The bioavailability and desorption characteristics of nonextractable soil-a
ged atrazine were investigated to examine the significance of this potentia
lly large contaminant fraction in agricultural soils. Radiolabeled atrazine
-applied soil was aged for 3 months and then extracted by one of three meth
ods-methanol-water (4:1) at 75 degrees C, acetone, and artificial soil wate
r-representing a range of extraction efficiencies. Viable microcosms were c
onstructed with the dried, extracted soil to compare rates and extents of m
icrobially facilitated release and mineralization with desorption rates in
sterile microcosms. The most rigorously extracted soil exhibited slow desor
ption over a 90-d period, but the other soil treatments showed continued sl
ow sorption after reaching an initial maximum desorption concentration with
in 1 to 5 d. No microbially facilitated release of the nonextractable atraz
ine was detected for any of the treatments. Rates of ring-and chain-labeled
atrazine mineralization declined with decreasing extractability of the soi
l-associated atrazine fraction. However, the extent of biodegradation (less
than 2% of the total atrazine for all extracted soil treatments) was less
than the extent of abiotic desorption. Mass-balance calculations suggest th
at all biodegradation occurred in the dissolved phase.