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Air Quality Criteria for Lead Volume II of II - (NEPIS)(EPA) - US ...

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to 0, 18,000, 24,000, and 33,000 µg/L <strong>of</strong> Pb (Ruparelia et al., 1989). Significant decreases in<br />

plasma glucose (hypoglycemic levels) were reported at concentrations <strong>of</strong> 24,000 and 33,000 Φg<br />

Pb/L after 14 and 21 days <strong>of</strong> exposure, and at 18,000 µg Pb/L after 21 days <strong>of</strong> exposure<br />

(Ruparelia et al., 1989). Plasma cholesterol levels dropped significantly in comparison to<br />

controls after 14 days <strong>of</strong> exposure to 33,000 µg Pb/L and in all test concentrations after 21 days<br />

<strong>of</strong> exposure (Ruparelia et al., 1989). Similarly, concentrations <strong>of</strong> blood serum protein, albumin,<br />

and globulin were identified as bioindicators <strong>of</strong> Pb stress in carp (Cyprinus carpio) exposed to<br />

Pb-nitrates at concentrations <strong>of</strong> 800 and 8000 µg Pb/L (Gopal et al., 1997).<br />

Tissues<br />

In fish, the gills serve as an active site <strong>for</strong> ion uptake. Recent studies have examined the<br />

competition between cations <strong>for</strong> binding sites at the fish gill (e.g., Ca 2+ , Mg 2+ , Na + , H + , Pb 2+ )<br />

(MacDonald et al., 2002; Rogers and Wood, 2003, 2004). Studies suggest that Pb 2+ is an<br />

antagonist <strong>of</strong> Ca 2+ uptake (Rogers and Wood, 2003, 2004). MacDonald et al. (2002) proposed a<br />

gill-Pb binding model that assumes Pb 2+ has a ∃100 times greater affinity <strong>for</strong> binding sites at the<br />

fish gill than other cations. More toxicity studies are required to quantify critical Pb burdens that<br />

could be used as indicators <strong>of</strong> Pb toxicity (Niyogi and Wood, 2003).<br />

Growth Responses<br />

A negative linear relationship was observed in the marine gastropod abalone (Haliotis)<br />

between shell length and muscle Pb concentrations (Arai et al., 2002). Abalones were collected<br />

from two sites along the Japanese coast. Haliotis discus hannai were collected from along the<br />

coast at Onagawa; Haliotis discus were collected from along the coast at Amatsu Kominato. The<br />

authors did not report significant differences between the two sampling sites. From samples<br />

collected at Onagawa, Pb concentrations <strong>of</strong> 0.03 and 0.01 µg/g were associated with abalone<br />

shell lengths <strong>of</strong> 7.7 cm (3 years old) and 12.3 cm (6 years old), respectively. From samples<br />

collected at Amatsu Kominato, Pb concentrations <strong>of</strong> 0.09 and 0.01 µg/g were associated with<br />

abalone shell lengths <strong>of</strong> 3.9 cm (0 years old) and 15.3 cm (8 years old), respectively (Arai et al.,<br />

2002). The authors theorized that young abalones, experiencing rapid growth, do not<br />

discriminate between the uptake <strong>of</strong> essential and nonessential metals. However, as abalones<br />

grow larger and their rate <strong>of</strong> growth decreases, they increasingly favor the uptake <strong>of</strong> essential<br />

AX7-161

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