Jp. Kaiser et al., MICROBIAL-METABOLISM OF PYRIDINE, QUINOLINE, ACRIDINE, AND THEIR DERIVATIVES UNDER AEROBIC AND ANAEROBIC CONDITIONS, Microbiological reviews, 60(3), 1996, pp. 483
Our review of the metabolic pathways of pyridines and aza-arenes showe
d that biodegradation of heterocyclic aromatic compounds occurs under
both aerobic and anaerobic conditions. Depending upon the environmenta
l conditions, different types of bacteria, fungi, and enzymes are invo
lved in the degradation process of these compounds. Our review indicat
ed that different organisms are using different pathways to biotransfo
rm a substrate. Our review also showed that the transformation rate of
the pyridine derivatives is dependent on the substituents. For exampl
e, pyridine carboxylic acids have the highest transformation rate foll
owed by monohydroxypyridines, methylypridines, aminopyridines, and hal
ogenated pyridines. Through the isolation of metabolites, it was possi
ble to demonstrate the mineralization pathway of various heterocyclic
aromatic compounds. By using C-14-labeled substrates, it was possible
to show that ring fission of a specific heterocyclic compound occurs a
t a specific position of the ring. Furthermore, many researchers have
been able to isolate and characterize the microorganisms or even the e
nzymes involved in the transformation of these compounds or their deri
vatives. In studies involving O-18 labeling as well as the use of cofa
ctors and coenzymes, it was possible to prove that specific enzymes (e
.g., mono- or dioxygenases) are involved in a particular degradation s
tep. By using (H2O)-O-18, it could be shown that in certain transforma
tion reactions, the oxygen was derived from water and that therefore t
hese reactions might also occur under anaerobic conditions.