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Published online 2 February 2006
Published in J Environ Qual 35:450-458 (2006)
DOI: 10.2134/jeq2005.0316
© 2006 American Society of Agronomy, Crop Science Society of America, and Soil Science Society of America
677 S. Segoe Rd., Madison, WI 53711 USA
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Risk Assessment Test for Lead Bioaccessibility to Waterfowl in Mine-Impacted Soils

Olha Furmana, Daniel G. Strawna,*, Gary H. Heinzb and Barbara Williamsa

a University of Idaho, Moscow, ID 83844-2339
b Patuxent Wildlife Research Center, Laurel, MD 20708


Figure 1
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Fig. 1. The pH effect on Pb extractability in the waterfowl physiologically based extraction test gizzard phase. Error bars are standard deviations of triplicates (R2 = 0.97).

 

Figure 2
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Fig. 2. Extraction time effect on Pb solubility in the waterfowl physiologically based extraction test gizzard phase. Error bars are standard deviations of triplicates.

 

Figure 3
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Fig. 3. Effect of grinding on Pb extractability in the waterfowl physiologically based extraction test gizzard phase. Error bars are standard deviations of triplicates.

 

Figure 4
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Fig. 4. Relationship between Pb concentrations in the waterfowl physiologically based extraction test gizzard phase and soil/fluid ratio in the simulated gizzard solution (R2 = 0.96).

 

Figure 5
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Fig. 5. Correlations between (a) gizzard Pb concentrations and (b) log gizzard Pb concentrations in the waterfowl physiologically based extraction test and Pb concentrations in the blood (blood Pb data from Heinz et al., 2004).

 

Figure 6
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Fig. 6. Bioaccessible Pb from P-amended and unamended soils from the Lower Coeur d'Alene River Basin. The W-PBET Pb concentrations were logarithmically transformed to allow a better relative comparison with respect to waterfowl bioavailability. Error bars are standard deviations (n = 4).

 





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