The present study explores the feasibility of biotreatment of 2,4,6-trinitr
otoluene (TNT) and hexahydro-1,3,5-trinitro-1,3,5-triazine (RDX)contaminate
d soils in slurry batch reactors. Radiorespirometric assays showed that ana
erobic sludge was able to mineralize 59% RDX to CO2 although significant mi
neralization of TNT was not observed in all cases. TNT and RDX at concentra
tions higher than 50 and 100 mg/L respectively were inhibitory to methanoge
nesis (used as a bioindicator), however, methanogenesis recovered after TNT
was transformed into less toxic triaminotoluene. Bioslurry batch reactors
containing 40% of contaminated soil (2000 mg RDX and 1000 mg TNT/kS dry soi
l) were operated under various conditions. Both TNT and RDX were persistent
to soil indigenous microbes. Degradation of both TNT and RDX was enhanced
by the municipal sludge amendment, although degradation of RDX was only ach
ieved under anaerobic conditions.