Environ. Sci. Technol., 37 (18), 4083 -4090, 2003. 10.1021/es0340580 S0013-936X(03)04058-6
Web Release Date: August 19, 2003

Copyright © 2003 American Chemical Society

Arsenic Speciation and Reactivity in Poultry Litter

Yuji Arai,* A. Lanzirotti, S. Sutton, J. A. Davis, and D. L. Sparks

Department of Plant and Soil Sciences, University of Delaware, Newark, Delaware 19717, U.S. Geological Survey, Water Resource Division, 345 Middlefield Road, MS 465, Menlo Park, California 94025, and Consortium for Advanced Radiation Sources and Department of Geophysical Sciences, University of Chicago, Chicago, Illinois 60637

Received for review January 21, 2003

Revised manuscript received June 26, 2003

Accepted July 10, 2003

Abstract:

Recent U.S. government action to lower the maximum concentration levels (MCL) of total arsenic (As) (10 ppb) in drinking water has raised serious concerns about the agricultural use of As-containing biosolids such as poultry litter (PL). In this study, solid-state chemical speciation, desorbability, and total levels of As in PL and long-term amended soils were investigated using novel synchrotron-based probing techniques (microfocused () synchrotron X-ray fluorescence (SXRF) and -X-ray absorption near-edge structure (XANES) spectroscopies) coupled with chemical digestion and batch experiments. The total As levels in the PL were as high as 50 mg kg-1, and As(II/III and V) was always concentrated in abundant needle-shaped microscopic particles (20 m × 850 m) associated with Ca, Cu, and Fe and to a lesser extent with S, Cl, and Zn. Post-edge XANES features of litter particles are dissimilar to those of the organo-As(V) compound in poultry feed (i.e., roxarsone), suggesting possible degradation/transformation of roxarsone in the litter and/or in poultry digestive tracts. The extent of As desorption from the litter increased with increasing time and pH from 4.5 to 7, but at most 15% of the total As was released after 5 d at pH 7, indicating the presence of insoluble phases and/or strongly retained soluble compounds. No significant As accumulation (<15 mg kg-1) was found in long-term PL-amended agricultural surface soils. This suggests that As in the PL may have undergone surface and subsurface transport processes. Our research results raise concerns about long-term PL amendment effects on As contamination in surrounding soil-water environments.


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