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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 Contaminant<br />

b<br />

Concentration<br />

b<br />

LC50<br />

paraquat 0-10.0 mg/L 8.1, 4.2,<br />

3.2 mg/L<br />

parathion 14.7<br />

(13.5-<br />

16.0)<br />

EC50 b<br />

mean<br />

P=0.33;<br />

G=0.46<br />

TI d<br />

TI (P):<br />

44.6; TI<br />

(G): 32.0;<br />

TI (N):<br />

2.7<br />

Table 5 - FETAX Studies - 16<br />

MCIG d<br />

NOEL d<br />

LOEL d<br />

Effects/Notes de<br />

For the formulation product LC50 values<br />

were (mg/L): >8.1 (96h), 6.2 (10d), 6.2<br />

(30d).<br />

Significantly decreased growth. 10-fold<br />

less potent than metabolite paraoxon.<br />

Minimal curvature to severe notochordal<br />

bending. Barrel-shaped embryos. (p=<br />

effect <strong>of</strong> abnormal pigmentation<br />

observed; g= effect <strong>of</strong> abnormal gut<br />

observed; n= abnormal notochord).<br />

Pb 0.02-3.0 mg/L Short-term effects: no Pb uptake in<br />

tissues between 72 <strong>and</strong> 96 h. 0.02-0.1<br />

µg/L conc. treatments after 3 weeks<br />

displayed delayed lordoscolosis<br />

(dorsal/ventral <strong>and</strong> lateral flexure <strong>of</strong> the<br />

tail).<br />

Pb acetate 0 - > 1 mg/L Lethality <strong>and</strong>/or abnormalities occurred<br />

above 1 mg/L.<br />

PCB 126 17.1 pmol/mL -<br />

15.5 µmol/mL<br />

PCB 126 17.1 pmol/mL -<br />

15.5 µmol/mL<br />

Reference k<br />

Linder et al. 1990<br />

Snawder <strong>and</strong> Chambers 1989<br />

Sobotka <strong>and</strong> Rahwan 1995<br />

Kanunura <strong>and</strong> Tanimura<br />

1985 k<br />

Larvae; 29% <strong>of</strong> the animals died within<br />

first 10 days, 48% died over whole<br />

experimental period. 93% <strong>of</strong> animals<br />

were malformed when exposed to 6.4<br />

µmol/mL <strong>of</strong> PCB 126. Oedema,<br />

misformed eyes, tails <strong>and</strong> lack <strong>of</strong> gut<br />

coiling were most common<br />

malformations.<br />

Gutleb et al. 1998<br />

No effect on rate <strong>of</strong><br />

malformations,growth <strong>and</strong> development<br />

in FETAX assay.<br />

Gutleb et al. 1998<br />

7.8 - 9.2 0.01 Metal contaminated soils also tested. Fort et al. 1995b<br />

pentachlorophenol 0.39 - 0.03 -<br />

0.46 0.05<br />

pentachlorophenol 0.52 - 0.07 - 5.6 - 7.43 0.15 -<br />

Conc. as low as 0.5 µg/L inhibited tail Fort <strong>and</strong> Stover 1996<br />

0.56 0.10<br />

0.18<br />

resorption.<br />

pentachlorophenol 0.5-25.0 µg/L 5.0 10.0 Stage 60-66 embryo. Fort <strong>and</strong> Stover 1997<br />

pentanoic acid 183.6-<br />

Valproic acid:petanoic acid <strong>and</strong> butyric Dawson <strong>and</strong> Wilke 1991a<br />

274-5<br />

acid:petanoic acid = conc. additive<br />

mg/L<br />

(TU=1.0).<br />

pentanoic acid 0-360.0 mg/L 227.7<br />

EC50 in mixture: 23.2 (21.6-24.8) TU in Dawson 1991<br />

(216.0-<br />

mixture for malformation: 0.102 (0.095-<br />

238.5)<br />

0.109).

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