Although hexahydro-1,3,5 -trinitro-1,3,5-triazine (also called RDX or hexog
n) is a potentially toxic explosive compound that persists in soil, its eco
toxicological effects on soil organisms have rarely been assessed. In this
study, two uncontaminated garden soils were spiked with 10 to 12,500 mg RDX
/kg dry soil. Soil microbial activities, i.e., potential nitrification, nit
rogen fixation, dehydrogenase, basal respiration, and substrate-induced res
piration were chosen as bioindicators and were determined after 1-, 4-, and
12-weeks of exposure. Experimental results indicate that RDX showed signif
icant inhibition (up to 36% of control) on indigenous soil microbial commun
ities over the period of this study. All five bioindicators; responded simi
larly to the RDX challenge. The length of exposure also affected the microb
ial toxicity of RDX, with 12-week exposure exerting more significant effect
s than the shorter exposure periods, suggesting that soil microorganisms mi
ght become more vulnerable to RDX when exposure is extended. The estimated
lowest observable adverse effect concentration of RDX was 1,235 mg/kg. No b
iodegradation products of RDX were detected at all three sampling times. Co
mpared with 2,4,6-trinitrotoluene (TNT), RDX is less toxic to microbes, pro
bably because of its resistance to biodegradation under aerobic conditions,
which precludes metabolic activation of nitro groups.