A remote site in the Tallgrass Prairie Preserve (Osage County, OK) was cont
aminated with crude oil by a pipeline break in 1992. In 1996, the contamina
ted soil was bioremediated by blending with uncontaminated soil, prairie ha
y, buffalo manure, and commercial fertilizers, and spreading in a shallow l
ayer over uncontaminated soil to create a landfarm. The landfarm was monito
red for two years for aerobic and anaerobic bacteria, soil gases indicative
of microbial activity, and for changes in the concentration of total petro
leum hydrocarbons (TPH). Levels of hydrocarbon degraders and soil gas indic
ators of aerobic degradation were stimulated in the landfarm during the fir
st warm season relative to uncontaminated prairie soil. However, these same
indicators were less conclusive during the second warm season, indicating
depletion of the more easily degradable hydrocarbons, although the landfarm
still contained 6,800 mg/kg TPH on the average at the beginning of the sec
ond warm season. Methane formation and methanogen counts were clearly stimu
lated in the first warm season relative to uncontaminated prairie soil, ind
icating that methanogenesis plays an important role in the mineralization o
f hydrocarbons even in these shallow soils.