Little is known of the long-term fate of biosolids-applied heavy metal
s in soil. The objective of this study was to quantify percent recover
y of biosolids-applied heavy metals in a well-drained soil. Three annu
al applications of biosolids resulted in cumulative biosolids loadings
of 0, 60, 120, and 180 Rig ha(-1). Cumulative metal loadings for the
180 Big ha(-1) biosolids rate were 25, 141, 127, 43, 173, and 348 kg h
a(-1) fur Cd, Cr, Cu, Ni, Pb, and Zn, respectively. Soils were sampled
to a depth of 0.9 m. Soil organic carbon (OC) was measured. Soil was
extracted with 1 M IINO3 and metals were determined in the supernatant
s. Soil OC concentrations were linearly correlated to biosolids loadin
gs and did not change significantly during die 16 yr after biosolids a
pplications. Concentrations of extractable Cd, Cr, Cu, Ni, ph, and Zn
in biosolids-treated soils were much greater than the control to a dep
th of 0.30 m (P < 0.01), slightly greater at 0.30 to 0.45 nl (P < 0.05
) and same as the control below 0.45 m. For the 180 Mg ha(-1) biosolid
s loading, percent recoveries for Cd, Cr, Cu, Ni, ph, and Zn were 112,
59, 119, 114, 102, and 97%, respectively. Low recovery of Cr was prob
ably due to incomplete extraction from the soil. These results show th
at complete recovery of biosolids-applied heavy metals is possible whe
n plot size is large enough to prevent cross-mixing of treated soils d
uring tillage operations and when sediment losses are minimal.