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PFHxS

Perfluorohexane sulfonate

1,1,2,2,3,3,4,4,5,5,6,6,6-tridecafluorohexane-1-sulfonic acid

Also known as PFHxS
Perfluorohexanesulfonic acid1,1,2,2,3,3,4,4,5,5,6,6,6-Tridecafluorohexane-1-sulfonic acidPerfluorohexane-1-sulphonic acidPFHxSZU6Y1E592SPFHS cpdPFHxS perfluorohexanesulfonic acidperfluorohexane sulfonate potassium salt

A 6-carbon long-chain PFSA with 2024 NPDWR individual MCL of 10 ppt. EPA's 2023 IRIS RfD targets developmental immune effects; detected at 3,144 utilities serving 71M people across 46 states.

Group
PFAS
Regulatory status
Primary
NPDWR — federally enforced MCL
Top removal tech
Activated carbon

Primary concern: Developing immune system and thyroid hormone (T4) effects

Affected organ systems

Liver Immune Developmental Endocrine Affecting the body's hormone system — thyroid, adrenal, reproductive, or metabolic hormones. Thyroid Kidney

Health effects

Carcinogen A substance known or reasonably suspected to cause cancer based on human or animal studies. Immunotoxin Suppresses or alters the immune system. Can increase risk of infection or reduce vaccine effectiveness. Endocrine disruptor Mimics or blocks the body's hormones (estrogen, thyroid, testosterone). Can affect development, reproduction, and metabolism at very low doses. Developmental toxin Causes harm during development before birth or in early childhood — birth defects, low birth weight, delayed growth, or learning problems later in life. Hepatotoxin Damages the liver. Effects range from elevated liver enzymes on a blood test to fatty liver disease and, with prolonged exposure, liver cancer.

Exposure routes

Drinking water Dietary Occupational In utero Breast milk

Vulnerable populations

Pregnant Infants Children

Overview

Perfluorohexanesulfonic acid (PFHxS) is a 6-carbon perfluoroalkyl sulfonic acid (C6HF13O3S, MW 400) — the shortest-chain PFAS to receive an individual federal Maximum Contaminant Level under the 2024 NPDWR. EPA finalized the PFHxS IRIS toxicological review in 2023, identifying decreased serum free thyroxine (T4) and reduced antibody response to childhood vaccines as the dose-defining endpoints, and set the federal MCL at 10 parts per trillion with a matching MCLG of 10 ppt — the MCLG is not zero because IARC has not classified PFHxS as a Group 1 carcinogen, unlike PFOA and PFOS. PFHxS is also a regulated component of the NPDWR Hazard Index mixture alongside PFNA, HFPO-DA, and PFBS. Like PFOS, PFHxS persists indefinitely in the environment and bioaccumulates in human serum with one of the longest measured PFAS half-lives — published central values cluster around 8.5 years (Olsen 2007, 3M production-worker cohort). PFHxS appears in U.S. drinking water at 3,144 public water systems serving roughly 71 million people across 46 states; dozens of large municipal utilities measure at or above the 10 ppt federal MCL.

Pollution sources

Industry Military AFFF Aqueous Film-Forming Foam — firefighting foam used at military bases and airports for fuel fires. The leading source of PFAS contamination in groundwater near former training sites. Manufacturing Consumer products

Sources

PFHxS reaches drinking water predominantly through three legacy pathways. (1) Aqueous film-forming foam (AFFF) release at military installations and civilian airports is the dominant signature — the PFHxS top-occurrence list reads like an AFB roster: Stratmoor Hills and Security Water District in Colorado Springs (155.5 and 132.0 ppt) sit downstream of the Peterson Space Force Base / former Peterson AFB AFFF impact area; Fort Campbell on the Kentucky/Tennessee line (30.1 ppt at both on-base and county-supply systems); Wright-Patterson AFB in Ohio (23.2 ppt across 22 of 22 tests); Camp Pendleton North in California (22.2 ppt, 156 of 162 tests); and Fort Riley, Kansas (18.8 ppt). (2) 3M-era PFOS-based Scotchgard manufacturing and use, of which PFHxS was a minor synthesis impurity and co-precursor — Bemidji, MN (84.2 ppt over 51 tests) sits within the Bemidji Regional Airport AFFF and 3M Cottage Grove regional influence area, and the Oakdale, MN system (10.6 ppt) traces directly to 3M Cottage Grove. (3) Industrial discharges from chrome plating, semiconductor fabrication, and other industries where PFHxS replaced PFOS as a mist suppressant in the mid-2000s — Hannah Heights HOA in Friday Harbor, WA (725.9 ppt average across 2 of 4 tests) and Oatman Water in Scottsdale, AZ (710.0 ppt) are the two highest PFHxS detections in the national occurrence dataset and reflect localized point-source impacts. Major municipal systems exceeding the 10 ppt federal MCL include the City of Greensboro, NC (11.1 ppt serving 318,057 people) and Fayetteville Public Works Commission, NC (10.7 ppt serving 214,137 people) — both within the Cape Fear basin Chemours influence area.

Health risks

EPA's 2023 IRIS toxicological review identifies two co-critical endpoints for PFHxS: decreased serum free thyroxine (T4) in adults and reduced antibody response to childhood vaccines (the immune-developmental endpoint). The chronic Reference Dose is 4×10⁻⁷ mg/kg/day — orders of magnitude lower than EPA's PFHxA RfD of 5×10⁻⁴ mg/kg/day, which is why the surrogate-derived health benchmarks for long-chain PFSAs sit in the single-digit-ppt range versus thousand-ppt for PFHxA. Commonly listed PFHxS health concerns are cancer, immune system damage, hormone disruption, harm to fetal growth and child development, and harm to the liver. PFHxS has not been formally classified as a carcinogen by IARC or NTP, which is why the federal MCLG is set at 10 ppt rather than zero — the MCLG-of-zero approach EPA used for PFOA and PFOS reflects their IARC Group 1 cancer classifications, and PFHxS does not yet share that designation. PFHxS bioaccumulates: serum elimination half-life in humans is among the longest of any PFAS measured, with Olsen 2007 reporting a median of 8.5 years (range roughly 3-30 years across the 3M production-worker cohort). Detectable PFHxS appears in essentially 100% of U.S. adults sampled by NHANES, and serum levels have declined more slowly than PFOS since the 2002 3M phaseout.

Effective treatments

Activated carbon Granular or block carbon that traps organic contaminants as water flows through. The most common point-of-use filter media — handles chlorine taste, VOCs, pesticides, and many PFAS. Reverse osmosis A semipermeable membrane that pushes water through under pressure, leaving most dissolved contaminants behind. Removes a very broad range — PFAS, lead, arsenic, nitrate, salts — at the cost of slower flow and some wastewater. Ion exchange Resin beads that swap unwanted ions (lead, calcium, certain PFAS, perchlorate) for harmless ones like sodium. Common in water softeners and PFAS treatment columns.

Does not remove

UV Ultraviolet light that disrupts the DNA of bacteria, viruses, and protozoa as water flows past the lamp. Disinfects but doesn't remove chemicals or particles. Chlorination Adds chlorine or hypochlorite to kill bacteria and viruses. The most common disinfection method in US water systems; leaves a residual that keeps water protected through the distribution pipes. Boil Kills bacteria, viruses, and protozoa after a one-minute rolling boil. Does NOT remove chemicals like lead, nitrate, or PFAS — boiling actually concentrates them as water evaporates.

NSF certifications

NSF/ANSI 53 Health-related contaminants NSF/ANSI 58 Reverse osmosis systems

Water treatment

PFHxS responds well to the same treatment technologies used for PFOS and other long-chain PFSAs: granular activated carbon (GAC), anion exchange resin, and high-pressure membranes (reverse osmosis, nanofiltration). The sulfonate head group provides strong electrostatic affinity for anion exchange media, and the 6-carbon perfluorinated tail provides adequate hydrophobic adsorption onto GAC — PFHxS breakthrough on GAC occurs later than the short-chain PFCAs (PFBA, PFHxA) but earlier than PFOS, and design loading rates fall between those two reference points. Conventional treatment processes — coagulation, sand filtration, disinfection, UV, and ozonation — do not remove PFHxS. Boiling concentrates rather than removes it. NSF/ANSI 53 and NSF P473 certify point-of-use filters for general PFAS reduction; NSF/ANSI 58 covers RO systems. Utilities targeting the 10 ppt federal MCL with GAC, AIX, or RO will incidentally control PFHxS to well below the federal Hazard Index threshold and will simultaneously reduce the other long-chain PFSAs (PFOS, PFHpS) that share treatment behavior; the surrogate-derived 0.001-ppt health benchmark sits below analytical reporting limits and is not operationally verifiable.

Gallery

Related contaminants

Chemistry + classification data sourced from public databases (PubChem, EPA CompTox, IARC monographs); 3D molecular models from 3d.nih.gov where available.