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

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ecosystems. Just as in the terrestrial environment, the speciation <strong>of</strong> Pb and other trace metals in<br />

natural freshwaters and seawater plays a crucial role in determining their reactivity, mobility,<br />

bioavailability, and toxicity. Many <strong>of</strong> the same speciation techniques employed <strong>for</strong> the<br />

speciation <strong>of</strong> Pb in terrestrial ecosystems (see Section AX7.1.1 and AX7.1.2) are applicable in<br />

aquatic ecosystems.<br />

There is now a better understanding <strong>of</strong> the potential effects <strong>of</strong> sampling, sample handling,<br />

and sample preparation on aqueous-phase metal speciation. Thus, a need has arisen <strong>for</strong> dynamic<br />

analytical techniques that are able to capture a metal’s speciation, in-situ and in real time. Some<br />

<strong>of</strong> these recently developed dynamic trace metal speciation techniques include:<br />

• Diffusion gradients in thin-film gels (DGT)<br />

• Gel integrated microelectrodes combined with voltammetric in situ pr<strong>of</strong>iling<br />

(GIME-VIP)<br />

• Stripping chronopotentiometry (SCP)<br />

• Flow-through and hollow fiber permeation liquid membranes (FTPLM and HFPLM)<br />

• Donnan membrane technique (DMT)<br />

• Competitive ligand-exchange/stripping voltammetry (CLE-SV)<br />

Various dynamic speciation techniques were compared in a study by Sigg et al. (2006) using<br />

freshwaters collected in Switzerland. They found that techniques involving in-situ measurement<br />

(GIME-VIP) or in-situ exposure (DGT, DMT, and HFPLM) appeared to the most appropriate <strong>for</strong><br />

avoiding Pb and other trace metal speciation artifacts associated sampling and sample handling.<br />

AX7.2.1.2 Ambient Water <strong>Quality</strong> <strong>Criteria</strong>: Development<br />

The <strong>EPA</strong>’s procedures <strong>for</strong> deriving AWQC are described in Stephan et al. (1985) and are<br />

summarized here. With few exceptions, AWQC are derived based on data from aquatic toxicity<br />

studies conducted in the laboratory. In general, both acute (short term) and chronic (long term)<br />

AWQC are developed. Depending on the species, the toxicity studies considered <strong>for</strong> developing<br />

acute criteria range in length from 48 to 96 hours. Acceptable endpoints <strong>for</strong> acute AWQC<br />

development are mortality and/or immobilization, expressed as the median lethal concentration<br />

(LC50) or median effect concentration (EC50). For each species, the geometric mean <strong>of</strong> the<br />

acceptable LC50/EC50 data is calculated to determine the species mean acute value (SMAV).<br />

AX7-108

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