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<br />\ qq 3 oeYR-/r6j et- aJ <br /> <br />cr\.rIH '.J\Jf:~vironmenlal Toxicology and Chemistry. Vol. 13. pp. 101-107. 1994 <br />Printed in the USA. Pergamon Press Ltd. <br /> <br />"lIP <br />077CJY <br />~ <br /> <br />Copyright @ 1993 SET AC <br /> <br />TOXICITY OF CARBARYL AND MALATHION TO TWO FEDERALLY <br />ENDANGERED FISHES, AS ESTIMATED BY REGRESSION AND ANOVA <br /> <br />~ <br /> <br />DANIEL W. BEYERS, *t THOMAS J. KEEFE+ and CLARENCE A. CARLSONt <br />tLarval Fish Laboratory, Department of Fishery and Wildlife Biology and <br />tDepartment of Environmental Health, Colorado State University, Fort Collins, Colorado 80523 <br /> <br />(Received 2 November 1992; Accepted 19 April 1993) <br /> <br />Abstract- Toxicity of technical carbaryl, Sevin@-4-0il, and technical malathion to federally endangered Colorado squaw fish <br />(Ptychocheilus lucius) and bony tail (Gila elegans) was estimated by 4-d renewal-acute and 32-d early life-stage (ELS) tests. Me- <br />dian lethal concentrations were estimated by probit analysis. Effect concentrations for ELS tests were estimated by ANOVA <br />and an alternative procedure using a linear-plateau regression model. Linear-plateau regression estimated a threshold concen- <br />tration above which toxic effects began to occur. Median lethal concentrations and 950/0 confidence limits (in parentheses) for <br />carbaryl, Sevin-4-0il, and malathion were 1.31 (1.23, 1.40), 3.18 (2.87, 3.52), and 9.14 mg/L (8.36, 10.0) for Colorado squaw- <br />fish and 2.02 (1.78, 2.25), 3.31 (3.06, 3.55), and 15.3 mg/L (14.4, 16.4) for bony tail. NOECs for Colorado squawfish were <br />445 /lg/L carbaryl and 1,680 /lg/L malathion. The NOECs for bony tail were 650 /lg/L carbaryl and 990 /lg/L malathion. Thresh- <br />old concentrations for Colorado squawfish in ELS tests were 364 /lg/L carbaryl and 455 /lg/L malathion. Threshold concen- <br />trations for bony tail were 217 /lg/L carbaryl and 521 /lg/L malathion. Estimates of effect concentrations from linear-plateau <br />regression were consistently lower than those estimated by hypothesis testing. Linear-plateau regression models accounted for <br />a significant amount of total variation and adequately described the observed concentration-response relation. <br /> <br />Keywords - Endangered species <br /> <br />Malathion <br /> <br />Carbaryl <br /> <br />INTRODUCTION <br /> <br />The insecticides carbaryl and malathion are used to control <br />grasshopper infestations on rangeland and cropland through- <br />out the western United States. Both chemicals exert their <br />toxic effects by inhibiting the enzyme acetylcholinesterase <br />(AChE), thereby causing disruption of the central nervous <br />system. Insecticides used to control grasshopper infestations <br />may pose a particular threat to fishes because although no- <br />spray buffer zones are observed around aquatic habitats, pes- <br />ticide may be deposited by accidental drift or mobilized from <br />upland areas by runoff [1]. <br />The Colorado squawfish (Ptychocheilus lucius) and bony- <br />tail (Gila elegans) are large minnows that historically oc- <br />curred throughout the Colorado River Basin [2J. Populations <br />of both species have declined as a result of construction of <br />reservoirs and other management practices in the basin [3J. <br />In response to the rapid decline and threat of extinction of <br />these fishes, the U.S. Fish and Wildlife Service authorized <br />listing Colorado squawfish and bony tail as federally endan- <br />gered species in 1967 and 1980, respectively. Although the <br />scarcity and federally endangered status of these fishes have <br />made study of their habits in the wild difficult, some infor- <br />mation on life history and behavior has been collected [4,5J. <br />During the first several months of life (June-October), young <br />Colorado squawfish and bonytail occupy shallow, low-veloc- <br />ity, near-shore habitats. Because these habitats have low rates <br />of water exchange, pesticides deposited in them may be <br />present long enough for toxic effects to occur. Grasshopper <br /> <br />I <br /> <br />, <br /> <br />'To whom correspondence may be addressed. <br />Contribution 55, Larval Fish Laboratory, Colorado State <br />University. <br /> <br />Threshold concentration <br /> <br />Regression <br /> <br />control programs and life histories of Colorado squaw fish <br />and bonytail overlap such that potentially sensitive life stages <br />(<30 d old) are at risk of exposure. <br />Toxicity of carbaryl and malathion to fish and aquatic in- <br />vertebrates has been thoroughly studied [6J, but none of the <br />previously tested fishes is closely related to the native fishes <br />of the Colorado River Basin. Because of uncertainty of pre- <br />dicting the sensitivity of Colorado squaw fish and bonytail to <br />carbaryl and malathion, we estimated toxicity of these chem- <br />icals using prescribed methods for 4-d acute [7J and 32-d early <br />life-stage (ELS) toxicity tests [8]. Data from toxicity tests <br />were analyzed by ANOVA hypothesis testing and an alter- <br />native procedure using a linear-plateau regression model. Ste- <br />phan and Rogers [9J described the computational and <br />conceptual advantages of using regression analysis for con- <br />centration-response data, We present comparisons of the ef- <br />fect-concentration estimates obtained by the two alternative <br />statistical methods. The purpose of this study was to estimate <br />the toxicity of technical carbaryl, Sevin@-4-0il (a formula- <br />tion of carbaryl), and technical malathion to Colorado <br />squawfish and bony tail. The objectives were to (a) estimate <br />4-d median lethal concentrations, (b) estimate and compare <br />effect concentrations for survival and growth, and (c) com- <br />pare estimates of effect concentrations obtained by hypoth- <br />esis testing and regression analysis. <br /> <br />MATERIALS AND METHODS <br />Experimental animals <br /> <br />Fertilized eggs of Colorado squawfish and bony tail were <br />obtained from Dexter National Fish Hatchery (Dexter, NM). <br />Hatchery researchers artificially induced spawning of Col- <br />orado squaw fish [1OJ and bony tail [11], and fertilized eggs <br /> <br />101 <br />