Biodegradation of polychlorinated biphenyls (PCBs) in soil is considered to
be very complex due to various physico-chemical factors involved. Isotope
labelling technique is the best to trace fate of the xenobiotic in the envi
ronment. In this work, the uniformly C-14-labelled PCB congener 11(3,3'-chl
orobiphenyl) was chosen as a low chlorinated coplanar biphenyl which was as
sumed to be readily degraded by microorganisms. Pleurotus ostreatus and two
Pseudomonas species, representing white rot fungi and soil bacteria were u
sed separately or in a consortium. The amount of liberated (CO2)-C-14 and r
adio-HPLC, HPLC, GC-MS, and radio-TLC analyses of extracts at the end of a
two-month experiment showed that the mineralization of PCB 11 was < 0.4%, v
olalilization < 3.1%, and 30% of radioactivity was irreversibly bound to th
e soil matrix. The respective contents of all intermediate metabolites were
4.7 to 10.5 and 2.5 to 2.7% where Pseudomonas alcaligenes alone or in comb
ination with P. putida was applied. 3-Chlorobenzoic acid was the major biod
egradation product.