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Aquatic Toxicology
Volume 79, Issue 3, 12 September 2006, Pages 268-277
 
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doi:10.1016/j.aquatox.2006.06.015    How to Cite or Link Using DOI (Opens New Window)
Copyright © 2006 Elsevier B.V. All rights reserved.

Larval exposure to environmentally relevant mixtures of alkylphenolethoxylates reduces reproductive competence in male fathead minnows

Travis J. Bistodeaua, Larry B. Barberb, Stephen E. Bartella, Roberto A. Cediela, Kent J. Grovea, Jacob Klaustermeiera, Janet C. Woodarda, Kathy E. Leec and Heiko L. Schoenfussa, Corresponding Author Contact Information, E-mail The Corresponding Author

aDepartment of Biological Sciences, Saint Cloud State University, 720 Fourth Avenue South, St. Cloud, MN 56301, United States bU.S. Geological Survey, 3215 Marine Street, Boulder, CO 80303, United States cU.S. Geological Survey, 2280 Woodale Drive, Mounds View, MN 55112, United States

Received 8 April 2006; 
revised 22 June 2006; 
revised 23 June 2006. 
Available online 30 June 2006.

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Abstract

The ubiquitous presence of nonylphenolethoxylate/octylphenolethoxylate (NPE/OPE) compounds in aquatic environments adjacent to wastewater treatment plants (WWTP) warrants an assessment of the endocrine disrupting potential of these complex mixtures on aquatic vertebrates. In this study, fathead minnow larvae were exposed for 64 days to a mixture of NPE/OPE, which closely models the NPE/OPE composition of a major metropolitan WWTP effluent. Target exposure concentrations included a total NPE/OPE mixture load of 200% of the WWTP effluent concentration (148 μg/L), 100% of the WWTP effluent concentration (74 μg/L) and 50% of the WWTP effluent concentration (38 μg/L). The NPE/OPE mixture contained 0.2% 4-t-octylphenol, 2.8% 4-nonylphenol, 5.1% 4-nonylphenolmonoethoxylate, 9.3% 4-nonylphenoldiethoxylate, 0.9% 4-t-octylphenolmonoethoxylate, 3.1% 4-t-octylphenoldiethoxylate, 33.8% 4-nonylphenolmonoethoxycarboxylate, and 44.8% 4-nonylphenoldiethoxycarboxylate. An additional exposure of 5 μg/L 4-nonylphenol (nominal) was conducted. The exposure utilized a flow-through system supplied by ground water and designed to deliver consistent concentrations of applied chemicals. Following exposure, larvae were raised to maturity. Upon sexual maturation, exposed male fish were allowed to compete with control males in a competitive spawning assay. Nest holding ability of control and exposed fish was carefully monitored for 7 days. All male fish were then sacrificed and analyzed for plasma vitellogenin, developmental changes in gonadal tissues, alterations in the development of secondary sexual characters, morphometric changes, and changes to reproductive behavior. When exposed to the 200% NPE/OPE treatment most larvae died within the first 4 weeks of exposure. Both the 100% and 50% NPE/OPE exposures caused a significant decrease in reproductive behavior, as indicated by an inability of many of the previously exposed males to acquire and hold a nest site required for reproduction. In contrast, the 5 μg/L 4-nonylphenol exposure resulted in significantly enhanced reproductive behavior compared to that of control males and a majority of the nesting sites were held by previously exposed males. No significant change in the development of gonadal tissues was observed. The 100% NPE/OPE exposure resulted in a significant reduction in the gonadal somatic index and in the prominence of secondary sexual characteristics of exposed larvae. This study indicates that NPE/OPE mixtures have an effect on the reproductive competence of previously exposed male fathead minnows. In addition, 4-nonylphenol concentrations utilized in all exposures were below regulatory guidelines, suggesting that evaluation of 4-nonylphenol alone may not be sufficient for identifying potentially adverse effects of this suite of compounds usually found as mixtures in the aquatic environment.

Keywords: Alkylphenolethoxylates; Nonylphenolethoxylates; Octylphenolethoxylate; Fathead minnow; Reproduction; Wastewater treatment plant effluent

Article Outline

1. Introduction
2. Material and methods
2.1. Chemicals and exposure
2.2. Exposure animals
2.3. Exposure overview
2.4. Endpoints
2.4.1. Survival
2.4.2. Sex ratio
2.4.3. Vitellogenin analysis
2.4.4. Gonadal somatic index
2.4.5. Histopathology
2.4.6. Secondary sexual characters
2.4.7. Competitive spawning assay
2.5. Statistical analysis
3. Results
3.1. Survival
3.2. Sex ratio
3.3. Vitellogenin analysis
3.4. Gonadal somatic index
3.5. Histological analysis
3.6. Secondary sexual characters
3.7. Competitive spawning assay
4. Discussion
Acknowledgements
References





Aquatic Toxicology
Volume 79, Issue 3, 12 September 2006, Pages 268-277
 
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