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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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Contaminant a Species<br />

Code b<br />

Lifestage Exposure<br />

Route f<br />

Table 4 - Laboratory Studies - 28<br />

Study<br />

Endpoint g Temp h pH Contaminant<br />

Concentration<br />

e<br />

dimethoate RATI egg IMMER DEVOBS 30-38 0.0001- 0.001<br />

%<br />

dimethoate RATI egg IMMER DEVOBS 30-38 0.0001-<br />

0.0009 %<br />

Results, Residues, Effects <strong>and</strong>/or Remarks d,e<br />

Delayed <strong>and</strong> deceased incidence <strong>of</strong> metamorphosis in exposed<br />

eggs; < 0.0002 % no effects.<br />

Eggs treated with 0.0001 - 0.0009 % exhibited increased time<br />

to metamorphosis, decreased average larval length at<br />

metamorphosis <strong>and</strong> conc. dependent mortality. No eggs<br />

treated with 0.001 - 0.009 % dimethoate reached<br />

Reference k<br />

Mohanty-Hejmadi <strong>and</strong> Dutta<br />

1981 k<br />

Dutta <strong>and</strong> Mohanty-Hejmadi<br />

1978 k<br />

dimethoate RATI tadpole IMMER DEVOBS 30-38<br />

metamorphosis.<br />

80% metamorphosed at 0.001 %; < 0.001 no effect. Delayed Mohanty-Hejmadi <strong>and</strong> Dutta<br />

(limb bud)<br />

metamorphosis at 0.0001 - 0.001 %.<br />

1981 k<br />

dimethoate RATI tadpoles IMMER DEVOBS 30-38 0.0001- Increased exposure conc. lead to increased time to<br />

Dutta <strong>and</strong> Mohanty-Hejmadi<br />

0.0009 % metamorphosis <strong>and</strong> decreased avg length at metamorphosis.<br />

1978 k<br />

dimethoate XELA < 2 d IMMER MORT 20 100 d NOEL: Mortality= 1; Development= 32; Growth= 32<br />

mg/L.<br />

Slo<strong>of</strong>f <strong>and</strong> Canton 1983 k<br />

dimethyl disulfide AMTI adult DERMAL BEHAV 0.1- 0.5 M Lavage with dimethyl disulfide decreased response to<br />

dimethyl disulfide in behaviour tests.<br />

Mason <strong>and</strong> Morton 1982<br />

dinitrocresol XELA < 2 d IMMER MORT 20 100 d NOEL: Mortality= 0.32; Development= 0.32; Growth=<br />

Slo<strong>of</strong>f <strong>and</strong> Canton 1983<br />

0.32 mg/L.<br />

k<br />

dinocap XELA adult IMMER MORT 0-1.0 mg/L Adult vs. development toxicity ratios varied for chemical <strong>and</strong> Daston et al. 1991<br />

between other animal species tested. A/D ratio=>10.<br />

dinocap XELA embryo IMMER MORT 0-10 mg/L Death <strong>and</strong> defects were noted in embryos exposed for 4 d<br />

post-fertilization.<br />

Daston et al. 1991<br />

dinoseb XELA adult IMMER MORT 0- 0.1 mg/L Adult vs. development toxicity ratios varied for chemical <strong>and</strong> Daston et al. 1991<br />

between other animal species tested. A/D ratio=>5.<br />

dinoseb XELA embryo IMMER MORT 0- 0.1 mg/L All tadpoles died from exposure. Daston et al. 1991<br />

diphacin PICA adult ORAL MORT fed avg. <strong>of</strong><br />

14.74 mg<br />

18 snakes showed no observable effects when fed rats. Brock 1965<br />

diquat RAPI egg IMMER DEVOBS 18 100 Reduced viability <strong>and</strong> increased exogastrulation. None<br />

survived beyond 14 d post-hatch.<br />

Bimber <strong>and</strong> Mitchell 1978 k<br />

diquat RAPI embryo<br />

(gastrula)<br />

IMMER DEVOBS 2-10 mg/L 15 d old embryo exhibited increased survival over gastrula<br />

stage embryos (78 % vs 34 % respectively). At 10 mg/L > 70<br />

% survival 16 d post treatment in 2 <strong>and</strong> 5 mg/L.<br />

Dial <strong>and</strong> Dial 1987 k<br />

diquat RATE adult INJECT PHYSIO 20-25 4 µL/g body wt Labeled compounds were taken up by various tissues. Lindquist et al. 1988<br />

diquat XELA embryo<br />

(tail bud)<br />

IMMER DEVOBS 0.5-2.0 Reduced body size <strong>and</strong> pigmentation; 15 ppm produced some<br />

distortion in body shape; 95 % survival at 0.5 ppm; 20 %<br />

survival at 20 ppm.<br />

Anderson <strong>and</strong> Prahlad 1976 k<br />

diquat, nabam XELA embryo<br />

(tail bud)<br />

IMMER PHYSIO 0.75 diquat/2<br />

nabam<br />

100 % mortality within 6 d. Size <strong>of</strong> larvae reduced, melanin<br />

synthesis retarded, muscle fibres less developed.<br />

Anderson <strong>and</strong> Prahlad 1976 k<br />

distillery effluent RAHE egg IMMER HATSUC 31 0.3-2.1% Rate <strong>of</strong> hatching decreased <strong>and</strong> rate <strong>of</strong> mortality increased<br />

with increasing effluent conc. Hatching was delayed by 1 - 2 d<br />

<strong>and</strong> hatching success dropped to 42 - 46 %.<br />

Andrews et al. 1990

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