Anaerobic enrichment cultures with sediment from an intertidal strait as in
oculum were established under denitrifying, sulfate-reducing, iron-reducing
and methanogenic conditions to examine the biodegradation of mono-fluoroph
enol and mono-fluorobenzoate isomers. Both phenol and benzoate were utilize
d within 2-6 weeks under all electron-accepting conditions. However, no deg
radation of the fluorophenols was observed within 1 year under any of the a
naerobic conditions tested. Under denitrifying conditions, 2-fluorobenzoate
and 4-fluorobenzoate were depleted within 84 days and 28 days, respectivel
y. No loss of 3-fluorobenzoate was observed. All three fluorobenzoate isome
rs were recalcitrant under sulfate-reducing, iron-reducing, and methanogeni
c conditions. The degradation of the fluorobenzoate isomers under denitrify
ing conditions was examined in more detail using soils and sediments from d
ifferent geographic regions around the world. Stable enrichment cultures we
re obtained on 2-fluorobenzoate or 4-fluorobenzoate with inoculum from most
sites. Fluoride was released stoichiometrically, and nitrate reduction cor
responded to the values predicted for oxidation of fluorobenzoate to CO2 co
upled to denitrification. The 2-fluorobenzoate-utilizing and 4-fluorobenzoa
te-utilizing cultures were specific for fluorobenzoates and did not utilize
other halogenated (chloro-, bromo-, iodo-) benzoic acids. Two denitrifying
strains were isolated that utilized 2-fluorobenzoate and 4-fluorobenzoate
as growth substrates. Preliminary characterization indicated that the strai
ns were closely related to Pseudomonas stutzeri.