Regulating PFAS Under the Clean Water Act
Congressional research reportJul 16, 2026
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Updated July 16, 2026
Regulating PFAS Under the Clean Water Act
In recent decades, improvements in analytical methods and
monitoring technologies, along with health research, have
increased national attention to the presence of emerging
contaminants in surface water. Detections of one particular
group of contaminants, per- and polyfluoroalkyl substances
(PFAS), have heightened public and congressional interest
in the U.S. Environmental Protection Agency’s (EPA’s)
authorities under the Clean Water Act (CWA) to address
PFAS in surface water.
Overview
EPA has several CWA authorities it may use to address
contaminants, such as PFAS, in surface water. A primary
mechanism in the CWA to control contaminants in surface
waters is through permits. The statute prohibits the
discharge of pollutants from any point source to waters of
the United States without a permit. The CWA authorizes
EPA and states with delegated CWA permitting authority to
limit or prohibit discharges of pollutants in their National
Pollutant Discharge Elimination System (NPDES) permits.
These permits incorporate technology-based and waterquality-based requirements.
The CWA requires EPA to establish technology-based
effluent (i.e., discharge) limits for industrial dischargers,
known as Effluent Limitation Guidelines (ELGs). EPA is
also required to issue water quality criteria for use in
establishing water quality standards for surface waters and
water-quality-based effluent limitations. The CWA also
authorizes EPA to utilize certain NPDES permit authorities
to address contaminants; to set pollutant limits and
monitoring and reporting requirements for contaminants in
biosolids (i.e., sewage sludge from wastewater treatment
facilities) if sufficient scientific evidence shows there is
potential harm to human health or the environment; and to
designate contaminants as toxic or hazardous pollutants.
In 2021, EPA first announced projected timelines for
several actions to address PFAS using CWA authorities in
its PFAS Strategic Roadmap. EPA released some annual
progress reports on the 2021 Roadmap. In February 2026,
EPA provided an update on its PFAS actions and referred to
ongoing CWA efforts. To date, EPA has not finalized any
ELGs to address any PFAS, has not set requirements for
PFAS in biosolids, and has not designated any PFAS as a
toxic pollutant or hazardous substance. EPA has published
water quality criteria for certain PFAS, and in some
instances has used NPDES permit authorities to address
PFAS and has encouraged states to use such authorities.
Effluent Limitation Guidelines
The CWA requires EPA to publish ELGs, which are the
required minimum standards for specific pollutants in
industrial wastewater discharges. EPA has developed ELGs
for 59 industrial source categories. For industrial facilities
that discharge directly to regulated waters, EPA or states
incorporate the limits established in ELGs into the NPDES
permits they issue. For indirect dischargers—facilities that
discharge to publicly owned treatment works (POTWs)—
pretreatment standards established in ELGs to prevent pass
through and interference at the POTW apply.
The CWA also requires EPA to annually review all existing
ELGs and publish a biennial plan that includes a schedule
for review and revision of promulgated ELGs, identifies
categories of industrial sources discharging toxic or
nonconventional pollutants that do not have ELGs, and
establishes a schedule for promulgating ELGs for any
newly identified categories. EPA’s recent ELG biennial
plans and related actions have included efforts to identify
and characterize PFAS discharges, including the types and
concentrations of PFAS discharged and the significant
sources of PFAS discharges. The plans have also included
details on the agency’s efforts to determine whether the
agency should update ELGs for certain industrial source
categories to set effluent limitations for PFAS.
In the 2021 Roadmap, EPA established timelines for action,
including data collection or rulemaking, on 11 industrial
categories. EPA targeted the end of 2024 as the deadline for
“significant progress in its ELG regulatory work.” EPA
released its latest preliminary ELG plan in December 2024,
updating some of the agency’s timelines. In these
documents, EPA indicated that the agency
• planned to publish proposed rules revising ELGs for the
Organic Chemicals, Plastics, and Synthetic Fibers
(OCPSF) Category (by fall 2024), the Metal Finishing
and Electroplating Categories (by spring 2026), and the
Landfills Category (in 2027);
• would continue its study of the Textile Mills Category;
• published a proposed information collection rule (in
2024) for a POTW Influent Study to collect nationwide
data on industrial discharges of PFAS to POTWs; and
• would continue to monitor several other sectors.
Since 2024, specific updates on EPA’s progress on its ELG
work and influent study have been limited. The 2026
Regulatory Agenda (posted July 3, 2026) includes new
timelines for a proposed OCPSF rule (July 2026) and a
proposed Metal Finishing rule (February 2027).
NPDES Authorities
In cases where EPA has not established an ELG for a
particular industrial category or type of facility, or where
pollutants or processes were not considered when an ELG
was developed, the permitting authority (EPA or states)
may still impose technology-based effluent limits on a caseby-case basis. The permitting authority may also require
facilities with NPDES permits to monitor pollutants or
conduct special studies to collect data to support future
permit limits. The permitting authority may also include
best management practices (BMPs) in permits on a case-by-
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Regulating PFAS Under the Clean Water Act
case basis. However, the use of some of these authorities
can be limited when analytical methods to detect specific
pollutants are not available.
In the 2021 Roadmap, EPA discussed plans to leverage
some of these NPDES authorities. Central to these plans
was the September 2021 publication of a draft EPA
analytical method (Method 1633A) to test for 40 PFAS
compounds in eight environmental media, including surface
water and wastewater. EPA finalized this method in
January 2024, along with a second method (Method 1621)
that can screen for thousands of known PFAS compounds
in water samples. In the 2024 Roadmap progress report,
EPA stated that it would propose the two methods for
adoption in regulations, “a necessary step for them to be
nationally required for CWA use.” EPA published a
proposed rule to adopt these methods in January 2025 (with
a final rule expected in July 2026). The 2026 Regulatory
Agenda also lists a rulemaking to update requirements for
some existing NPDES permit applications to address PFAS
monitoring and reporting. EPA anticipates a proposed rule
by January 2027 and a final rule by May 2027.
EPA also issued two memoranda regarding PFAS and
NPDES permits. The first (issued in April 2022) detailed
how the agency would address PFAS discharges in EPAissued NPDES permits and for indirect dischargers where
EPA is the pretreatment control authority. It recommended
that EPA permit writers include certain permit conditions
for industrial facilities where PFAS are expected or likely
to be present in discharges. These conditions include
effluent monitoring for the 40 PFAS detectable by EPA’s
draft Method 1633A and BMPs and pollution prevention
conditions. The memorandum also recommended permit
conditions for POTWs where EPA is the permitting
authority or the pretreatment control authority, including
effluent, influent, and biosolids monitoring requirements;
BMPs; and pollution prevention practices. In December
2022, EPA issued a second memorandum to states with
guidance on using similar NPDES authorities.
Water Quality Criteria
CWA Section 304(a) requires EPA to develop and publish
and “from time to time thereafter revise” criteria for water
quality that accurately reflect the latest scientific
knowledge. Water quality criteria provide concentrations
for specific contaminants or conditions in a water body that,
if not exceeded, will protect designated uses of the water
body (e.g., aquatic life, public drinking water supply,
recreation). These criteria are recommendations to states
and tribal governments for use in developing their own
water quality standards, which they use to protect and
restore waters and to inform water-quality-based effluent
limits in permits. EPA has developed several types of
criteria targeted to protect different designated uses, such as
human health, aquatic life, and recreational criteria.
In the 2021 Roadmap, EPA announced plans to develop
national ambient water quality criteria for PFAS to protect
human health and aquatic life. EPA targeted fall 2024 for
publishing human health criteria for perfluorooctanoic acid
(PFOA) and perfluorooctane sulfonate (PFOS). In
December 2024, EPA published for public comment draft
human health criteria for PFOA, PFOS, and
perfluorobutane sulfonic acid (PFBS). These criteria have
not been finalized. EPA targeted winter 2022 for publishing
aquatic life criteria for PFOA and PFOS. EPA published
final aquatic life criteria for PFOA and PFOS in October
2024. EPA issued benchmarks for eight PFAS that do not
have sufficient data to define an aquatic life criteria value.
Biosolids Requirements
Biosolids (i.e., sewage sludge) are a product of the
wastewater treatment process. Biosolids may be applied to
land for beneficial purposes (e.g., agriculture) or disposed
of through incineration or surface disposal. CWA Section
405(d) requires EPA to establish numeric limits and
management practices to protect public health and the
environment from the reasonably anticipated adverse
effects of pollutants during biosolid use or disposal. Section
405(d) also requires EPA to review its biosolids regulations
at least every two years to identify additional toxic
pollutants that may be present in biosolids and promulgate
regulations for those pollutants if sufficient scientific
evidence shows they may adversely affect public health or
the environment. EPA’s process to determine whether a
pollutant may warrant regulation includes sewage sludge
surveys (to identify the presence of pollutants in biosolids
using samples taken from wastewater treatment plants), risk
screening for pollutants found in biosolids, and risk
assessments for pollutants identified in biosolids that
exceed a level of concern.
EPA has not established numeric limits or monitoring or
reporting requirements for PFAS in biosolids. In the 2021
Roadmap, EPA said it would complete, by winter 2024, a
risk assessment for PFOA and PFOS in biosolids, which it
would use to determine whether to regulate them. In
January 2025, EPA published a draft risk assessment for
PFOA and PFOS in biosolids for public comment. In June
2026, EPA issued draft guidance for public comment. It did
not finalize the risk assessment. In the draft guidance
memorandum, EPA stated that the agency determined the
draft risk assessment had “a number of serious flaws.” EPA
opted to issue guidance to stakeholders to clarify potential
risks from PFOA and PFOS and recommend practices to
mitigate those risks when managing biosolids.
Toxic Pollutants or Hazardous Substances
The CWA authorizes EPA to designate contaminants as
toxic pollutants (§307) or as hazardous substances (§311),
which may trigger other actions under the CWA and the
Comprehensive Environmental Response, Compensation,
and Liability Act. EPA has not designated any PFAS as
toxic pollutants or hazardous substances under CWA
authorities and has not indicated that it plans to do so.
Recent Congressional Action
PFAS-related issues have generated congressional interest
in recent years. Recent Congresses have held hearings and
introduced and passed legislation to address PFAS. The
Infrastructure Investment and Jobs Act provided $1 billion
over five fiscal years to address emerging contaminants
(including PFAS) in wastewater through the Clean Water
State Revolving Fund. In the 119th Congress, Members
introduced several bills related to PFAS in surface water.
Laura Gatz, Specialist in Environmental Policy
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Regulating PFAS Under the Clean Water Act
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