Laboratory microcosm experiments were conducted to evaluate the feasib
ility of benzene, toluene, ethylbenzene, m-xylene, and o-xylene (BTEX)
biodegradation under denitrifying conditions. Nine different sources
of inocula, including contaminated and uncontaminated soil cores from
four different sites and activated sludge, were used to establish micr
ocosms. BTEX was not degraded under denitrifying conditions in microco
sms inoculated with aquifer material from Rocky Point and Traverse Cit
y. However, rapid depletion of glucose under denitrifying conditions w
as observed in microcosms containing Rocky Point aquifer material. TEX
degradation was observed in microcosms containing Rocky Point aquifer
material. TEX degradation was observed in microcosms containing aquif
er material from Fort Bragg and Sleeping Bear Dunes and sewage sludge.
Benzene was recalcitrant in all microcosms tested. The degradation of
o-xylene ceased after toluene, ethylbenzene, and m-xylene were deplet
ed in the Fort Bragg and sludge microcosms, but o-xylene continued to
degrade in microcosms with contaminated Sleeping Bear Dunes soil. The
most probable number (MPN) of denitrifiers in these nine different ino
cula were measured using a microtiter technique. There was no correlat
ion between the MPN of denitrifiers and the TEX degradation rate under
denitrifying conditions. Experimental results indicate that the degra
dation sequence and TEX degradation rate under denitrifying conditions
may differ among sites. Results also indicate that denitrification al
one may not be a suitable bioremediation technology for gasoline-conta
minated aquifers because of the inability of denitrifiers to degrade b
enzene.