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

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organisms. The authors believe there may be two reasons <strong>for</strong> this. First, metal uptake routes in<br />

soils are generally more complex than those in water, because exposure via pore water and<br />

exposure via ingestion <strong>of</strong> soil particles may, in principle, both be important. Second, it remains<br />

very difficult to univariately control the composition <strong>of</strong> the soil pore water and the metal<br />

concentrations in the pore water, due to re-equilibration <strong>of</strong> the system following modification <strong>of</strong><br />

any <strong>of</strong> the soil properties (including addition <strong>of</strong> metal salts).<br />

Steenbergen et al. (2005) assessed acute copper toxicity to the earthworm Aporrectodea<br />

caliginosa using the BLM. To overcome the a<strong>for</strong>ementioned problems inherent in soil toxicity<br />

tests they developed an artificial flow-through exposure system consisting <strong>of</strong> an inert quartz sand<br />

matrix and a nutrient solution, <strong>of</strong> which the composition was univariately modified. Thus, the<br />

obstacles in employing the BLM to terrestrial ecosystems seem to be surmountable, and future<br />

research may provide useful in<strong>for</strong>mation on Pb bioavailability and toxicity to terrestrial<br />

organisms.<br />

AX7.1.1.5 Soil Amendments<br />

The removal <strong>of</strong> contaminated soil to mitigate exposure <strong>of</strong> terrestrial ecosystem<br />

components to Pb can <strong>of</strong>ten present both economic and logistic problems. Because <strong>of</strong> this,<br />

recent studies have focused on in situ methodologies to lower soil-Pb RBA (Brown et al.,<br />

2003a,b). To date, the most common methods studied include the addition <strong>of</strong> soil amendments<br />

in an ef<strong>for</strong>t either to lower the solubility <strong>of</strong> the Pb <strong>for</strong>m or to provide sorbtion sites <strong>for</strong> fixation <strong>of</strong><br />

pore-water Pb. These amendments typically fall within the categories <strong>of</strong> phosphate, biosolid,<br />

and Al/Fe/Mn-oxide amendments.<br />

Phosphate Amendments<br />

Phosphate amendments have been studied extensively and, in some cases, <strong>of</strong>fer the most<br />

promising results (Brown et al., 1999; Ryan et al., 2001; Cotter-Howells and Caporn, 1996;<br />

Hettiarachchi et al., 2001, 2003; Rabinowitz, 1993; Yang et al., 2001; Ma et al., 1995). Research<br />

in this area stems from early work by Nriagu (1973) and Cotter-Howells and Caporn (1996), who<br />

pointed out the very low solubilities <strong>for</strong> many Pb-phosphates (Ksp !27 to !66), particularly<br />

chloropyromorphite [Pb5(PO4)3Cl]. The quest to trans<strong>for</strong>m soluble Pb mineralogical <strong>for</strong>ms into<br />

chloropyromorthite continues to be the primary focus <strong>of</strong> most studies. Sources <strong>of</strong> phosphorous<br />

AX7-19

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