RATL: A Database of Reptile and Amphibian Toxicology Literature

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Table 2 - Field Studies - 15 Contaminant a Species Code b Lifestage Exposure Route f Study Endpoint g Pesticide Appl. Rate Location, Area, State, Country c endrin RATE adult PESTAPP MORT 0.047 mg/L artificially evacuated pool, unknown estradiol ALMI juvenile ENVIRON PHYSIO L. Apopka and L.Woodruff, FL, USA Study Date Effects de < 1979 Wild population had strong leg cramps and paralysis of limbs and died. 7 weeks after treatment repopulated pond. < 1995 Synthesis of 17ß-estradiol was sig. dif. when ovaries from the cont. and control lakes were compared in vitro. Additionally, testes obtained from the cont. lake, L. Apopka, synthesized significantly higher conc. Reference k Wohlgemuth and Trnkova 1979 k Guillette et al. 1995 ethyl guthion RACA tadpole PESTAPP MORT 0.22 , 0.90 kg/ha pond (0.025 ha), unknown < 1963 No mortality after 24 h. Mulla et al. 1963 k fenitrothion BUAM not specified PESTAPP MORT 0.14 kg/ha pond, NB, CAN < 1969 No mortality. Pearce and Teeple 1969 k fenitrothion RACA tadpole PESTAPP MORT 0.14 kg/ha (2 appl.) Fundy National Park, NB, CAN < 1974 No mortality. Rick and Price 1974 k fenitrothion RACL not specified PESTAPP MORT 0.14 kg/ha pond, NB, CAN < 1969 No mortality. Pearce and Teeple 1969 k fenitrothion RASE adult ENVIRON POPSUR northern NB, CAN 1991 Areas that have been heavily sprayed over the previous 5 yrs had a lower abundance of mink frogs. McAlpine 1997a fenitrothion RASE adult PESTAPP POPSUR 210 g /ha (2 9 lakes and ponds within 1991 Low spray areas (not sprayed after McAlpine et al. 1998 appl.) forested areas, Northern 1987): mean frog density=7.09 and New Brunswick, NB, CAN 20.95; Medium spray areas (sprayed in 1990 only): mean frog density= 65.43 and 12.05; High spray areas: mean frog densities= 0.71, 3.52, 3.86, 3.99, 6.15. fenitrothion RASY adult PESTAPP MORT 0.14 kg/ha (2 appl.) Fundy National Park, NB, CAN < 1974 No mortality. Rick and Price 1974 k fenitrothion RASY tadpole PESTAPP MORT 0.14 kg/ha (2 appl.) Fundy National Park, NB, CAN < 1974 No mortality. Rick and Price 1974 k fenitrothion XXFR adult PESTAPP MORT 0.5 kg/ha rice fields, India < 1973 100% mortality. Thirumurthi et al. 1973 k fenoprop XXFR adult PESTAPP POPSUR Long Pond, NY, USA 1957 No obvious effect on local population of frogs, no change in abundance. Pierce 1958 fenoprop XXFR adult PESTAPP POPSUR Long Pond, NY, USA 1959 No effect noted in frogs, obvious population changes were not evident. Pierce 1960 fenoprop XXXT adult PESTAPP POPSUR Long Pond, NY, USA 1957 No obvious effect on local abundance of adults. Pierce 1958 fenthion XXFR adult PESTAPP POPSUR 24 L/12 Njoro Dam and Gicheha 1988 Populations were not affected after Keith et al. 1994 min.at150 farm, E. Africa, Kenya treatments (7.7-15 ppb for 20 and km/h 30 min). fenthion XXFR adult PESTAPP MORT 0.5 kg/ha rice field, India < 1973 100 % mortality. Thirumurthi et al. 1973 k
Contaminant a Species Code b Lifestage Exposure Route f Study Endpoint g Pesticide Appl. Rate fenthion XXFR tadpole PESTAPP POPSUR 24 L/12 min at150 km/h Table 2 - Field Studies - 16 Location, Area, State, Country c Njoro Dam and Gicheha farm, E. Africa, Kenya Study Date Effects de 1988 Tadpoles were not affected after treatments (17ppb exposure for 10 min). Reference k Keith et al. 1994 FLII MLO RACA adult PESTAPP MORT 2.24 L/ha (4 sprays) pond, Butte Co., CA, USA 1971 No mortality. Hagen et al. 1973 k flocoumafen CYAE adult ENVIRON POPSUR Mana Island, New Zealand 1986-93 Captures increased significantly between 85/86 and 86/87 then fell between 86/87 and 87/88; subsequently, numbers caught remained low and fell again between 89/90 and 90/91 but increased between 90/91 and 91/92. Newman 1994 flocoumafen CYMA adult ENVIRON POPSUR Mana Island, New Zealand 1986-93 After 1989 (date of mouse eradication program) there was a sig. increase in the number of individuals caught. No toxicity data given. Newman 1994 flocoumafen HOMA adult ENVIRON POPSUR Mana Island, New Zealand 1986-93 After 1989 (date of mouse eradication program) there was a sig. increase in the number of individuals caught. No toxicity data given. Newman 1994 flocoumafen LENI adult ENVIRON POPSUR Mana Island, New Zealand 1986-93 Capture rates were usually low, yet declined significantly between 1985/1986 and 86/87 and between 86/87 and 87/88. From 88/89 captures rose, but fell significantly again between 90/91 and 91/92. No tox data given. Newman 1994 fluoranthene, UV AMMA larvae IMMER MORT Corvallis, OR, USA
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RATL: A Database of Reptile and Amp
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RATL: A Database of Reptile and Amp
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ABSTRACT Many amphibian and reptile
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PRÉFACE De nombreuses populations
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TABLE OF CONTENTS Abstract………
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LIST OF TABLES Table 1: Contaminant
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INTRODUCTION Why is there a need fo
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Limitations of RATL The RATL databa
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Contaminant a Species Code b Lifest
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Table 1- Field Residues - 20 Contam
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Table 1- Field Residues - 54 Contam
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Contaminant a Species Code b tar XE
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Table 4: Laboratory studies not inc
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Contaminant a Species Code b Cd AMG
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Table 5: FETAX data. [FETAX (Frog E
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Table 5 - FETAX Studies - 3 Contami
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Contaminant a Contaminant b Concent
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Table 5 - FETAX Studies - 11 Contam
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Table 6: pH study data. (Studies th
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Table 6 - pH Studies - 3 Species Co
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Species Code b Lifestage Study Endp
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Table 6 - pH Studies - 13 Species C
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Table 7: Reviews of primary literat
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Table 7 - Reviews - 3 Review Title
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Table 8 - Population Status - 2 Pop
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Table Notes Note a : see Appendix 2
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References - 2 Anderson, L.M. and R
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References - 4 Bantle, J.A., D.J. F
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References - 6 Beresford, W.A. , M.
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References - 8 Bishop, C.A, P. Ng,
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References - 10 Bragg, A.N. 1964. M
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References - 12 Burke, E.M. and F.H
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References - 14 Chattopadhyay, D.P.
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References - 16 Cooke, A.S. 1974. T
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References - 18 Dash, M.C. and A.K.
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References - 20 DeWitt, J.B., D.G.
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References - 22 Dutta, S.K. and P.
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References - 24 Elisyeyeva, K.H., H
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References - 26 Fontenot, L., C. Ro
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References - 28 Frisbie, M.P. and R
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References - 30 Godet, F., M. Babut
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References - 32 Gunther, R. and J.
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References - 34 Harfenist, A., T. P
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References - 36 Herkovits, J. and C
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References - 38 Hota, A. K. and M.C
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References - 40 Johnson, C.R. 1972a
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References - 42 Karns, D.R. 1984. T
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References - 44 Kraskowski, H.V., K
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References - 46 Leblanc, G.A. and L
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References - 48 Lotshaw, D.P. 1977.
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References - 50 Massot, M., J. Clob
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References - 52 Mendonca, M., J. Sh
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References - 54 Munro, D.F. 1949. E
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References - 56 Oliveira, E.M., D.V
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References - 58 Paulov, S. 1977b. T
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References - 60 Pierce, M.E. 1958.
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References - 62 Raj, T.P., A. Jeban
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References - 64 Rolfe, G. L., A. Ha
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References - 66 Sassaman, J.F. 1978
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References - 68 Semlitsch, R.D. and
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References - 70 Sparling, D.W., T.P
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References - 72 Surova, G.S. and A.
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References - 74 Tomar, V. and A. K.
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References - 76 Vijverberg, H.P.M.,
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References - 78 White, D.H. and A.J
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References - 80 Wyman, R.L. and J.
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Appendix 1a: Species codes in alpha
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Appendix 1a - Species Codes - 3 Cla
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Appendix 1a - Species Codes - 11 Cl
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Appendix 1a - Species Codes - 13 Cl
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Appendix 1b - Species Common Names
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Appendix 1c - Species Scientific Na
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Appendix 2a: Contaminant codes foun
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Appendix 2a - Contaminant Codes - 3
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Appendix 2b: Contaminants sorted by
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Appendix 2b - Contaminant Type - 3
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Appendix 4: Descriptions of exposur
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Appendix 6a: Glossary of Abbreviati
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Appendix 6b: Relevant biological an
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Appendix 6b - Glossary of RATL term
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RATL: A Database of Reptile and Amphibian Toxicology Literature

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