Tag: EPA

EPA’s Contaminant List Includes All PFAS

We previously reported on the EPA’s announcement for its Draft Fifth Contaminant Candidate List (CCL 5), which contemplated listing all PFAS as an entire class on the Contaminant List. On October 28, 2022, the EPA issued its prepublication version of the final CCL 5 rule. The EPA’s contaminant list final version is the first step in the Safe Drinking Water Act regulatory process, which will allow the EPA to begin its assessment into any of the over 12,000 PFAS as to whether they should be included in a drinking water enforceable limit. Such a move would build upon the EPA’s current progress towards regulating PFOA and PFOS with an enforceable drinking water limit, and open the door to significant future enforcement action and litigation.

EPA’s Contaminant List and PFAS

On October 28, 2022, the EPA announced its Final Fifth Contaminant Candidate List (CCL 5). The CCL is a list of contaminants that are currently not subject to any proposed or promulgated national primary drinking water regulations, but are known or anticipated to occur in public water systems. Contaminants listed on the CCL may require future regulation under the Safe Drinking Water Act (SDWA). On the CCL 5 are 66 individual chemicals, but notably PFAS as an entire class are also listed on the CCL 5. Simply because PFAS are listed on the CCL 5 does not guarantee that regulation will occur; however, it does open doors to research that are not otherwise available without the listing on the CCL.

The EPA’s contaminant list rule is not the only step the agency has taken with respect to PFAS and drinking water, but developing the CCL is the first step under the Safe Drinking Water Act (SDWA) in potentially regulating drinking water contaminants. SDWA requires EPA to publish a list of currently unregulated contaminants that are known or anticipated to occur in public water systems and that may require regulation. EPA must publish a CCL every five years. The CCL does not create or impose regulatory burden on public water systems or state, local, or Tribal governments. EPA has completed four rounds of CCLs since 1996. The last cycle of CCL, CCL 4, was published in November 2016. EPA began the development of the CCL 5 in 2018 by asking the public to nominate chemicals, microbes, or other materials for consideration for the CCL 5.

Impact On Businesses and Litigation

Many companies assume that any regulation under the Safe Drinking Water Act will not impact them, as virtually no industries, aside from water utilities, have any direct impact on drinking water. However, this belief provides a false sense of security that must immediately be dispelled. There are three specific ways that drinking water limits for PFAS will trigger scrutiny on environmental practices of businesses: (1) elffluent discharges into water sources; (2) waste sent to landfills that may leach into drinking water sources; and (3) properties abutting or in the vicinity of water sources.

Direct industry effluent discharges into water sources (which may not be drinking water sources, but may feed into drinking water sources) will be the low-hanging fruit target for local environmental agencies at the state level. Companies must ensure that they have all permitting in order, and it is advisable that the permitting specifically encompasses PFAS. Failing to do so will cause issues down the line when local environmental regulatory bodies look to determine, even retroactively, who PFAS water polluters are or were, as those agencies seek to hold businesses responsible for the costs associated with cleaning up PFAS in drinking water.

Companies that send their industrial waste to landfills are also well advised to do a full compliance check. While many companies do not use PFAS directly in their own manufacturing processes, do the parts or other raw materials used in the manufacturing process have PFAS contamination issues? If so, a company could unknowingly send PFAS-laden industrial waste products to landfills, and so these are questions that companies must get answers to. Over time, it is possible that the PFAS may leach out of the landfill and find their way into local water sources. Environmental regulatory agencies will look to these sites, the owners of the sites, and potentially companies sending waste to the sites as responsible parties for PFAS contamination in waterways.

Finally, even businesses having nothing to do with PFAS or manufacturing from which PFAS could be a contaminant need to follow news regarding PFAS regulations. For example, has the property on which your business sits ever had fires that have required a local fire department to extinguish flames using foam (historically, a PFAS containing product)? What did the owner of the site prior to you use the site for? Were there possible PFAS contamination issues stemming from that prior business? Did your due diligence reports and tests when purchasing the property take PFAS into consideration? If PFAS were a contaminant on the land on which your business now operates, local environmental agencies will pursue cleanup costs from any such business regardless of knowledge or intent, and regardless of whether the PFAS issues were the result of a prior company on the site. These investigations and remediations can be extremely expensive and disruptive to businesses.

Should the EPA broaden its regulations for PFAS in drinking water to include more than PFOA and PFOS, this will trigger considerable enforcement action at the state level to identify responsible parties and ensure that the parties pay for remediation costs. Historically, this has also led to civil litigation, as companies identified as responsible parties litigate the percent allocation that they are responsible for the alleged pollution, and look to bring in additional companies to reduce allocation shares for remediation costs.

Conclusion

Future regulatory steps for certain PFAS under the Safe Drinking Water Act will require states to act (and some states may still enact stronger regulations than the EPA). Both the federal and the state level regulations will impact businesses and industries of many kinds, even if their contribution to drinking water contamination issues may seem on the surface to be de minimus. In states that already have PFAS drinking water standards enacted, businesses and property owners have already seen local environmental agencies scrutinize possible sources of PFAS pollution much more closely than ever before, which has resulted in unexpected costs. Companies absolutely must begin preparing now for regulatory actions that will have significant financial impacts down the road.

Article By John Gardella of CMBG3 Law

For more environmental legal news, click here to visit the National Law Review.

©2022 CMBG3 Law, LLC. All rights reserved.

CERCLA PFAS Designation Major Step Forward

On January 10, 2022, the EPA submitted a plan for a PFAS Superfund designation to the White House Office of Management and Budget (OMB) when it indicated an intent to designate two legacy PFAS – PFOA and PFOS – as “hazardous substances” under the Comprehensive Environmental Response, Compensation & Liability Act (CERCLA, also known as the Superfund law). The EPA previously stated its intent to make the proposed designation by March 2022 when it introduced its PFAS Roadmap in October 2021. Under the Roadmap, the EPA planned to issue its proposed CERCLA designation in the spring of 2022. On Friday, a CERCLA PFAS designation took a significant step forward when the OMB approved the EPA’s plan for PFOA and PFOS designation. This step opens the door for the EPA to put forth its proposed designation of PFOA and PFOS under CERCLA and engage in the required public comment period.

Any PFAS designation will have enormous financial impacts on companies with any sort of legacy or current PFOA and PFOS pollution concerns. Corporations, insurers, investment firms, and private equity alike must pay attention to this change in law when considering risk issues.

Opposition to CERCLA Designation

Since the EPA’s submission of its intent to designate PFOA and PFOS as hazardous substance to the OMB, the EPA has been met with industry pushback on the proposal. Three industries met with the OMB earlier in 2022 to explain the enormity of regulatory and cleanup costs that the industries would face with a CERCLA designation of PFOA and PFOS – water utilities, waste management companies, and the International Liquid Terminals Association. These industries in particular are concerned about bearing the burden of enormous cleanup costs for pollution that third parties are responsible for. Industries are urging the OMB and EPA to consider other ways to achieve regulatory and remediation goals aside from a CERCLA designation.

During an April 5, 2022 meeting of the Environmental Council of the States (ECOS), several states also expressed concerns regarding the impact that a CERCLA designation for PFAS types would have in their states and on their constituent companies. The state environmental leaders discussed with EPA representatives how the EPA would view companies in their states that fall into categories such as waste management and water utilities, who are already facing uphill battles in disposing of waste or sludge that contains PFAS.

Realizing that the EPA is likely set on its path to designate at least two PFAS as “hazardous substances”, though, industries are asking the EPA to consider PFAS CERCLA exemptions for certain industries, which would exempt certain industry types from liability under CERCLA. Industries are also pushing the EPA, OMB and the U.S. Chamber of Commerce to conduct a robust risk analysis to fully vet the impact that the designation will have on companies financially. The EPA is statutorily required to conduct a risk analysis as part of its CERCLA designation process, so it is likely that the EPA’s delay in issuing a proposed hazardous substance designation until it feels that adequate time has passed for its designation to survive the likely legal challenges that will likely follow the designation.

CERCLA PFAS Designation: Impact On Businesses

Once a substance is classified as a “hazardous substance” under CERCLA, the EPA can force parties that it deems to be polluters to either cleanup the polluted site or reimburse the EPA for the full remediation of the contaminated site. Without a PFAS Superfund designation, the EPA can merely attribute blame to parties that it feels contributed to the pollution, but it has no authority to force the parties to remediate or pay costs. The designation also triggers considerable reporting requirements for companies. Currently, those reporting requirements with respect to PFAS do not exist, but they would apply to industries well beyond just PFAS manufacturers.

The downstream effects of a PFOA and PFOS designation would be massive. Companies that utilized PFOA and PFOS in their industrial or manufacturing processes and sent the PFOA/PFOS waste to landfills or otherwise discharged the chemicals into the environment will be at immediate risk for enforcement action by the EPA given the EPA’s stated intent to hold all PFAS polluters of any kind accountable. Waste management companies should be especially concerned given the large swaths of land that are utilized for landfills and the likely PFAS pollution that can be found in most landfills due to the chemicals’ prevalence in consumer goods. These site owners may be the first targeted when the PFOA/PFOS designation is made, which will lead to lawsuits filed against any company that sent waste to the landfills for contribution to the cost of cleanup that the waste management company or its insured will bear.

Also of concern to companies are the re-opener possibilities that a CERCLA designation would result in. Sites that are or were previously designated as Superfund sites will be subject to additional review for PFOA/PFOS concerns. Sites found to have PFOA/PFOS pollution can be re-opened by the EPA for investigation and remediation cost attribution to parties that the EPA finds to be responsible parties for the pollution. Whether through direct enforcement action, re-opener remediation actions, or lawsuits for contribution, the costs for site cleanup could amount to tens of millions of dollars, of course depending on the scope of pollution.

Conclusion

Now more than ever, the EPA is clearly on a path to regulate PFAS contamination in the country’s water, land and air. The EPA has also for the first time publicly stated when they expect such regulations to be enacted. These regulations will require states to act, as well (and some states may still enact stronger regulations than the EPA). Both the federal and the state level regulations will impact businesses and industries of many kinds, even if their contribution to drinking water contamination issues may seem on the surface to be de minimus. In states that already have PFAS drinking water standards enacted, businesses and property owners have already seen local environmental agencies scrutinize possible sources of PFAS pollution much more closely than ever before, which has resulted in unexpected costs. Beyond drinking water, though, the EPA PFAS plan shows the EPA’s desire to take regulatory action well beyond just drinking water, and companies absolutely must begin preparing now for regulatory actions that will have significant financial impacts down the road.

Article By John Gardella of CMBG3 Law

For more energy and environmental legal news, click here to visit the National Law Review.

©2022 CMBG3 Law, LLC. All rights reserved.

EPA Updates Safer Chemical Ingredients List, Adding 22 Chemicals and Changing the Status of One Chemical

The U.S. Environmental Protection Agency (EPA) announced on August 11, 2022, that it updated the Safer Chemical Ingredients List (SCIL), “a living list of chemicals by functional-use class that EPA’s Safer Choice program has evaluated and determined meet the Safer Choice Standard.” EPA added 22 chemicals to the SCIL. EPA states that to expand the number of chemicals and functional-use categories on the SCIL, it encourages manufacturers to submit their safer chemicals for review and listing on the SCIL. In support of the Biden Administration’s goals, the addition of chemicals to the SCIL “incentivizes further innovation in safer chemistry, which can promote environmental justice, bolster resilience to the impacts of climate change, and improve water quality.” According to EPA, chemicals on the SCIL “are among the safest for their functional use.”

EPA also changed the status for one chemical on the SCIL and will remove the chemical from the list in one year “because of a growing understanding of the potential health and environmental effects.” According to EPA, the chemical was originally listed on the SCIL based on data from a closely related substance that EPA marked with a grey square earlier this year. EPA’s process for removing a chemical from the SCIL is first to mark the chemical with a grey square on the SCIL web page to provide notice to chemical and product manufacturers that the chemical may no longer be acceptable for use in Safer Choice-certified products. A grey square notation on the SCIL means that the chemical may not be allowed for use in products that are candidates for the Safer Choice label, and any current Safer Choice-certified products that contain this chemical must be reformulated unless relevant health and safety data are provided to justify continuing to list the chemical on the SCIL. EPA states that the data required are determined on a case-by-case basis. In general, data useful for making such a determination provide evidence of low concern for human health and environmental impacts. Unless information provided to EPA adequately justifies continued listing, EPA then removes the chemical from the SCIL 12 months after the grey square designation.

According to EPA, after this update is made, there will be 1,055 chemicals listed on the SCIL. EPA is committed to updating the SCIL with safer chemicals on a regular basis. EPA states that the SCIL is a resource that can help many different stakeholders:

  • Product manufacturers use the SCIL to help make high-functioning products that contain safer ingredients;
  • Chemical manufacturers use the SCIL to promote the safer chemicals they manufacture;
  • Retailers use the SCIL to help shape their sustainability programs; and
  • Environmental and health advocates use the SCIL to support their work with industry to encourage the use of the safest possible chemistry.

EPA’s Safer Choice program certifies products containing ingredients that have met the program’s rigorous human health and environmental safety criteria. The Safer Choice program allows companies to use its label on products that meet the Safer Choice Standard. The EPA website contains a complete list of Safer Choice-certified products.

Article By Lynn L. Bergeson and Carla N. Hutton of Bergeson & Campbell, P.C.

For more environmental legal news, click here to visit the National Law Review.

©2022 Bergeson & Campbell, P.C.

PFAS Health Advisories Under Legal Attack…Again

On June 15, 2022, the EPA issued Health Advisories (HAs) for five specific PFAS, including PFOA and PFOS. On July 29, 2022, the American Chemistry Council filed a petition in the Court of Appeals for the District of Columbia challenging the validity of the EPA’s PFOA and PFOS HAs. The group alleges that the EPA did not follow proper procedure in setting the HAs and that the EPA’s determinations were scientifically flawed. The petition follows closely on the heels of a similar challenge to the EPA’s HA for GenX PFAS. Industries that will be impacted by upcoming EPA PFAS regulations will closely follow the petition as it makes its way through court, as it may provide predictive indicators of arguments that will unfold as the EPA’s PFAS regulations increase.

PFAS Health Advisories

In October 2021, the EPA released its PFAS Roadmap, which stated explicit goals and deadlines for over twenty action items specific to PFAS. As part of the Roadmap, the EPA pledged to re-assess the existing Health Advisories (HAs) for PFOA and PFOS, as well as establish HAs for PFBS and GenX chemicals. In June 2022, the EPA fulfilled its promise on all fronts when it set HAs for PFOA (interim), PFOS (interim), PFBS (final) and GenX (final). While not enforceable levels for PFAS in drinking water, the EPA’s PFAS Health Advisories are nevertheless incredibly significant for a variety of reasons, including influence on future federal and state drinking water limits, as well as potential impacts on future PFAS litigation.

The levels set by the EPA’s PFAS Health Advisories were as follows:

PFOA

.004 ppt

PFOS

.02 ppt

GenX

10 ppt

PFBS

2,000 ppt

Legal Challenge To PFAS Health Advisories

On July 13, 2022, The Chemours Company filed a petition challenging the validity of the EPA’s GenX HA. On July 29, 2022, the American Chemistry Council (ACC) followed suit and petitioned to have the EPA’s HAs for PFOA and PFOS vacated. In the petition, the ACC argues that the EPA circumvented procedural requirements in the Safe Drinking Water Act by setting interim HAs for PFOA and PFOS and that the EPA is improperly attempting to create enforcement standards for drinking water that are unattainable. While the HAs themselves are not enforceable, the ACC argues that the HAs are relied upon by states when they set their own drinking water standards and signal an EPA intent to set unachievably low levels of enforceable PFAS standards at the federal level. The ACC points to recent findings by the Science Advisory Board (SAB) that criticized the EPA’s reliance on the same studies and scientific articles upon which the HAs were based.

Conclusion

Now more than ever, the EPA is clearly on a path to regulate PFAS contamination in the country’s water, land and air. The EPA has also for the first time publicly stated when they expect such regulations to be enacted. These regulations will require states to act, as well (and some states may still enact stronger regulations than the EPA). Both the federal and the state level regulations will impact businesses and industries of many kinds, even if their contribution to drinking water contamination issues may seem on the surface to be de minimus. In states that already have PFAS drinking water standards enacted, businesses and property owners have already seen local environmental agencies scrutinize possible sources of PFAS pollution much more closely than ever before, which has resulted in unexpected costs. Beyond drinking water, though, the EPA PFAS Roadmap shows the EPA’s desire to take regulatory action well beyond just drinking water, and companies absolutely must begin preparing now for regulatory actions that will have significant financial impacts down the road.

Article By John Gardella of CMBG3 Law

For more environmental legal news, click here to visit the National Law Review.

©2022 CMBG3 Law, LLC. All rights reserved.

After EPA Rule Changes, Which ASTM Phase I ESA Standard Should You Use?

On November 1, 2021, ASTM International released its revised standard for Phase I Environmental Site Assessments. On March 14, 2022, the U.S. Environmental Protection Agency (the “EPA”) published a Direct Final Rule that confirmed the new ASTM standard, ASTM E1527-21, could be used to satisfy the EPA’s All Appropriate Inquiry (“AAI”) regulations. That, in turn, would mean that satisfying the ASTM E1527-21 standard could help a potential buyer of contaminated property satisfy some of the EPA’s requirements to qualify as a Bona Fide Prospective Purchaser, which may lead to being protected from liability under the federal Superfund statute.

However, on May 2, 2022, EPA withdrew the Final Rule it had published on March 14, 2022, and indicated it would address the comments it received concerning the previously Final Rule in a subsequent final action.

Why the change and, more importantly, which ASTM standard should a potential purchaser of contaminated property use when having a Phase I Site Assessment prepared?

EPA withdrew its Direct Final Rule in response to the negative comments it received concerning that rule. EPA had planned to allow both the November 2021 ASTM standard and its predecessor from 2013 (the ASTM E1527-13 standard) to be used to satisfy certain AAI requirements. Those commenting said that approach would lead to confusion in the marketplace, and would allow reports that did not meet the ASTM E1527-21 standard to be considered adequate, even though the 2021 ASTM standard represented what the real estate and environmental community had determined to be good commercial and customary practice. In other words, because the 2021 standard required a more rigorous approach to the relevant environmental due diligence work needed to prepare a Phase I Environmental Site Assessment, EPA’s approach would have meant that less thorough reports could have been deemed sufficient.  As noted in the comment letter submitted to the EPA by the Environmental Bankers Association, “ASTM E1527-21 includes important updates that will reduce the risk of Users [of the ESA report] failing to identify conditions indicative of hazardous substance releases, potentially jeopardizing landowner [and prospective purchaser] liability protections to [potential] CERCLA [liability].” All of that makes sense: the better the environmental due diligence, the less risk of unpleasant surprises later.

But, where does that leave potential purchasers of contaminated real estate? Should they have their consultants prepare their Phase I Site Assessment reports based on the 2021 ASTM standard, or its 2013 predecessor, or both?

Contaminated real estate buyers, and any other parties involved in the transaction, such as lenders and equity investors, should require their environmental consultants to prepare their Phase I Environmental Site Assessment in conformance with the ASTM E1527-13 standard, because that is the ASTM standard that is currently referenced in EPA’s AAI regulations. It is necessary to do so, at least for now, in order to be able to qualify for Bona Fide Prospective Purchaser protection from CERCLA liability.

Those parties should also consider having their environmental consultants prepare the same Phase I Environmental Site Assessment in conformance with the updated ATSM E1527-21 standard. While some additional cost may be involved, nonetheless it may be worthwhile in order to meet what ASTM sees as the current standard of practice regarding these reports.

Another important consideration in the preparation of these reports is whether additional issues that are not formally included in the scope of either the ASTM E1527-13 or the ASTM E1527-21 standard should be addressed. For example, as noted in an appendix to the E1527-21 standard, petroleum products are within the scope of the practice “because they are of concern with respect to commercial real estate, and current custom and usage is to include an inquiry into the [past or present] presence of petroleum products when doing an environmental site assessment of commercial real estate.” That is so even though petroleum products generally do not lead to liability under CERCLA.

The non-scope issues appendix to the ASTM E1527-21 standard also addresses “substances not defined as hazardous substances” and does a good job addressing why a user of an ASTM-compliant report should at least consider whether to include certain emerging contaminants such as per- and polyfluoroalkyl substances, also known as PFAS, within its scope. The point is to think about whether to evaluate potential environmental liability for PFAS on a case-by-case basis in light of state law considerations, even though PFAS compounds have not yet been designated “hazardous substances” under CERCLA.

EPA’s recent rule-making activities have not provided clear guidance for potential purchasers of contaminated property regarding which ASTM standard should be used in preparing environmental site assessment reports that comply with EPA’s AAI regulations. At the moment, what seems to make the most sense is to have these reports prepared so that they comply with the ASTM E1527-13 standard and to consider whether to comply with the E1527-21 standard in addition. The user should also carefully evaluate whether certain considerations, such as potential PFAS contamination, should be included within the scope of the report.

Article By Ned Abelson and Justin Rheingold of Goulston & Storrs

For more environmental legal news, click here to visit the National Law Review.

2022 Goulston & Storrs PC.

PFAS GenX Health Advisories Challenged In Court

On June 15, 2022, the EPA issued Health Advisories (HAs) for five specific PFAS, including GenX PFAS chemicals. The PFAS GenX health advisories set levels at 10ppt for this chemical group. On July 13, 2022, The Chemours Co. filed a petition in the Third Circuit challenging the validity of the EPA’s GenX HA. The company alleges that the EPA acted outside of its bounds of authority, as well as arbitrarily and capriciously, among other arguments. Other industries that will be impacted by upcoming EPA PFAS regulations will closely follow the lawsuit as it makes its way through court, as it may provide predictive indicators of arguments that will unfold as the EPA’s PFAS regulations increase.

PFAS GenX Health Advisories

In October 2021, the EPA released its PFAS Roadmap, which stated explicit goals and deadlines for over twenty action items specific to PFAS. As part of the Roadmap, the EPA pledged to re-assess the existing Health Advisories (HAs) for PFOA and PFOS, as well as establish HAs for PFBS and GenX chemicals. In June 2022, the EPA fulfilled its promise on all fronts when it set HAs for PFOA (interim), PFOS (interim), PFBS (final) and GenX (final). While not enforceable levels for PFAS in drinking water, the EPA’s PFAS Health Advisories are nevertheless incredibly significant for a variety of reasons, including influence on future federal and state drinking water limits, as well as potential impacts on future PFAS litigation.

The levels set by the EPA’s PFAS Health Advisories were as follows:

PFOA .004 ppt
PFOS .02 ppt
GenX 10 ppt
PFBS 2,000 ppt

Chemours Challenge To GenX Health Advisories

Chemours is challenging the EPA’s PFAS GenX Health Advisories primarily on the grounds that the HAs are “arbitrary and capricious.” The company alleges that the HAs are arbitrary and capricious because (1) they incorporated toxicity assumptions that deviate from the EPA’s own standard methods; and (2) “EPA incorporated grossly incorrect and overstated exposure assumptions―in essence, EPA used the wrong chemical when making its exposure assumptions, thereby resulting in a significantly less tolerant health advisory for [GenX] than is warranted by the data. In addition, Chemours argues that the EPA failed to go through the necessary public comment period before issuing its final GenX HA, and that in creating the GenX HA, the EPA exceeded its authority under the Safe Drinking Water Act.

Conclusion

Now more than ever, the EPA is clearly on a path to regulate PFAS contamination in the country’s water, land and air. The EPA has also for the first time publicly stated when they expect such regulations to be enacted. These regulations will require states to act, as well (and some states may still enact stronger regulations than the EPA). Both the federal and the state level regulations will impact businesses and industries of many kinds, even if their contribution to drinking water contamination issues may seem on the surface to be de minimus. In states that already have PFAS drinking water standards enacted, businesses and property owners have already seen local environmental agencies scrutinize possible sources of PFAS pollution much more closely than ever before, which has resulted in unexpected costs. Beyond drinking water, though, the EPA PFAS Roadmap shows the EPA’s desire to take regulatory action well beyond just drinking water, and companies absolutely must begin preparing now for regulatory actions that will have significant financial impacts down the road.

Article By John Gardella of CMBG3 Law

For more environmental legal news, click here to visit the National Law Review.

©2022 CMBG3 Law, LLC. All rights reserved.

EPA’s Spring 2022 Unified Agenda Includes Proposed and Final TSCA and TRI Rules

The U.S. Environmental Protection Agency’s (EPA) spring 2022 Unified Agenda, published on June 21, 2022, includes the following rulemakings under the Toxic Substances Control Act (TSCA) or the Toxics Release Inventory (TRI).

Proposed Rule Stage

  • Tiered Data Reporting to Inform Prioritization, Risk Evaluation, and Risk Management under TSCA (2070-AK62): EPA is developing a rulemaking under TSCA Sections 8(a) and (d) to establish reporting requirements based upon a chemical’s status in the Risk Evaluation/Risk Management (RE/RM) Lifecycle and update the reporting requirements under the 40 C.F.R. Part 711 Chemical Data Reporting (CDR) regulation. Specifically, EPA is seeking occupational, environmental, and consumer exposure information. EPA is developing this rule to obtain information about potential hazards and exposure pathways related to certain chemicals, particularly occupational, environmental, and consumer exposure information. According to the Unified Agenda item, EPA needs this information to inform prioritization, risk evaluation, and risk management of chemical substances under TSCA Section 6. EPA intends to issue a notice of proposed rulemaking (NPRM) in May 2023 and a final rule in September 2024. More information on EPA’s July 27, 2021, webinar on development of the proposed rule is available in our July 29, 2021, memorandum.
  • Revisions to the TSCA Fees Rule (2070-AK64): In January 2021, EPA proposed updates and adjustments to the 2018 TSCA fees rule. EPA proposed modifications to the TSCA fees and fee categories for fiscal years (FY) 2022, 2023, and 2024 and explained the methodology by which the proposed TSCA fees were determined. EPA proposed to add three new fee categories: A Bona Fide Intent to Manufacture or Import Notice, a Notice of Commencement of Manufacture or Import, and an additional fee associated with test orders. In addition, EPA proposed exemptions for entities subject to certain fee-triggering activities, including an exemption for research and development (R&D) activities; an exemption for entities manufacturing less than 2,500 pounds of a chemical subject to an EPA-initiated risk evaluation fee; an exemption for manufacturers of chemical substances produced as a non-isolated intermediate; and exemptions for manufacturers of a chemical substance subject to an EPA-initiated risk evaluation if the chemical substance is imported in an article, produced as a byproduct, or produced or imported as an impurity. EPA updated its cost estimates for administering TSCA, relevant information management activities, and individual fee calculation methodologies. EPA proposed a volume-based fee allocation for EPA-initiated risk evaluation fees in any scenario where a consortium is not formed and is proposing to require export-only manufacturers to pay fees for EPA-initiated risk evaluations. EPA also proposed various changes to the timing of certain activities required throughout the fee payment process. In light of public comments, EPA states that it has decided to issue a supplemental NPRM in October 2022 and seek additional public comment on changes to the January 2021 proposal. More information on the proposed rule is available in our December 30, 2020, memorandum.
  • New Chemicals Procedural Regulations to Reflect the 2016 Amendments to TSCA (2070-AK65): On June 22, 2016, the Frank R. Lautenberg Chemical Safety for the 21st Century Act (Lautenberg Act) was signed into law, amending TSCA and impacting how EPA reviews and makes determinations on new chemical notices under TSCA Section 5. EPA states that as a result of these increased responsibilities, it has become more challenging to complete reviews within 90 days. This rulemaking seeks to revise the new chemicals procedural regulations in 40 C.F.R. Part 720 to improve the efficiency of EPA’s review process and to align its processes and procedures with the new statutory requirements. This rulemaking seeks to increase the quality of information initially submitted in new chemicals notices and improve EPA’s processes to reduce unnecessary rework in the risk assessment and, ultimately, the length of time that new chemicals are under review. EPA intends to publish an NPRM in February 2023.
  • Confidential Business Information (CBI) Claims under TSCA (2070-AK68): EPA is considering proposing new and amended rules concerning the assertion and maintenance of claims of CBI under TSCA. Amendments to TSCA in 2016 included several new provisions concerning the assertion and EPA review and treatment of confidentiality claims. EPA states that it is considering procedures for submitting and supporting such claims in TSCA submissions, including substantiation requirements, exemptions, electronic reporting enhancements, and maintenance or withdrawal of confidentiality claims. EPA is also considering whether the proposed rule should also elaborate on EPA’s procedures for reviewing and communicating with TSCA submitters about confidentiality claims. EPA expects the proposed rule to include new provisions, as well as revisions to existing rules on asserting confidentiality claims to conform to the 2016 amendments to TSCA. As reported in our May 17 and May 18, 2022, memoranda, EPA issued a proposed rule on May 12, 2022. EPA intends to issue a final rule in May 2023.
  • Chemical-Specific Rulemakings under TSCA Section 6(a): TSCA Section 6 requires EPA to address unreasonable risks of injury to health or the environment that the Administrator has determined are presented by a chemical substance under the conditions of use. Following risk evaluations for the following chemicals carried out under the authority of TSCA Section 6, EPA initiated rulemakings to address unreasonable risks of injury to health identified in the final risk evaluations:
    • Methylene Chloride (2070-AK70): EPA’s risk evaluation for methylene chloride, describing the conditions of use and presenting EPA’s determinations of unreasonable risk, is in docket EPA-HQ-OPPT-2019-0437, with additional information in docket EPA-HQ-OPPT-2016-0742. EPA intends to issue an NPRM in February 2023 and a final rule in August 2024. More information on EPA’s draft revision to its risk determination for methylene chloride will be available in a forthcoming memorandum;
    • 1-Bromopropane (2070-AK73): EPA’s risk evaluation for 1-bromopropane, describing the conditions of use and presenting EPA’s determinations of unreasonable risk, is in docket EPA-HQ-OPPT-2019-0235, with additional information in docket EPA-HQ-OPPT-2016-0741. EPA intends to publish an NPRM in May 2023 and a final rule in August 2024;
    • Carbon Tetrachloride (2070-AK82): EPA’s risk evaluation, describing the conditions of use and presenting EPA’s determinations of unreasonable risk, is in docket EPA-HQ-OPPT-2019-0499, with additional information in docket EPA-HQ-OPPT-2016-0733. EPA intends to publish an NPRM in April 2023 and a final rule in August 2024;
    • Trichloroethylene (TCE) (2070-AK83): EPA’s risk evaluation for TCE, describing the conditions of use and presenting EPA’s determinations of unreasonable risk, is in docket EPA-HQ-OPPT-2019-0500, with additional information in docket EPA-HQ-OPPT-2016-0737. EPA intends to publish an NPRM in March 2023 and a final rule in August 2024. More information on EPA’s draft revision to its risk determination for TCE will be available in a forthcoming memorandum;
    • Perchloroethylene (PCE) (2070-AK84): EPA’s risk evaluation for PCE, describing the conditions of use and presenting EPA’s determinations of unreasonable risk, is in docket EPA-HQ-OPPT-2019-0502, with additional information in docket EPA-HQ-OPPT-2016-0732. EPA intends to publish an NPRM in February 2023 and a final rule in August 2024. More information on EPA’s draft revision to its risk determination for PCE will be available in a forthcoming memorandum;
    • N-Methylpyrrolidone (NMP) (2070-AK85): EPA’s risk evaluation for NMP, describing the conditions of use and presenting EPA’s determinations of unreasonable risk, is in docket EPA-HQ-OPPT-2019-0236, with additional information in docket EPA-HQ-OPPT-2016-0743. EPA intends to publish an NPRM in May 2023 and a final rule in August 2024. More information on EPA’s draft revision to its risk determination for NMP will be available in a forthcoming memorandum; and
    • Asbestos (Part 1: Chrysotile Asbestos) (2070-AK86): EPA’s risk evaluation for chrysotile asbestos, describing the conditions of use and presenting EPA’s determinations of unreasonable risk, is in docket EPA-HQ-OPPT-2019-0501, with additional information in docket EPA-HQ-OPPT-2016-0736. More information on EPA’s proposed rule to prohibit ongoing uses of chrysotile asbestos is available in our April 7, 2022, memorandum. EPA intends to publish a final rule in November 2023.
  • Procedures for Chemical Risk Evaluation under TSCA (2070-AK90): As required under TSCA Section 6(b)(4), EPA published a final rule on July 20, 2017, that established a process for conducting risk evaluations to determine whether a chemical substance presents an unreasonable risk of injury to health or the environment, without consideration of costs or other non-risk factors, including an unreasonable risk to a potentially exposed or susceptible subpopulation, under the conditions of use. This process incorporates the science requirements of the amended statute, including best available science and weight of the scientific evidence. The final rule established the steps of a risk evaluation process, including: scope, hazard assessment, exposure assessment, risk characterization, and risk determination. EPA states that it is now considering revisions to that final rule and will solicit public comment through an NPRM. EPA intends to publish the NPRM in September 2022. More information on EPA’s 2017 rule is available in our June 26, 2017, memorandum.
  • Asbestos; Reporting and Recordkeeping Requirements under TSCA (2070-AK99): This rulemaking, under the authority of TSCA Section 8(a), would require certain persons that manufactured (including imported) or processed asbestos and asbestos-containing articles (including as an impurity) to report certain exposure-related information, including quantities of asbestos and asbestos-containing articles manufactured (including imported) or processed, types of asbestos used, and employee data. Reported information would be used by EPA and other federal agencies in considering the regulation of asbestos. EPA notes that this rulemaking is the result of a settlement agreement stemming from litigation pursuant to TSCA Section 21. See Asbestos Disease Awareness Organization v. EPA, No. 19-CV-00871; State of California et al. v. EPA, No. 19-CV-03807. More information on EPA’s proposed reporting and recordkeeping requirements is available in our May 6, 2022, memorandum. EPA intends to publish a final rule in November 2022.
  • Other Chemical Substances Undergoing TSCA Section 6 Risk Evaluation; Significant New Use Rule (SNUR) for Certain Non-Ongoing Uses (2070-AL05): EPA is developing TSCA Section 5(a)(2) SNURs on conditions of use identified as not currently ongoing in the final scope documents for the high-priority substances undergoing TSCA Section 6 risk evaluations. EPA states that it will use the SNURs to require notice to EPA before chemical substances and mixtures are used in new ways that might create concerns. Persons subject to a SNUR who intend to manufacture (including import) or process the chemical substance for the significant new use must notify EPA at least 90 days prior to initiating activities via a significant new use notice (SNUN). EPA intends to publish an NPRM in December 2022 and a final rule in May 2024.
  • The Unified Agenda includes the following chemical-specific SNURs for certain non-ongoing uses:
    • Phthalates; SNUR for Certain Non-Ongoing Uses (2070-AL06): EPA intends to publish an NPRM in November 2022 and a final rule in May 2024;
    • Flame Retardants; SNUR for Certain Non-Ongoing Uses (2070-AL07): EPA intends to publish an NPRM in December 2022 and a final rule in November 2023; and
    • Certain Solvents; SNUR for Certain Non-Ongoing Uses (2070-AL08): EPA intends to publish an NPRM in December 2022 and a final rule in May 2024.
  • Inactive Inventory Per- and Polyfluoroalkyl Substances (PFAS) SNUR (2070-AL10): EPA is developing a SNUR under TSCA Section 5(a)(2) for certain uses of Inactive Inventory PFAS. Persons subject to the Inactive Inventory PFAS SNUR would be required to notify EPA at least 90 days before commencing manufacture or processing for any use that EPA has determined is a significant new use. The required notifications would initiate EPA’s evaluation of the intended use within the applicable review period. Manufacture and processing for the significant new use would be unable to commence until EPA has conducted a review of the notice, made an appropriate determination on the notice, and taken such actions as are required in association with that determination. EPA intends to publish an NPRM in September 2022 and a final rule in June 2023.
  • TRI; Response to Petition to Add Diisononyl Phthalate (DINP) to the TRI List of Toxic Chemicals (2025-AA17): According to EPA, this action arises from a petition received by EPA to add DINP to the list of toxic chemicals reportable under Section 313 of the Emergency Planning and Community Right to Know Act (EPCRA). In response to the petition, EPA initiated a rulemaking on September 5, 2000, proposing to add DINP to the TRI list. On June 14, 2005, EPA issued a notice of data availability seeking comments on EPA’s revised hazard assessment for DINP in further support of EPA’s proposal to add DINP to the TRI list. EPA states that the addition of DINP to the TRI list would make it subject to all the reporting requirements under the Toxic Chemical Release Reporting Rule. EPA intends to publish a supplemental NPRM in July 2022 and a final rule in May 2023;
  • Changes to Reporting Requirements for PFAS; Community Right-to-Know Toxic Chemical Release Reporting (2070-AK97): EPA is developing a proposal to add PFAS subject to reporting under EPCRA Section 313 and Section 6607 of the Pollution Prevention Act (PPA) to the list of Lower Thresholds for Chemicals of Special Concern (Chemicals of Special Concern). EPA states that the addition of the PFAS to the Chemicals of Special Concern list will eliminate the use of the de minimis exemption, eliminate the option to use Form A, and limit the use of range reporting. In addition, EPA is proposing to eliminate the use of the de minimis exemption under the Supplier Notification Requirements for facilities that manufacture or process all chemicals included on the Chemicals of Special Concern list. According to EPA, Chemicals of Special Concern may be found in products below de minimis levels; this is especially true for PFAS that are used at low concentrations in many products. Because of the widespread use of PFAS and their (or their degradants) persistence in the environment, however, even concentrations below de minimis levels can contribute significantly to environmental loading. The elimination of the de minimis exemption for supplier notification purposes will help facilities to identify potential sources of PFAS and other Chemicals of Special Concern. EPA believes that the elimination of the de minimis exemption under the Supplier Notification Requirements for PFAS and other Chemicals of Special Concern will result in a more complete picture of the releases and waste management quantities for these chemicals. EPA intends to publish an NPRM in September 2022 and a final rule in November 2023.
  • Addition of Certain PFAS to the TRI (2070-AL03): EPA is developing a rulemaking to add certain PFAS to the list of chemicals reportable under EPCRA Section 313. EPA states that the addition of these PFAS is in direct response to a statutory mandate under Section 7321(d) of the National Defense Authorization Act for Fiscal Year 2020 (NDAA). Under Section 7321(d), EPA was required to evaluate whether certain specific PFAS meet the EPCRA Section 313 listing criteria by December 2021 and is required to add any PFAS that EPA determines meet the listing criteria by December 2023. EPA intends to publish an NPRM in February 2023 and a final rule in November 2023.
  • Community Right-to-Know; Adopting 2022 North American Industry Classification System (NAICS) Codes for TRI Reporting (2070-AL09): EPA is developing a proposed rule to incorporate the revised 2022 North American Industry Classification System (NAICS) codes for TRI reporting purposes. According to EPA, the Office of Management and Budget (OMB) updates the NAICS codes every five years. OMB approved the 2022 NAICS codes on December 21, 2021 (86 Fed. Reg. 72277), with an effective date of January 1, 2022. EPA currently uses 2017 NAICS codes, and with this proposed rule would implement the 2022 codes for TRI Reporting Year 2022. Facilities reporting to the TRI would be required to use 2022 NAICS codes on reports that are due to EPA by July 1, 2023. This rule also proposed to update the C.F.R. to clarify the scope of facilities required to report to the TRI. According to EPA, the actual data required by a TRI form would not change as a result of this rulemaking, nor would the rule affect the universe of TRI reporting facilities that are required to submit reports to EPA under EPCRA Section 313. EPA intended to publish an NPRM in June 2022 and a final rule in November 2022.

Final Rule Stage

  • Significant New Uses of Chemical Substances; Updates to the Hazard Communication Program and Regulatory Framework; Minor Amendments to Reporting Requirements for Premanufacture Notices (PMN) (2070-AJ94): In 2016, EPA proposed changes to the existing regulations governing significant new uses of chemical substances under TSCA (40 C.F.R. Part 721, specifically “Protection in the Workplace” (40 C.F.R. Section 721.63) and “Hazard Communication Program” (40 C.F.R. Section 721.72)) to align these regulations with revisions to the Occupational Safety and Health Administration’s (OSHA) Hazard Communications Standard (HCS) (29 C.F.R. Section 1910.1200), which are proposed to be cross referenced, and with changes to the OSHA Respiratory Protection Standard and the National Institute for Occupational Safety and Health (NIOSH) respirator certification requirements pertaining to respiratory protection of workers from exposure to chemicals. EPA also proposed changes to the significant new uses of chemical substance regulations based on issues that have been identified by EPA and issues raised by public commenters for SNURs previously proposed and issued under these regulations. Additionally, EPA proposed a minor change to reporting requirements for PMNs and other TSCA Section 5 notices. EPA states that it expects these changes to have minimal impacts on the costs and burdens of complying, while updating the significant new use reporting requirements to assist in addressing any potential effects to human health and the environment. EPA is reviewing the comments received and is planning to issue a final rule. EPA intends to issue a final rule in October 2022. More information on the proposed rule is available in our July 29, 2016, memorandum.
  • Reporting and Recordkeeping for PFAS under TSCA Section 8(a)(7) (2070-AK67): EPA published a proposed rule on June 28, 2021, addressing reporting and recordkeeping requirements for PFAS under TSCA Section 8(a)(7). In accordance with obligations under TSCA Section 8(a), as amended by NDAA Section 7351, persons that manufacture (including import) or have manufactured these chemical substances in any year since January 1, 2011, would be subject to the reporting and recordkeeping requirements. In addition to fulfilling statutory obligations under TSCA, EPA states that it expects that the proposed rule would enable it to characterize better the sources and quantities of manufactured PFAS in the United States. EPA intends to publish a final rule in December 2022. More information on EPA’s proposed rule is available in our June 11, 2021, memorandum.
  • TRI; Response to Petition from the Toxics Use Reduction Institute (TURI) to Add 25 Chemicals (2070-AK26): The Toxics Use Reduction Institute (TURI) submitted a petition under EPCRA Section 313(e)(1) to add 25 chemicals to the EPCRA Section 313 list of toxic chemicals subject to reporting under the TRI. Three of the 25 chemicals were added to the EPCRA Section 313 list through actions unrelated to the petition. EPA states that it evaluated the remaining 22 chemicals to determine if they met the listing criteria of EPCRA Section 313(d)(2). EPA proposed the addition of 12 of the 22 chemicals that were determined to meet the EPCRA Section 313(d)(2) criteria and for which reports were expected to be filed. EPA is reviewing the comments received and is planning to issue a final rule. EPA intends to issue a final rule in November 2022.
  • Parent Company Definition for TRI Reporting (2070-AK42): In 2021, EPA proposed to codify the definition of “parent company” for purposes of reporting to the TRI. Although the existing regulation requires facilities reporting to the TRI to identify their parent company in annual reporting forms, no codified definition of this data element exists. Among the facilities reporting to the TRI are those with complicated corporate ownership structures. As such, effort is required each year by reporting facilities and EPA to clarify how the parent company data element should be represented on the form. According to EPA, a codified definition of parent company would allow EPA to address various corporate ownership scenarios explicitly and reduce the reporting burden caused by regulatory uncertainty. EPA states that the proposed rule would clarify existing regulations to reporting facilities and add a foreign parent company data element, if applicable, while improving EPA’s data quality. EPA is reviewing the comments received and is determining next steps. EPA intends to publish a final rule in October 2022.
  • NDAA Mandated Addition of Certain PFAS to the TRI for Reporting Year 2022 (2070-AL04): According to EPA, NDAA Section 7321 provides a framework for PFAS to be added automatically to the TRI list on January 1 of the year following certain EPA actions. In December 2021, EPA announced the statutory addition of the PFAS chemicals covered by the NDAA to the list of chemical substances subject to reporting for the TRI. This regulatory action amends the EPCRA regulations in 40 C.F.R. Part 372 to reflect this statutory addition. EPA intended to publish a final rule in June 2022.

Article By Lynn L. Bergeson and Carla N. Hutton of Bergeson & Campbell, P.C.

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©2022 Bergeson & Campbell, P.C.

Key Takeaways from U.S. Supreme Court Decision in West Virginia v. EPA

On June 30, 2022, the U.S. Supreme Court issued its decision in West Virginia v. EPA, 597 U.S. __, 2022 WL 2347278 (June 30, 2022), a case involving the Obama Administration’s Clean Power Plan (CPP) and the Trump Administration’s Affordable Clean Energy (ACE) Rule. Applying the “major questions” doctrine, the Court held that EPA exceeded its statutory authority when promulgating the CPP. This decision has implications for the Biden Administration’s planned re-work and reissuance of the CPP and other options for reducing greenhouse gas (GHG) emissions from the electric power and other sectors. It also carries implications outside the environmental realm, providing litigants a powerful new administrative law precedent to challenge agency rules.

Key Takeaways and Issues to Watch

1. “Major questions” doctrine. The most significant takeaway of the opinion is the Court’s elaboration and application of the “major questions” doctrine, as a limit on federal agency regulatory authority. Chief Justice Roberts’ majority opinion held that in “certain extraordinary cases” where an agency asserts broad authority of “economic and political significance,” courts should look for a clear statement of congressional authorization before green-lighting the action. Based on the “major questions” doctrine, the Court rejected the CPP’s partial reliance on generation shifting (from coal-fired power plants to natural gas or renewable electricity generation) as a component of the “best system of emission reduction” (BSER) for reducing carbon dioxide from coal-fired power plants. The Court held that Clean Air Act Section 111(d), 42 U.S.C. § 7411(d), a rarely-used statutory provision, was not sufficient to support a rulemaking that “restructure[ed] the Nation’s overall mix of electricity generation….” Because the Court determined this result would carry consequences of economic and political significance, the Court found the rule triggered the “major questions” doctrine. The Court reiterated that although Section 111(d) authorizes EPA to establish emission guidelines for existing major sources of air pollution based on BSER, the Agency could not do so using such transformative measures.

This decision represents the Supreme Court’s first formal assertion of the “major questions” doctrine, applicable when an agency claims broad authority based on new interpretations of older statutes or statutes in which the grant of authority is not explicitly stated. Although this was not the first Supreme Court case employing this logic, this was the first case where the Court formally used the phrase “major questions” doctrine. Other cases the Court pointed to include a 2000 case rejecting the asserted authority of the Food and Drug Administration (FDA) to regulate tobacco products, like cigarettes, as drug-delivery “devices,” and more recent cases from this Supreme Court term concerning the authority of the Occupational Safety and Health Administration and the Centers for Disease Control and Prevention (CDC) to apply long-extant legal authorities in the context of COVID-19.

2. Chevron deference doctrine. The Court does not strike down Chevron as some parties had predicted or sought. That doctrine—requiring courts to defer to an agency’s reasonable construction of an ambiguous statute it is charged with administering—survives for now. Indeed, the majority opinion did not even cite Chevron deference.

3. Biden EPA. This decision immediately affects the scope of the Biden Administration’s approach to regulating power sector GHG emissions. The Administration has said that it wants to start these rules from a clean slate.

a. On-site measures. As noted in the decision, the Administration may be more likely to consider on-site measures as the BSER. Such options might include partial carbon capture and storage (CCS) or natural gas co-firing. The Obama EPA had declined to use those options for existing sources because it believed generation shifting was a less expensive way for industry to comply. But EPA had used partial carbon capture to set the limits for new sources, so it may review that issue now. Since the CPP’s issuance, the IRS Section 45Q tax credit for CCS and commercialization of CCS technologies that did not exist when the CPP was drafted may also affect the EPA’s approach now.

b. Generation shifting off the table. At least for setting the stringency of BSER, EPA will not be able to rely on generation-shifting measures. Advances in CCS technologies and the Section 45Q tax credit may also affect how EPA defines BSER for coal-fired plants in particular.

c. Seeking GHG reductions as “co-benefits” of other power sector rules. The Biden EPA may also consider other power plant emission rules under other CAA programs to achieve GHG reductions as “co-benefits.” Programs for regional haze, interstate air pollution, and hazardous air pollutants regulate other emissions, but often have the effect of reducing GHGs as well.

d. Other climate authorities will likely get a more intense look. The decision may also likely cause the Biden EPA to consider other, more clearly established GHG sources or authorities to seek additional GHG emissions reductions (e.g., mobile sources, HFCs).

4. Congressional action remains key. The Court’s decision underscores that certain rulemakings will need to rely on clear legislative authority to withstand legal challenges. Notably, the decision does not divest Congress from the ability to delegate “major questions” like this to federal agencies; it only requires that such delegations be clearly stated. Congress retains authority to act in any number of ways on climate change—including with economy-wide emissions programs (as it considered during the first Obama term), or by drafting clearer EPA authority—but with a narrowly-divided House and Senate, these actions seem unlikely.

5. Power sector practical effects. The practical outcome for the power sector is limited. That sector, in many respects, has already decarbonized at a rate faster than provided for by the CPP, largely for economic reasons.

6. States. This decision will likely encourage some states to use their authority to regulate GHG emissions, given the narrowed scope of EPA’s authority.

7. Future challenges. Expect litigants to rely heavily on the West Virginia decision in other rulemaking challenges going forward, whenever agencies act under existing authorities in a way that, in the Chief Justice’s words, “raises an eyebrow.” This may include not only EPA regulatory efforts to address modern environmental challenges, but actions of other federal agencies such as efforts by the Federal Communications Commission to regulate internet service providers to impose net neutrality, or efforts by the Securities and Exchange Commission to establish ESG disclosure requirements. Litigants will have a powerful tool to challenge those rules if they can persuasively phrase the question in “major question” terms.

Article By Eric L. Christensen, Brook J. Detterman, David M. Friedland, Jennifer J. Leech, and Zachary B. Pilchen of Beveridge & Diamond PC

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© 2022 Beveridge & Diamond PC