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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 - 7<br />

Study<br />

Endpoint g Temp h pH Contaminant<br />

Concentration<br />

e<br />

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

Reference k<br />

atrazine (nnitrosoatrazine)<br />

PLWA larvae IMMER GENOTOX 20 8 0-3.75-15 51-93/1000 micronucleated erythrocytes. L'Haridon et al. 1993<br />

atropine, soman RACA adult TISPREP PHYSIO 22-23 10µM (soman Neuron membrane potentials were measured; effects are Heppner <strong>and</strong> Fiekers 1992<br />

<strong>and</strong> atropine) mediated by activation <strong>of</strong> muscarinic receptors.<br />

Ba RACA adult TISPREP PHYSIO K stimulated pNPPase seems to be completely dependent on<br />

magnesium; Barium is a completely insufficient substitute for<br />

Mg in this respect.<br />

Ray 1980<br />

Ba RANI adult IMMER PHYSIO 3-5 mM Mobilization <strong>of</strong> the ACh quanta readily available for release<br />

might be a common mechanism underlying both frequency<br />

facilitation <strong>and</strong> two components <strong>of</strong> PTP in muscle tissue<br />

(augmentation <strong>and</strong> potentiation).<br />

Maeno <strong>and</strong> Shibuya 1988<br />

BaP PLWA larvae IMMER GENOTOX 0.025- 0.1 Fequency <strong>of</strong> micronucleated erythrocytes: 0.025 ppm= 27;<br />

0.1 ppm= 304.<br />

Fern<strong>and</strong>ez et al. 1989<br />

BaP PLWA larvae IMMER RESIDUE 0.075- 0.3<br />

x10 -3<br />

Ratio <strong>of</strong> BaP in larvae to that in surrounding water after 12 h<br />

was approximately 200; not dependent on dose; maximal<br />

levels attained after 12 h. Contaminated larvae placed in<br />

uncontaminated water lost 99% contaminant after 100 h.<br />

Grinfeld et al. 1986 k<br />

BaP PLWA larvae<br />

(stage 23)<br />

TISPREP PHYSIO 0.01- 0.75 Increase incidence <strong>of</strong> micronucleated erythrocytes after >2 d<br />

<strong>of</strong> exposure.<br />

Grinfeld et al. 1986 k<br />

BaP PLWA newt INJECT PHYSIO 0.166 mg-150<br />

x10 +6 Organosoluble- <strong>and</strong> water-soluble compounds were collected Marty et al. 1995<br />

cpm in in the medium <strong>of</strong> injected animals demonstrating the<br />

200 µl DMSO capability <strong>of</strong> PAWL to metabolize BaP into hydroxylated<br />

products.<br />

BaP RAPI adult TISPREP GENOTOX 0.01 mg/mL Three fold increase in sister chromatid exchange at 0.01<br />

mg/mL in ambient water. Mitotic index reduced <strong>and</strong> cell<br />

cycling time lengthened in dose-dependent manner.<br />

Geard <strong>and</strong> Soutter 1986 k<br />

BaP XELA tadpoles IMMER PHYSIO 22 0-4.0 mg/L Frequency <strong>of</strong> micronucleated erythrocytes increased with<br />

increasing conc. (68/1000 at 0.5 mg/L; stage 50); a decrease<br />

in micronucleated erythrocytes was observed at doses higher<br />

than 0.5 mg/L (26/1000 at 1.0 mg/L).<br />

Van Hummelen et al. 1989<br />

BaP XELA tadpoles IMMER DEVOBS 31-248 nM Mean numbers <strong>of</strong> micronucleated erythrocytes were 1.7, 6.3 Sadinski et al. 1995<br />

BaP<br />

<strong>and</strong> 16.4/1000 after exposure to BaP. Levels <strong>of</strong> both DNA<br />

adducts <strong>and</strong> micronuclei were greatly reduced in animals<br />

exposed previously to 31 <strong>and</strong> 248 BaP, but assayed at<br />

metamorphosis.<br />

BaP XXFR adult TISPREP GENOTOX < 20.0 µg/mL No evidence <strong>of</strong> genotoxicity after 1 wk in eye lens<br />

epithelium.<br />

Kung et al. 1987 k<br />

Be XXFR embryo IMMER DEVOBS Development interfered with at N/5000 to N/1000.<br />

Dilling <strong>and</strong> Healey 1926 k

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