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

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Protection Agency, 1986a). In fact, the main issue identified by the <strong>EPA</strong> (U.S. Environmental<br />

Protection Agency, 1986a) related to invertebrate uptake <strong>of</strong> Pb was not toxicity to the<br />

invertebrates, but accumulation <strong>of</strong> Pb to levels that may be toxic to their consumers. Several<br />

authors suggest that shrews are a good indicator <strong>of</strong> metal contamination, because they tend to<br />

accumulate higher levels <strong>of</strong> metals than herbivorous small mammals (see data summary in<br />

Sample et al. (1998)). Shrews accumulate higher levels <strong>of</strong> metals in contaminated habitats,<br />

because their diet mainly consists <strong>of</strong> detritivores (i.e., earthworms) and other soil invertebrates in<br />

direct contact with the soil (Beyer et al., 1985).<br />

Physical/Environmental Factors<br />

Plants<br />

The uptake and distribution <strong>of</strong> Pb into higher plants from the soil is affected by various<br />

chemical and physical factors including the chemical <strong>for</strong>m <strong>of</strong> Pb, the presence <strong>of</strong> other metal<br />

ions, soil type, soil pH, cation exchange capacity (CEC), the amount <strong>of</strong> Fe/Mn-oxide films<br />

present, organic matter content, temperature, light, and nutrient availability. A small fraction <strong>of</strong><br />

Pb in soil may be released into the soil water, which is then available to be taken up by plants<br />

(U.S. Environmental Protection Agency, 1986a).<br />

The <strong>for</strong>m <strong>of</strong> Pb has an influence on its toxicity to plants. For example, Pb-oxide is less<br />

toxic than more bioavailable <strong>for</strong>ms such as Pb-chloride or Pb-acetate. In a study by Khan and<br />

Frankland (1983), radish plants were exposed to Pb-oxide and Pb-chloride in a loamy sand at pH<br />

5.4, in a 42-day study. In a tested concentration range <strong>of</strong> 0 to 5000 mg/kg, root growth was<br />

inhibited by 24% at 500 mg/kg <strong>for</strong> Pb-chloride and an EC50 <strong>of</strong> 2400 mg/kg was calculated from a<br />

dose-response curve. Plant growth ceased at 5000 mg/kg and shoots exhibited an EC50 <strong>of</strong><br />

2800 mg/kg. For Pb-oxide exposure (concentration range <strong>of</strong> 0 to 10,000 mg/kg), reported results<br />

indicate an EC50 <strong>of</strong> 12,000 mg/kg <strong>for</strong> shoot growth and an EC50 <strong>of</strong> 10,000 mg/kg <strong>for</strong> root growth.<br />

There was no effect on root growth at 500 mg/kg and a 26% reduction at 1000 mg/kg Pb oxide.<br />

Soil pH is the most influential soil property with respect to uptake and accumulation <strong>of</strong> Pb<br />

into plant species. This is most likely due to increased bioavailability <strong>of</strong> Pb created by low soil<br />

pH. At low soil pH conditions, markedly elevated Pb toxicity was reported <strong>for</strong> red spruce<br />

(P. rubens) (Seiler and Paganelli, 1987). At a soil pH <strong>of</strong> 4.5, ryegrass (Lolium hybridum)<br />

AX7-51

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