Various surveys indicate that denitrifying bacteria represent 10-15% o
f the bacterial population in soil, water and sediment. They occur in
almost every type of environmental niche examined to date and are thus
likely to be available in a great variety of threatened or polluted e
cosystems. Although systems undergoing bioremediation depend largely o
n metabolically adaptable aerobic bacteria and fungi for recycling the
majority of the nutrients and elements, anaerobic zones containing po
lluting materials are commonly encountered, or entire contaminated sys
tems may be oxygen-poor or anoxic. Bacterial denitrification can suppl
y the most effective type of biotransformation in these environments,
especially if nitrate or other N-oxides are naturally available or add
ed. Denitrifiers use a broad range of inorganic and Organic compounds
as sources of carbon and energy with an efficiency of phosphorylation
which is 67-71% of that during electron transport to oxygen. Moreover,
nitrate is more soluble and often less expensive than oxygen. In this
minireview; the distribution of denitrifiers and their ability to rem
ove toxic inorganic and organic pollutants from soil environment is ev
aluated.