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a Research and Development Complex, 6001 West Pershing Road, Cicero, IL 60804
b Yale University, School of Nursing, New Haven, CT 06536-0740
c Metropolitan Water Reclamation District of Greater Chicago, Fulton County Laboratory, Canton, IL 61520
d Metropolitan Water Reclamation District of Greater Chicago, retired
* Corresponding author (thomas.granato{at}mwrdgc.dst.il.us)
Received for publication November 14, 2003. From 1974 to 1984, 543 Mg ha1 of biosolids were applied to portions of a land-reclamation site in Fulton County, IL. Soil organic C increased to 5.1% then decreased significantly (p < 0.01) to 3.8% following cessation of biosolids applications (19851997). Metal concentrations in amended soils (19951997) were not significantly different (p > 0.05) (Ni and Zn) or were significantly lower (p < 0.05) (6.4% for Cd and 8.4% for Cu) than concentrations from 19851987. For the same biosolids-amended fields, metal concentrations in corn (Zea mays L.) either remained the same (p > 0.05, grain Cu and Zn) or decreased (p < 0.05, grain Cd and Ni, leaf Cd, Cu, Ni, Zn) for plants grown in 19951997 compared with plants grown immediately following termination of biosolids applications (19851987). Biosolids application increased (p < 0.05) Cd and Zn concentrations in grain compared with unamended fields (0.01 to 0.10 mg kg1 for Cd and 23 to 28 mg kg1 for Zn) but had no effect (p > 0.05) on grain Ni concentrations. Biosolids reduced (p < 0.05) Cu concentration in grain compared with grain from unamended fields (1.9 to 1.5 mg kg1). Biosolids increased (p < 0.05) Cd, Ni, and Zn concentrations in leaves compared with unamended fields (0.3 to 5.6 mg kg1 for Cd, 0.2 to 0.5 mg kg1 for Ni, and 32 to 87 mg kg1 for Zn), but had no significant effect (p > 0.05) on leaf Cu concentrations. Based on results from this field study, USEPA's Part 503 risk model overpredicted transfer of these metals from biosolids-amended soil to corn.
Abbreviations: UC, uptake coefficient
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