Publication Cover
Journal of Environmental Science and Health, Part A
Toxic/Hazardous Substances and Environmental Engineering
Volume 44, 2009 - Issue 12
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ARTICLES

Perfluoroalkyl sulfonic and carboxylic acids: A critical review of physicochemical properties, levels and patterns in waters and wastewaters, and treatment methods

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Pages 1145-1199 | Received 05 May 2009, Published online: 04 Sep 2009
 

Abstract

Perfluorinated acids (PFAs) are an emerging class of environmental contaminants present in various environmental and biological matrices. Two major PFA subclasses are the perfluorinated sulfonic acids (PFSAs) and carboxylic acids (PFCAs). The physicochemical properties and partitioning behavior for the linear PFA members are poorly understood and widely debated. Even less is known about the numerous branched congeners with varying perfluoroalkyl chain lengths, leading to confounding issues around attempts to constrain the properties of PFAs. Current computational methods are not adequate for reliable multimedia modeling efforts and risk assessments. These compounds are widely present in surface, ground, marine, and drinking waters at concentrations that vary from pg L− 1 to μg L− 1. Concentration gradients of up to several orders of magnitude are observed in all types of aquatic systems and reflect proximity to known industrial sources concentrated near populated regions. Some wastewaters contain PFAs at mg L− 1 to low g L− 1 levels, or up to 10 orders of magnitude higher than present in more pristine receiving waters. With the exception of trifluoroacetic acid, which is thought to have both significant natural and anthropogenic sources, all PFSAs and PFCAs are believed to arise from human activities. Filtration and sorption technologies offer the most promising existing removal methods for PFAs in aqueous waste streams, although sonochemical approaches hold promise. Additional studies need to be conducted to better define opportunities from evaporative, extractive, thermal, advanced oxidative, direct and catalyzed photochemical, reductive, and biodegradation methods. Most PFA treatment methods exhibit slow kinetic profiles, hindering their direct application in conventional low hydraulic residence time systems.

Acknowledgments

S.R. thanks the Natural Sciences and Engineering Research Council (NSERC) of Canada for partial financial support of this work.

Notes

aLog10 P from ref.[ Citation 24 ]

bFrom ref.[ Citation 5 ]

cFrom ref.[ Citation 200 ]

dCalculated with SPARC (August 2007 release w4.0.1219-s4.0.1219; http://ibmlc2.chem.uga.edu/sparc/).[ Citation 87 , Citation 204 , Citation 205 ] using SMILES molecular notation[ Citation 94 , Citation 95 ] as inputs.

elog10 D from ref.[ Citation 52 ]

flog10 P from ref.[ Citation 80 ]

aCalculated with SPARC (August 2007 release w4.0.1219–s4.0.1219; http://ibmlc2.chem.uga.edu/sparc)[ Citation 87 , Citation 204 , Citation 205 ] using SMILES molecular notation[ Citation 94 , Citation 95 ] as inputs.

bCalculated with EPI Suite EPIWEB v.4.0 (http://www.epa.gov/oppt/exposure/pubs/episuite.htm) using SMILES molecular notation as inputs with the following modules: KOWWIN v1.67, MPBPVP v1.43, WSKOW v1.41, HENRYWIN v3.20, KOAWIN v1.10, BIOWIN v4.10, BioHCwin v1.01, AEROWIN v1.00, AopWin v1.92, KOCWIN v2.00, and BCFBAF v3.00.

dFrom ref.[ Citation 12 ]

eSaturated subcooled liquid vapor pressure.

fDimensionless air-water partitioning constant.

gOctanol-water partitioning constant.

hOctanol-air partitioning constant.

aCalculated with SPARC (August 2007 release w4.0.1219–s4.0.1219; http://ibmlc2.chem.uga.edu/sparc/)[ Citation 87 , Citation 204 , Citation 205 ] using SMILES molecular notation[ Citation 94 , Citation 95 ] as inputs.

bCalculated with EPI Suite EPIWEB v.4.0 (http://www.epa.gov/oppt/exposure/pubs/episuite.htm) using SMILES molecular notation as inputs with the following modules: KOWWIN v1.67, MPBPVP v1.43, WSKOW v1.41, HENRYWIN v3.20, KOAWIN v1.10, BIOWIN v4.10, BioHCwin v1.01, AEROWIN v1.00, AopWin v1.92, KOCWIN v2.00, and BCFBAF v3.00.

dFrom ref.[ Citation 12 ]

eSaturated subcooled liquid vapor pressure.

fDimensionless air-water partitioning constant.

gOctanol-water partitioning constant.

hOctanol-air partitioning constant.

aFrom ref.[ Citation 52 ]

bFrom ref.[ Citation 97 ]

cFrom ref.[ Citation 12 ]

aFrom ref.[ Citation 52 ]

b From ref.[ Citation 12 ]

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