Fate of 14C-bisphenol A in soils

Bisphenol A (BPA; 2,2-(4,4'-dihydroxydiphenyl)propane) is predominantly used as an intermediate in the production of polycarbonate plastics and epoxy resins. Traces of BPA released into the environment can reach the soil via application of sewage sludge from wastewater treatment systems that receive wastewaters containing BPA, or from leachate from uncontrolled landfills. The biodegradability of BPA has been previously investigated in several studies designed to simulate surface waters and biological wastewater treatment systems. However, there is little information available about the fate of BPA in soil. Therefore, laboratory soil degradation and batch adsorption studies were conducted with C-14-BPA and four soils according to international guidelines. The soils represented a broad range of physico-chemical properties. An important result of the degradation study was that, independent of the soil type, C-14- BPA was rapidly dissipated and not detectable in soil extracts following 3 days of incubation. Based on this result, a dissipation half-life of less than 3 days was estimated. The major route of dissipation of 14 GBPA in soil was the formation of bound residues that could not be recovered by exhaustive Soxhlet extraction. 14 C-BPA was also shown to be transiently converted to up to five metabolites, but within 3 days, neither 14 GBPA nor C-14-metabolites were detectable in the soils. After 120 days incubation, significant amounts (up to 20% of the radioactivity applied) of the parent compound were recovered as (CO2)-C-14. Soil adsorption experiments indicated that the distribution coefficients (K-oc) were between 636 and 931, classifying BPA as having low mobility for all tested soils. From the results of this study, it was concluded that if BPA reaches the soil compartment, it is not expected to be stable, mobile, or bioavailable. (C) 2003 Elsevier Science Ltd. All rights reserved.