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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 - 27<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 LC100 e<br />

Effects eg<br />

Reference k<br />

RAPI embryo DEVOBS 4.2-6.5 20±2 Al 0, 0.25, mg/L In embryos <strong>and</strong> pre-stage 25 tadpoles, Al Freda <strong>and</strong> McDonald 1990<br />

0.5, 0.75,<br />

ameliorated the toxic effects <strong>of</strong> very low<br />

1.0<br />

pHs (4.2-4.4), while becoming toxic at<br />

higher pH (4.6-4.8). Although both embryos<br />

<strong>and</strong> pre-stage 25 tadpoles were killed by low<br />

pH (4.2-4.4 <strong>and</strong> 4.2, respectively).<br />

RAPI embryo HATSUC 4.2 bog, 7.5 fen No eggs hatched at pH 4.2; 98.5 % hatched<br />

at pH 7.5.<br />

Karns 1984 k<br />

RAPI embryo MORT 4.2-4.8 20 Al 0-1.0<br />

At 100%<br />

Nontoxic (5% mortality) without Al. Al was Freda et al. 1990<br />

mg/L<br />

artificial<br />

toxic only at pH 4.8. Organic compounds<br />

s<strong>of</strong>t water<br />

(DOC 5.7 to 16.2 mg/L) complexed the Al<br />

= 0.471<br />

<strong>and</strong> thus increased the LC50 for total Al by<br />

mg/L (for<br />

more than two-fold. 100% artificial s<strong>of</strong>t<br />

Al).<br />

water <strong>and</strong> the four dilutions <strong>of</strong> pond water<br />

were toxic to embryos.<br />

RAPI embryo BEHAV < 3.8-5.0 One <strong>of</strong> the most common species noted. Glooschenko et al. 1986<br />

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

accelerated Na efflux. Increased external Ca<br />

slowed loss <strong>of</strong> Ca. Initial body Na content<br />

was inversely correlated with acid tolerance.<br />

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

RAPI prestage 25 DEVOBS 4.2-6.5 20±2 Al 0, 0.25, mg/L In embryos <strong>and</strong> pre-stage 25 tadpoles, Al Freda <strong>and</strong> McDonald 1990<br />

tadpoles<br />

0.5, 0.75,<br />

ameliorated the toxic effects <strong>of</strong> very low<br />

1.0<br />

pHs (4.2-4.4), while becoming toxic at<br />

higher pH (4.6-4.8). Although both embryos<br />

<strong>and</strong> pre-stage 25 tadpoles were killed by low<br />

pH (4.2-4.4 <strong>and</strong> 4.2, respectively).<br />

RAPI tadpoles DEVOBS 96 h exposure to bog water (pH 4.2): there<br />

was 0% survival (controls had 97.5%<br />

survival).<br />

Karns 1992<br />

RAPI tadpoles DEVOBS 4.4-5.8 Linear increase in survival time <strong>and</strong> thus pH<br />

tolerance during first 8 wks <strong>of</strong> development.<br />

Tadpoles grew at rates <strong>of</strong> 5.9 - 36 mg/d.<br />

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

RAPI tadpoles BEHAV 4.0, 4.5 20-22 4.06 (96<br />

No significant difference in activity level Freda <strong>and</strong> Taylor 1992<br />

h);<br />

after acidification was initiated. Tadpoles<br />

N=30/treat<br />

avoided pH 4.0 <strong>and</strong> 4.5 (along with BUAM<br />

-ment<br />

they were the most sensitive species tested).<br />

RAPR embryo BEHAV Breeding habitats in the Rocky Mountains do Corn <strong>and</strong> Vertucci 1992<br />

not appear to be sufficiently acidic to kill<br />

embryos.<br />

RARI adult<br />

(abdominal<br />

PHYSIO 2.5 Increase in influx <strong>and</strong> backflux <strong>of</strong> Ca <strong>and</strong><br />

mannitol <strong>and</strong> in backflux <strong>of</strong> Na at pH 2.5 in<br />

Ferreira <strong>and</strong> Hill 1982<br />

skin)<br />

short circuited skin. Total conductance <strong>and</strong><br />

short-circuit current increased at pH 2.5.<br />

k

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