Investigation into PCB biodegradation using uniformly 14C-labelled dichlorobiphenyl
Jazyk angličtina Země Anglie, Velká Británie Médium print
Typ dokumentu časopisecké články, práce podpořená grantem, Research Support, U.S. Gov't, Non-P.H.S.
- MeSH
- biodegradace MeSH
- biotransformace MeSH
- kinetika MeSH
- látky znečišťující půdu metabolismus farmakokinetika MeSH
- Pleurotus metabolismus MeSH
- plynová chromatografie s hmotnostně spektrometrickou detekcí MeSH
- polychlorované bifenyly metabolismus farmakokinetika MeSH
- Pseudomonas putida metabolismus MeSH
- Pseudomonas metabolismus MeSH
- radioizotopy uhlíku MeSH
- Publikační typ
- časopisecké články MeSH
- práce podpořená grantem MeSH
- Research Support, U.S. Gov't, Non-P.H.S. MeSH
- Názvy látek
- 3,3'-dichlorobiphenyl MeSH Prohlížeč
- látky znečišťující půdu MeSH
- polychlorované bifenyly MeSH
- radioizotopy uhlíku MeSH
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 environment. In this work, the uniformly 14C-labelled PCB congener 11 (3,3'-chlorobiphenyl) was chosen as a low chlorinated coplanar biphenyl which was assumed to be readily degraded by microorganisms. Pleurotus ostreatus and two Pseudomonas species, representing white rot fungi and soil bacteria were used separately or in a consortium. The amount of liberated 14CO2 and radio-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%, volatilization < 3.1%, and 30% of radioactivity was irreversibly bound to the 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 combination with P. putida was applied. 3-Chlorobenzoic acid was the major biodegradation product.
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