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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 6 - pH Studies - 30<br />

Species<br />

Code b<br />

Lifestage Study<br />

Endpoint g<br />

pH Level(s)<br />

Temp h Additional<br />

Contam a<br />

Cont.<br />

Conc.<br />

Conc.<br />

e<br />

Units<br />

e<br />

LC50<br />

RASY embryo MORT 4.10 for<br />

hatching<br />

LC100 e<br />

Effects eg<br />

Less pH-associated embryonic mortality<br />

observed among more tolerant RASY; more<br />

larval RASY survived pH 4.1 in lab when<br />

initially contained with AMJE than at pH ><br />

6.0 due to reduced survival <strong>and</strong> subsequent<br />

predation by AMJE at pH 4.1.<br />

RASY embryo HATSUC 4.5-8.1 5.6-6.2 Low pH led to 45% decrease in hatching<br />

success; but did not affect hatch timing.<br />

Lower temperatures <strong>and</strong> low pH resulted in a<br />

decrease in frog length.<br />

RASY embryo MORT 4.15-6.23 Al 0.031-<br />

1.155<br />

RASY embryo HATSUC 4.3-4.8 Al 34-46<br />

ig/L<br />

RASY embryo (4h<br />

)<br />

mg/L<br />

(total<br />

Al)<br />

Mortality correlated only with pH. In two<br />

low-pH ponds, high conc. <strong>of</strong> dissolved<br />

organic compounds might have been a toxic<br />

component. Generally, decreases in<br />

mortality occurred with pH below 5.0<br />

(exceptions did occur).<br />

pH 4.8 <strong>and</strong> 37 µg/L Al did not affect eggs <strong>of</strong><br />

RASY ; pH 4.3 <strong>and</strong> 46 µg/L were more toxic<br />

to RASY than 34 - 35 µg/L Al.<br />

MORT 15 Differences in acid tolerance among<br />

populations <strong>of</strong> embryos was not related to<br />

levels <strong>of</strong> acidity in ponds.<br />

Reference k<br />

Sadinski <strong>and</strong> Dunson 1992<br />

Schalk et al. 1998<br />

Freda <strong>and</strong> McDonald 1993<br />

Clark <strong>and</strong> Hall 1985<br />

Pierce <strong>and</strong> Harvey 1987 k<br />

RASY larvae MORT 3, 4, 5 100 % mortality within 2 h. No differences<br />

in development noted at any other<br />

treatment.<br />

Ling et al. 1986 k<br />

RASY larvae DEVOBS 3.25-7.6 15 Acid tolerance <strong>of</strong> larvae was not related to<br />

ovum size nor to capsule thickness.<br />

Pierce et al. 1987<br />

RASY larvae PHYSIO 2.5-4.0 Acute exposure depressed Na influx <strong>and</strong><br />

markedly accelerated Na efflux - resulting<br />

net loss <strong>of</strong> 50 % <strong>of</strong> body Na was fatal.<br />

Chronic exposure caused 21-62 % reduction<br />

in body Na level K content did not change.<br />

Freda <strong>and</strong> Dunson 1985 k<br />

RASY larvae MORT 3.75-7.6 All survived for 24 h at pH 7.2 - 7.6; 37%<br />

survival at pH 3.5.<br />

Pierce <strong>and</strong> Sik<strong>and</strong> 1985 k<br />

RASY larvae HATSUC 2.0-7.6 Early feeding stage: 100 % survival at > 4.0;<br />

Pierce et al. 1984<br />

metamorphosed larvae 90 - 100 % at pH 3.5<br />

<strong>and</strong> above.<br />

k<br />

RASY larvae POPSUR 4.5-5.5 15-20 Al 100-300 µg/L Interactive effects <strong>of</strong> pH <strong>and</strong> metals on a<br />

freshwater, palustrine wetl<strong>and</strong> assemblage<br />

were measured in 500L outdoor mesocosms.<br />

Horne <strong>and</strong> Dunson 1995<br />

RASY larvae POPSUR 4.5-5.5 15-20 Cu 6-9 µg/L Interactive effects <strong>of</strong> pH <strong>and</strong> metals on a<br />

freshwater, palustrine wetl<strong>and</strong> assemblage<br />

were measured in 500L outdoor mesocosms.<br />

Horne <strong>and</strong> Dunson 1995

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