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45 <br />residue half-life in Daphnia was 44 h; however, neither <br />trout nor Daphnia appeared to degrade HCB sig- <br />nificantly. Preliminary food chain studies indicated <br />that bluegills accumulated HCB to a level 1 to 2 times <br />that observed for DDT when they were fed Daphnia <br />containing residues of 50 ng/g. In comparison, <br />bluegills accumulated residues about half that of DDT <br />in water exposure at concentrations of only 0.05 to <br />0.15,ug/L. After 5 days of incubation, both aerobically <br />and anaerobically, hydrosoil samples inoculated with <br />ring labeled HCB showed an 80 to 90% loss of mate- <br />rial. Although phenolic volatilization may be <br />responsible for some of this loss, degradation products <br />were revealed, one of which has been tentatively iden- <br />tified as pentachlorophenol. <br />NOTE: Flow-through toxicity tests produced <br />TILC50's ranging from 0.54 mg/L for rainbow trout to <br />6.60 mg/L for fathead minnows. Cumulative toxicity <br />indices ranged only from 1.20 to 3.14, indicating little <br />or no cumulative toxic action. Sublethal effects were <br />prominent in flow-through tests at concentrations <br />considerably below acutely lethal levels. Such effects <br />included early cessation of feeding, hypersensitivity, <br />and erratic swimming, followed by a loss of motor <br />function, hemorrhage in the dorsal fin region, and <br />occurrence of a characteristic "broken back" syn- <br />drome. This condition remained for extended periods <br />until terminated by death from secondary causes. <br />HOUGHTO-SAFE 1120 KEPONE <br />Chemical Name: Mixture of tri-aryl phosphate esters <br />containing phenyl, tolyl (cresyl), xylyl, and ethyl Chemical Name: Decachlorooctahydro-1,3,4-metheno- <br />substituted benzene groups 2H-cyclobuta [cd] pentalen-2-one <br />Alternate Names: Tri-aryl phosphate ester Alternate Names: CAS 143-50-0, ENT-16391, GC- <br />1899,Chlordecone <br />Principal Use: Hydraulic fluids <br />Sample Description: Commercial formulations, 100% <br />SUMMARY OF ACUTE TOXICITY <br />96-h LC50 <br />Test Stage or Temp 95% CI <br />organism wt (g) (C) (mg/L) <br />G. pseudolimnaeus M 20 0.708 <br />0.53-0.92 <br />Coho salmon 0.4 12 1.2b <br /> 0.9-1.5 <br />Rainbow trout 1.4 12 1.7 <br /> 1.2-2.5 <br />Brook trout 4.0 12 3.6b <br /> 3.1-4.2 <br />Fathead minnow 1.2 17 35 <br /> 24.49 <br />Principal Use: Insecticide <br />Sample Description: Technical material, 90.7% <br />SUMMARY OF ACUTE TOXICITY <br />96-h LC50 <br />Test Stage or Temp 95% CI <br />organism wt (g) (C) (µg/L) <br />Daphnia magna 11 17 2608 <br />200-345 <br />G. pseudolimnaeus M 17 180 <br />110-290 <br />Chironomus I4 22 320a <br />220-450 <br />Rainbow trout 1.1 12 30 <br />24-38 <br />Channel catfish 1.6 18 225 <br />Channel catfish 1.6 21 43 Bluegill <br />31-59 <br />Bluegill <br />0.6 20 12 <br />8-19 <br />Yellow perch 7.2 12 0.54a.b <br />0.42-0.70 <br />aTested in hard water. <br />bFlow-through toxicity test. <br />2-5 24 72 <br />Redear sunfish 1.0 24 44 <br />41-47 <br />848-h EC50. <br />NOTE: Variation in water hardness from 44 to 272 <br />ppm did not alter toxicity to rainbow trout. An in- <br />crease in temperature from 7 ° to 29 °C produced a 4.8- <br />fold increase in toxicity.