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Anaerobic microbial degradation of acridine and the application of remote fiber spectroscopy to monitor the transformation process
Author(s) -
Knezovich John P.,
Bishop Dorothy J.,
Kulp Thomas J.,
GrbićGalić Dunja,
Dewitt John
Publication year - 1990
Publication title -
environmental toxicology and chemistry
Language(s) - English
Resource type - Journals
SCImago Journal Rank - 1.1
H-Index - 171
eISSN - 1552-8618
pISSN - 0730-7268
DOI - 10.1002/etc.5620091002
Subject(s) - acridine , chemistry , environmental chemistry , biodegradation , sulfate , microbial biodegradation , degradation (telecommunications) , denitrifying bacteria , microcosm , chromatography , organic chemistry , nitrogen , denitrification , bacteria , microorganism , biology , telecommunications , computer science , genetics
Anaerobic microbial transformation of a polynuclear nitrogen heterocycle, acridine, was studied in laboratory microcosms with three different inocula: a stabilized, mixed culture growing on ferulic acid that was originally enriched from anaerobic sewage sludge, and sulfate‐reducing and methanogenic aquifer materials from two sites at a groundwater aquifer contaminated by landfill leachate. Acridine degradation was investigated under methanogenic, denitrifying and sulfate‐reducing conditions at concentrations of 1 to 6 μg /ml. Substrate degradation was followed using two standard analytical techniques (HPLC and GC‐MS) and a new, in situ remote fiber spectroscopic (RFS) technique. This RFS was used successfully to follow changes in concentration of acridine with time, which indicates the technique has a significant potential for monitoring the degradation process in environmental media. Acridine was degraded extensively in one to three weeks under each of the conditions studied. A range of heterocyclic, homocyclic aromatic and aliphatic intermediates was identified by GC‐MS analyses. On the basis of these compounds, a tentative route of anaerobic acridine transformation is proposed that begins with oxidation and proceeds through the common degradative route for oxidized aromatic compounds.
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