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PFAS Testing Methods and Guidance for Sample Filtration

What are poly- and perfluorylalkyl substances (PFAS)?

PFAS are poly- and perfluorylalkyl substances known as “forever chemicals” and comprise a group of over 4,000 varieties of long- and short-chain perfluorinated compounds.1 PFAS are used in a variety of industries for their excellent oil-, water-, temperature-, chemical-, and fire-resistant properties and noted for their use in polymerization reactions of fluoropolymers such as Teflon® by companies such as 3M and Dupont. Products that contain PFAS and related compounds are ubiquitous in industrial and consumer products, including product packaging, cosmetics, non-stick cookware, stain repellents, polishes, paints, coatings, and firefighting foams.

The excellent properties and broad use of PFAS have led to the persistent accumulation of these man-made chemicals in environmental and biological matrices, recently linked to liver damage, cancer, weakened immune system, and high cholesterol in humans.1-3

PFAS and the Regulatory Landscape

In response, agencies in the US and Europe have taken regulatory action. The Stockholm Convention proposed regulations for two of the commonest PFAS compounds—perfluorooctanoic acid (PFOA) and perfluorooctanesulfonic acid (PFOS)—with certain exemptions, effective in 2020. The US Environmental Protection Agency (EPA) published an Action Plan in 2019 followed by recommendations for testing water matrices for PFAS compounds under the Safe Drinking Water Act in early 2020, with a drinking water advisory concentration of 70 parts per trillion (ppt). The European Union (EU) proposed a PFOA limit of 25 parts per billion (ppb) in mid-2020. In response to regulatory proposals and actions, academic and industrial testing labs have developed analytical methods for testing and monitoring PFAS in a variety of matrices. These regulations are important to understanding the extent of human exposure and environmental contamination to inform future remediation efforts.

Analytical Methods for Determining PFAS in Water Samples

Currently, most analytical methods for water matrices involve solid phase extraction (SPE) sample preparation after the addition of internal standards and fortification of samples with surrogate standards, prior to liquid chromatography and tandem mass spectrometry (LS/MS/MS) for the detection of selected per- and polyfluorinated alkyl substances (usually 20-30 compounds).

Drinking water is considered a “clean” matrix and often does not require filtration ahead of sample preparation. However, methods such as SW-846 Method 8327, ASTM D7968-17a, ASTM D7979-20, and ISO 21675 involve matrices such as wastewater that could have a higher degree of particulates. Particulates in solution must be removed prior to LC/MS/MS as they can be detrimental to sample analysis, column longevity, and overall instrument function. These methods identify the need for filtration using membranes in a syringe filter format.

Filtration Media and PFAS Contamination

In recent studies, there has been concern about adding PFAS contamination to samples from a variety of sources including collection bottles, storage vials, tubing components, and any other plastic that contacts the sample. This includes membrane filters and filter housing; for example, adsorption of PFAS onto filtration media is dependent on filter type and type of PFAS molecule.4-5 Further, some filters may show trace amounts of contamination that may interfere with LC-MS/MS detection.6 In some cases, both contamination, and sorption onto filtration media can be reduced by washing with methanol.6-7

Testing Millex® Filtration Devices in PFAS Workflows

Materials and Methods

To alleviate this concern, three lots of polyethersulfone (PES) Millex® syringe filter devices were tested for PFAS extractables according to EPA Method 537.1 with some additional PFAS compounds not required by the method, including next-generation PFAS compound, GenX. The compounds tested are listed in Table 1. EPA 537.1 does not require sample filtration, but filtration was used to provide a clean sample to test extractable contamination levels from the syringe filter. A comparison of those compounds tested to the compounds required by ASTM D7979-19, SW-846 Method 8327, and ISO 21675 are also included in Table 1.

Table 1.A comparison of the PFAS compounds used in the current study compared with EPA 537.1, ASTM D7979-19, SW-846 Method 8327, and ISO 21675.

a Sample filtration required and/or suggested by the method

EPA 537.1 was used to test for PFAS contamination of filtration media in collaboration with SGS North America (Orlando, FL location). Briefly, a 250 mL PFAS-free DI water sample was spiked with surrogates. The internal standard spike of 0.08 ppb was used for QC blanks. To determine if sample filtration media contributes to PFAS contamination, the entire sample was passed through the filter and into a styrene divinylbenzene (SDVB) SPE cartridge. The sample bottles and tubes were rinsed with basic methanol, passed through the filter and into the cartridge. The entire sample was then subjected to SPE and concentrated to 1 mL in 96:4% (v/v) methanol:water prior to LC/MS/MS analysis using a C18 column. Analysis was performed using internal standards. The filters tested included three lots of Millex®-GP syringe filters (non-sterile, 33 mm filter with PES membrane) in both 0.22 µm (Cat. No. SLGP033N and 0.45 µm (Cat. No. SLHP033N) pore sizes.

PFAS Testing Results

There were no detectable PFAS contaminants in the 33 mm non-sterile PES Millex® devices tested, even given the very low minimum detection limits (MDL) of the method (Table 2). The results were the same for the three different lots of the 0.22 and 0.45 mm PES membranes. These results suggest that PES Millex® filtration devices are reliable and appropriate to utilize in the filtration of samples for the analysis of PFAS compounds in environmental matrices. Similar results were found using PES membranes alone (without housing and filtered using a 25 mm Swinnex® filter holder device).

Table 2.Detection of PFAS after filtration with Millex® PES devices using LC/MS/MS according to EPA 537.1

Abbreviations: RL = reporting limit (ppb); MDL = minimum detection limit (ppb); ND = not detected below both RL and MDL.

Sample Preparation in PFAS Testing

PFAS are a class of over 4,000 chemicals labeled as “forever chemicals” due to their persistence in the environment. Increasing concern about their threat to human health has sparked a cascade of regulatory action in the US and Europe. The primary focus is on water matrices starting with drinking water and then focusing on higher particulate water matrices and beyond. The primary analytical method for testing PFAS in water is solid phase extraction followed by liquid chromatography tandem mass spectrometry.

In all analytical methods, sample preparation should be carefully considered, especially for higher particulate samples which require filtration. However, in PFAS workflows, additional factors could complicate PFAS analyses downstream. Thus, we tested PES membranes within a PFAS detection workflow to determine levels of contamination and found that none of the filters had any detectable levels of PFAS contamination. Therefore, when filtration of higher particulate samples is needed in a PFAS workflow, PES Millex® filters provide a suitable option.

Products and Catalog Numbers
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Alternative diameter PES Millex® syringe filters and Millipore® cut disc membranes are also available.

References

1.
Kwiatkowski CF, Andrews DQ, Birnbaum LS, Bruton TA, DeWitt JC, Knappe DRU, Maffini MV, Miller MF, Pelch KE, Reade A, et al. 2020. Scientific Basis for Managing PFAS as a Chemical Class. Environ. Sci. Technol. Lett.. 7(8):532-543. http://dx.doi.org/10.1021/acs.estlett.0c00255
2.
Winchell LJ, Wells MJ, Ross JJ, Fonoll X, Norton JW, Kuplicki S, Khan M, Bell KY. 2021. Analyses of per- and polyfluoroalkyl substances (PFAS) through the urban water cycle: Toward achieving an integrated analytical workflow across aqueous, solid, and gaseous matrices in water and wastewater treatment. Science of The Total Environment. 774145257. http://dx.doi.org/10.1016/j.scitotenv.2021.145257
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Pérez F, Nadal M, Navarro-Ortega A, Fàbrega F, Domingo JL, Barceló D, Farré M. 2013. Accumulation of perfluoroalkyl substances in human tissues. Environment International. 59354-362. http://dx.doi.org/10.1016/j.envint.2013.06.004
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Lath S, Knight ER, Navarro DA, Kookana RS, McLaughlin MJ. 2019. Sorption of PFOA onto different laboratory materials: Filter membranes and centrifuge tubes. Chemosphere. 222671-678. http://dx.doi.org/10.1016/j.chemosphere.2019.01.096
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Labadie P, Chevreuil M. 2011. Biogeochemical dynamics of perfluorinated alkyl acids and sulfonates in the River Seine (Paris, France) under contrasting hydrological conditions. Environmental Pollution. 159(12):3634-3639. http://dx.doi.org/10.1016/j.envpol.2011.07.028
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So MK, Taniyasu S, Lam PKS, Zheng GJ, Giesy JP, Yamashita N. 2006. Alkaline Digestion and Solid Phase Extraction Method for Perfluorinated Compounds in Mussels and Oysters from South China and Japan. Arch Environ Contam Toxicol. 50(2):240-248. http://dx.doi.org/10.1007/s00244-005-7058-x
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Yamashita N, Kannan K, Taniyasu S, Horii Y, Petrick G, Gamo T. 2005. A global survey of perfluorinated acids in oceans. Marine Pollution Bulletin. 51(8-12):658-668. http://dx.doi.org/10.1016/j.marpolbul.2005.04.026