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Download fileIn Vitro Gastrointestinal Bioavailability of Arsenic in Soils Collected near CCA-Treated Utility Poles
journal contribution
posted on 2006-07-01, 00:00 authored by Priscilla Pouschat, Gerald J. ZaguryBecause of the potentially high arsenic concentrations
found in soils immediately adjacent to chromated copper
arsenate (CCA)-treated wood structures and utility poles, CCA-contaminated soil ingestion may be a significant exposure
route to arsenic for children. Therefore, a strong need
exists to provide accurate data on oral relative bioavailability
(RBA) of arsenic (in vivo or in vitro) in field-collected CCA-contaminated soils. The objectives of this study were
(1) to assess arsenic bioaccessibility in contaminated soils
collected near in-service CCA-treated utility poles, (2) to
determine the influence of soil properties and arsenic
fractionation on arsenic bioaccessibility, and (3) to estimate
an average daily arsenic intake from incidental soil
ingestion. Arsenic bioaccessibility (in vitro gastrointestinal
(IVG) method) was determined on surface soil samples
collected immediately adjacent to 12 CCA-treated utility
poles after 18 months of service. Bioaccessible arsenic was
also determined in 3 certified reference materials. Total
arsenic concentrations in soils (<300 μm) varied from 37
± 2 to 251 ± 12 mg/kg, irrespective of soil organic matter
content with the major soil-bound arsenic species being As(V). Arsenic bioaccessibility ranged between 25.0 ± 2.7 and
66.3 ± 2.3% (mean value 40.7 ± 14.9%). The mean value
was in agreement with the in vivo arsenic RBA reported by
Casteel et al. (2003) in soil near CCA-treated utility poles.
Bioaccessible arsenic was positively correlated with total
organic carbon content (r2 = 0.36, p < 0.05) and with water-soluble arsenic (r2 = 0.51, p < 0.01), and was negatively
correlated with clay content (r2 = 0.43, p < 0.05). Using
conservative exposure parameters, the mean daily arsenic
intake from incidental ingestion of contaminated soil
near CCA-treated utility poles was 0.18 ± 0.09 μg As kg-1
d-1. This arsenic intake appeared negligible compared
to the daily intake of inorganic arsenic from water and food
ingestion for children.