Literature DB >> 15772881

Assessing contaminant sensitivity of endangered and threatened aquatic species: part I. Acute toxicity of five chemicals.

F J Dwyer1, F L Mayer, L C Sappington, D R Buckler, C M Bridges, I E Greer, D K Hardesty, C E Henke, C G Ingersoll, J L Kunz, D W Whites, T Augspurger, D R Mount, K Hattala, G N Neuderfer.   

Abstract

Assessment of contaminant impacts to federally identified endangered, threatened and candidate, and state-identified endangered species (collectively referred to as "listed" species) requires understanding of a species' sensitivities to particular chemicals. The most direct approach would be to determine the sensitivity of a listed species to a particular contaminant or perturbation. An indirect approach for aquatic species would be application of toxicity data obtained from standard test procedures and species commonly used in laboratory toxicity tests. Common test species (fathead minnow, Pimephales promelas; sheepshead minnow, Cyprinodon variegatus; and rainbow trout, Oncorhynchus mykiss) and 17 listed or closely related species were tested in acute 96-hour water exposures with five chemicals (carbaryl, copper, 4-nonylphenol, pentachlorophenol, and permethrin) representing a broad range of toxic modes of action. No single species was the most sensitive to all chemicals. For the three standard test species evaluated, the rainbow trout was more sensitive than either the fathead minnow or sheepshead minnow and was equal to or more sensitive than listed and related species 81% of the time. To estimate an LC50 for a listed species, a factor of 0.63 can be applied to the geometric mean LC50 of rainbow trout toxicity data, and more conservative factors can be determined using variance estimates (0.46 based on 1 SD of the mean and 0.33 based on 2 SD of the mean). Additionally, a low- or no-acute effect concentration can be estimated by multiplying the respective LC50 by a factor of approximately 0.56, which supports the United States Environmental Protection Agency approach of multiplying the final acute value by 0.5 (division by 2). When captive or locally abundant populations of listed fish are available, consideration should be given to direct testing. When direct toxicity testing cannot be performed, approaches for developing protective measures using common test species toxicity data are available.

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Year:  2005        PMID: 15772881     DOI: 10.1007/s00244-003-3038-1

Source DB:  PubMed          Journal:  Arch Environ Contam Toxicol        ISSN: 0090-4341            Impact factor:   2.804


  8 in total

1.  Toxicity of pentachlorophenol to native aquatic species in the Yangtze River.

Authors:  Xiaowei Jin; Jinmiao Zha; Yiping Xu; John P Giesy; Zijian Wang
Journal:  Environ Sci Pollut Res Int       Date:  2011-09-01       Impact factor: 4.223

2.  Molecular characterization of heat-shock protein 90 gene and its expression in Gobiocypris rarus juveniles exposed to pentachlorophenol.

Authors:  Qiuping Liu; Shuting Huang; Chuan Deng; Li Xiong; Xiang Gao; Yun Chen; Chunqing Niu; Yan Liu
Journal:  Fish Physiol Biochem       Date:  2015-06-29       Impact factor: 2.794

3.  Acute toxicity of copper, lead, cadmium, and zinc to early life stages of white sturgeon (Acipenser transmontanus) in laboratory and Columbia River water.

Authors:  David W Vardy; Robert Santore; Adam Ryan; John P Giesy; Markus Hecker
Journal:  Environ Sci Pollut Res Int       Date:  2014-03-29       Impact factor: 4.223

4.  Seasonal availability and sensitivity of two field-collected mayflies for the development of a standardized toxicity test.

Authors:  Brandi S Echols; R J Currie; D S Cherry; J R Voshell
Journal:  Environ Monit Assess       Date:  2012-05-04       Impact factor: 2.513

5.  Variability in the dynamics of mortality and immobility responses of freshwater arthropods exposed to chlorpyrifos.

Authors:  Mascha N Rubach; Steven J H Crum; Paul J Van den Brink
Journal:  Arch Environ Contam Toxicol       Date:  2010-08-15       Impact factor: 2.804

6.  Histopathological and estrogen effect of pentachlorophenol on the rare minnow (Gobiocypris rarus).

Authors:  Xiaozheng Zhang; Li Xiong; Yan Liu; Chuan Deng; Siyu Mao
Journal:  Fish Physiol Biochem       Date:  2013-11-12       Impact factor: 2.794

7.  Sensitivity of early life stages of white sturgeon, rainbow trout, and fathead minnow to copper.

Authors:  David W Vardy; Johanna Oellers; Jon A Doering; Henner Hollert; John P Giesy; Markus Hecker
Journal:  Ecotoxicology       Date:  2012-11-05       Impact factor: 2.823

8.  Acute sensitivity of white sturgeon (Acipenser transmontanus) and rainbow trout (Oncorhynchus mykiss) to copper, cadmium, or zinc in water-only laboratory exposures.

Authors:  Robin D Calfee; Edward E Little; Holly J Puglis; Erinn Scott; William G Brumbaugh; Christopher A Mebane
Journal:  Environ Toxicol Chem       Date:  2014-09-05       Impact factor: 3.742

  8 in total

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