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Last modified
8/11/2009 11:32:55 AM
Creation date
8/10/2009 3:11:54 PM
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UCREFRP
UCREFRP Catalog Number
7200
Author
Odenkirchen, E. W. and R. Eisler.
Title
Chlorpyrifos Hazards to Fish, Wildlife, and Invertebrates
USFW Year
1988.
USFW - Doc Type
A Synoptic Review.
Copyright Material
NO
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<br />lABORATORY INVESTIGATIONS <br /> <br />AQUATIC ORGANISMS <br /> <br />During 96-hour toxicity tests, several species of freshwater and marine <br />invertebrates and fishes died at chlorpyrifos concentrations between 0.035 and <br />0.58 ug/l. lC-50 (96-hour) values, in ug chlorpyrifos/l, for sensitive <br />species tested were 0.035 for mysid shrimp, Mysidopsis bahia; 0.11 for <br />amphipod, Gammarus lacustris; 0.13 for fathead minnow, Pimephales promelas; <br />0.38 for stonefly, pteronarcella badia; and 0.58 for striped bass, Morone <br />saxatilis; (Mayer and Ellersieck 1986; Table 3). Toxicity was usually greater <br />at elevated temperatures and at increasing pH levels (Johnson and Finley <br />1980). In general, arthropods were the most sensitive group assayed and <br />molluscs the most tolerant (Borthwick and Walsh 1981; Table 3). The bullfrog <br />(Rana catesbeiana) also appears to be comparatively tolerant to chlorpyrifos, <br />as judged by a single oral lD-50 value of >400 mg/kg body weight (Hudson et <br />a 1. 1984). <br /> <br />Sublethal effects of chlorpyrifos exposure have been documented for many <br />species of freshwater and marine fauna; they include inhibition of <br />cholinesterase (ChE) activity levels in brain and hematopoietic organs, <br />sluggishness, motor incoordination, delayed maturation and growth, <br />reproductive impairment, and reduced feed intake (Rongsriyan et al. 1968; <br />Thirugnanam and Forgash 1977; Marshall and Roberts 1978; Tagatz et al. 1982; <br />Jarvinen et al. 1983; EPA 1985,1986; Goodman et al. 1985b; Norberg and Mount <br />1985; Hansen et al. 1986). Reproductive impairment, for example, was observed <br />in Daphnia magna at 0.08 ug chlorp.yrifos/l (EPA 1985). Reduction in setting <br />rate was shown in oyster larvae after exposure to 0.1 ug/l for 8 days (Tagatz <br />et al. 1982). In fathead minnows exposed to 0.12 ug chlorpyrifos/l for 200 <br />days, ChE activity was significantly reduced, fecundity was reduced, <br />maturation delayed and, in second generation fish, growth and maturation were <br />reduced (Jarvinen et al. 1983). Equilibrium loss was documented in 50% of <br />brown shrimp (Penaeus aztecus) after exposure to 0.32 ug chlorpyrifos/l for 24 <br />hours (Marshall and Roberts 1978). Growth of the California grunion <br />(leuresthes tenuis) was reduced 20% in an early life stage during immersion in <br />0.5 ug chlorpyrifos/l for 35 days and 26% in fry after exposure to 1.0 ug/l <br />for 26 days (Goodman et al. 1985b). Additional and more comprehensive data on <br />sublethal effects of chlorpyrifos to aquatic biota are listed elsewhere (EPA <br />1986). <br /> <br />6 <br />
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