Aquatic risk assessment of alcohol ethoxylates in North America and Europe.

An environmental risk assessment for alcohol ethoxylates (AE) is presented that integrates wastewater treatment plant monitoring, fate, and ecotoxicity research with a new application of mixture toxicity theory based on simple similar concentration addition of AE homologs in a species-sensitivity distribution (SSD) context. AEs are nonionic surfactants composed of a homologous series of molecules that range in alkyl chain length from 12 to 18 carbons and ethoxylates from 0 to 18 units. Chronic ecotoxicity of AE is summarized for 17 species in 60 tests and then normalized to monitoring data for AE mixtures. To do so, chronic aquatic toxicity was first expressed as EC10 per species (the concentration predicted to cause a 10% reduction in an important ecological endpoint). Normalization integrated several new quantitative structure-activity relationships for algae, daphnids, fish, and mesocosms and provided an interpretation of toxicity test data as a function of individual homologs in an AE mixture. SSDs were constructed for each homolog and the HC5 (hazardous concentration protective of 95% of species based on a small biological effect [the chronic EC10]) was predicted. Total mass of AE in monitored effluents from 29 sites in Europe, Canada, and the United States averaged 6.8, 2.8, and 3.55 microg/L, respectively. For risk assessment purposes, correction of exposure to account for fatty alcohol derived from sources other than AE and for sorbed components based on experimental evidence was used to determine AE concentrations in undiluted (100%) effluents from North America and Europe. Exposure and effect findings were integrated in a toxic unit (TU)-based model that considers the measured distribution of individual AE homologs in effluent with their corresponding SSDs. Use of environmentally relevant exposure corrections (bioavailability and accounting for AE-derived alcohol) resulted in TUs ranging from 0.015 to 0.212. Low levels of risk are concluded for AE in the aquatic environments of Europe and North America.

[1]  Tom C. J. Feijtel,et al.  Exposure modeling of detergent surfactants—prediction of 90th‐percentile concentrations in the Netherlands , 1999 .

[2]  Martin Stafford Holt,et al.  Environmental monitoring for linear alkylbenzene sulfonate, alcohol ethoxylate, alcohol ethoxy sulfate, alcohol sulfate, and soap , 1999 .

[3]  H. Hauthal CESIO 2004: Dynamic surfactants and nanostructured surfaces for an innovative industry , 2004 .

[4]  T Aldenberg,et al.  Uncertainty of the hazardous concentration and fraction affected for normal species sensitivity distributions. , 2000, Ecotoxicology and environmental safety.

[5]  D. Roberts,et al.  Application of Hydrophobicity Parameters to Prediction of the Acute Aquatic Toxicity of Commercial Surfactant Mixtures , 1995 .

[6]  R. Lizotte,et al.  An assessment of the ecological effects of a C9--11 linear alcohol ethoxylate surfactant in stream mesocosm experiments , 1997 .

[7]  P. Dorn,et al.  Effects of a nonionic surfactant (c14–15 AE-7) on fish survival, growth and reproduction in the laboratory and in outdoor stream mesocosms , 1996 .

[8]  W. E. Bishop,et al.  Aquatic Toxicology and Hazard Assessment: Sixth Symposium , 1983 .

[9]  R. Sudo,et al.  The growth inhibition of planktonic algae due to surfactants used in washing agents , 1984 .

[10]  Gerrit Schüürmann,et al.  Quantitative structure-activity relationships in environmental sciences, VII , 1997 .

[11]  P. Gramatica,et al.  Water quality objectives for mixtures of toxic chemicals: problems and perspectives. , 2003, Ecotoxicology and environmental safety.

[12]  David J. Hansen,et al.  Technical basis for narcotic chemicals and polycyclic aromatic hydrocarbon criteria. I. Water and tissue , 2000 .

[13]  D. Versteeg,et al.  Effect of organic carbon on the uptake and toxicity of quaternary ammonium compounds to the fathead minnow, Pimephales promelas , 1992 .

[14]  Branson,et al.  Aquatic Toxicology and Hazard Assessment , 1981 .

[15]  W. Eckhoff,et al.  Monitoring of environmental fingerprints of alcohol ethoxylates in Europe and Canada. , 2006, Ecotoxicology and environmental safety.

[16]  Nagamany Nirmalakhandan,et al.  Toxicity of mixtures of organic chemicals to microorganisms , 1994 .

[17]  S. Talmage Environmental and Human Safety of Major Surfactants: Alcohol Ethoxylates and Alkylphenol Ethoxylates , 1994 .

[18]  A stream mesocosm study on the ecological effects of a C12-15 linear alcohol ethoxylate surfactant. , 2004, Ecotoxicology and environmental safety.

[19]  D. T. Stanton,et al.  Effects of surfactants on the rotifer, Brachionus calyciflorus, in a chronic toxicity test and in the development of qsars , 1997 .

[20]  G. Suter,et al.  Species Sensitivity Distributions in Ecotoxicology , 2001 .

[21]  P. Dorn,et al.  Chronic toxicity of a homologous series of linear alcohol ethoxylate surfactants to Daphnia magna in 21 day flow‐through laboratory exposures , 1999 .

[22]  Gary M. Rand,et al.  Fundamentals of aquatic toxicology: effects, environmental fate, and risk assessment , 1995 .

[23]  Marilynn D. Hoglund,et al.  Use of joint toxic response to define the primary mode of toxic action for diverse industrial organic chemicals , 1995 .

[24]  W. Eckhoff,et al.  A comparison of alcohol ethoxylate environmental monitoring data using different analytical procedures , 2006, Environmental toxicology and chemistry.

[25]  D. Versteeg,et al.  A laboratory-scale model for evaluating effluent toxicity in activated sludge wastewater treatment plants , 1990 .

[26]  Mj Taylor Effect of Diet on the Sensitivity of Daphnia magna to Linear Alkylbenzene Sulfonate , 1985 .

[27]  Davidson,et al.  Responses of aquatic communities to 25-6 alcohol ethoxylate in model stream ecosystems. , 2000, Aquatic toxicology.

[28]  D. H. Davidson,et al.  Validation of a four‐day Ceriodaphnia toxicity test and statistical considerations in data analysis , 1991 .

[29]  R. Schwarzenbach,et al.  Baseline toxicity (narcosis) of organic chemicals determined by in vitro membrane potential measurements in energy-transducing membranes. , 2002, Environmental science & technology.

[30]  T Wind,et al.  Ecotoxicity quantitative structure-activity relationships for alcohol ethoxylate mixtures based on substance-specific toxicity predictions. , 2006, Ecotoxicology and environmental safety.

[31]  R. A. Rapaport,et al.  Prediction of consumer product chemical concentrations as a function of publicly owned treatment works treatment type and riverine dilution , 1988 .

[32]  M. Lewis,et al.  Environmental modification of the photosynthetic response of lake plankton to surfactants and significance to a laboratory-field comparison , 1986 .

[33]  R. Brereton,et al.  SAS (statistical analysis system) , 1986 .

[34]  A. Maki Correlations Between Daphnia magna and Fathead Minnow (Pimephales promelas) Chronic Toxicity Values for Several Classes of Test Substances , 1979 .

[35]  R. Lizotte,et al.  The effects of a C12–13 linear alcohol ethoxylate surfactant on periphyton, macrophytes, invertebrates and fish in stream mesocosms , 1997 .

[36]  T. Federle,et al.  Fate of free and linear alcohol-ethoxylate-derived fatty alcohols in activated sludge. , 2006, Ecotoxicology and environmental safety.

[37]  Tom C. J. Feijtel,et al.  Predicted no‐effect concentrations and risk characterization of four surfactants: Linear alkyl benzene sulfonate, alcohol ethoxylates, alcohol ethoxylated sulfates, and soap , 1999 .

[38]  D. Versteeg,et al.  A statistical procedure for modeling continuous toxicity data , 1992 .

[39]  D. Robaugh,et al.  Derivatization LC/MS for the simultaneous determination of fatty alcohol and alcohol ethoxylate surfactants in water and wastewater samples. , 2001, Environmental science & technology.

[40]  W. Eckhoff,et al.  Removal and environmental exposure of alcohol ethoxylates in US sewage treatment. , 2006, Ecotoxicology and environmental safety.

[41]  A. Leo,et al.  Substituent constants for correlation analysis in chemistry and biology , 1979 .

[42]  S. Belanger,et al.  Acute and chronic aquatic toxicity structure-activity relationships for alcohol ethoxylates. , 2003, Ecotoxicology and environmental safety.

[43]  R. Lizotte,et al.  Responses of fish exposed to a C9--11 linear alcohol ethoxylate nonionic surfactant in stream mesocosms , 1997 .

[44]  Edwin J. Routledge,et al.  Estrogenic activity of surfactants and some of their degradation products assessed using a recombinant yeast screen , 1996 .

[45]  Scott E. Belanger,et al.  Understanding single‐species and model ecosystem sensitivity: Data‐based comparison , 1999 .

[46]  P. Dorn,et al.  Predicting the sorption of fatty alcohols and alcohol ethoxylates to effluent and receiving water solids. , 2006, Ecotoxicology and environmental safety.

[47]  H. Könemann,et al.  Fish toxicity tests with mixtures of more than two chemicals: a proposal for a quantitative approach and experimental results. , 1981, Toxicology.

[48]  Damià Barceló,et al.  Analysis and Fate of Surfactants in the Aquatic Environment , 2003 .

[49]  M. Servos REVIEW OF THE AQUATIC TOXICITY, ESTROGENIC RESPONSES AND BIOACCUMULATION OF ALKYLPHENOLS AND ALKYLPHENOL POLYETHOXYLATES , 1999 .

[50]  P. Dorn,et al.  Assessing the effects of a C14-15 linear alcohol ethoxylate surfactant in stream mesocosms. , 1996, Ecotoxicology and environmental safety.

[51]  Drew C. McAvoy,et al.  Association of Linear Alkylbenzenesulfonates with Dissolved Humic Substances and Its Effect on Bioavailability , 1996 .

[52]  H. Könemann Quantitative structure-activity relationships in fish toxicity studies. Part 1: relationship for 50 industrial pollutants. , 1981, Toxicology.

[53]  D. Roberts QSAR issues in aquatic toxicity of surfactants. , 1991, The Science of the total environment.