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RATL: A Database of Reptile and Amphibian Toxicology Literature

RATL: A Database of Reptile and Amphibian Toxicology Literature

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Table 2 - Field Studies - 31<br />

Contaminant a Species<br />

Code b<br />

Lifestage Exposure<br />

Route f<br />

Study<br />

Endpoint g<br />

Pesticide<br />

Appl. Rate<br />

Location, Area, State,<br />

Country c<br />

toxaphene/ CHPI adult PESTAPP MORT Walborn Ranch, Tullock<br />

camphechlor<br />

Creek, MT, USA<br />

Study<br />

Date<br />

Effects de<br />

1959 74 were found alive 1 d after<br />

spraying, 67 were found alive 12 d<br />

after spraying, some displayed<br />

symptoms <strong>of</strong> poisoning , a lack <strong>of</strong><br />

coordination, 15 were found dead<br />

(others may have been lost to a<br />

raccoon predator).<br />

Reference k<br />

Finley 1960<br />

toxaphene/<br />

camphechlor<br />

RACA tadpole PESTAPP MORT 0.11, 0.56<br />

kg/ha<br />

field tests, CA, USA < 1962 100 % kill <strong>of</strong> tadpoles.<br />

Mulla 1962 k<br />

toxaphene/<br />

camphechlor<br />

RACA tadpole PESTAPP MORT 0.11, 0.56<br />

kg/ha<br />

pond, CA, USA 1962 0 % mortality at 0.11 kg/ha; 100 %<br />

Mulla 1963<br />

mortality at 0.56 kg/h after 1 d.<br />

k<br />

toxaphene/ RAPI adult PESTAPP MORT Walborn Ranch, Tullock 1959 19 were found dead after spraying. Finley 1960<br />

camphechlor<br />

Creek, MT, USA<br />

toxaphene/<br />

camphechlor<br />

SCHA juvenile PESTAPP MORT 1.12, 2.24<br />

kg/ha<br />

golf course greens < 1962 95 - 98 % control <strong>of</strong> juvenile toads. k<br />

Mulla 1963<br />

toxaphene/ THSI adult PESTAPP MORT Walborn Ranch, Tullock 1959 2 were found dead after spraying. Finley 1960<br />

camphechlor<br />

Creek, MT, USA<br />

trichlorphon GAGA adult PESTAPP PHYSIO 10 kg/ha Canary Isl<strong>and</strong>s, Spain < 1993 High sensitivity to OP <strong>and</strong><br />

extremely slow recovery <strong>of</strong> serum<br />

BChE with respect to other<br />

vertebrate species; high correlation<br />

found between the destructive<br />

biomarker brain AChE <strong>and</strong> the<br />

nondestructive biomarker serum<br />

BChE 24 h after treatment.<br />

Fossi et al. 1995<br />

UV BUBO egg RAD HATSUC Cascade Mntns., OR, USA < 1994 BUBO exhibited reduced hatching<br />

success compared to HYRE.<br />

Blaustein et al. 1994b<br />

UV HYRE egg RAD HATSUC Cascade Mntns., OR, USA < 1994 HYRE experienced greater hatching Blaustein et al. 1994b<br />

success than BUBO <strong>and</strong> RACS.<br />

UV RACS egg RAD HATSUC Cascade Mntns., OR, USA < 1994 RACS exhibited lower hatching<br />

success than HYRE.<br />

Blaustein et al. 1994b<br />

UV-B AMGR embryo RAD HATSUC OR, USA 1994 The hatching success <strong>of</strong> AMGR was<br />

significantly greater under sunlight<br />

lacking UV-B than under unfiltered<br />

sunlight or sunlight filtered to<br />

remove shorter wavelengths but not<br />

UV-B.<br />

Blaustein et al. 1995<br />

UV-B AMTI egg RAD POPSUR CO, USA < 1996 Sig. mortality occurred at UV-B<br />

levels between 95.8 <strong>and</strong> 273<br />

uW/cm 2 .<br />

Carey et al. 1996<br />

UV-B BUBO embryo RAD HATSUC 280-340 nm Rocky Mountain National 1994 No difference in hatching success Corn 1998<br />

UV-B Park, CO, USA<br />

for embryos exposed to 0-100%<br />

ambient UV-B radiation.<br />

UV-B BUBU embryo RAD MORT Sierra de Gredos, Central 1996 UV-B radiation had a detrimental Lizana <strong>and</strong> Pedraza 1998<br />

Spain, Spain<br />

effect on embryo survival.<br />

UV-B BUCA embryo RAD MORT Sierra de Gredos, Central 1996 No difference found between Lizana <strong>and</strong> Pedraza 1998<br />

Spain, Spain<br />

treatments <strong>and</strong> controls.

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