Environmental regulation in Texas is pervasive. Texas has been delegated authority to implement most major federal programmes, including the Clean Air Act, the Clean Water Act, and the Resource Conservation and Recovery Act. In many instances, however, Texas’ regulatory programmes contain unique state-specific requirements. For example, Texas’ Solid Waste Disposal Act (SWDA) goes beyond the liability framework for hazardous substances under the Comprehensive Environmental Response, Compensation, and Liability Act (CERCLA) and extends to other solid wastes.
In Texas, the Texas Commission on Environmental Quality (TCEQ) oversees various environmental programs and regulations; however, certain environmental activities within the oil and gas industry fall under the jurisdiction of the Texas Railroad Commission (RRC). A memorandum of understanding (MOU) exists between the two agencies, outlining the general divisions of jurisdiction over the environmental regulation of various oil and gas activities. The MOU resides in the Texas Administrative Code. Thus, when doing business in Texas, compliance considerations must go beyond mere compliance with federal programmes.
Texas’ regulatory programmes are prescriptive, and enforcement allows for assessment of per diem, per-violation penalties. In addition to federal and state environmental programmes, certain larger local jurisdictions, including Harris County and the cities of Houston and Dallas, have enacted robust environmental ordinances and have strong independent enforcement arms.
Myriad agencies administer environmental regulation in Texas. The TCEQ has jurisdiction over most traditional environmental programmes. The RRC, however, administers certain environmental regulatory programmes involving the oil and gas industry. The MOU between TCEQ and RRC sets forth specific requirements for oil and gas activities related to waste management, water quality, injection wells, and incident reporting within each agency’s respective jurisdiction. Other Texas agencies have jurisdiction over specific programmes, including the Texas General Land Office (GLO), the Texas Parks and Wildlife Department (TPWD), and the Texas Department of State Health Services (DSHS).
Texas’ regulatory programmes are generally prescriptive in nature and its environmental agencies have active enforcement arms. Despite this, agency personnel are generally available, knowledgeable, and open to discussing compliance issues in a blind or site-specific context. Moreover, Texas has implemented effective programmes that foster compliance. For example, the TCEQ promulgated rules creating what is known as the Voluntary Clean-up Programme or VCP. This programme allows parties to self-implement site clean-up under agency supervision, which, when complete, can afford immunity from clean-up liability to both the landowner and the transferee.
A further example of co-operative compliance is the state’s Environmental, Health, and Safety Audit Privilege Act (Audit Act), pursuant to which a regulated entity can secure immunity for certain violations identified by an environmental audit conducted in accordance with the Audit Act.
Both the TCEQ and RRC administer the Audit Act. While certain exceptions exist, immunity can be conferred when disclosure and corrective actions are completed in a timely manner, provided disclosures are submitted via certified mail. To qualify, operators must submit a Notice of Audit (NOA) before evaluating the compliance of existing operations (and before any enforcement is initiated), as the Audit Act’s immunity only applies to violations discovered during an environmental audit conducted after filing the NOA. The audit must generally be completed within six months, and disclosures must be made promptly, with corrections generally made within six months of the disclosure. The Audit Act can also be used in connection with pre-acquisition due diligence to mitigate post-closing liability for pre-closing discoveries.
Texas protects the environment through detailed statutes and regulations. Important statutes include the Texas Clean Air Act, the Texas Water Code, and the Texas SWDA, which respectively govern the environmental media of air, water, and waste management. Texas has detailed air, water, and waste-permitting programmes, as well as detailed licensing programmes relating to naturally occurring radioactive materials and low-level radioactive waste. Due to the nature of the oil and gas industry, injection well regulation often necessitates additional attention. In Texas, underground injection control regulations are primarily managed by the RRC for oil and gas-related injection wells, and by the TCEQ for other well types. RRC and TCEQ regulations set forth detailed permitting, construction, and closure requirements for various injection well classes within their respective jurisdictions.
Texas has its own endangered species and wetlands programs in addition to federal initiatives. While there is no direct equivalent to the federal National Environmental Policy Act (NEPA) at the state level, projects regulated by the state must adhere to a similar process. Texas employs a framework of state laws, which are overseen by the TCEQ and the TPWD. For example, TPWD collaborates with pipeline operators to adjust routes by proposing alternative routes that minimise environmental harm to specific properties, particularly state-owned wildlife management areas (WMAs) and other environmentally sensitive areas.
Non-compliance in Texas can lead to serious consequences. Enforcement is multi-layered, involving state, federal, and in some cases, local authorities. Texas has statutory authority for civil, administrative, and criminal enforcement. The law allows for per diem and per-violation penalties, and injunctive relief may also be available. In addition to state authorities, Region 6 of the US Environmental Protection Agency (EPA) actively enforces environmental programmes in Texas. Many federal environmental statutes provide for direct “citizen suits” to enforce permit requirements in federal court. In recent years, Region 6 has been particularly aggressive in enforcing air emissions regulations, with a focus on the oil and gas industry.
Generally, Texas’ statutory authorities confer broad investigative authority. When potential violations are found, there is usually prompt notice and an opportunity to discuss before formal enforcement begins. In some instances, resolution may occur without formal enforcement. It is good practice for regulated entities to respond promptly in writing to any notice and document compliance efforts.
Texas has a wide and varied permitting programme. Virtually all air emissions, as well as discharges to state waters and waste management activities, must be authorised. Texas has one of the most comprehensive air permitting programmes in the US and industrial companies should consult with technical consultants and counsel familiar with the state’s labyrinthine rules before and during facility planning.
In many instances, permitting will entail public notice, pursuant to which “affected persons” may object to the issuance of a permit. Such “protesters” may even have the right to a hearing before the State Office of Administrative Hearings to determine if a draft permit should be finalised and issued. This is tantamount to a mini-trial and may involve technical experts and legal counsel. Recent litigation has granted contested case hearing standing to protesters well beyond TCEQ’s prior default threshold of a one-mile geographic radius from the facility.
Texas permitting often involves providing notice to affected parties and local officials, as well as posting site-specific notices and advertisements in local publications, including those in alternative languages. The process has specific timelines. Certain permit actions require the applicant to prepare a Public Involvement Plan, including disclosure of community and demographic information. If a permit is denied and administrative remedies are exhausted, the decision can be appealed to a state court. The Texas legislature’s business courts initiative recently formed the Fifteenth Court of Appeals, which now has statewide exclusive jurisdiction over permitting challenges and enforcement actions involving industries regulated by TCEQ and RRC, rather than Austin’s Third Court of Appeals.
The TCEQ-RRC MOU identifies specific requirements applicable to waste generated from oil and gas activities, including drilling, production, completions, treatment, and other field operations, as well as associated disposal activities, such as recycling, on-site waste treatment, and commercial disposal operations. The RRC recently adopted new comprehensive regulations, effective 1 July 2025, governing the handling, storage, treatment, and disposal of oil and gas waste. The new RRC rules update the requirements for oil and gas pits by requiring registration for common pits. The RRC imposes pit liner requirements if groundwater is present within 50 feet, the pit holds fluids with a high solids concentration, or the pit is used to treat and recycle produced water.
Commercial waste management facilities, including oil and gas waste landfills, must comply with updated siting, design, and operational requirements, provide increased financial security, and implement groundwater monitoring programmes, in addition to record-keeping and reporting requirements.
State agencies and the EPA each have detailed enforcement policies and/or matrices that can be reviewed to understand the basis for potential penalties. Generally, permitting liability is considered strict, meaning liability can be conferred without fault or intent to violate. While EPA Region 6 typically does not share penalty calculations, Texas agencies, including the TCEQ, will typically provide the basis for their penalty calculations. Texas penalty assessments take into account the degree of environmental harm; however, the duration of the violation and other specific factors are implicated. Finally, in Texas, a regulated entity’s compliance history can be considered in penalty assessment and permit renewal applications, which may subject facilities to higher enforcement penalties and stricter permit conditions. Compliance scores are publicly available.
Whether an environmental permit is transferable is programme-specific. In many instances, air permits can be transferred, while other permits cannot. Each environmental permit should be reviewed for specific conditions that could affect transfer, and of course, statutory and regulatory provisions should also be carefully reviewed. Sale or merger transactions involving changes in ownership, operation, or identity often trigger permit transfer obligations. Permit transfers may have time restrictions related to agency approvals that are relevant to closing date requirements.
Breaching permit terms or operating without a permit can have significant consequences. It is important to understand that facilities must operate as represented in a permit application. Thus, changes to equipment or operations will typically be considered a violation. Federal and state statutes authorise per-violation fines and penalties, and the cost of challenging assessments that are not negotiated can be significant. In certain circumstances, criminal enforcement can be sought, as can injunctive relief.
Regarding liability, operators generally face strict liability for permit and other programmatic violations. In 2023, the Texas legislature approved penalties of up to USD40,000 per day for certain violations related to the release of pollutants, an increase from its previous maximum of USD25,000 per day. Fines and penalties vary depending on the nature of the violation, and criminal liability can generally be imposed for knowingly violating the law. In certain cases, the amount of a penalty may depend on the size and profitability of the violator. Regarding clean-up, Texas typically enforces strict joint and several liability starting from “status.” That is, clean-up liability exists for owners and operators, based upon that status. Under federal law, arranger and transporter liability also exists. The Texas SWDA, however, specifically authorises liability apportionment. Regarding liability for environmental contamination, plaintiffs may also seek common law recovery of property damages by alleging private causes of action such as negligence, nuisance and trespass. Personal injury claims may also seek recovery based on alleged exposure to environmental contaminants.
In Texas, current landowners and operators can be held liable for historical contamination based upon their status as current owners or operators. Prior owners and operators may be held liable if a release occurred during their tenure at the facility. The Texas SWDA specifically recognises liability apportionment if a release is “divisible.” Divisibility generally assesses whether the waste released can be managed separately under a remedial action plan.
Clean-up liability can also exist under other Texas statutes, depending on the nature of the substance or source of material released. Statutes to consider include the Texas Water Code, the Texas Natural Resources Code, and the Oil Spill Prevention and Response Act, among others.
Texas provides for clean-up and incident response liability, as well as potential civil liability for injured parties. Enforcement liability exists for non-compliance and releases. Defences are fact-specific and may, among other things, focus on causation, the party with a duty to comply, and the divisibility of the harm. The SWDA incorporates defences that are similar, but not identical to those found in the federal CERCLA statute.
In Texas, an innocent operator defence to contamination liability requires the property owner to provide evidence, usually in the form of environmental site assessments, demonstrating that the contamination came from an off-site source. The Texas Innocent Operator Programme (IOP) provides an avenue for an innocent owner or operator to receive an IOP certificate if their property is contaminated because of a release or migration of contaminants from a source not located on the property, provided the owner or operator did not cause or contribute to the source of contamination. The IOP serves as a defence to state clean-up liability. The TCEQ also has specific procedures for entities claiming affirmative defences to unauthorised air emission events.
Generally, statutory laws in Texas do not differentiate liability based on corporate status. Regarding penalties, some differentiation exists under Texas statutory law, and it is a factor that may be considered in agency penalty policies. For instance, corporations that are “repeat violators” with “unsatisfactory” compliance history scores may receive increased penalty adjustments.
Texas does not impose a specific environmental tax (for example, there is no carbon or greenhouse gas (GHG) tax in Texas). Although these are not technically classified as “taxes,” the state does collect substantial fees related to air emissions and air inspections. Annual air emission fees apply to major sources, based on tons of pollution emitted. Air investigation fees are based on the Standard Industrial Classification (SIC) code of a regulated entity. Other activity-specific environmental fees, which relate to other environmental programmes, are also assessed by the TCEQ.
While Texas does not impose material environmental taxes, it does offer broad incentives for the utilisation of property or equipment for pollution control. Under Texas law, a tax exemption may be obtained for real or personal property used wholly or partly as a facility, device, or method for controlling air, water, or land pollution, based on a “positive use determination.” The nature of “qualifying property” is listed by rule. Other important property tax exemptions are available for certain renewable projects.
Texas generally follows traditional corporate standards for piercing the corporate veil. Regarding statutory liability, the degree of control exercised by officers, directors, shareholders, parents, or affiliates can affect their risk for being deemed an “operator”. The US Supreme Court case of US v Best Foods provides sound legal guidance on this issue.
At this time, there is no mandatory ESG reporting in Texas. Rather, reporting is market-driven. Many public and private companies, however, prepare and publish ESG or sustainability reports. Companies should not overstate, but rather be specific, consistent, and use data to substantiate assertions related to recycling, climate change, sustainability, and similar issues, thereby avoiding the risk and potential uncertainty of defending “greenwashing” claims.
Generally, there are no mandatory self-auditing requirements. Various environmental programmes, however, require inspection, reporting, and corrective action. Similar provisions are also included within facility authorisations. The Audit Act (discussed above) enables a prospective buyer to assess a target company’s environmental liabilities and compliance systems prior to a merger or acquisition, thereby allowing the buyer to better understand potential financial risks and identify any required corrective actions to avoid future liabilities that may be detrimental to the acquired asset’s value.
Regarding statutory liability, the degree of control exercised by officers, directors, and shareholders can affect their risk for being deemed an “operator.” The US Supreme Court case of US v Best Foods also provides legal guidance on this issue.
Reasonable insurance products are generally available in Texas on a site-specific basis. Pollution Legal Liability (PLL) policies are offered by a number of underwriters. These policies, among other things, offer insurance protection against the discovery of pollution conditions. In some instances, coverage for pre-existing conditions may be available. Such PLL policies often have a “voluntary investigation exclusion,” which precludes coverage for sampling conducted outside of an agency’s directive.
Furthermore, in a transactional context, representation and warranty insurance may be available in some instances. Each of these coverages will typically require diligence and disclosure to underwriters, usually with exclusions for known conditions. Other exclusions often include intentional acts, underground storage tanks (USTs), prior knowledge, assumed contractual liability of third parties, lead, asbestos, contamination from per- and poly-fluorinated substances (PFAS), failure to maintain controls, changed use, and others.
In some instances, a well-designed environmental liability insurance programme can address D&O liability for pollution events, typically in those situations where corporate liability could exist. Environmental insurance coverage is not static, and policies may often be manuscripted.
Lender liability for contaminated assets is governed by federal and state legislation. Under both federal and state law, a key touchstone is whether the lender constitutes an “owner” or “operator” of the secured collateral. The federal CERCLA statute has an established liability carve-out for lenders who hold indications of ownership (eg, a mortgage) to protect a security interest, without participating in the management of the secured asset. Texas has adopted specific protections from liability arising under state clean-up regimes, which are largely consistent with the federal safe harbour. Texas, however, has certain defined criteria to ensure the safe harbour is met. First, the lender must sell, lease or undertake a government-approved clean-up within a “commercially reasonable time” after the foreclosure (or similar event). A presumption of divestiture exists if the asset is listed or advertised within 12 months after the title is acquired. The Texas safe harbour can be lost if pollution conditions arise after foreclosure.
Touchstones exist to mitigate the potential for lender liability. First, there must be an awareness of the safe harbour. Second, due diligence is critical not only of the asset to be taken as collateral, but also of the borrower’s environmental management team. Third, it is important to maintain an ongoing understanding of the asset during the loan term, as well as ensuring that the loan documentation provides protections and assurances appropriate for the asset. Finally, experienced post-foreclosure staffing should have operational experience in the relevant industry to avoid environmental liability that could arise post-foreclosure and avert the Texas safe harbour.
Civil claims may be brought under several Texas environmental statutes, depending on the relevant facts. Additionally, claims at common law may be brought under traditional common law theories, including nuisance, negligence, and trespass. Suits may also be brought in a transactional context based upon common law or statutory fraud, as well as breach of applicable contractual provisions.
These damages can be waived by contract, but otherwise may be available in cases where the plaintiff seeks recovery for damages resulting from “fraud, malice, or gross negligence.” The basis for these damages must be proven by “clear and convincing evidence.” Under certain circumstances, these damages may be available in a statutory fraud case.
Class actions or multi-plaintiff cases may be brought in Texas, including those involving alleged environmental harm.
Texas has been home to several landmark environmental cases. For example, Cooper Industries, Inc. v Aviall Services, Inc. addressed the circumstances under which CERCLA claims for cost recovery may be available. Upon remand to the federal district court in Texas, it addressed the relationship between certain Texas statutory and contractual claims. Furthermore, the Matter of Bell Petroleum, Inc. was a Fifth Circuit Court of Appeals holding and allowed for apportionment of CERCLA liability, utilising theories derived from the Restatement (Second) of Torts. Certain recent cases decided outside of Texas courts will certainly affect business in Texas. For example, in Sackett v EPA, the US Supreme Court recently held that jurisdictional “waters of the United States” must generally be relatively permanent or continuously flowing bodies of water.
Further, in 2024, the US Supreme Court overruled the Chevron deference doctrine in Loper Bright Enterprises v Raimondo, which had provided a judicial review framework for statutory interpretations by federal agencies for 40 years. In 2025, following Loper Bright, the US Supreme Court in Seven County Infrastructure Coalition v Eagle County Colorado upheld the US Surface Transportation Board’s decision to approve an application to construct a railroad line after the Board analysed an Environmental Impact Statement prepared under NEPA. Seven County addressed judicial deference post-Loper Bright, emphasising that the “central principle” of judicial review is deference in NEPA cases. In other words, agencies must be afforded “substantial deference,” and courts should not “micromanage” agency decisions, provided such decisions “fall within the broad zone of reasonableness.”
In Texas, liability for environmental matters may generally be allocated between the parties to a transaction. Allocation mechanisms may include indemnities, assumptions of liability and/or releases or covenants not to sue. The parties’ allocation framework is not binding upon the regulatory authorities. Regarding indemnities for strict liability and similar provisions, it is good practice for the language to be conspicuous and expressly state the scope of the risk allocated. Oil and gas transactions often include reference to a relatively unique concept called an “environmental defect,” for which a seller may retain responsibility, provide indemnity, or a price adjustment. “Environmental defects” in oil and gas transactions commonly include matters related to soil and groundwater contamination and regulatory non-compliance relating to contamination, in addition to unique historical concepts related to orphan wells and liabilities associated with the presence of improperly plugged or abandoned wells. It is important, however, to review this language carefully to determine whether it would include air permitting and emissions regulation, as well as other regulatory programs that can impose significant liabilities on oil and gas assets. Further attention should be paid to monetary caps and aggregation of costs associated with similar environmental defects.
The SWDA and its implementing regulations serve as the starting point in Texas for addressing site clean-up and responsibility. The Texas Natural Resources Code and its regulations govern contamination resulting from oil and gas operations. Texas rules allow risk-based closures based on site-specific factors and consider the actual risks caused by contaminants.
The persons responsible for clean-up generally mirror federal law:
Parties can contractually delegate these responsibilities, but contractual arrangements are not binding on regulatory authorities.
Statutory clean-up liability is generally strict and joint and several, but the Texas SWDA allows for apportionment. Liability apportionment is fact-specific and the party seeking apportionment bears the burden of proof.
Regarding contaminated properties, the state is authorised under statutory authority to assert claims for clean-up liability against the four general classes of responsible parties under federal law. Texas law also gives responsible parties the right of contribution. Other Texas statutes authorise causes of action to address clean-up and are programme and/or fact-specific.
Releases of regulated materials are subject to detailed release reporting and response obligations. The TCEQ-RRC MOU outlines notification and clean-up requirements for certain oil and gas activities. Under certain circumstances, Texas rules permit self-implementation of clean-ups. The state has a vibrant Voluntary Clean-up Programme (VCP) that allows parties to obtain a release upon site closure. The VCP may also serve as a tool to protect property buyers of a contaminated site, depending on the situation. Texas also has a state Superfund Program.
Currently, there are no specific laws addressing the issue of climate change. Local initiatives do exist, however, and many of Texas’ major cities have established initiatives that should be considered in legal and business analyses relating to facility development and operations. In 2023, the Texas legislature passed a law providing that the state of Texas, not local governments, has exclusive jurisdiction over the regulation of GHG emissions, to the extent not pre-empted by federal law. This law prohibits cities and counties from creating or enforcing ordinances that directly regulate GHGs.
Texas currently does not have mandatory GHG emission reduction targets. Policy and emission reduction targets are largely being set at the local level by larger cities.
Texas has not established formal carbon emission targets. However, starting 1 September 2023, the Texas legislature made changes to the Natural Resources Code, which now prohibits state agencies from assisting with or enforcing federal laws that attempt to regulate oil and gas operations in Texas, where the state has already enacted its own legislation. The effect of this legislation on federal GHG reduction efforts is unclear. Texas entities operating in California should also be aware of a new California law with disclosure requirements for entities making claims regarding achievements of “net zero emissions,” “carbon neutrality,” or “significant reductions” in GHG emissions. By 1 January 2025, entities making these claims must post accurate information supporting their basis for these assertions. Reporting entities are required to update their disclosures at least annually under this California law.
The Texas DSHS has the responsibility to administer federal asbestos regulations and enforce the asbestos NESHAP in Texas. The DSHS also implements the Texas Asbestos Health Protection Rules, which require licensing and registration for asbestos abatement workers or workers in any asbestos-related regulated activity:
The TCEQ administers the industrial solid waste regulatory programme that governs PCB waste generated by industrial activity in Texas. Further, the RRC governs PCB waste from oil and gas activities.
The SWDA and the Texas Water Code create a framework that aligns closely with federal environmental laws. Although the requirements do not perfectly align with federal waste regulations, Texas offers a more detailed classification of waste streams.
Waste generators are generally liable for their waste, even after it is legally disposed of or transferred to another party.
Texas requires television and computer equipment manufacturers to offer consumers a used equipment collection and recycling programme under the Computer Recycling and TV Recycling Programmes. Television and computer equipment retailers are also subject to these rules. Retailers may only sell labelled equipment and must order and sell equipment from manufacturers that are on TCEQ’s list of manufacturers with an approved recycling programme.
Waste generators and waste facility operators generally bear responsibility consistent with federal law. Texas, however, has a detailed waste classification system, which expands regulation to wastes based on differing classifications, other than merely hazardous or non-hazardous.
Texas law includes numerous spill, release, and incident reporting to environmental media, including ambient air. Specific reporting requirements depend on the substance released and the nature of the source. In most instances, release reporting will be to the TCEQ. If, however, the source in question is an oil and gas facility, reporting will likely fall under the jurisdiction of the RRC. There are notable exceptions, including that the TCEQ permits and regulates certain discharges from oil and gas activities associated with produced water, hydrostatic test water, and gas plant effluent. The RRC, however, maintains authority over the disposal of oil and gas wastewater through methods that do not discharge into state waters. Likewise, spills involving crude oil and gas at exploration and production sites must be reported to the RRC.
However, certain spills must be reported to the TCEQ, including those involving hazardous substances, solid waste, and refined petroleum products during transportation. Reporting requirements will vary depending on the media impacted as well as the nature of the material released (eg, hazardous substance, crude oil, other petroleum product, etc).
Texas law contains broad and complex reporting requirements for releases of regulated materials. Regarding releases to state waters, the Texas Water Code stipulates that if a release causes or may cause pollution, the person in charge of the facility or activity must provide notice within 24 hours.
Jurisdiction for release reporting is not limited to a single agency. The general reporting requirements are outlined below. Facilities should have a thorough understanding of agency jurisdiction. These reporting requirements are to the TCEQ and are within 24 hours, unless separately noted:
The RRC has specific reporting requirements for oil and gas facilities under its jurisdiction. Generally, facilities must immediately report any incidents of fire, leak, spill, or break. However, notice is not required for releases of less than five barrels of crude oil. Notice is typically followed by a letter giving a full description of the event, including the volume of materials lost. General RRC reporting includes:
The Texas GLO also requires reporting of certain releases:
Additionally, TCEQ air emissions rules contain broad provisions requiring reporting of specific air emission events, and RRC rules also require reporting for certain venting events. TCEQ requires operators to report certain air emission events, including:
Texas provides a litany of resources where the public can obtain environmental information on regulated operations. State environmental agencies maintain an online database of relevant permitting and other documentation by site or operator. These databases are developing, however, and do not always include all the relevant documents. State environmental agencies are also subject to the Texas Public Information Act, which acts like a state version of the FOIA process.
Publicly traded entities are required to disclose environmental information in accordance with the rules established by the US Securities and Exchange Commission (SEC).
Texas does not have traditional state-led “green financing”, but does have programmes such as the Clean Water State Revolving Fund (authorised by the Texas Clean Water Act), which seeks to provide lower-cost financial assistance for the planning, acquisition, design, and construction of wastewater, wastewater reuse, and stormwater infrastructure.
Environmental due diligence has a heightened focus in Texas because the state is home to so many industrial concerns. Phase I and Phase II assessments are common. Moreover, because so many transactions involve industrial concerns and Texas has very detailed regulatory programmes, it is especially important to conduct additional diligence relating to permitting and regulatory compliance. Furthermore, Texas is home to myriad endangered species, as well as wetlands, and in some areas, coastal-specific issues. These issues are important to consider, particularly regarding project development.
Texas law requires disclosure of certain environmental conditions, depending on the nature of the transaction. Disclosures required by statute include:
Other, broader disclosures may include information about asbestos, flood zone status, lead paint, soil stability, methamphetamine use, and other risks, depending on the nature of the transaction. In addition to statutory obligations, disclosure obligations should be considered to avert potential fraud claims. Texas has a specific statutory provision authorising statutory fraud claims specifically in stock and real estate transactions. The statute is broad and allows for fraud to be alleged in situations where a failure to disclose exists, in addition to a misrepresentation.
The most common environmental legal issues arising in transactions in Texas involve:
Texas has a robust oil and gas exploration and production industry, particularly in West Texas. Despite the division of authority between the RRC and TCEQ, some operators should place additional focus on TCEQ-related obligations for air emissions.
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Introduction
Immediately upon taking office, the Trump Administration embarked upon an unprecedented effort to rollback and streamline environmental regulation intended to enable expedited permitting and foster energy and project development. This “agenda” was initially laid out in several Executive Orders and later clarified in a March 2025 pronouncement (“Pronouncement”) by the EPA (Environmental Protection Agency) Administrator Lee Zeldin. The Pronouncement identified 31 regulatory measures that EPA would review for reform. These initiatives generally focused on fostering energy production through the rollback of air emission regulations, but also went further, in addition to mitigating regulatory burdens associated with energy production. Additionally, EPA has signalled throughout 2025 that it would address burdensome wetlands and PFAS regulation, and chemical usage bans. To achieve these goals, the EPA heavily relies on recent judicial precedents, previous EPA policies, statutory interpretations, and advancing scientific knowledge. EPA’s utilisation of these touchstones is especially apparent in its efforts to reform air regulations impacting the energy industry.
EPA’s Rollback of Air Emissions Rules
EPA has primarily concentrated on reforming methane regulations and standards for air toxics that impact power plant emissions. EPA’s proposed methane deregulation is discussed below and impacts at least six regulatory regimes, including EPA’s:
Proposal to rescind the Finding
On 1 August 2025, EPA published its proposal to rescind the Finding, which describes how and why greenhouse gases (“GHGs”) threaten human health and welfare. The Finding pertained to vehicle emissions but formed the basis for the EPA to regulate stationary sources, including the oil and gas and energy sectors. Many legal experts believe that, absent the Finding, EPA lacked authority to regulate methane in any meaningful way. EPA’s proposal attacked the Finding in several ways. First, EPA noted it was the first time ever that regulation of domestic emissions was “based on global climate change concerns rather than air pollution that endangers public health and welfare through local or regional exposure.” EPA noted that in 2009, the agency stated it could issue “standalone” findings triggering a duty to regulate without considering pollutant-specific standards, because the Clean Air Act (“CAA”) was silent on the issue. As such, the EPA then made separate findings that “global” concentrations of six “well-mixed GHGs” constituted air pollution, that GHG emissions from all motor vehicles contributed to global GHGs, and that GHGs generally constitute air pollution that endangers public health and welfare. This Finding was based on several assumptions. First, global GHG concentrations from sources of all countries are the “largest driver” of climate change. Second, climate change increases morbidity and mortality, most likely indirectly through increased temperatures, impacts on food production, and extreme weather. The current administration identified flaws in this approach, noting that these findings do not support a contribution of air pollutants to local or regional issues. Inconsistencies were also identified in the logic behind the Finding. In 2009, the EPA focused on six GHGs collectively without analysing their individual characteristics and health effects and acknowledged that its conceptualisation of public health and welfare was atypical. Further, EPA acted “independently from any new congressional mandate.”
The current EPA found support in recent judicial decisions, eg, the US Supreme Court (“USSC”) rejected a prior attempt to extend GHG emission standards to stationary sources subject to Title I and Title V in Utility Regulation Group v EPA and in West Virginia v EPA, the USSC held that EPA could not “shift the power grid from using fossil fuels through GHG standards for exiting power plants” because such actions implicated a major national question that must be clearly Congressionally authorised – much like regulating a global emissions issue. Further, the recent USSC Loper Bright decision generally overturned the concept that courts should defer to agency action, particularly where statutes are silent. The EPA now asserts that it would exercise discretion differently, stating that today’s science differs from that in 2009, and that the 2009 projections the EPA relied on were overly pessimistic. Additionally, the EPA notes that certain climate change mandates were “based on inaccurate assumptions” and data.
EPA now concludes that the CAA authorises review of existing emission standards and that the CAA governs regional and local, not global exposures. Finally, a more defined nexus of specific air pollutants themselves to causation and/or contribution to local or regional health and welfare impacts is necessary to regulate.
Repeal of the Clean Power Plan 2.0
On 17 June 2025, the EPA proposed repealing GHG standards applicable to fossil fuel-fired electric generating units (“EGUs”). The proposal repeals all GHG standards applicable to these EGUs, including the:
Specifically, the EPA must make a finding that GHG emissions from a source category significantly contribute to air pollution that endangers public health and welfare before the EPA can regulate GHGs from that source category. EPA concurrently determined that GHGs from these EGUs do not contribute to dangerous air pollution. EPA also proposed a more limited alternative approach to rollback EGU regulation. Alternatively, EPA proposes to repeal EGs for existing fossil fuel EGUs and the carbon capture and storage (“CCS”) requirements for coal-fired steam generating units subject to a major modification and certain other CCS requirements for new base load stationary combustion turbines.
This is important for the electric generation sector. If promulgated, the proposal would breathe life into the fossil fuel EGU sector. The profitability and operational stability of this industry should be more certain and scalable, absent the necessity of stringent controls as called for by the Plan. In turn, this should lead to less costly energy production, which is necessary for the US to effectively compete in the AI race.
Reform of the GHGRP
On 16 September 2025, the EPA proposed rolling back the GHGRP, a mandatory information collection requirement imposed on industry. It is not, however, related to a specific rule. EPA estimates this rollback will save US businesses about USD2.4 billion, and that, in the absence of this burden, industry will be able to allocate compliance costs to matters having “tangible environmental benefits.” The GHGRP is understood to regulate over 8,000 facilities in 47 “source categories.” The proposal repeals all GHG reporting requirements except for the petroleum and natural gas sectors as mandated by the EPA’s WEC under CAA §136(g). Data collected from this sector has been delayed until 2034, pursuant to recent legislation called The One Big Beautiful Bill (“BBB”).
In conclusion, the EPA determined that, except for the petroleum and natural gas sector, there is no statutory basis for collecting GHG emissions data. EPA notes that industry may independently collect such data, but refrained from establishing a voluntary reporting program, which could result in incomplete, piecemeal, or reports based on different assumptions.
Rollback of the WEC
The WEC was established under the 2022 Inflation Reduction Act. At its core, it is a tax on methane emissions from the oil and gas sector, subject to reporting under the GHGRP. From its inception, the WEC’s implementation was fraught with opaque, if not inconsistent, rule-making. Its deadlines may not have been practicable based on supply chain vagaries and equipment supplier shortages.
Two actions accomplish the rollback. First, pursuant to the Congressional Review Act, the WEC’s final implementing regulations were voided. To address the tax’s statutory implementation and reporting obligations, the BBB delays reporting and payment of the WEC until calendar year 2034 or later. This delay should enable the industry to better plan for potential implementation (if any) and avoid short-term heightened capital costs for upgrades where equipment may be in short supply. Furthermore, if the WEC is implemented, the maturation of technology should enable more cost-effective emissions reductions, thereby reducing the capital costs necessary to mitigate the tax. Obviously, the industry will also have a more reasonable timetable to prepare for the complex methane accounting necessary for WEC calculations.
Delayed implementation of Quad Ob/Oc standards
Quad Ob and Oc were Biden-era rules establishing standards of performance for new (and modified/reconstructed) oil and gas industry sources, emission sources, and guidelines for existing ones. The rules’ breadth was substantial, establishing emission standards and practices for equipment not previously covered and imposing more stringent standards on certain equipment covered by prior rules. In addition, Quad Oc created guidelines for existing sources consistent with the stringent Quad Ob standards intended to be implemented through state plans. In response to the massive rules package, commenters advised the EPA that not only could equipment unavailability affect timely compliance, but also that labs and testing companies lacked the capacity to conduct analyses and performance testing nationwide within the rules’ timeframes. Another challenge presented by the rules is the no identifiable emissions (“NIE”) standard applicable to closed vent systems. Commentators advised the EPA that NIE presented, among other issues, practicality challenges based on fugitive emissions caused by normal wear and tear. EPA’s proposal is not a pass for industry. Rather, it proposes extensions with more realistic compliance time frames, including for the states. The EPA is signalling that it expects the oil and gas industry to mitigate emissions, but will allow the industry to do so in a manner that is not crippling to business prospects or operations.
The social cost of carbon
The Office of Management and Budget provided official guidance making clear that agencies must modify their regulations and/or rescind guidance to eliminate GHG considerations, except where necessary to meet a statutory requirement. Hence, a monetary value of the SSC may not be considered in rule-making. This is logical. The SCC was often used to justify the regulations’ benefits, even if compliance costs could, in some instances, be business-shattering. Ascribing a dollar value to carbon has always been more voodoo than science. The Obama EPA pegged the SCC at about USD73/ton, while the first Trump Administration revised it to be around USD3-5/ton, and the succeeding Biden administration revised the number to USD51/ton, escalating to USD190/ton by 2023. There was no true formula. Now, regulatory decisions will likely be grounded in more verifiable cost/benefit analyses.
The Evolution (or Revolution) in Wetlands Regulation
In the ongoing tug-of-war between environmental and business/private property interests regarding wetlands, the US Supreme Court and the current administration have tipped the scales decidedly in favour of business and private property interests. For many, this shift is a breath of fresh air. Developers, for example, will continue to benefit from an increasingly tailored definition of wetlands and waters of the US. In Texas, where wetlands are not independently regulated, federal loosening of wetlands regulation is the final word. But that is not the case everywhere: for example, Florida and Massachusetts have their own state and local regulations. As a result, some wetlands in those and other similarly situated states will remain protected even as federal oversight fades.
Why the fuss about wetlands? Wetlands protections are derived from the federal Clean Water Act (“CWA”), 33 U.S.C. 1251, in recognition of the many benefits that wetlands provide: acting as natural filters against water pollution, capturing greenhouse gases like carbon dioxide and methane, reducing flooding potential by filling during significant water events, and providing habitat for certain important plants and animals. Take cattails, for example, which anchor soil and help channel surface water into groundwater, a critical drinking water source for many Texans and Americans. Notably, even when regulated, many wetland areas are still developable. In most instances, federal permits authorising impacts to regulated wetlands and other waters of the US are and have been available, often with mitigation requirements (creating wetlands elsewhere or contributing to a wetlands mitigation bank for restoration).
The US Supreme Court’s decision in Sackett v United States Environmental Protection Agency, 598 US 651 (2023), marked a recent turning point in wetlands regulation. The Court ruled that wetlands lacking a “continuous surface connection” to another body of water in the US are no longer protected under the CWA. The EPA is now poised to propose a new rule that goes even further and is expected to eliminate federal protections for even more wetlands. Under the soon-to-be proposed rule, which is expected to be final by year-end 2025, the federal government will only regulate wetlands if the wetlands meet a two-part test: first, they must contain surface water throughout the wet season, and second, they must abut and touch a river, stream, or other waterbody that also flows through the wet season.
The upshot? We expect that far fewer wetlands will require permitting in advance of impacts. When wetlands permits are not required, no review under the Endangered Species Act takes place, eliminating another potential barrier for business or private property interests. (Section 7 of the Endangered Species Act requires interagency cooperation to ensure that other agencies’ authorisations are “not likely to jeopardise the continued existence of any endangered or threatened species or result in the destruction or adverse modification of habitat of such species…”).
Is it wrong for a nation to prioritise business and private property interests over the environment? Not necessarily. The US is not alone in making such choices. Still, wherever and whenever possible, we should strive to be responsible stewards of our land, waters, and native species – not just for ourselves, but for generations of Americans to come.
The Changing Landscape for PFAS
Over the last several years, EPA has been at the centre of a whirlwind of regulatory activity for the emerging contaminants per- and polyfluoroalkyl substances (PFAS). The current administration is holding the line on some rules, while tweaking or possibly abandoning others, and the landscape is changing rapidly.
In a major milestone in April 2024, the EPA set drinking water standards for six PFAS compounds under the Safe Drinking Water Act. Although the Trump administration emphasised deregulation, the EPA announced in May 2025 that it would keep the drinking water standards for perfluorooctanoic acid (PFOA) and perfluorooctanesulfonic acid (PFOS). The EPA plans to give public water systems a break and extend the regulatory deadlines for meeting these standards. EPA anticipates issuing a proposed rule for this extension in late 2025. As a bigger change, EPA announced that it plans to rescind and reconsider the determinations for the remaining four PFAS compounds and mixtures regulated under the April 2024 rule (PFHxS, PFNA, HFPO-DA (GenX), and the Hazard Index mixture of these three PFAS plus PFBS). In ongoing litigation, the EPA argues that the prior administration should have allowed two separate comment periods regarding these four mixtures, to allow the public to comment first on whether the substances should be regulated, and then on the standards. As a result, EPA asks that the rule be vacated for these four PFAS mixtures. This may be a tactic to eliminate the standards for these PFAS, as the EPA has placed rescinding the rule for these mixtures on its planned agenda for upcoming regulatory proposals.
Another 2024 Biden administration headline was the EPA finalising its designation of PFOA and PFOS as hazardous substances under the Comprehensive Environmental Response, Compensation, and Liability Act (CERCLA). During the current administration, the Department of Justice (DOJ) has claimed EPA might walk back this rule. In early September 2025, the DOJ even asked for a pause in a CERCLA cost recovery case, citing the potential that the EPA would rescind the hazardous substance designation. However, by 17 September 2025, in its filings in litigation directly challenging the hazardous substance determination, the EPA stated that it planned to retain these as hazardous substances and defend the rule.
The CERCLA PFAS story doesn’t end there. Along with its 17 September announcement, EPA said it would create a “framework rule” to govern how additional chemicals may be designated as hazardous substances. Administrator Zeldin has also spotlighted the plight of “passive receivers” – entities such as municipal wastewater treatment facilities and landfills that handle PFAS-impacted materials but didn’t create or use PFAS themselves. Zeldin has called for federal legislation to address their unique challenges and pledged EPA’s support for such efforts.
Meanwhile, the EPA is gearing up for a review of regulations under the Toxic Substances Control Act (TSCA), which was passed to implement statutory requirements to collect information on the use of PFAS in US commerce from 2011 to 2022. This reporting requirement, applicable to manufacturers and importers of PFAS compounds, originally required reporting in 2024, but the EPA delayed it due to concerns about how to receive the data. EPA has now pushed the reporting period to 2026. The EPA will use the delay as an opportunity to review the information it seeks to collect, including whether certain PFAS compounds can be excluded from reporting entirely.
Despite an overall deregulatory tone, the EPA seems determined to press ahead with regulations for PFOS and PFOA – the two PFAS compounds most commonly found in the environment. For other PFAS, however, the regulatory future remains uncertain, with some measures likely to be postponed or dropped altogether.
Usage Bans: Postponing Deadlines and Reconsidering Rules Affecting TCE
Trichloroethylene (“TCE”) is a chlorinated solvent widely used in the manufacture or processing of numerous industrial, commercial and consumer products, including within the oilfield service and energy industry. It is primarily used in the manufacture of refrigerants and as a degreasing agent. TCE has been tied, however, to increased risks of adverse cancer and non-cancer health effects. Consequently, on 17 December 2024, the Environmental Protection Agency (EPA) issued a final rule under the Toxic Substances Control Act that prohibits almost all uses of TCE, with most uses prohibited within one year. The rule was to become effective on 16 January 2025.
Under the published rule, several industries and applications using TCE were granted multi-year exemptions from the TCE usage ban. The exemptions applied to TCE usage within the aerospace industry, the armed forces, the lead acid battery separator manufacturing industry, certain polymer sheet manufacturing, laboratory activities, and in the disposal of TCE-contaminated waters. Qualification for most of the exempted uses, however, hinged on a regulated party’s compliance with a Workplace Chemical Protection Program (WCPP). That program, in turn, is tied to a TCE chemical exposure limit of 0.2 parts per million (“ppm”), which, if exceeded, would trigger the need for stringent personal protective equipment (PPE) for exposed individuals.
Litigation followed – and the EPA received petitions for an administrative stay of the effective date of the rules on behalf of industry participants under the former and current administrations. EPA, under the previous administration, denied the requests. Industry representatives submitted renewed petitions to the EPA under the new administration on the 20th and 21st of January, 2025, to stay the effective date of the rule or, in the alternative, for an administrative stay of the final rule’s WCPP. EPA also received thirteen petitions for review of the final rule in various circuits of the US Courts of Appeals, seeking emergency stays of the rule’s effective date and WCPP requirements. Before the rules became effective, the Fifth Circuit granted a motion for a temporary administrative stay of the final rule’s effective date while the court considered an emergency stay. The petitions for review were consolidated in the US Court of Appeals for the Third Circuit as USW v US EPA, Case No 25-1055.
According to industry representatives, the prescribed 0.2 ppm exposure limit under the WCPP was set at a level more than 20 times below what is achievable using state-of-the-art engineering and administrative controls, and orders of magnitude below equivalent standards in Europe and the United Kingdom, thus making the use of PPE a foregone conclusion. Industry representatives also contend that the high level of prescribed PPE would itself carry health and safety concerns for manufacturing employees, and was not sustainable on an all-day, every-day basis.
EPA, under the new administration, took industry’s input seriously, acknowledging that industry representatives have “raised serious questions regarding the WCPP.” See 90 Fed. Reg. 40,534 (20 August 2025). EPA has, on four occasions, delayed the effective date of the WCPP requirements – currently until 17 November 2025. Id. EPA has also advised the Third Circuit Court of Appeals that EPA plans to reconsider the rules at issue through formal notice and comment rule-making, and thus does not oppose a judicial stay of the subject WCPP rules. While the results of the new rule-making are currently unknown, the new administration’s stay of the WCPP requirements and its decision to reconsider them are another example of pursuing less regulation when faced with the choice. Reconsideration of the WCPP rules and the related TCE exposure limits could provide more operational flexibility for heavy industry uses that are not immediately subject to the TCE ban.
Conclusion
EPA’s review of existing regulations is ongoing. The EPA’s approach aims to align regulatory efficiency with heightened energy production and project development. In some areas, the EPA has declined to repeal regulations, but rather sought to afford deadline extensions. Many of these actions will be judicially challenged. Absent a top-flight crystal ball, it is challenging to predict just how this litigation will be resolved. The regulated community should follow these matters with heightened attention.
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