustion engine in §117.10 already includes the term "reciprocating." Existing paragraph (3), renumbered as paragraph (5), concerning exempt units, continues to apply to stationary gas turbines with a maximum rated capacity less than 10.0 million British thermal units per hour (MMBtu/hr). Existing paragraph (3), renumbered as paragraph (5), would further include the new acronym "MMBtu/hr" for "million British thermal units per hour."

The commission proposes new §117.203(6) to specify that ICI process heaters with a maximum rated capacity equal to or less than 5.0 MMBtu/hr are exempt from the provisions of Subchapter B, Division 2. The commission identified nine process heaters in the 2022 point source EI, with all nine units located at the same major source of NOX in the Bexar County ozone nonattainment area. Because three units had reported heat input equal to or less than 5.0 MMBtu/hr, the commission anticipates that these three units would qualify for exemption from the proposed rulemaking. Because the remaining six units had reported heat inputs equal to or greater than the proposed exemption threshold of 5.0 MMBtu/hr, these six units are anticipated to require NOX emission reductions to meet the proposed NOX emission specification requirements for ICI process heaters in proposed revised §117.205. This exemption level is proposed in §117.203 due to the relatively small contribution of NOX emissions from units that are equal to or less than 5.0 MMBtu/hr and the impracticality of installing and maintaining NOX controls on such units for this proposed rulemaking.

The proposed rulemaking would specify in new §117.203(7) that natural gas-fired ovens with a maximum rated capacity equal to or less than 5.0 MMBtu/hr are exempt from the provisions of Subchapter B, Division 2. The commission identified seven ovens in the 2022 point source EI, with all seven units located at the same major source of NOX in the Bexar County ozone nonattainment area. Because three units had reported heat input equal to or less than 5.0 MMBtu/hr, the commission anticipates that these three units would qualify for exemption from the proposed rulemaking. Because the remaining four units had reported heat inputs equal to or greater than the proposed exemption threshold of 5.0 MMBtu/hr, these four units are anticipated to require NOX emission reductions to meet the proposed NOX emission specification requirements for natural gas-fired ovens in proposed revised §117.205. Similar to the exemption proposed for ICI process heaters, this exemption level for natural gas-fired ovens is proposed due to the relatively small contribution of NOX emissions from units that are equal to or less than 5.0 MMBtu/hr and the impracticality of installing and maintaining NOX controls on such units for this proposed rulemaking.

Proposed new §117.203(8) would add an exemption for flares from the provisions of Subchapter B, Division 2. Proposed new §117.203(9) would exempt incinerators with a maximum rated capacity less than 40 MMBtu/hr from the provisions of Subchapter B, Division 2. The proposed exemptions for these unit types located at major sources of NOX in the Bexar County ozone nonattainment area are consistent with existing exemptions for the Dallas-Fort Worth (DFW) eight-hour ozone nonattainment area major sources, in existing §117.403(a)(3), and for the Houston-Galveston-Brazoria (HGB) ozone nonattainment area major sources, in existing §117.303(a)(4). The commission identified four incinerators in the 2022 point source EI at major sources of NOX in the Bexar County ozone nonattainment area, with all four units expected to qualify for exemption under proposed new §117.203(9). Existing §117.203(4) is proposed to be renumbered as §117.203(10).

Section 117.205, Emission Specifications for Reasonably Available Control Technology (RACT)

The commission proposes to revise §117.205(a)(3) as part of a broader effort to include additional types of stationary internal combustion engines located at major sources of NOX. Currently, §117.205(a)(3) specifies NOX emission limits for only gas-fired lean-burn engines not fired on landfill gas. The proposed revision would expand these specifications to include two additional engine types: gas-fired lean-burn engines fired on landfill gas and diesel engines. Proposed new §117.205(a)(3)(A)(i) would specify that gas-fired lean-burn engines fired on landfill gas would be subject to a NOX emission standard of 0.60 grams per horsepower-hour (g/hp-hr). The landfill gas fired in these stationary engines is a byproduct of the decomposition of organic waste in a nearby municipal solid waste landfill, with methane composing much of the waste gas. The proposed Bexar County NOX emission specification for stationary engines that are fired on landfill gas is based on the NOX emission specification for similar units located at NOX major sources in the DFW eight-hour ozone nonattainment area, §117.410(a)(4)(B)(ii)(I), and in the HGB ozone nonattainment area, §117.310(a)(9)(B)(i), respectively. The proposed emission specification of 0.60 g/hp-hr in §117.205(a)(3)(A)(i) is expected to be achievable through combustion modifications. The existing NOX emission standard of 0.50 g/hp-hr in §117.205(a)(3), for gas-fired lean-burn stationary reciprocating internal combustion engines, is proposed to be moved to new §117.205(a)(3)(A)(ii).

The proposed changes to §117.205(a)(3) further add a new subparagraph (B) that would establish NOX emission standards for stationary diesel engines based on the size of the stationary diesel engine and the date the engine was installed, modified, reconstructed, or relocated in the Bexar County ozone nonattainment area. The proposed NOX standards in new §117.205(a)(3)(B) are based on EPA's Tier 4 emission standards for non-road diesel engines listed in 40 CFR §1039.101, Table 1 (effective July 29, 2021). While EPA's Tier 4 emission standards are also based on engine size, they differ from TCEQ's standards in proposed new §117.205(a)(3)(B) in that they are also based on the engine model year and the dedicated end-use for larger diesel engines.

With promulgation of the new Tier 4 diesel emission standards in 40 CFR Part 1039, EPA established another comprehensive, new program to phase in more stringent Tier 4 emission standards for all diesel engine sizes, similar to its earlier rulemaking efforts for the Tier 2 and Tier 3 emission standards. The Tier 4 emission standards were phased in beginning with model year 2008, requiring lower standards for certain engine sizes and model years 2011 and 2012, and being fully implemented by 2015. Some of the Tier 4 NOX emission standards for certain engine sizes and model years overlap with some of EPA's prior tier emission standards.

Because some of EPA's Tier 4 exhaust emission standards for diesel engines are expressed in terms of nonmethane hydrocarbons (NMHC) + NOX, the commission used Table 7: Tier 2 and Tier 3 Combined and Estimated Pollutant-Specific Emissions Standards for Nonroad Diesel Engines from EPA's Exhaust and Crankcase Emission Factors for Nonroad Engine Modeling--Compression-Ignition, Report No. NR-009C (EPA420-P-04-009, revised April 2004) to split the combined NMHC + NO X Tier 4 standards into single pollutant emission standards for NOX, where necessary.

Proposed new §117.205(a)(3)(B)(i) - (iv) would establish NOX emissions performance standards for stationary diesel engines rated less than 25 hp and through 750 hp and that are installed, modified, reconstructed, or relocated on or after March 1, 2026. Proposed new §117.205(a)(3)(B)(v) would establish a NOX emission specification for stationary diesel engines rated greater than 750 hp that are electric generator sets and are installed, modified, reconstructed, or relocated on or after March 1, 2026. Proposed new §117.205(a)(3)(B)(vi) would establish a NOX emission specification for stationary diesel engines rated greater than 750 hp that exclude electric generator sets and are installed, modified, reconstructed, or relocated on or after March 1, 2026.

Proposed revisions to §117.205(a) include a new paragraph (4) to specify new NOX emission specifications for process heaters located at NOX major sources in the Bexar County ozone nonattainment area. Proposed new §117.205(a)(4)(A) would include a NOX emission specification of 0.025 pounds per million British thermal units (lb/MMBtu) for process heaters with a maximum rated capacity equal to or greater than 40 million British thermal units per hour (MMBtu/hr). Proposed new §117.205(a)(4)(B) would include a NOX emission limit of 0.036 lb/MMBtu (or alternatively, 30 parts per million by volume (ppmv), at 3.0% oxygen (O2), dry basis) for process heaters with a maximum rated capacity less than 40 MMBtu/hr. Post-combustion NOX control such as selective catalytic reduction (SCR) may be necessary for some gas-fired process heaters with a maximum rated capacity equal to or greater than 40 MMBtu/hr to comply with the proposed 0.025 lb/MMBtu emission specification. Given advancements in burner technology to produce the same output with fewer NOX emissions, some units of this size category may be able to meet the proposed limit of 0.025 lb/MMBtu through combustion modifications such as low-NOX burners (LNB), or more specifically the next generation of LNB or ultra low-NOX burners (ULNB). Owners or operators of gas-fired process heaters with maximum rated capacities less than 40 MMBtu/hr may be required to install LNB, ULNB, or make other combustion modifications to comply with the proposed 0.036 lb/MMBtu (or 30 ppmv, at 3.0% O2, dry) emission specification. No liquid-fired process heaters were identified in the 2022 point source EI in the Bexar County ozone nonattainment area; however, SCR may be necessary for a liquid-fired process heater to comply with the proposed emission specifications. The NOX emission standards for units located in Bexar County are proposed at the same NOX performance level for ICI process heaters located at major NOX sources in the DFW eight-hour ozone nonattainment area, §117.410(a)(3), and in the HGB ozone nonattainment area, §117.310(a)(8)(A), respectively.

Proposed new §117.205(a)(5) would establish a 0.036 lb/MMBtu NOX emission specification for natural gas-fired ovens used in industrial, commercial, or institutional processes. This proposed new emission specification is anticipated to be achievable through combustion modifications, such as burner modifications or installation of LNB or possibly ULNB. The proposed emission limit in new §117.205(a)(5) aligns with the NOX emission specification for natural gas-fired ovens subject to §117.410(a)(12) for the DFW eight-hour ozone nonattainment area. The commission did not identify in the 2022 point source EI for the Bexar County ozone nonattainment area any ovens using fuels other than natural gas. However, for ovens using fuels other than natural gas, particularly liquid fuels, NOX emissions controls in addition to or beyond burner modifications, LNB, or ULNB may be necessary.

The commission further proposes a new §117.205(a)(6) to establish a NOX emission specification for incinerators that would not qualify for the proposed exemption under proposed new §117.203(9). Owners or operators of these units would be required to comply with a 0.030 lb/MMBtu emission specification. While this proposed emission specification for incinerators may be achievable through installation of LNB or through other combustion modifications, SCR may be necessary to achieve the 0.030 lb/MMBtu emission specification. This proposed new NOX limit for incinerators in the Bexar County ozone nonattainment area is set at the same NOX performance level as for incinerators subject to the provisions of Subchapter B, Divisions 3 and 4 for the HGB and DFW areas (§117.310(a)(16)(B) and §117.410(a)(9)(B)), respectively.

Proposed revisions to §117.205(b), concerning NOX averaging times for units subject to a NOX emission specification under §117.205(a), include repealing existing §117.205(b)(1) and proposing it as new §117.205(b)(2), with amendments. Proposed new §117.205(b)(2) would specify that compliance with the NOX emission specifications in §117.205(a) must be determined on a block one-hour averaging time, in the units of the applicable NOX emission specification, for units that do not operate with a NOX continuous emission monitoring system (CEMS) or predictive emission monitoring system (PEMS) under §117.240 of Subchapter B, Division 2. Proposed new §117.205(b)(2) would provide for the same requirements as existing §117.205(b)(1) and further specify that the block one-hour averaging time would apply to owners or operators of units that do not operate with a NOX CEMS or PEMS. Proposed new §117.205(b)(2) further includes a new provision for owners or operators of process heaters in the Bexar County ozone nonattainment area by providing an alternative NOX averaging time for demonstrating compliance with the NOX limits in §117.205(a). If a process heater that is subject to §117.205(a) is not operated with a NOX CEMS or PEMS under §117.240, under proposed new §117.205(b)(2) the owner or operator may choose to calculate the actual NOX emissions rate from the unit on a pounds per hour basis by multiplying the unit's maximum rated capacity by the unit's applicable NOX emission specification in lb/MMBtu and using this calculated result to show compliance with the applicable specifications in Subchapter B, Division 2. Under this alternative NOX averaging time, where the owner or operator shows compliance on a block one-hour average in pounds per hour as opposed to on a block one-hour average in the units of the applicable NOX emission specification, the calculated value for the process heater would be compared to the performance evaluation result obtained through the emissions stack testing that would be required by the initial demonstration of compliance provisions under §117.235 of Subchapter B, Division 2. This alternative would allow for a direct comparison between the calculated theoretical emissions and the measured actual emissions, providing an alternative method to verify compliance with the applicable NOX standard.

Existing §117.205(b)(2) is proposed to be renumbered as §117.205(b)(1), and three new subparagraphs would also be added. For units, except process heaters, that operate with a NOX CEMS or PEMS under §117.240, the owner or operator would be able to choose between two different NOX averaging times to show compliance with the NOX emission specifications in §117.205(a). Proposed new §117.205(b)(1)(A) offers flexibility to comply with the specifications in §117.205(a) on a 30-day rolling average in the units of the applicable emission standard. Proposed new §117.205(b)(1)(B) offers flexibility to comply with the specifications in §117.205(a) on a block one-hour average in the units of the applicable emission standard. The owner or operator of a process heater in the Bexar County ozone nonattainment area would have an additional option in proposed new §117.205(b)(1)(C). As an alternative to the 30-day rolling average in the units of the applicable emission standard in proposed new §117.205(b)(1)(A) and to the block one-hour average in the units of the applicable emission standard in proposed new §117.205(b)(1)(B), proposed new §117.205(b)(1)(C) for process heaters would offer flexibility to comply with the specifications in §117.205(a) on a block one-hour average in pounds per hour. Like the alternative for process heaters under proposed new §117.205(b)(2), with amendments, the owner or operator may choose to calculate the actual NOX emissions rate from the unit on a pounds per hour basis by multiplying the unit's maximum rated capacity by the unit's applicable NOX emission specification in lb/MMBtu and using this calculated result to show compliance with the applicable NOX emission specifications in Subchapter B, Division 2. The commission further proposes to rearrange the wording of the NOX averaging time for 30 days from "rolling 30-day average" to "30-day rolling average," to keep use of this term within the chapter consistent with how the term is worded within its definition in §117.10.

The reclassification of the Bexar County ozone nonattainment area to serious resulted in the identification of additional major source NOX emissions units, including flares and incinerators. For purposes of ozone attainment, it is necessary to prevent circumvention due to the transfer of NOX emissions associated with chemical-bound nitrogen from a unit under which these emissions would be controlled to a unit that is not subject to the NOX emission specifications in §117.205(a), and therefore uncontrolled. Proposed changes to §117.205(d) add a new paragraph (3) that would prohibit changes to a unit subject to a NOX emission specification in §117.205(a) that would result in increased NOX emissions from a unit that is not subject to the NOX emission specifications in §117.205(a). An example of this type of change that would be prohibited under proposed new §117.205(d)(3) would be redirecting one or more fuel or waste streams containing chemical-bound nitrogen to an incinerator with a maximum rated capacity less than 40 MMBtu/hr, or a flare. The redirection of the fuel or waste stream would result in increased NOX emissions from the unit not subject to a NOX emission specification in §117.205(a). Consequently, these additional NOX emissions would not have been accounted for in the SIP revision for the ozone nonattainment area and either deemed insignificant or not needing additional NOX emissions control. The proposed prohibition threshold date of December 19, 2019, was the modeling base year for the attainment demonstration SIP revision required at the time that the Bexar County ozone nonattainment area was classified as moderate. The 2019 base year was also used in the concurrent proposed Bexar County 2015 ozone NAAQS serious attainment demonstration SIP revision, thus the December 19, 2019, date remains appropriate for the prohibition threshold. Therefore, any changes after December 19, 2019, to a unit subject to §117.205(a) that would result in increased NOX emissions from another unit not subject to §117.205(a) would be prohibited, unless certain criteria are met, as explained below.

An owner or operator would be allowed to make such changes that would otherwise be prohibited under proposed new §117.205(d)(3) only if both of the conditions under proposed new §117.205(d)(3)(A) and (B) were satisfied. Under proposed new §117.205(d)(3)(A), the increase in NOX emissions from the unit not subject to the NOX emission specifications in §117.205(a) must be determined either using a NOX CEMS or PEMS that meets the requirements in §117.240 of Subchapter B, Division 2 or through emissions stack testing that meets the requirements in §117.235 of Subchapter B, Division 2. Under proposed new §117.205(d)(3)(B), emission credits that are equal to the increase in NOX emissions from the unit not subject to the NOX emission specifications in §117.205(a) must be obtained and used in accordance with §117.9800 of Subchapter H, Division 2. Any change to a unit subject to §117.205(a) that resulted in increased NOX emissions from another unit not subject to §117.205(a) after December 19, 2019, and before the effective date of this proposed rulemaking, if adopted, would still be prohibited. Existing §117.205(d)(3) is proposed as renumbered §117.205(d)(4).

Proposed revisions to §117.205 further include a new subsection (e) that would prohibit an owner or operator of a stationary diesel engine in the Bexar County ozone nonattainment area from starting or operating the stationary diesel engine between the hours of 6:00 a.m. and noon for testing or maintenance of the engine itself, with three specified exceptions to the prohibition. This proposed new requirement on starting or operating restrictions for stationary diesel engines would delay the emissions of NOX, a key ozone precursor, until after noon (12:00 p.m.) to limit ozone formation. Proposed new §117.205(e)(1) would allow the starting or operation of the stationary diesel engine between the hours of 6:00 a.m. and noon if it is for a manufacturer's specific recommended testing requiring a run of over 18 consecutive hours. Proposed new §117.205(e)(2) would allow the starting or operation of the stationary diesel engine between the hours of 6:00 a.m. and noon if it is to verify reliability of emergency equipment (e.g., emergency generators or pumps) immediately after unforeseen repairs. Routine maintenance, such as an oil change, is not considered to be an unforeseen repair since it can be scheduled outside the 6:00 a.m. to noon time period. Finally, proposed new §117.205(e)(3) would allow the starting or operation of the stationary diesel engine between the hours of 6:00 a.m. and noon if it is for the purpose of using firewater pumps that are used for emergency response training conducted between April 1 and October 31 of a calendar year.

Section 117.230, Operating Requirements

The commission proposes a new subsection (a) in existing §117.230 to require that the owner or operator of any unit subject to the NOx emission specifications in §117.205(a) must operate the unit in compliance with those limitations. The existing introductory rule text in §117.230 is moved to new subsection (b) in §117.230. The commission further proposes in new paragraphs (1) - (2) of proposed renumbered §117.230(b) operational requirements for owners or operators of process heaters that use forced draft flue gas recirculation (FGR) or induced draft FGR for control of NOX emissions. Proposed new §117.230(b)(3) would specify operational requirements for owners or operators of units that use steam or water injection for control of NOX emissions. Existing §117.230(1) is proposed to be renumbered as §117.230(b)(4). Existing §117.230(2) is proposed to be renumbered as §117.230(b)(5). Similar to the existing provisions under §117.230(1) and (2), before proposed changes, for operational requirements for post-combustion NOX control techniques and gas-fired lean-burn stationary engines, the purpose of proposed new §117.230(b)(1) - (3) is to require that equipment be operated in such a manner as to reduce NOX emissions over the entire operating range. These proposed new requirements would ensure that NOX reductions are achieved, particularly for units that operate without a NOX emissions monitor, i.e. a NOX CEMS or PEMS. Finally, the commission proposes in renumbered §117.230(b)(5) to replace the term "gas-fired lean-burn stationary reciprocating internal combustion engine" with the new term "stationary internal combustion engine." This proposed change in existing §117.230(2), renumbered as §117.230(b)(5), would require that all stationary internal combustion engines covered under Subchapter B, Division 2, and not only gas-fired lean-burn stationary engines, must be checked for proper engine operation according to §117.8140(b) of Subchapter G, Division 2. This change would be necessary to be consistent with the proposed changes for new §117.205(a)(3) as part of this proposed rulemaking.

Section 117.235, Initial Demonstration of Compliance

The commission proposes in revised §117.235(a) that the owner or operator of any NOX emissions unit that does not qualify for an exemption from the NOX emission specifications in Subchapter B, Division 2 is required to conduct emissions performance testing for each unit that is subject to a NOX emission specification of the division.

The commission proposes in revised §117.235(e) to specify that for units operating without a NOX emissions monitor, the initial demonstration of compliance with the NOX emission specifications of Subchapter B, Division 2 must be performed according to the requirements in §117.8000 of Subchapter G, Division 1. The word "initially" was previously not part of the rule provision language for §117.235(e). Proposed revisions to §117.235(e) would follow the same intent as existing requirements in §117.235(f).

Proposed revisions to §117.235(f) include minor rewording to the subsection to make clear that if an owner or operator of a unit subject to the emission specifications in §117.205(a) is required or otherwise elects to use a NOX CEMS or PEMS, which must be installed, calibrated, maintained, and operated in accordance with §117.240 of Subchapter B, Division 2, the NOX monitor must undergo monitor certification testing first before being used to monitor NOX emissions from the unit for both the initial compliance demonstration required under §117.235 and ongoing compliance demonstrations required under §117.240. Requirements for a NOX specification on a block one-hour average are deleted from §117.235(f) and moved to new §117.235(f)(2), as described below.

The commission proposes a new §117.235(f)(1) to specify how an owner or operator demonstrating compliance with proposed revised §117.235(f) must determine the NOX emissions from the unit to demonstrate initial compliance with the emission specifications of §117.205(a) for an emission specification expressed in units of lb/MMBtu and based on a 30-day rolling average. Proposed new §117.235(f)(2) would specify how an owner or operator demonstrating compliance with proposed revised §117.235(f) must determine the NOX emissions from the unit to demonstrate initial compliance with the emission specifications of §117.205(a) for an emission specification on a block one-hour average. These rule provisions for demonstrating initial compliance with the applicable NOX emission specifications for owners or operators of units operating with a NOX monitor align with other similar provisions that exist in other parts of Chapter 117, specifically in §117.435(e)(1) and (2) for the DFW eight-hour ozone nonattainment area and in §117.335(f)(1) and (2) for the HGB ozone nonattainment area, respectively. To be consistent with the two options for the NOX averaging time provided in proposed renumbered §117.205(b)(1), notwithstanding the third option specific to owners or operators of process heaters choosing compliance in units of pounds per hour, proposed new subsection (f)(1) and (2) are necessary for owners or operators of units operating with a NOX monitor to show compliance depending on the averaging time chosen by the owner or operator. If a 30-day rolling average is chosen under proposed new §117.205(b)(1)(A), the owner or operator is required to comply with proposed new §117.235(f)(1). If a block one-hour average is chosen under proposed new §117.205(b)(1)(B), the owner or operator is required to comply with proposed new §117.235(f)(2).

Proposed new §117.235(f)(1) would specify that the calculated initial 30-day average emission rate must be used to show initial compliance with the applicable NOX emission specification in §117.205(a). The 30-day average emission rate is calculated as the total NOX emissions from a unit, in pounds, during a 30-day test period divided by the total heat input to the unit, in MMBtu, during the same 30-day test period. Any 30-day test period may be chosen by the owner or operator so long as the unit operates for 30 successive days for the NOX emissions monitoring to occur. Proposed new §117.235(f)(2) would specify that any one-hour period of NOX emissions monitoring using the certified NOX monitor, while the unit operates at its maximum rated capacity, or as near thereto as practicable, must be used to show initial compliance with the applicable NOX emission specification in §117.205(a). Any one-hour period may be used by the owner or operator of the unit since a NOX emissions monitor used in compliance with Chapter 117 must be able to show compliance with EPA's regulations under 40 CFR Part 60 or Part 75, EPA-compliant NOX emissions monitors provide hourly averages of NOX emissions, and the averaging time for the initial compliance demonstration is on an hourly basis.

Section 117.240, Continuous Demonstration of Compliance

Existing §117.240(a)(2) provides alternatives to the requirements of §117.240(a)(1). The commission proposes to revise §117.240(a)(2)(C) by replacing the term "gas-fired lean-burn stationary reciprocating internal combustion engines" with the new term, "stationary internal combustion engines." This change would be necessary because the commission is proposing to expand the applicability of the rule provisions of Subchapter B, Division 2 to additional types of stationary engines. Proposed revised §117.240(a)(2)(C) would therefore specify that the alternative in existing §117.240(a)(2)(C) to the totalizing fuel flow metering requirement in §117.240(a)(1) would be available to an owner or operator of any stationary internal combustion engine that triggers applicability under proposed revised §117.200.

Existing §117.240(b)(2) specifies that units subject to the NOX CEMS requirements of 40 CFR Part 75 are not required to install a NOX CEMS or PEMS under §117.240(b). The commission proposes to expand §117.240(b)(2) to incorporate new provisions for stationary diesel engines. The commission proposes to move the existing exception provided to units subject to 40 CFR Part 75 to a proposed new §117.240(b)(2)(A). Proposed new §117.240(b)(2)(B) would provide an exception for owners or operators of stationary diesel engines with SCR systems from the requirement to install a NOX CEMS or PEMS. To qualify for the exception, the stationary diesel engine must operate with an SCR emissions control system for NOX and meet all the criteria in proposed new §117.240(b)(2)(B)(i) - (vi). Stationary diesel engines operated in this manner are expected to be newer diesel engines that would already be certified to EPA's Tier 4 emission standards in 40 CFR §1039.101, Table 1 (effective July 29, 2021). Currently, most diesel engine manufacturers incorporate SCR emissions control systems to produce engines that can be certified to EPA's Tier 4 emission standards for NOX. The SCR emissions control system built into the operational design of the diesel engine makes the operation of the diesel engine without the SCR practically impossible. The criteria specified in proposed new §117.240(b)(2)(B)(i) - (iv) are from 40 CFR Part 1039, Subpart B for monitoring reductant use and unit and control system diagnostic functions. Consequently, an owner or operator of a stationary diesel engine operating with an SCR system and according to the conditions in proposed new §117.240(b)(2)(B) would not need to monitor exhaust NOX with a NOX CEMS or PEMS under §117.240(b). The proposed rule provisions for stationary diesel engines under §117.240(b)(2)(B) do not waive the requirement for an owner or operator to demonstrate initial compliance with the NOX emission specifications of Subchapter B, Division 2 according to §117.235, ongoing compliance with the engine monitoring requirements in §117.240(e), or ongoing compliance with the retesting provisions in §117.240(h)(2), if retesting is triggered.

Similar to the proposed revision to §117.240(a)(2)(C), proposed revisions to §117.240(e) include replacing the term, gas-fired lean-burn stationary reciprocating internal combustion engine, with the new term, stationary internal combustion engine. Like other changes proposed in this rulemaking for stationary engines, this change would be necessary to extend existing engine monitoring requirements to all stationary engines that would trigger applicability to the rule provisions of Subchapter B, Division 2 through proposed revised §117.200. The commission also proposes to add language to §117.240(e) to make clear that the requirement to stack test is for engines that are not equipped with a NOX CEMS or PEMS. For stationary engines not required to operate with a NOX monitor, or for those units for which the owner or operator elects not to use a NOX monitor, owners or operators of stationary engines that trigger the engine emissions monitoring requirement under §117.240(e) would be required to conduct periodic emissions testing in accordance with the provisions in §117.8140(a). This requirement to conduct periodic emissions testing for stationary engines exists in §117.440(h) for stationary gas engines in the DFW eight-hour ozone nonattainment area and in §117.340(h) for all stationary engines in the HGB ozone nonattainment area.

Section §117.240(f) requires owners or operators of stationary gas turbines or gas-fired lean-burn stationary reciprocating internal combustion engines to record the unit's operating time with a non-resettable elapsed run time meter if the unit is claimed exempt using the exemption in §117.203(1)(D). Proposed revised §117.240(f) would extend the existing run time meter and operating time recording requirement to owners or operators of units claimed exempt using the exemptions in proposed new §117.203(2) or in proposed new §117.203(3). Like other proposed changes for stationary engines in this proposed rulemaking, the commission proposes to also replace the term gas-fired lean-burn stationary reciprocating internal combustion engine with the new term stationary internal combustion engine in proposed revised §117.240(f). These proposed new inclusions for §117.240(f) would mirror, as necessary, existing rule provision requirements for stationary gas turbines and stationary internal combustion engines for units claimed exempt in the DFW eight-hour ozone nonattainment area, in §117.440(i), and in the HGB ozone nonattainment area, in §117.340(j).

To be consistent with the proposed clarification in §117.240(e) concerning stationary engines that do not operate with a NOX emissions monitor, either a CEMS or PEMS, the commission proposes to clarify in §117.240(h)(2) that for units not operating with a NOX monitor, owners or operators of such units must retest their units, as specified in §117.235, within 60 days after any modification to a unit that could reasonably be expected to increase the NOX emissions rate from the modified unit. The NOX emissions retesting would be conducted according to §117.235(a), (e), and (g) of Subchapter B, Division 2. The emissions retesting provision in §117.240(h)(2) applies to any unit subject to a NOX emission specification in §117.205(a) that does not use a NOX monitor and for which a modification occurs that could reasonably be expected to increase the NOX emissions rate from the unit.

Section 117.245, Notification, Recordkeeping, and Reporting Requirements

The commission proposes to move the existing notification requirements for owners or operators of units subject to the NOX emission specifications in §117.205(a) from §117.245(b) to new paragraphs (1) and (2) within the subsection. The purpose is to make clearer, by separating into two new paragraphs, the existing notification requirements for emissions testing conducted under §117.235, in proposed new §117.245(b)(1), and the existing notification requirements for NOX monitor performance evaluations conducted under §117.240, in proposed new §117.245(b)(2).

Proposed revisions to §117.245(e) include replacing the existing term, "gas-fired engine," with the new term, "stationary internal combustion engine." This change would be necessary to be consistent with the other changes proposed in this rulemaking to extend the applicability of the rule provisions of Subchapter B, Division 2 to additional stationary engine types. Therefore, owners or operators of stationary gas-fired lean-burn engines not fired on landfill gas, stationary gas-fired engines fired on landfill gas, and stationary diesel engines, subject to the NOX emission specifications of §117.205(a), would be required to report in writing to the commission on a semiannual basis any excess emissions and air-fuel ratio monitoring system performance, as applicable.

The current rule provision reference to §117.230(a)(2) in §117.245(e)(1) is proposed to be revised to new §117.230(b)(5) to be consistent with the proposed changes to §117.230. The commission further notes that the current rule provision reference to §117.230(a)(2) is incorrect; the correct current rule provision reference is §117.230(2).

The commission proposes to remove the word "daily" from existing §117.245(f)(2)(B) because current rule provisions under Subchapter B, Division 2 do not specify any NOX emission specifications on a daily basis. Current rule provisions under §117.205 and §117.235 specify compliance only on either a one-hour or a 30-day basis for units that operate with a NOX CEMS or PEMS. Proposed changes to §117.245(f)(3)(A)(i) would include revising the current rule provision reference from §117.230(2) to new §117.230(b)(5). This change would be necessary pursuant to the changes proposed to §117.230 of Subchapter B, Division 2. Section §117.245(f)(3)(A) specifies requirements for owners or operators of stationary internal combustion engines, subject to the NOX emission specifications of Subchapter B, Division 2, to maintain records of emissions measurements required by new §117.230(b)(5) and §117.240(e) of the division.

Proposed changes to §117.245(f)(4) would include adding rule provision references to new §117.203(2) and (3) to include the proposed new exemptions for stationary diesel engines that operate less than 100 hours per year based on a rolling 12-month basis. Section §117.245(f)(4) specifies requirements for owners or operators of units claimed exempt from the emission specifications of Subchapter B, Division 2. For exemptions based on hours per year of operation, maintaining records of monthly hours of operation is required. For exemptions based on dedicated use, keeping records of the unit's purpose of use is required. Furthermore, the commission proposes to add to §117.245(f)(4) a rule provision reference to the definition of emergency situation in §117.10(15). The term itself already exists within the rule provision text of §117.245(f)(4). The purpose is to remind owners or operators of potentially affected units that the term is defined for purposes of Chapter 117, and not all situations that may occur may qualify as an emergency situation for purposes of Chapter 117.

Proposed revisions to §117.245(f) concerning recordkeeping requirements include a new paragraph (7) for owners or operators of stationary diesel engines subject to the operating restrictions in proposed new §117.205(e). Similar to existing provisions for owners or operators of stationary diesel engine in the DFW eight-hour ozone nonattainment area, in §117.445(f)(9), and in the HGB ozone nonattainment area, in §117.345(f)(10), proposed new §117.245(f)(7) would require owners or operators to maintain records of each time a stationary diesel engine is operated for testing and maintenance of the engine itself, including the date(s) of engine operation; the start and end times of engine operation; the identification of the engine; and the total hours of engine operation for each month and for the most recent 12 consecutive months. This proposed new recordkeeping requirement would apply for each stationary diesel engine that is subject to the operating restrictions of §117.240(e) to ensure compliance with the proposed restriction on operating hours for testing and maintenance of a stationary diesel engine.

Subchapter H, Administrative Provisions

Division 1, Compliance Schedules

Section 117.9010, Compliance Schedule for Bexar County Ozone Nonattainment Major Sources

Proposed revisions to §117.9010(a) include new paragraphs (1) and (2) to specify when owners or operators of units subject to the requirements of Subchapter B, Division 2 are required to demonstrate compliance with those requirements. Proposed new §117.9010(a)(1) would preserve prior compliance deadlines for submittal of the control plan and all other requirements of Chapter 117, Subchapter B, Division 2 for units subject to the NOX emission specifications in §117.205(a) that were subject to the prior definition of "Major source" for the Bexar County ozone nonattainment in §117.10(29)(B) before the effective date of this current rulemaking - those that emit or have the potential to emit equal to or greater than 100 tpy of NOX. The prior compliance deadline of January 1, 2025, for control plans is proposed in new §117.9010(a)(1)(A). The prior compliance deadline of January 1, 2025, for all other requirements of Subchapter B, Division 2, when the area was classified as moderate ozone nonattainment, is proposed in new §117.9010(a)(1)(B). Proposed new §117.9010(a)(1)(B) further specifies that units that were required to demonstrate compliance by January 1, 2025, must continue to demonstrate compliance with the requirements of Subchapter B Division 2. Finally, the commission proposes in new §117.9010(a)(1)(C) that for units that became subject to the NOX emission specifications in §117.205(a) after January 1, 2025, compliance with the requirements of Subchapter B, Division 2 is required as soon as practicable but no later than 60 days after becoming subject. These changes are intended to provide clarity and distinguish between the prior compliance deadline of January 1, 2025, in proposed new §117.9010(a)(1)(A) - (C) relating to the compliance date for the Bexar County ozone nonattainment area under a moderate classification and the proposed new deadlines in new §117.9010(a)(2). These proposed changes in §117.9010(a) are not intended to change the existing requirements for those units that had a rule provision compliance deadline of January 1, 2025.

Proposed new §117.9010(a)(2)(A) - (B) would specify the compliance deadlines for units subject to the NOX emission specifications of §117.205(a) that become subject to the proposed revised definition of "Major Source" for the Bexar County ozone nonattainment area in proposed revised §117.10(29)(B). The commission proposes a compliance deadline of February 1, 2026, in proposed new §117.9010(a)(2)(A) for submission of the control plan required by §117.252 and March 1, 2026, in proposed new §117.9010(a)(2)(B) for demonstrating compliance with all other applicable requirements of Chapter 117, Subchapter B, Division 2. The compliance date assures that NOX reductions would occur by the start of ozone season in Bexar County in 2026, the year used to determine attainment with the 2015 eight-hour ozone NAAQS.

The commission does not propose any changes to existing §117.9010(b), which specifies that the owner or operator of any stationary source of NOX that becomes subject to the requirements of Chapter 117, Subchapter B, Division 2 on or after the applicable compliance date specified in subsection (a) of the section must comply with the requirements of the division as soon as practicable, but no later than 60 days after becoming subject to the requirements of the division. Considering the reclassification of the Bexar County ozone nonattainment area and the new NOX major source threshold, an owner or operator of any stationary source of NOX that becomes subject to the requirements of proposed revised Subchapter B, Division 2 on or after March 1, 2026, must comply with the requirements of Chapter 117, Subchapter B, Division 2 as soon as practicable, but no later than 60 days after becoming subject. For example, owners or operators of new units placed into service on or after March 1, 2026, would be required to demonstrate compliance with the requirements of the division within 60 days after startup of the unit. Owners or operators of existing units previously claimed exempt from the rule provisions but no longer qualifying for exemption after March 1, 2026, would be required to demonstrate compliance with the requirements of the division by no later than 60 days after the unit no longer qualifies for the previously claimed exemption.

Fiscal Note: Costs to State and Local Government

Kyle Girten, Analyst in the Budget and Planning Division, has determined that for the first five-year period the proposed rules are in effect, no significant fiscal implications are anticipated for TCEQ during implementation of the proposed rule. No fiscal implications are anticipated for other state or local government entities.

Public Benefits and Costs

Mr. Girten determined that for each year of the first five years the proposed rules are in effect, the public benefit anticipated will be compliance with federal law and continued protection of the environment and public health and safety combined with efficient and fair administration of NOX emission standards for Bexar County. Corrections of errors and other non-substantive changes within the rule would also benefit the public.

Costs would be incurred for affected businesses operating in Bexar County for implementation of requirements appliable to RACT. Revisions to §117.10 would lower the threshold for major sources from 100 tpy to 50 tpy NOX in Bexar County, so any sources emitting or with the potential to emit 50-100 tpy NOX in Bexar County would be impacted by this rulemaking. Additionally, revisions to Subchapter B, Division 2 would expand the applicability of RACT requirements as applicable to NOX to include gas engines fired on landfill gas, diesel engines, boilers, process heaters, ovens, and incinerators, so any applicable requirements in Chapter 117 would apply to all major sources with these technologies.

It is estimated that four businesses would be affected by this rulemaking. This includes one landfill/waste-to-gas management plant with five stationary diesel engines and four flares (subject to federal new source review requirements); one waste-to-gas energy production plant with six stationary gas-fired, lean-burn engines; one petroleum refinery with nine process heaters, four stationary diesel engines, two incinerators, and two flares (subject to federal new source review requirements); and one vehicle automotive manufacturer plant with two incinerators and seven ovens.

For the landfill/waste-to-gas management plant, total costs are estimated at $24,000-$39,000 for the first, third, and fifth year after the rulemaking is in effect, and $9,400-$18,400 in years two and four. Capital purchases were assumed to be annualized over 15 years with an 8.25% rate on the loan. Costs include purchase of new Tier 2, Tier 3, and Tier 4 diesel engines and other equipment, operating and maintenance costs, the purchase and operation of flow meters, and costs associated with stack testing.

For the waste-to-gas energy production plant, total costs are estimated at $35,000 in years one, three, and five and $5,800 in years two and four. Capital purchases were assumed to be annualized over 15 years with an 8.25% rate on the loan. Costs include the purchase of flow meters, annual operating and maintenance costs, stack testing costs, and costs associated with recordkeeping and reporting. None of the six engines at this site are anticipated to need to implement additional controls to meet proposed emissions specifications for stationary gas-fired, lean burn engines fired on landfill gas.

For the petroleum refinery, total costs are estimated at $199,000 in year one and $154,600 in years two through five. Capital purchases were assumed to be annualized over 15 years with an 8.25% rate on the loan. Costs include the purchase of ultra-low-NOX burners for six process heaters, tests of the burners, the purchase of flow meters, the purchase of non-resettable run time meters for four stationary diesel engines, stack testing costs, and costs associated with recordkeeping and reporting. It is assumed that four stationary diesel engines would qualify for an exemption, either based on dedicated use or low operational use; and two incinerators would qualify for an exemption based on unit size.

For the vehicle automotive manufacturer, total costs are estimated at $22,000 in year one and $2,200 in years two through five. Capital purchases were assumed to be annualized over 15 years with an 8.25% rate on the loan. Costs include the purchase of flow meters, operating and maintenance costs, stack testing costs, and costs associated with recordkeeping and reporting. It is assumed that two incinerators and three of the gas-fired ovens would qualify for an exemption from requirements based on unit size. The remaining four ovens are not anticipated to require additional control measures.

Local Employment Impact Statement

The commission reviewed this proposed rulemaking and determined that a Local Employment Impact Statement is not required because the proposed rulemaking is not anticipated to adversely affect a local economy in a significant way for the first five years that the proposed rule is in effect.

Rural Communities Impact Assessment

The commission reviewed this proposed rulemaking and determined that the proposed rulemaking does not adversely affect rural communities in a material way for the first five years that the proposed rules are in effect. This rulemaking applies to Bexar County, which has a large population; therefore, rural communities are not significantly impacted.

Small Business and Micro-Business Assessment

No adverse fiscal implications are anticipated for small or micro-businesses due to the implementation or administration of the proposed rule for the first five-year period the proposed rules are in effect. No small businesses have been identified that would be affected by this rulemaking.

Small Business Regulatory Flexibility Analysis

The commission reviewed this proposed rulemaking and determined that a Small Business Regulatory Flexibility Analysis is not required because the proposed rule does not adversely affect a small or micro-business in a material way for the first five years the proposed rules are in effect.

Government Growth Impact Statement

The commission prepared a Government Growth Impact Statement assessment for this proposed rulemaking. The proposed rulemaking does not create or eliminate a government program and will not require an increase or decrease in future legislative appropriations to the agency. The proposed rulemaking does not require the creation of new employee positions, eliminate current employee positions, nor require an increase or decrease in fees paid to the agency. The proposed rulemaking amends an existing regulation, and it does not increase or decrease the number of individuals subject to its applicability. During the first five years, the proposed rule should not impact positively or negatively the state's economy.

Draft Regulatory Impact Analysis Determination

The commission reviewed the proposed rulemaking in light of the regulatory impact analysis requirements of Texas Government Code, §2001.0225 and determined that the proposed rulemaking does not meet the definition of a major environmental rule as defined in that statute, and in addition, if it did meet the definition, would not be subject to the requirement to prepare a regulatory impact analysis. A major environmental rule means a rule, the specific intent of which is to protect the environment or reduce risks to human health from environmental exposure, and that may adversely affect in a material way the economy, a sector of the economy, productivity, competition, jobs, the environment, or the public health and safety of the state or a sector of the state. Additionally, the proposed rulemaking does not meet any of the four applicability criteria for requiring a regulatory impact analysis for a major environmental rule, which are listed in Tex. Gov't Code Ann., §2001.0225(a). Section 2001.0225 of the Texas Government Code applies only to a major environmental rule, the result of which is to: 1) exceed a standard set by federal law, unless the rule is specifically required by state law; 2) exceed an express requirement of state law, unless the rule is specifically required by federal law; 3) exceed a requirement of a delegation agreement or contract between the state and an agency or representative of the federal government to implement a state and federal program; or 4) adopt a rule solely under the general powers of the agency instead of under a specific state law.

The specific intent of these proposed rules is to comply with federal requirements for the implementation of control strategies necessary to attain and maintain the NAAQS for ozone mandated by 42 United States Code (USC), 7410, FCAA, §110 and required to be included in operating permits by 42 USC, §7661a, FCAA, §502, as specified elsewhere in this preamble. The proposed rulemaking addresses RACT requirements for the Bexar County 2015 eight-hour ozone nonattainment area as discussed elsewhere in this preamble. States are required to adopt SIPs with enforceable emission limitations and other control measures, means, or techniques, as well as schedules and timetables for compliance, as may be necessary or appropriate to meet the applicable requirements of the FCAA. As discussed in the FISCAL NOTE portion of this preamble, the proposed rules are not anticipated to add any significant additional costs to affected individuals or businesses beyond what is necessary to attain the ozone NAAQS on the economy, a sector of the economy, productivity, competition, jobs, the environment, or the public health and safety of the state or a sector of the state.

If a state does not comply with its obligations under 42 USC, §7410, FCAA, §110 to submit SIPs, states are subject to discretionary sanctions under 42 USC, §7410(m) or mandatory sanctions under 42 USC, §7509, FCAA, §179; as well as the imposition of a federal implementation plan (FIP) under 42 USC, §7410, FCAA, §110(c). Under 42 USC, §7661a, FCAA, §502, states are required to have federal operating permit programs that provide authority to issue permits and assure compliance with each applicable standard, regulation, or requirement under the FCAA, including enforceable emission limitations and other control measures, means, or techniques, which are required under 42 USC, §7410, FCAA, §110. Similar to requirements in 42 USC, §7410, FCAA, §110, states are not free to ignore requirements in 42 USC, §7661a, FCAA, §502 and must develop and submit programs to provide for operating permits for major sources that include all applicable requirements of the FCAA. Lastly, states are also subject to the imposition of sanctions under 42 USC, §7661a(d) and (i), FCAA, §502(d) and (i) for failure to submit an operating permits program, the disapproval of any operating permits program, or failure to adequately administer and enforce the approved operating permits program.

The requirement to provide a fiscal analysis of regulations in the Texas Government Code was amended by Senate Bill (SB) 633 during the 75th legislative session in 1997. The intent of SB 633 was to require agencies to conduct a regulatory impact analysis of extraordinary rules. These are identified in the statutory language as major environmental rules that will have a material adverse impact and will exceed a requirement of state law, federal law, or a delegated federal program, or are adopted solely under the general powers of the agency. With the understanding that this requirement would seldom apply, the commission provided a cost estimate for SB 633 that concluded "based on an assessment of rules adopted by the agency in the past, it is not anticipated that the bill will have significant fiscal implications for the agency due to its limited application." The commission also noted that the number of rules that would require assessment under the provisions of the bill was not large. This conclusion was based, in part, on the criteria set forth in the bill that exempted rules from the full analysis unless the rule was a major environmental rule that exceeds a federal law. Because of the ongoing need to meet federal requirements, the commission routinely proposes and adopts rules incorporating or designed to satisfy specific federal requirements. The legislature is presumed to understand this federal scheme. If each rule proposed by the commission to meet a federal requirement was considered to be a major environmental rule that exceeds federal law, then each of those rules would require the full regulatory impact analysis (RIA) contemplated by SB 633. Requiring a full RIA for all federally required rules is inconsistent with the conclusions reached by the commission in its cost estimate and by the Legislative Budget Board (LBB) in its fiscal notes. Since the legislature is presumed to understand the fiscal impacts of the bills it passes, and that presumption is based on information provided by state agencies and the LBB, the that the intent of SB 633 was only to require the full RIA for rules that are extraordinary in nature. While the proposed rules may have a broad impact, that impact is no greater than is necessary or appropriate to meet the requirements of the FCAA, and in fact creates no additional impacts since the proposed rules do not impose burdens greater than required to demonstrate attainment of the ozone NAAQS as discussed elsewhere in this preamble. For these reasons, the proposed rules fall under the exception in Texas Government Code, §2001.0225(a), because they are required by, and do not exceed, federal law.

The commission has consistently applied this construction to its rules since this statute was enacted in 1997. Since that time, the legislature has revised the Texas Government Code, but left this provision substantially unamended. It is presumed that "when an agency interpretation is in effect at the time the legislature amends the laws without making substantial change in the statute, the legislature is deemed to have accepted the agency's interpretation." (Central Power & Light Co. v. Sharp, 919 S.W.2d 485, 489 (Tex. App. Austin 1995), writ denied with per curiam opinion respecting another issue, 960 S.W.2d 617 (Tex. 1997); Bullock v. Marathon Oil Co., 798 S.W.2d 353, 357 (Tex. App. Austin 1990, no writ). Cf. Humble Oil & Refining Co. v. Calvert, 414 S.W.2d 172 (Tex. 1967); Dudney v. State Farm Mut. Auto Ins. Co., 9 S.W.3d 884, 893 (Tex. App. Austin 2000); Southwestern Life Ins. Co. v. Montemayor, 24 S.W.3d 581 (Tex. App. Austin 2000, pet. denied); and Coastal Indust. Water Auth. v. Trinity Portland Cement Div., 563 S.W.2d 916 (Tex. 1978).) The commission's interpretation of the RIA requirements is also supported by a change made to the Texas Administrative Procedure Act (APA) by the legislature in 1999. In an attempt to limit the number of rule challenges based upon APA requirements, the legislature clarified that state agencies are required to meet these sections of the APA against the standard of "substantial compliance" (Texas Government Code, §2001.035). The legislature specifically identified Texas Government Code, §2001.0225 as falling under this standard.

As discussed in this analysis and elsewhere in this preamble, the commission has substantially complied with the requirements of Texas Government Code, §2001.0225. The proposed rulemaking implements the requirements of the FCAA as discussed in this analysis and elsewhere in this preamble. The proposed rules were determined to be necessary to attain the ozone NAAQS and are required to be included in permits under 42 USC, §7661a, FCAA, §502 and will not exceed any standard set by state or federal law. These proposed rules are not an express requirement of state law. The proposed rules do not exceed a requirement of a delegation agreement or a contract between state and federal government, as the proposed rules, if adopted by the commission and approved by EPA, will become federal law as part of the approved SIP required by 42 U.S.C. §7410, FCAA, §110. The proposed rules were not developed solely under the general powers of the agency but are authorized by specific sections of Texas Health and Safety Code, Chapter 382 (also known as the Texas Clean Air Act), and the Texas Water Code, which are cited in the Statutory Authority section of this preamble, including Texas Health and Safety Code, §§382.011, 382.012, and 382.017. Therefore, this proposed rulemaking action is not subject to the regulatory analysis provisions of Texas Government Code, §2001.0225(b).

The commission invites public comment regarding the Draft Regulatory Impact Analysis Determination during the public comment period. Written comments on the Draft Regulatory Impact Analysis Determination may be submitted to the contact person at the address listed under the Submittal of Comments section of this preamble.

Takings Impact Assessment

Under Texas Government Code, §2007.002(5), taking means a governmental action that affects private real property, in whole or in part or temporarily or permanently, in a manner that requires the governmental entity to compensate the private real property owner as provided by the Fifth and Fourteenth Amendments to the United States Constitution or §17 or §19, Article I, Texas Constitution; or a governmental action that affects an owner's private real property that is the subject of the governmental action, in whole or in part or temporarily or permanently, in a manner that restricts or limits the owner's right to the property that would otherwise exist in the absence of the governmental action; and is the producing cause of a reduction of at least 25% in the market value of the affected private real property, determined by comparing the market value of the property as if the governmental action is not in effect and the market value of the property determined as if the governmental action is in effect. The commission completed a takings impact analysis for the proposed rulemaking action under the Texas Government Code, §2007.043.

The primary purpose of this proposed rulemaking action, as discussed elsewhere in this preamble, is to meet federal requirements for the implementation of control strategies necessary to attain and maintain the NAAQS for ozone mandated by 42 United States Code (USC), 7410, FCAA, §110 and required to be included in operating permits by 42 USC, §7661a, FCAA, §502. The proposed rulemaking addresses RACT requirements for the Bexar County 2015 eight-hour ozone nonattainment area as discussed elsewhere in this preamble.

States are required to adopt SIPs with enforceable emission limitations and other control measures, means, or techniques, as well as schedules and timetables for compliance, as may be necessary or appropriate to meet the applicable requirements of the FCAA. If a state does not comply with its obligations under 42 USC, §7410, FCAA, §110 to submit SIPs, states are subject to discretionary sanctions under 42 USC, §7410(m) or mandatory sanctions under 42 USC, §7509, FCAA, §179; as well as the imposition of a FIP under 42 USC, §7410, FCAA, §110(c). Under 42 USC, §7661a, FCAA, §502, states are required to have federal operating permit programs that provide authority to issue permits and assure compliance with each applicable standard, regulation, or requirement under the FCAA, including enforceable emission limitations and other control measures, means, or techniques, which are required under 42 USC, §7410, FCAA, §110. Similar to requirements in 42 USC, §7410, FCAA, §110, regarding the requirement to adopt and implement plans to attain and maintain the national ambient air quality standards, states are not free to ignore requirements in 42 USC, §7661a, FCAA, §502 and must develop and submit programs to provide for operating permits for major sources that include all applicable requirements of the FCAA. Lastly, states are also subject to the imposition of sanctions under 42 USC, §7661a(d) and (i), FCAA, §502(d) and (i) for failure to submit an operating permits program, the disapproval of any operating permits program, or failure to adequately administer and enforce the approved operating permits program.

The proposed rules will not create any additional burden on private real property beyond what is required under federal law, as the proposed rules, if adopted by the commission and approved by EPA, will become federal law as part of the approved SIP required by 42 U.S.C. §7410, FCAA, §110. The proposed rules will not affect private real property in a manner that would require compensation to private real property owners under the United States Constitution or the Texas Constitution. The proposal also will not affect private real property in a manner that restricts or limits an owner's right to the property that would otherwise exist in the absence of the governmental action. Therefore, the proposed rulemaking will not cause a taking under Texas Government Code, Chapter 2007.

Consistency with the Coastal Management Program

The commission reviewed the proposed rulemaking and found the proposal is a rulemaking identified in the Coastal Coordination Act Implementation Rules, 31 TAC §29.11(b)(2) (or §29.11(b)(4), whichever is applicable) relating to rules subject to the Coastal Management Program, and will, therefore, require that goals and policies of the Texas Coastal Management Program (CMP) be considered during the rulemaking process. Note: §29.11(b)(2) applies only to air pollutant emissions, on-site sewage disposal systems, and underground storage tanks. §29.11(b)(4) applies to all other actions.

The commission reviewed this rulemaking for consistency with the CMP goals and policies in accordance with the regulations of the Coastal Coordination Advisory Committee and determined that the rulemaking will not affect any coastal natural resource areas because the rules only affect counties outside the CMP area and is, therefore, consistent with CMP goals and policies.

Written comments on the consistency of this rulemaking may be submitted to the contact person at the address listed under the SUBMITTAL OF COMMENTS section of this preamble.

Effect on Sites Subject to the Federal Operating Permits Program

Chapter 117 is an applicable requirement under 30 TAC Chapter 122, Federal Operating Permits Program. Once adopted, owners or operators of affected sites subject to the federal operating permit program must, consistent with the revision process in Chapter 122, upon the effective date of the rulemaking, revise their operating permit to include the new Chapter 117 requirements.

Announcement of Hearing

The commission will offer a public hearing on this proposal in San Antonio on July 15, 2025, at 7:00 p.m. Central Daylight Time in Suite 101 at 2700 Northeast Loop 410 in San Antonio, Texas 78217. The hearing is structured for the receipt of oral or written comments by interested persons. Individuals may present oral statements when called upon in order of registration. Open discussion will not be permitted during the hearing; however, commission staff members will be available to discuss the proposal 30 minutes prior to the hearing. Persons who have special communication or other accommodation needs who are planning to attend the hearing should contact Sandy Wong, Office of Legal Services at (512) 239-1802 or 1-800-RELAY-TX (TDD). Requests should be made as far in advance as possible.

Submittal of Comments

Written comments may be submitted to Gwen Ricco, MC 205, Office of Legal Services, Texas Commission on Environmental Quality, P.O. Box 13087, Austin, Texas 78711-3087, or faxed to fax4808@tceq.texas.gov. Electronic comments may be submitted at: https://tceq.commentinput.com/comment/search . File size restrictions may apply to comments being submitted via the TCEQ Public Comments system. All comments should reference Rule Project Number 2025-007-117-AI. The comment period closes on July 21, 2025. Please choose one of the methods provided to submit your written comments.

Copies of the proposed rulemaking can be obtained from the commission's website at https://www.tceq.texas.gov/rules/propose_adopt.html . For further information, please contact Javier Galván, Air Quality Planning Section, at javier.galvan@tceq.texas.gov.

SUBCHAPTER A. DEFINITIONS

30 TAC §117.10

Statutory Authority

The amendments are proposed under Texas Water Code (TWC), §5.102, concerning general powers; §5.103, concerning Rules; TWC, §5.105, concerning General Policy, which authorize the commission to adopt rules necessary to carry out its powers and duties under the TWC; TWC, §7.002, concerning Enforcement Authority, which authorizes the commission to enforce the provisions of the Water Code and the Health and Safety Code within the commission's jurisdiction; and under Texas Health and Safety Code, §382.017, concerning Rules, which authorizes the commission to adopt rules consistent with the policy and purpose of the Texas Clean Air Act.

The amendments are also proposed under Texas Healthy and Safety Code (THSC), §382.002, concerning Policy and Purpose, which establishes the commission's purpose to safeguard the state's air resources, consistent with the protection of public health, general welfare, and physical property; THSC, §382.011, concerning General Powers and Duties, which authorizes the commission to control the quality of the state's air; and THSC, §382.012, concerning the State Air Control Plan, which authorizes the commission to prepare and develop a general, comprehensive plan for the proper control of the state's air.

The proposed amendments implement Texas Water Code, §§5.102, 5.103, 5.105 and 7.002; and Texas Health and Safety Code, §§382.002, 382.011, 382.012, 382.017.

§117.10. Definitions.

Unless specifically defined in the Texas Clean Air Act or Chapter 101 of this title (relating to General Air Quality Rules), the terms in this chapter have the meanings commonly used in the field of air pollution control. Additionally, the following meanings apply, unless the context clearly indicates otherwise. Additional definitions for terms used in this chapter are found in §3.2 and §101.1 of this title (relating to Definitions).

(1) Annual capacity factor--The total annual fuel consumed by a unit divided by the fuel that could be consumed by the unit if operated at its maximum rated capacity for 8,760 hours per year.

(2) Applicable ozone nonattainment area-The following areas, as designated under the 1990 Federal Clean Air Act Amendments.

(A) Beaumont-Port Arthur ozone nonattainment area--An area consisting of Hardin, Jefferson, and Orange Counties.

(B) Bexar County ozone nonattainment area-An area consisting of Bexar County.

(C) Dallas-Fort Worth eight-hour ozone nonattainment area--An area consisting of:

(i) for the purposes of Subchapter D of this chapter (relating to Combustion Control at Minor Sources in Ozone Nonattainment Areas), Collin, Dallas, Denton, Ellis, Johnson, Kaufman, Parker, Rockwall, and Tarrant Counties; or

(ii) for all other divisions of this chapter, Collin, Dallas, Denton, Ellis, Johnson, Kaufman, Parker, Rockwall, Tarrant, and Wise Counties.

(D) Houston-Galveston-Brazoria ozone nonattainment area--An area consisting of Brazoria, Chambers, Fort Bend, Galveston, Harris, Liberty, Montgomery, and Waller Counties.

(3) Auxiliary steam boiler--Any combustion equipment within an electric power generating system, as defined in this section, that is used to produce steam for purposes other than generating electricity. An auxiliary steam boiler produces steam as a replacement for steam produced by another piece of equipment that is not operating due to planned or unplanned maintenance.

(4) Average activity level for fuel oil firing--The product of an electric utility unit's maximum rated capacity for fuel oil firing and the average annual capacity factor for fuel oil firing for the period from January 1, 1990, to December 31, 1993.

(5) Block one-hour average--An hourly average of data, collected starting at the beginning of each clock hour of the day and continuing until the start of the next clock hour.

(6) Boiler--Any combustion equipment fired with solid, liquid, and/or gaseous fuel used to produce steam or to heat water.

(7) Btu--British thermal unit.

(8) Chemical processing gas turbine-A gas turbine that vents its exhaust gases into the operating stream of a chemical process.

(9) Continuous emissions monitoring system (CEMS)--The total equipment necessary for the continuous determination and recordkeeping of process gas concentrations and emission rates in units of the applicable emission limitation.

(10) Daily--A calendar day starting at midnight and continuing until midnight the following day.

(11) Diesel engine--A compression-ignited two- or four-stroke engine that liquid fuel injected into the combustion chamber ignites when the air charge has been compressed to a temperature sufficiently high for auto-ignition.

(12) Duct burner--A unit that combusts fuel and that is placed in the exhaust duct from another unit (such as a stationary gas turbine, stationary internal combustion engine, kiln, etc.) to allow the firing of additional fuel to heat the exhaust gases.

(13) Electric generating facility (EGF)--A unit that generates electric energy for compensation and is owned or operated by a person doing business in this state, including a municipal corporation, electric cooperative, or river authority.

(14) Electric power generating system--One electric power generating system consists of either:

(A) for the purposes of Subchapter C, Divisions 1, 2, and 4 of this chapter (relating to Beaumont-Port Arthur Ozone Nonattainment Area Utility Electric Generation Sources; Bexar County Ozone Nonattainment Area Utility Electric Generation Sources; and Dallas-Fort Worth Eight-Hour Ozone Nonattainment Area Utility Electric Generation Sources), all boilers, auxiliary steam boilers, and stationary gas turbines (including duct burners used in turbine exhaust ducts) at electric generating facility (EGF) accounts that generate electric energy for compensation; are owned or operated by an electric cooperative, municipality, river authority, public utility, independent power producer, or a Public Utility Commission of Texas regulated utility, or any of its successors; and are entirely located in one of the following ozone nonattainment areas:

(i) Beaumont-Port Arthur;

(ii) Bexar County; or

(iii) Dallas-Fort Worth eight-hour;

(B) for the purposes of Subchapter C, Division 3 of this chapter (relating to Houston-Galveston-Brazoria Ozone Nonattainment Area Utility Electric Generation Sources), all boilers, auxiliary steam boilers, and stationary gas turbines (including duct burners used in turbine exhaust ducts) at EGF accounts that generate electric energy for compensation; are owned or operated by an electric cooperative, municipality, river authority, public utility, or a Public Utility Commission of Texas regulated utility, or any of its successors; and are entirely located in the Houston-Galveston-Brazoria ozone nonattainment area;

(C) for the purposes of Subchapter B, Division 3 of this chapter (relating to Houston-Galveston-Brazoria Ozone Nonattainment Area Major Sources), all units in the Houston-Galveston-Brazoria ozone nonattainment area that generate electricity but do not meet the conditions specified in subparagraph (B) of this paragraph, including, but not limited to, cogeneration units and units owned by independent power producers; or

(D) for the purposes of Subchapter E, Division 1 of this chapter (relating to Utility Electric Generation in East and Central Texas), all boilers, auxiliary steam boilers, and stationary gas turbines at EGF accounts that generate electric energy for compensation; are owned or operated by an electric cooperative, independent power producer, municipality, river authority, or public utility, or any of its successors; and are located in Atascosa, Bastrop, Brazos, Calhoun, Cherokee, Fannin, Fayette, Freestone, Goliad, Gregg, Grimes, Harrison, Henderson, Hood, Hunt, Lamar, Limestone, Marion, McLennan, Milam, Morris, Nueces, Parker, Red River, Robertson, Rusk, Titus, Travis, Victoria, or Wharton County, or in Bexar County until December 31, 2024.

(15) Emergency situation--As follows.

(A) An emergency situation is any of the following:

(i) an unforeseen electrical power failure from the serving electric power generating system;

(ii) the period of time that an Electric Reliability Council of Texas, Inc. (ERCOT)-issued emergency notice or energy emergency alert (EEA) (as defined in ERCOT Nodal Protocols, Section 2: Definitions and Acronyms (August 13, 2014) and issued as specified in ERCOT Nodal Protocols, Section 6: Adjustment Period and Real-Time Operations (August 13, 2014)) is applicable to the serving electric power generating system. The emergency situation is considered to end upon expiration of the emergency notice or EEA issued by ERCOT;

(iii) an unforeseen failure of on-site electrical transmission equipment (e.g., a transformer);

(iv) an unforeseen failure of natural gas service;

(v) an unforeseen flood or fire, or a life-threatening situation;

(vi) operation of emergency generators for Federal Aviation Administration licensed airports, military airports, or manned space flight control centers for the purposes of providing power in anticipation of a power failure due to severe storm activity; or

(vii) operation of an emergency generator as part of ERCOT's emergency response service (as defined in ERCOT Nodal Protocols, Section 2: Definitions and Acronyms (August 13, 2014)) if the operation is in direct response to an instruction by ERCOT during the period of an ERCOT EEA as specified in clause (ii) of this subparagraph.

(B) An emergency situation does not include:

(i) operation for training purposes or other foreseeable events; or

(ii) operation for purposes of supplying power for distribution to the electric grid, except as specified in subparagraph (A)(vii) of this paragraph.

(16) Functionally identical replacement--A unit that performs the same function as the existing unit that it replaces, with the condition that the unit replaced must be physically removed or rendered permanently inoperable before the unit replacing it is placed into service.

(17) Heat input--The chemical heat released due to fuel combustion in a unit, using the higher heating value of the fuel. This does not include the sensible heat of the incoming combustion air. In the case of carbon monoxide (CO) boilers, the heat input includes the enthalpy of all regenerator off-gases and the heat of combustion of the incoming CO and of the auxiliary fuel. The enthalpy change of the fluid catalytic cracking unit regenerator off-gases refers to the total heat content of the gas at the temperature it enters the CO boiler, referring to the heat content at 60 degrees Fahrenheit, as being zero.

(18) Heat treat furnace--A furnace that is used in the manufacturing, casting, or forging of metal to heat the metal so as to produce specific physical properties in that metal.

(19) High heat release rate--A ratio of boiler design heat input to firebox volume (as bounded by the front firebox wall where the burner is located, the firebox side waterwall, and extending to the level just below or in front of the first row of convection pass tubes) greater than or equal to 70,000 British thermal units per hour per cubic foot.

(20) Horsepower rating--The engine manufacturer's maximum continuous load rating at the lesser of the engine or driven equipment's maximum published continuous speed.

(21) Incinerator--As follows.

(A) For the purposes of this chapter, the term "incinerator" includes both of the following:

(i) a control device that combusts or oxidizes gases or vapors (e.g., thermal oxidizer, catalytic oxidizer, vapor combustor); and

(ii) an incinerator as defined in §101.1 of this title (relating to Definitions).

(B) The term "incinerator" does not apply to boilers or process heaters as defined in this section, or to flares as defined in §101.1 of this title.

(22) Industrial boiler--Any combustion equipment, not including utility or auxiliary steam boilers as defined in this section, fired with liquid, solid, or gaseous fuel, that is used to produce steam or to heat water.

(23) International Standards Organization (ISO) conditions--ISO standard conditions of 59 degrees Fahrenheit, 1.0 atmosphere, and 60% relative humidity.

(24) Large utility system--All boilers, auxiliary steam boilers, and stationary gas turbines that are located in the Dallas-Fort Worth eight-hour ozone nonattainment area, and were part of one electric power generating system on January 1, 2000, that had a combined electric generating capacity equal to or greater than 500 megawatts.

(25) Lean-burn engine--A spark-ignited or compression-ignited, Otto cycle, diesel cycle, or two-stroke engine that is not capable of being operated with an exhaust stream oxygen concentration equal to or less than 0.5% by volume, as originally designed by the manufacturer.

(26) Low annual capacity factor boiler, process heater, or gas turbine supplemental waste heat recovery unit--An industrial, commercial, or institutional boiler; process heater; or gas turbine supplemental waste heat recovery unit with maximum rated capacity:

(A) greater than or equal to 40 million British thermal units per hour (MMBtu/hr), but less than 100 MMBtu/hr and an annual heat input less than or equal to 2.8 (1011) British thermal units per year (Btu/yr), based on a rolling 12-month average; or

(B) greater than or equal to 100 MMBtu/hr and an annual heat input less than or equal to 2.2 (1011) Btu/yr, based on a rolling 12-month average.

(27) Low annual capacity factor stationary gas turbine or stationary internal combustion engine--A stationary gas turbine or stationary internal combustion engine that is demonstrated to operate less than 850 hours per year, based on a rolling 12-month average.

(28) Low heat release rate--A ratio of boiler design heat input to firebox volume less than 70,000 British thermal units per hour per cubic foot.

(29) Major source--Any stationary source or group of sources located within a contiguous area and under common control that emits or has the potential to emit:

(A) at least 50 tons per year (tpy) of nitrogen oxides (NOX) and is located in the Beaumont-Port Arthur ozone nonattainment area;

(B) at least 50 [100] tpy of NOX and is located in the Bexar County ozone nonattainment area;

(C) at least 25 tpy of NOX and is located in the Dallas-Fort Worth eight-hour ozone nonattainment area;

(D) at least 25 tpy of NOX and is located in the Houston-Galveston-Brazoria ozone nonattainment area; or

(E) the amount specified in the major source definition contained in the Prevention of Significant Deterioration of Air Quality regulations promulgated by the United States Environmental Protection Agency in 40 Code of Federal Regulations §52.21 as amended June 3, 1993 (effective June 3, 1994), and is located in Atascosa, Bastrop, Brazos, Calhoun, Cherokee, Comal, Fannin, Fayette, Freestone, Goliad, Gregg, Grimes, Harrison, Hays, Henderson, Hood, Hunt, Lamar, Limestone, Marion, McLennan, Milam, Morris, Nueces, Red River, Robertson, Rusk, Titus, Travis, Victoria, or Wharton County or in Bexar County until December 31, 2024.

(30) Maximum rated capacity--The maximum design heat input, expressed in million British thermal units per hour, unless:

(A) the unit is a boiler, utility boiler, or process heater operated above the maximum design heat input (as averaged over any one-hour period), in which case the maximum operated hourly rate must be used as the maximum rated capacity; or

(B) the unit is limited by operating restriction or permit condition to a lesser heat input, in which case the limiting condition must be used as the maximum rated capacity; or

(C) the unit is a stationary gas turbine, in which case the manufacturer's rated heat consumption at the International Standards Organization (ISO) conditions must be used as the maximum rated capacity, unless limited by permit condition to a lesser heat input, in which case the limiting condition must be used as the maximum rated capacity; or

(D) the unit is a stationary, internal combustion engine, in which case the manufacturer's rated heat consumption at Diesel Equipment Manufacturer's Association or ISO conditions must be used as the maximum rated capacity, unless limited by permit condition to a lesser heat input, in which case the limiting condition must be used as the maximum rated capacity.

(31) Megawatt (MW) rating--The continuous MW output rating or mechanical equivalent by a gas turbine manufacturer at International Standards Organization conditions, without consideration to the increase in gas turbine shaft output and/or the decrease in gas turbine fuel consumption by the addition of energy recovered from exhaust heat.

(32) Nitric acid--Nitric acid that is 30% to 100% in strength.

(33) Nitric acid production unit--Any source producing nitric acid by either the pressure or atmospheric pressure process.

(34) Nitrogen oxides (NOX)--The sum of the nitric oxide and nitrogen dioxide in the flue gas or emission point, collectively expressed as nitrogen dioxide.

(35) Parts per million by volume (ppmv)--All ppmv emission specifications specified in this chapter are referenced on a dry basis. When required to adjust pollutant concentrations to a specified oxygen (O2) correction basis, the following equation must be used.

Figure: 30 TAC §117.10(35) (No change.)

(36) Peaking gas turbine or engine--A stationary gas turbine or engine used intermittently to produce energy on a demand basis.

(37) Plant-wide emission rate--The ratio of the total actual nitrogen oxides mass emissions rate discharged into the atmosphere from affected units at a major source when firing at their maximum rated capacity to the total maximum rated capacities for those units.

(38) Plant-wide emission specification--The ratio of the total allowable nitrogen oxides mass emissions rate dischargeable into the atmosphere from affected units at a major source when firing at their maximum rated capacity to the total maximum rated capacities for those units.

(39) Predictive emissions monitoring system (PEMS)--The total equipment necessary for the continuous determination and recordkeeping of process gas concentrations and emission rates using process or control device operating parameter measurements and a conversion equation or computer program to produce results in units of the applicable emission limitation.

(40) Process heater--Any combustion equipment fired with liquid and/or gaseous fuel that is used to transfer heat from combustion gases to a process fluid, superheated steam, or water for the purpose of heating the process fluid or causing a chemical reaction. The term "process heater" does not apply to any unfired waste heat recovery heater that is used to recover sensible heat from the exhaust of any combustion equipment, or to boilers as defined in this section.

(41) Pyrolysis reactor--A unit that produces hydrocarbon products from the endothermic cracking of feedstocks such as ethane, propane, butane, and naphtha using combustion to provide indirect heating for the cracking process.

(42) Reheat furnace--A furnace that is used in the manufacturing, casting, or forging of metal to raise the temperature of that metal in the course of processing to a temperature suitable for hot working or shaping.

(43) Rich-burn engine--A spark-ignited, Otto cycle, four-stroke, naturally aspirated or turbocharged engine that is capable of being operated with an exhaust stream oxygen concentration equal to or less than 0.5% by volume, as originally designed by the manufacturer.

(44) Small utility system--All boilers, auxiliary steam boilers, and stationary gas turbines that are located in the Dallas-Fort Worth eight-hour ozone nonattainment area, and were part of one electric power generating system on January 1, 2000, that had a combined electric generating capacity less than 500 megawatts.

(45) Stationary gas turbine--Any gas turbine system that is gas and/or liquid fuel fired with or without power augmentation. This unit is either attached to a foundation or is portable equipment operated at a specific minor or major source for more than 90 days in any 12-month period. Two or more gas turbines powering one shaft must be treated as one unit.

(46) Stationary internal combustion engine--A reciprocating engine that remains or will remain at a location (a single site at a building, structure, facility, or installation) for more than 12 consecutive months. Included in this definition is any engine that, by itself or in or on a piece of equipment, is portable, meaning designed to be and capable of being carried or moved from one location to another. Indicia of portability include, but are not limited to, wheels, skids, carrying handles, dolly, trailer, or platform. Any engine (or engines) that replaces an engine at a location and that is intended to perform the same or similar function as the engine being replaced is included in calculating the consecutive residence time period. An engine is considered stationary if it is removed from one location for a period and then returned to the same location in an attempt to circumvent the consecutive residence time requirement. Nonroad engines, as defined in 40 Code of Federal Regulations §89.2, are not considered stationary for the purposes of this chapter.

(47) System-wide emission rate--The ratio of the total actual nitrogen oxides mass emissions rate discharged into the atmosphere from affected units in an electric power generating system or portion thereof located within a single ozone nonattainment area when firing at their maximum rated capacity to the total maximum rated capacities for those units. For fuel oil firing, average activity levels must be used in lieu of maximum rated capacities for the purpose of calculating the system-wide emission rate.

(48) System-wide emission specification--The ratio of the total allowable nitrogen oxides mass emissions rate dischargeable into the atmosphere from affected units in an electric power generating system or portion thereof located within a single ozone nonattainment area when firing at their maximum rated capacity to the total maximum rated capacities for those units. For fuel oil firing, average activity levels must be used in lieu of maximum rated capacities for the purpose of calculating the system-wide emission specification.

(49) Thirty-day rolling average--An average, calculated for each day that fuel is combusted in a unit, of all the hourly emissions data for the preceding 30 days that fuel was combusted in the unit.

(50) Twenty-four hour rolling average--An average, calculated for each hour that fuel is combusted (or acid is produced, for a nitric or adipic acid production unit), of all the hourly emissions data for the preceding 24 hours that fuel was combusted in the unit.

(51) Unit--A unit consists of either:

(A) for the purposes of §§117.105, 117.305, 117.405, 117.1005, and 117.1205 of this title (relating to Emission Specifications for Reasonably Available Control Technology (RACT)) and each requirement of this chapter associated with §§117.105, 117.305, 117.405, 117.1005, and 117.1205 of this title, any boiler, process heater, stationary gas turbine, or stationary internal combustion engine, as defined in this section;

(B) for the purposes of §§117.110, 117.310, 117.1010, and 117.1210 of this title (relating to Emission Specifications for Attainment Demonstration) and each requirement of this chapter associated with §§117.110, 117.310, 117.1010, and 117.1210 of this title, any boiler, process heater, stationary gas turbine, or stationary internal combustion engine, as defined in this section, or any other stationary source of nitrogen oxides (NOX) at a major source, as defined in this section;

(C) for the purposes of §117.2010 of this title (relating to Emission Specifications) and each requirement of this chapter associated with §117.2010 of this title, any boiler, process heater, stationary gas turbine (including any duct burner in the turbine exhaust duct), or stationary internal combustion engine, as defined in this section;

(D) for the purposes of §117.2110 of this title (relating to Emission Specifications for Eight-Hour Attainment Demonstration) and each requirement of this chapter associated with §117.2110 of this title, any stationary internal combustion engine, as defined in this section;

(E) for the purposes of §117.3310 of this title (relating to Emission Specifications for Eight-Hour Attainment Demonstration) and each requirement of this chapter associated with §117.3310 of this title, any stationary internal combustion engine, as defined in this section;

(F) for the purposes of §117.410 and §117.1310 of this title (relating to Emission Specifications for Eight-Hour Attainment Demonstration) and each requirement of this chapter associated with §117.410 and §117.1310 of this title, any boiler, process heater, stationary gas turbine, or stationary internal combustion engine, as defined in this section, or any other stationary source of NOX at a major source, as defined in this section;

(G) for the purposes of §117.205 of this title (relating to Emission Specifications for Reasonably Available Control Technology (RACT)) and each requirement of this chapter associated with §117.205 of this title, any process heater, stationary gas turbine (including any duct burner used in the turbine exhaust duct), or [gas-fired lean-burn] stationary [reciprocating ] internal combustion engine, as defined in this section, or any other stationary source of NOX at a major source, as defined in this section; or

(H) for the purposes of §117.1105 of this title (relating to Emission Specifications for Reasonably Available Control Technology (RACT)) and each requirement of this chapter associated with §117.1105 of this title, any utility boiler, auxiliary steam boiler, or stationary gas turbine (including any duct burner used in turbine exhaust ducts), as defined in this section.

(52) Utility boiler--Any combustion equipment owned or operated by an electric cooperative, municipality, river authority, public utility, or Public Utility Commission of Texas regulated utility, fired with solid, liquid, and/or gaseous fuel, used to produce steam for the purpose of generating electricity. Stationary gas turbines, including any associated duct burners and unfired waste heat boilers, are not considered to be utility boilers.

(53) Wood--Wood, wood residue, bark, or any derivative fuel or residue thereof in any form, including, but not limited to, sawdust, sander dust, wood chips, scraps, slabs, millings, shavings, and processed pellets made from wood or other forest residues.

The agency certifies that legal counsel has reviewed the proposal and found it to be within the state agency's legal authority to adopt.

Filed with the Office of the Secretary of State on July 11, 2025.

TRD-202502368

Charmaine K. Backens

Deputy Director, Environmental Law Division

Texas Commission on Environmental Quality

Earliest possible date of adoption: August 24, 2025

For further information, please call: (512) 239-0682


SUBCHAPTER B. COMBUSTION CONTROL AT MAJOR INDUSTRIAL, COMMERCIAL, AND INSTITUTIONAL SOURCES IN OZONE NONATTAINMENT AREAS

DIVISION 2. BEXAR COUNTY OZONE NONATTAINMENT AREA MAJOR SOURCES

30 TAC §§117.200, 117.203, 117.205, 117.230, 117.235, 117.240, 117.245

Statutory Authority

The amendments are proposed under Texas Water Code (TWC), §5.102, concerning general powers; §5.103, concerning Rules; TWC, §5.105, concerning General Policy, which authorize the commission to adopt rules necessary to carry out its powers and duties under the TWC; TWC, §7.002, concerning Enforcement Authority, which authorizes the commission to enforce the provisions of the Water Code and the Health and Safety Code within the commission's jurisdiction; and under Texas Health and Safety Code (THSC), §382.017, concerning Rules, which authorizes the commission to adopt rules consistent with the policy and purpose of the Texas Clean Air Act.

The amendments are also proposed under THSC, §382.002, concerning Policy and Purpose, which establishes the commission's purpose to safeguard the state's air resources, consistent with the protection of public health, general welfare, and physical property; THSC, §382.011, concerning General Powers and Duties, which authorizes the commission to control the quality of the state's air; THSC, §382.012, concerning the State Air Control Plan, which authorizes the commission to prepare and develop a general, comprehensive plan for the proper control of the state's air; THSC, §382.016, concerning Monitoring Requirements; Examination of Records, which authorizes the commission to prescribe reasonable requirements for measuring and monitoring the emissions of air contaminants; and THSC, §382.021, concerning Sampling Methods and Procedures.

The proposed amendments implement TWC, §§5.102, 5.103, and 7.002; and THSC, §§382.002, 382.011, 382.012, 382.016, 382.017, and 382.021.

§117.200. Applicability.

This division applies to the following units located at any major stationary source of nitrogen oxides located in the Bexar County ozone nonattainment area:

(1) stationary gas turbines;

(2) duct burners used in turbine exhaust ducts; [and]

(3) [gas-fired lean-burn] stationary [reciprocating ] internal combustion engines; [.]

(4) industrial, commercial, or institutional process heaters;

(5) natural gas-fired ovens;

(6) flares; and

(7) incinerators.

§117.203. Exemptions.

The following units are exempt from the provisions of this division, except as specified in §§117.205(e), 117.240(f), 117.245(f)(4) and (7) [(9)], and 117.252 of this title (relating to Emission Specifications for Reasonably Available Control Technology (RACT); Continuous Demonstration of Compliance; Notification, Recordkeeping, and Reporting Requirements; and Control Plan Procedures for Reasonably Available Control Technology [(RACT)]):

(1) stationary gas turbines and [gas-fired lean-burn] stationary [reciprocating] internal combustion engines that are used as follows:

(A) in research and testing of the unit;

(B) for purposes of performance verification and testing of the unit;

(C) solely to power other gas turbines or engines during startups;

(D) exclusively in emergency situations, except that operation for testing or maintenance purposes of the gas turbine or engine is allowed for up to 100 hours per year, based on a rolling 12-month basis. Any new, modified, reconstructed, or relocated stationary diesel engine placed into service on or after March 1, 2026, is ineligible for this exemption. For purposes of this subparagraph, the terms "modification" and "reconstruction" have the meanings defined in §116.10 of this title (relating to General Definitions) and 40 Code of Federal Regulations (CFR) §60.15 (December 16, 1975), respectively, and the term "relocated" means to newly install at an account, as defined in §101.1 of this title (relating to Definitions), a used engine from anywhere outside that account; or

(E) in response to and during the existence of any officially declared disaster or state of emergency;

(2) any stationary diesel engine placed into service before March 1, 2026, that:

(A) operates less than 100 hours per year, based on a rolling 12-month basis; and

(B) has not been modified, reconstructed, or relocated on or after March 1, 2026. For the purposes of this subparagraph, the terms "modification" and "reconstruction" have the meanings defined in §116.10 of this title and 40 CFR §60.15 (December 16, 1975), respectively, and the term "relocated" means to newly install at an account, as defined in §101.1 of this title, a used engine from anywhere outside that account;

(3) any new, modified, reconstructed, or relocated stationary diesel engine placed into service on or after March 1, 2026, that:

(A) operates less than 100 hours per year, based on a rolling 12-month basis, in other than emergency situations; and

(B) meets the corresponding emission standard for non-road engines listed in 40 CFR §1039.101, Table 1 (effective July 29, 2021), and in effect at the time of installation, modification, reconstruction, or relocation. For the purposes of this paragraph, the terms "modification" and "reconstruction" have the meanings defined in §116.10 of this title and 40 CFR §60.15 (December 16, 1975), respectively, and the term "relocated" means to newly install at an account, as defined in §101.1 of this title, a used engine from anywhere outside that account;

(4) [(2)] gas-fired lean-burn stationary [reciprocating] internal combustion engines with a horsepower (hp) rating less than 50 hp;

(5) [(3)] stationary gas turbines with a maximum rated capacity less than 10.0 million British thermal units per hour (MMBtu/hr); [and]

(6) industrial, commercial, or institutional process heaters with a maximum rated capacity equal to or less than 5.0 MMBtu/hr;

(7) natural gas-fired ovens with a maximum rated capacity equal to or less than 5.0 MMBtu/hr;

(8) flares;

(9) incinerators with a maximum rated capacity less than 40 MMBtu/hr; and

(10) [(4)] units located at a major source that is subject to Subchapter C, Division 2 of this chapter (related to Bexar County Ozone Nonattainment Area Utility Electric Generation Sources).

§117.205. Emission Specifications for Reasonably Available Control Technology (RACT).

(a) Emission specifications. No person shall allow the discharge into the atmosphere nitrogen oxides (NOX) [(NOx)] emissions in excess of the following emission specifications, in accordance with the applicable schedule in §117.9010 of this title (relating to Compliance Schedule for Bexar County Ozone Nonattainment Area Major Sources), except as provided in subsection (c) of this section:

(1) stationary gas turbines, 0.55 pounds [ pound] per million British thermal units [unit] (lb/MMBtu);

(2) duct burners used in turbine exhaust ducts, 0.55 lb/MMBtu; [and]

(3) [gas-fired lean-burn] stationary [reciprocating ] internal combustion engines: [, 0.5 gram per horsepower-hour.]

(A) gas-fired lean-burn engines:

(i) fired on landfill gas, 0.60 grams per horsepower-hour (g/hp-hr); and

(ii) all others, 0.50 g/hp-hr; and

(B) diesel engines:

(i) with a horsepower (hp) rating of less than 25 hp that are installed, modified, reconstructed, or relocated on or after March 1, 2026, 5.0 g/hp-hr;

(ii) with a hp rating of 25 hp or greater, but less than 75 hp, that are installed, modified, reconstructed, or relocated on or after March 1, 2026, 3.3 g/hp-hr;

(iii) with a hp rating of 75 hp or greater, but less than 175 hp, that are installed, modified, reconstructed, or relocated on or after March 1, 2026, 0.30 g/hp-hr;

(iv) with a hp rating of 175 hp or greater, but less than or equal to 750 hp, that are installed, modified, reconstructed, or relocated on or after March 1, 2026, 0.30 g/hp-hr;

(v) with a hp rating greater than 750 hp, that are electric generator sets, and that are installed, modified, reconstructed, or relocated on or after March 1, 2026, 0.50 g/hp-hr; and

(vi) with a hp rating greater than 750 hp, for all others that are not electric generator sets, and that are installed, modified, reconstructed, or relocated on or after March 1, 2026, 2.6 g/hp-hr;

(4) process heaters:

(A) with a maximum rated capacity equal to or greater than 40 million British thermal units per hour (MMBtu/hr), 0.025 lb/MMBtu; and

(B) with a maximum rated capacity less than 40 MMBtu/hr, 0.036 lb/MMBtu (or alternatively, 30 parts per million by volume (ppmv) NOX, at 3.0% oxygen (O 2), dry basis);

(5) natural gas-fired ovens, 0.036 lb/MMBtu; and

(6) incinerators, 0.030 lb/MMBtu.

(b) NOX averaging time. The emission specifications in subsection (a) of this section apply [on]:

[(1) a block one-hour average, in the units of the applicable standard; or]

(1) [(2)] If [if] the unit is operated with a NOX continuous emissions monitoring system (CEMS) or predictive emissions monitoring system (PEMS) under §117.240 of this title (relating to Continuous Demonstration of Compliance), either as: [a rolling 30-day average, in the units of the applicable standard.]

(A) a 30-day rolling average, in the units of the applicable standard;

(B) a block one-hour average, in the units of the applicable standard, or alternatively;

(C) a block one-hour average, in pounds per hour, for process heaters, calculated as the product of the process heater's maximum rated capacity and its applicable emission specification in lb/MMBtu.

(2) If the unit is not operated with a NOX CEMS or PEMS under §117.240 of this title, as a block one-hour average, in the units of the applicable standard. Alternatively for process heaters, the emission specification may be applied in pounds per hour, as specified in paragraph (1)(C) of this subsection.

(c) Compliance flexibility. An owner or operator may use §117.9800 of this title (relating to Use of Emission Credits for Compliance) to comply with the NOX emission specifications of this section.

(d) Prohibition of circumvention.

(1) The maximum rated capacity used to determine the applicability of the emission specifications in this section and the initial compliance demonstration, monitoring, testing requirements, and control plan requirements in §§117.235, 117.240, and 117.252 of this title (relating to Initial Demonstration of Compliance; Continuous Demonstration of Compliance; and Control Plan Procedures for Reasonably Available Control Technology) must be the greater of the following:

(A) the maximum rated capacity as of December 31, 2019;

(B) the maximum rated capacity after December 31, 2019; or

(C) the maximum rated capacity authorized by a permit issued under Chapter 116 of this title (relating to Control of Air Pollution by Permits for New Construction or Modification) after December 31, 2019.

(2) A unit's classification is determined by the most specific classification applicable to the unit as of December 31, 2019. For example, a unit that is classified as a gas-fired lean-burn stationary reciprocating internal combustion engine as of December 31, 2019, but subsequently is authorized to operate as a dual-fuel engine, is classified as a gas-fired lean-burn stationary reciprocating internal combustion engine for the purposes of this chapter.

(3) After December 31, 2019, changes to a unit subject to an emission specification in this section that would result in increased NOX emissions from a unit not subject to an emission specification in this section, are only allowed if:

(A) the increase in NOX emissions at the unit not subject to this section is determined:

(i) using a CEMS or PEMS that meets the requirements in §117.240 of this title, or

(ii) through stack testing that meets the requirements in §117.235 of this title; and

(B) emission credits equal to the increase in NOX emissions at the unit not subject to this section are obtained and used in accordance with §117.9800 of this title.

(4) [(3)] A source that met the definition of major source on December 31, 2019, is always classified as a major source for purposes of this chapter. A source that did not meet the definition of major source (i.e., was a minor source, or did not yet exist) on December 31, 2019, but becomes a major source at any time after December 31, 2019, is from that time forward always classified as a major source for purposes of this chapter.

(e) Operating restrictions. No person may start or operate any stationary diesel engine for testing or maintenance of the engine between the hours of 6:00 a.m. and noon, except:

(1) to comply with specific manufacturer's recommended testing requiring a run of over 18 consecutive hours;

(2) to verify reliability of emergency equipment (e.g., emergency generators or pumps) immediately after unforeseen repairs. Routine maintenance is not considered to be an unforeseen repair; or

(3) for firewater pumps used for emergency response training conducted from April 1 through October 31.

§117.230. Operating Requirements.

(a) The owner or operator shall operate any unit subject to the emission specifications in §117.205 of this title (relating to Emission Specifications for Reasonably Available Control Technology (RACT)) in compliance with those limitations.

(b) All units subject to the emission specifications in §117.205 of this title [(relating to Emission Specifications for Reasonably Available Control Technology (RACT))] must be operated to minimize nitrogen oxides (NOX) emissions, consistent with the emission control techniques selected, over the unit's operating or load range during normal operations. Such operational requirements include the following.

(1) Each process heater controlled with forced draft flue gas recirculation (FGR) to reduce NOX emissions must be operated such that the proportional design rate of FGR is maintained, consistent with combustion stability, over the operating range.

(2) Each process heater controlled with induced draft FGR to reduce NOX emissions must be operated such that the operation of FGR over the operating range is not restricted by artificial means.

(3) Each unit controlled with steam or water injection must be operated such that injection rates are maintained to limit NOX concentrations to less than or equal to the NOX concentrations achieved at maximum rated capacity (corrected to 15% oxygen on a dry basis for stationary gas turbines).

(4) [(1)] Each unit controlled with post-combustion control techniques must be operated such that the reducing agent injection rate is maintained to limit NOX concentrations to less than or equal to the NOX concentrations achieved at maximum rated capacity.

(5) [(2)] Each [gas-fired lean-burn] stationary [reciprocating] internal combustion engine must be checked for proper operation of the engine according to §117.8140(b) of this title (relating to Emission Monitoring for Engines).

§117.235. Initial Demonstration of Compliance.

(a) The owner or operator of any unit subject to the emission specifications in §117.205(a) of this title (relating to Emission Specifications for Reasonably Available Control Technology (RACT)) shall test each [the] unit for nitrogen oxides (NOX) and oxygen [(O2)] emissions while firing gaseous fuel or, as applicable, liquid and solid fuel.

(b) Initial demonstration of compliance testing must be performed in accordance with the schedule specified in §117.9010 of this title (relating to Compliance Schedule for Bexar County Ozone Nonattainment Area Major Sources).

(c) The initial demonstration of compliance tests required by subsection (a) of this section must use the methods referenced in subsection (e) or (f) of this section and must be used for determination of initial compliance with the emission specifications of this division (relating to Bexar County Ozone Nonattainment Area Major Sources). Test results must be reported in the units of the applicable emission specifications and averaging periods.

(d) Any continuous emissions monitoring system (CEMS) or any predictive emissions monitoring system (PEMS) required by §117.240 of this title (relating to Continuous Demonstration of Compliance) must be installed and operational before conducting testing under subsection (a) of this section. Verification of operational status must, at a minimum, include completion of the initial monitor certification and the manufacturer's written requirements or recommendations for installation, operation, and calibration of the device or system.

(e) For units operating without a CEMS or PEMS, initial compliance with the emission specifications of this division must be demonstrated according to the requirements in [of] §117.8000 of this title (relating to Stack Testing Requirements).

(f) For units operating with a CEMS or PEMS in accordance with §117.240 of this title, after monitor certification testing of the CEMS or PEMS in accordance with subsection (d) of this section, initial compliance with the emission specifications of this division must be demonstrated [after monitor certification testing] using the CEMS or PEMS as follows. [For units complying with a NOX emission specification on a block one-hour average, every one-hour period while operating at the maximum rated capacity (or as near thereto as practicable) is used to determine compliance with the NOX emission specification.]

(1) For units demonstrating compliance using a NOX emission specification in pounds per million British thermal units (lb/MMBtu) on a 30-day rolling average, NOX emissions from the unit are monitored for 30 successive unit operating days, and the 30-day average emission rate is used to determine compliance with the NOX emission specification. The 30-day average emission rate is calculated as the total NOX emissions (in pounds) from the unit for the 30-day test period divided by the total heat input (in MMBtu) for the unit during the same 30-day test period.

(2) For units demonstrating compliance using a NOX emission specification on a block one-hour average, any one-hour period while operating at the maximum rated capacity, or as near thereto as practicable, is used to determine compliance with the NOX emission specification.

(g) Compliance stack test reports must include the information required in §117.8010 of this title (relating to Compliance Stack Test Reports).

§117.240. Continuous Demonstration of Compliance.

(a) Totalizing fuel flow meters.

(1) The owner or operator of units subject to this division (relating to Bexar County Ozone Nonattainment Area Major Sources) shall install, calibrate, maintain, and operate a totalizing fuel flow meter, with an accuracy of ± 5%, to individually and continuously measure the gas and liquid fuel usage. A computer that collects, sums, and stores electronic data from continuous fuel flow meters is an acceptable totalizer. The owner or operator must continuously operate the totalizing fuel flow meter at least 95% of the time when the unit is operating during a calendar year. For the purpose of compliance with this subsection for units having pilot fuel supplied by a separate fuel system or from an unmonitored portion of the same fuel system, the fuel flow to pilots may be calculated using the manufacturer's design flow rates rather than measured with a fuel flow meter. The calculated pilot fuel flow rate must be added to the monitored fuel flow when fuel flow is totaled.

(2) The following are alternatives to the fuel flow monitoring requirements of paragraph (1) of this subsection.

(A) Units operating with a nitrogen oxides (NOX) and diluent continuous emissions monitoring system (CEMS) under subsection (c) of this section may monitor stack exhaust flow using the flow monitoring specifications of 40 Code of Federal Regulations (CFR) Part 60, Appendix B, Performance Specification 6 or 40 CFR Part 75, Appendix A.

(B) Units that vent to a common stack with a NOX and diluent CEMS under subsection (c) of this section may use a single totalizing fuel flow meter.

(C) Stationary [Gas-fired lean-burn stationary reciprocating] internal combustion engines and stationary gas turbines equipped with a continuous monitoring system that continuously monitors horsepower and hours of operation are not required to install totalizing fuel flow meters. The continuous monitoring system must be installed, calibrated, maintained, and operated according to manufacturers' recommended procedures.

(b) NOX monitors.

(1) The owner or operator of the following units shall install, calibrate, maintain, and operate a CEMS or predictive emissions monitoring system (PEMS) to monitor exhaust NO X [NOx]:

(A) units with a rated heat input greater than or equal to 100 million British thermal units (MMBtu) per hour;

(B) stationary gas turbines with a megawatt (MW) rating greater than or equal to 30 MW and operated more than 850 hours per year;

(C) units that use a chemical reagent for reduction of NOX; and

(D) units that the owner or operator elects to comply with the NOX emission specifications in [of] §117.205(a) of this title (relating to Emission Specifications for Reasonably Available Control Technology (RACT)) using a pound per MMBtu limit on a 30-day rolling average.

(2) The owner or operator of the following units is not required to install a CEMS or PEMS under this subsection: [ Units subject to the NOX CEMS requirements of 40 CFR Part 75 are not required to install CEMS or PEMS under this subsection.]

(A) units subject to the NOX CEMS requirements of 40 CFR Part 75; and

(B) stationary diesel engines equipped with selective catalytic reduction (SCR) systems that meet all of the following criteria.

(i) The SCR system must use a reductant other than the engine's fuel.

(ii) The SCR system must operate with a diagnostic system that monitors reductant quality and tank levels.

(iii) The diagnostic system must alert owners or operators to the need to refill the reductant tank before it is empty or to replace the reductant if the reductant does not meet applicable concentration specifications.

(iv) If the SCR system uses input from an exhaust NOX sensor (or other sensor) to alert owners or operators when the reductant quality is inadequate, the reductant quality does not need to be monitored separately by the diagnostic system.

(v) The reductant tank level must be monitored in accordance with the manufacturer's design to demonstrate compliance with this subparagraph.

(vi) The method of alerting an owner or operator must be a visual or audible alarm.

(3) The owner or operator shall use one of the following methods to provide substitute emissions compliance data during periods when the NOX monitor is off-line:

(A) if the NOX monitor is a CEMS:

(i) subject to 40 CFR Part 75, use the missing data procedures specified in 40 CFR Part 75, Subpart D (Missing Data Substitution Procedures); or

(ii) subject to 40 CFR Part 75, Appendix E, use the missing data procedures specified in 40 CFR Part 75, Appendix E, §2.5 (Missing Data Procedures);

(B) if the NOX monitor is a PEMS:

(i) use the methods specified in 40 CFR Part 75, Subpart D; or

(ii) use calculations in accordance with §117.8110(b) of this title (relating to Emission Monitoring System Requirements for Utility Electric Generation Sources);

(C) monitor operating parameters for each unit in accordance with 40 CFR Part 75, Appendix E, §1.1 or §1.2 and calculate NOX emission rates based on those procedures; or

(D) use the maximum block one-hour emission rate as measured during the initial demonstration of compliance required in §117.235(e) of this title (relating to Initial Demonstration of Compliance).

(c) CEMS requirements. The owner or operator of any CEMS used to meet a pollutant monitoring requirement of this section shall comply with the requirements in [of] §117.8100(a) of this title (relating to Emission Monitoring System Requirements for Industrial, Commercial, and Institutional Sources).

(d) PEMS requirements. The owner or operator of any PEMS used to meet a pollutant monitoring requirement of this section shall comply with the following.

(1) The PEMS must predict the pollutant emissions in the units of the applicable emission limitations of this division.

(2) The PEMS must meet the requirements in [ of] §117.8100(b) of this title.

(e) Engine monitoring. The owner or operator of any [gas-fired lean-burn] stationary [reciprocating] internal combustion engine subject to the emission specifications of this division that is not equipped with a NOX CEMS or PEMS shall stack test engine NOX emissions as specified in §117.8140(a) of this title (relating to Emission Monitoring for Engines).

(f) Run time meters. The owner or operator of any stationary gas turbine or [gas-fired lean-burn] stationary [reciprocating ] internal combustion engine claimed exempt using the exemption in [of] §117.203(1)(D), (2), or (3) of this title (relating to Exemptions) shall record the operating time with a non-resettable elapsed run time meter.

(g) Data used for compliance. After the initial demonstration of compliance required by §117.235 of this title, the methods required in this section must be used to determine compliance with the emission specifications of §117.205(a) of this title. For enforcement purposes, the executive director may also use other commission compliance methods to determine whether the unit is in compliance with applicable emission specifications.

(h) Testing requirements.

(1) The owner or operator of units that are subject to the emission specifications in [of] §117.205(a) of this title shall test the units as specified in §117.235 of this title in accordance with the applicable schedule specified in §117.9010 of this title (relating to Compliance Schedule for Bexar County [Eight-Hour ] Ozone Nonattainment Area Major Sources).

(2) The owner or operator of any unit [not equipped with CEMS or PEMS that are] subject to the emission specifications in [of] §117.205(a) of this title that is not equipped with a NOX CEMS or PEMS shall retest the unit as specified in §117.235 of this title within 60 days after any modification that could reasonably be expected to increase the NOX emission rate.

§117.245. Notification, Recordkeeping, and Reporting Requirements.

(a) Startup and shutdown records. For units subject to the startup and/or shutdown provisions in [of] §101.222 of this title (relating to Demonstrations), hourly records must be made of startup and/or shutdown events and maintained for a period of at least two years. Records must be available for inspection by the executive director, the United States Environmental Protection Agency, and any local air pollution control agency having jurisdiction upon request. These records must include but are not limited to: type of fuel burned; quantity of each type of fuel burned; and the date, time, and duration of the procedure.

(b) Notification. The owner or operator of a unit subject to the emission specifications in [of] §117.205(a) of this title (relating to Emission Specifications for Reasonably Available Control Technology (RACT)) shall submit [written] notification to the appropriate regional office and any local air pollution control agency having jurisdiction as follows: [ of any continuous emissions monitoring system (CEMS) or predictive emissions monitoring system (PEMS) relative accuracy test audit (RATA) conducted under §117.240 of this title (relating to Continuous Demonstration of Compliance) or any testing conducted under §117.235 of this title (relating to Initial Demonstration of Compliance) at least 15 days in advance of the date of the RATA or testing to the appropriate regional office and any local air pollution control agency having jurisdiction.]

(1) written notification of the date of any testing conducted under §117.235 of this title (relating to Initial Demonstration of Compliance) at least 15 days prior to such date; and

(2) written notification of the date of any continuous emissions monitoring system (CEMS) or predictive emissions monitoring system (PEMS) relative accuracy test audit (RATA) conducted under §117.240 of this title (relating to Continuous Demonstration of Compliance) at least 15 days prior to such date.

(c) Reporting of test results. The owner or operator of a unit subject to the emission specifications in [of] §117.205(a) of this title shall furnish the Office of Compliance and Enforcement, the appropriate regional office, and any local air pollution control agency having jurisdiction a copy of the results of any testing conducted under §117.235 of this title and any CEMS or PEMS RATA conducted under §117.240 of this title:

(1) within 60 days after completion of such testing or evaluation; and

(2) not later than the compliance schedule specified in §117.9010 of this title (relating to Compliance Schedule for Bexar County [Eight-Hour] Ozone Nonattainment Area Major Sources).

(d) Semiannual reports. The owner or operator of a unit required to install a CEMS or PEMS under §117.240 of this title shall report in writing to the executive director on a semiannual basis any exceedance of the applicable emission specifications of this division (relating to Bexar County Ozone Nonattainment Area Major Sources) and the monitoring system performance. All reports must be postmarked or received by the 30th day following the end of each calendar semiannual period (i.e., July 30 and January 30). Written reports must include the following information:

(1) the magnitude of excess emissions computed in accordance with 40 Code of Federal Regulations §60.13(h), any conversion factors used, the date and time of commencement and completion of each time period of excess emissions, and the unit operating time during the reporting period;

(2) specific identification of each period of excess emissions that occurs during startups, shutdowns, and malfunctions of the affected unit, the nature and cause of any malfunction (if known), and the corrective action taken, or preventative measures adopted;

(3) the date and time identifying each period when the continuous monitoring system was inoperative, except for zero and span checks and the nature of the system repairs or adjustments;

(4) when no excess emissions have occurred or the continuous monitoring system has not been inoperative, repaired, or adjusted, such information must be stated in the report; and

(5) if the total duration of excess emissions for the reporting period is less than 1.0% of the total unit operating time for the reporting period and the CEMS or PEMS downtime for the reporting period is less than 5.0% of the total unit operating time for the reporting period, only a summary report form (as outlined in the latest edition of the commission's Guidance for Preparation of Summary, Excess Emission, and Continuous Monitoring System Reports) must be submitted, unless otherwise requested by the executive director. If the total duration of excess emissions for the reporting period is greater than or equal to 1.0% of the total unit operating time for the reporting period or the CEMS or PEMS downtime for the reporting period is greater than or equal to 5.0% of the total unit operating time for the reporting period, a summary report and an excess emission report must both be submitted.

(e) Reporting for engines. The owner or operator of any stationary internal combustion [gas-fired] engine subject to the emission specifications in §117.205(a) of this title shall report in writing to the executive director on a semiannual basis any excess emissions and the air-fuel ratio monitoring system performance. All reports must be postmarked or received by the 30th day following the end of each calendar semiannual period (i.e., July 30 and January 30). Written reports must include the following information:

(1) the magnitude of excess emissions (based on the quarterly emission checks in [of] §117.230(b)(5) [§117.230(a)(2)] of this title (relating to Operating Requirements) and the biennial emission testing required for demonstration of emissions compliance in accordance with §117.240(e) of this title), computed in pounds per hour and grams per horsepower-hour, any conversion factors used, the date and time of commencement and completion of each time period of excess emissions, and the engine operating time during the reporting period; and

(2) specific identification, to the extent feasible, of each period of excess emissions that occurs during startups, shutdowns, and malfunctions of the engine or emission control system, the nature and cause of any malfunction (if known), and the corrective action taken, or preventative measures adopted.

(f) Recordkeeping. The owner or operator of a unit subject to the requirements of this division shall maintain written or electronic records of the data specified in this subsection. Such records must be kept for a period of at least five years and must be made available upon request by authorized representatives of the executive director, the United States Environmental Protection Agency, or local air pollution control agencies having jurisdiction. The records must include:

(1) for each unit subject to §117.240(a) of this title, records of annual fuel usage;

(2) for each unit using a CEMS or PEMS in accordance with §117.240 of this title, monitoring records of:

(A) hourly emissions and fuel usage (or stack exhaust flow) for units complying with an emission specification enforced on a block one-hour average; or

(B) daily emissions and fuel usage (or stack exhaust flow) for units complying with an emission specification enforced on a [daily or] rolling 30-day average. Emissions must be recorded in units of:

(i) pounds per million British thermal units (lb/MMBtu) heat input; and

(ii) pounds or tons per day;

(3) for each stationary internal combustion engine subject to the emission specifications of this division, records of:

(A) emissions measurements required by:

(i) §117.230(b)(5) [§117.230(2)] of this title; and

(ii) §117.240(e) of this title;

(B) catalytic converter, air-fuel ratio controller, or other emissions-related control system maintenance, including the date and nature of corrective actions taken; and

(C) daily average horsepower and total daily hours of operation for each engine that the owner or operator elects to use the alternative monitoring system allowed under §117.240(a)(2)(C) of this title;

(4) for units claimed exempt from emission specifications using the exemption in [of] §117.203(1)(D) , (2), or (3) of this title (relating to Exemptions), records of monthly hours of operation, for exemptions based on hours per year of operation. In addition, for each turbine or engine claimed exempt under §117.203(1)(D) or (E) of this title, written records must be maintained of the purpose of turbine or engine operation and, if operation was for an emergency situation, as defined in §117.10(15) of this title (relating to Definitions), identification of the type of emergency situation and the start and end times and date(s) of the emergency situation;

(5) records of the results of initial certification testing, evaluations, calibrations, checks, adjustments, and maintenance of CEMS or PEMS; [and]

(6) records of the results of performance testing, including initial demonstration of compliance testing conducted in accordance with §117.235 of this title; and [.]

(7) for each stationary diesel engine subject to the operating restrictions of §117.205(e) of this title, records of each time the engine is operated for testing and maintenance of the engine, including:

(A) date(s) of operation;

(B) start and end times of operation;

(C) identification of the engine; and

(D) total hours of operation for each month and for the most recent 12 consecutive months.

The agency certifies that legal counsel has reviewed the proposal and found it to be within the state agency's legal authority to adopt.

Filed with the Office of the Secretary of State on July 11, 2025.

TRD-202502369

Charmaine K. Backens

Deputy Director, Environmental Law Division

Texas Commission on Environmental Quality

Earliest possible date of adoption: August 24, 2025

For further information, please call: (512) 239-0682


SUBCHAPTER H. ADMINISTRATIVE PROVISIONS

DIVISION 1. COMPLIANCE SCHEDULES

30 TAC §117.9010

Statutory Authority

The amendments are proposed under Texas Water Code (TWC), §5.102, concerning general powers; §5.103, concerning Rules; TWC, §5.105, concerning General Policy, which authorize the commission to adopt rules necessary to carry out its powers and duties under the TWC; TWC, §7.002, concerning Enforcement Authority, which authorizes the commission to enforce the provisions of the Water Code and the Health and Safety Code within the commission's jurisdiction; and under Texas Health and Safety Code (THSC), §382.017, concerning Rules, which authorizes the commission to adopt rules consistent with the policy and purpose of the Texas Clean Air Act.

The amendments are also proposed under THSC, §382.002, concerning Policy and Purpose, which establishes the commission's purpose to safeguard the state's air resources, consistent with the protection of public health, general welfare, and physical property; THSC, §382.011, concerning General Powers and Duties, which authorizes the commission to control the quality of the state's air; THSC, §382.012, concerning the State Air Control Plan, which authorizes the commission to prepare and develop a general, comprehensive plan for the proper control of the state's air; THSC, §382.016, concerning Monitoring Requirements; Examination of Records, which authorizes the commission to prescribe reasonable requirements for measuring and monitoring the emissions of air contaminants; and THSC, §382.021, concerning Sampling Methods and Procedures.

The proposed amendments implement TWC, §§5.102, 5.103, and 7.002; and THSC, §§382.002, 382.011, 382.012, 382.016, 382.017, and 382.021.

§117.9010. Compliance Schedule for Bexar County Ozone Nonattainment Area Major Sources.

(a) The owner or operator of any stationary source of nitrogen oxides (NOX) in the Bexar County ozone nonattainment area that is a major source of NOX and is subject to §117.205(a) of this title (relating to Emission Specifications for Reasonably Available Control Technology (RACT)) shall comply with the requirements of Subchapter B, Division 2 of this chapter (relating to Bexar County Ozone Nonattainment Area Major Sources) as follows: [shall comply with the requirements of Subchapter B, Division 2 of this chapter as soon as practicable, but no later than January 1, 2025.]

(1) for units subject to the emission specifications in §117.205(a) of this title that emit or have the potential to emit equal to or greater than 100 tons per year (tpy) of NOX:

(A) submission of the control plan required by §117.252 of this title (relating to Control Plan Procedures for Reasonably Available Control Technology) was required by January 1, 2025;

(B) for units subject to the emission specifications in §117.205(a) of this title as of January 1, 2025, compliance with all other requirements of Subchapter B, Division 2 of this chapter was required by January 1, 2025, and these units must continue to comply with the requirements of Subchapter B, Division 2 of this chapter; and

(C) for units that became subject to the emission specifications in §117.205(a) of this title after January 1, 2025, compliance is required as specified in subsection (b) of this section.

(2) for units subject to the emission specifications in §117.205(a) of this title that emit or have the potential to emit equal to or greater than 50 tpy but less than 100 tpy of NOX:

(A) submission of the control plan required by §117.252 of this title is required no later than February 1, 2026; and

(B) compliance with all other requirements of Subchapter B, Division 2 of this chapter is required as soon as practicable but no later than March 1, 2026.

(b) The owner or operator of any stationary source of NOX that becomes subject to the requirements of Subchapter B, Division 2 of this chapter on or after the applicable compliance date specified in subsection (a) of this section[,] shall comply with the requirements of Subchapter B, Division 2 of this chapter as soon as practicable, but no later than 60 days after becoming subject.

The agency certifies that legal counsel has reviewed the proposal and found it to be within the state agency's legal authority to adopt.

Filed with the Office of the Secretary of State on July 11, 2025.

TRD-202502370

Charmaine K. Backens

Deputy Director, Environmental Law Division

Texas Commission on Environmental Quality

Earliest possible date of adoption: August 24, 2025

For further information, please call: (512) 239-0682