Nitrate immobilization into organic matter is thought to require catalysis
by the enzymes of soil microorganisms. However, recent studies suggest that
nitrate added to soil is immobilized rapidly and this process may include
abiotic pathways. We amended living and sterilized soil with N-15-labeled n
itrate and nitrite to investigate biotic and abiotic immobilization. We rep
ort rapid transformation of nitrate in incubations of the O layer of forest
soils that have been sterilized to prevent microbial activity and to denat
ure microbial enzymes. Approximately 30, 40, and 60% of the N-15-labeled ni
trate added to live, irradiated, or autoclaved organic horizon soil disappe
ared from the extractable inorganic-N pool in less than 15 minutes. About 5
% or less of the nitrate was recovered as insoluble organic N in live and s
terilized soil, and the remainder was determined to be soluble organic N. A
dded N-15-nitrite, however, was either lost to gaseous N or incorporated in
to an insoluble organic N form in both live and sterile organic soils. Henc
e, the fate and pathway of apparent abiotic nitrate immobilization differs
from the better-known mechanisms of nitrite reactions with soil organic mat
ter. Nitrate and nitrite added to live A-horizon soil was largely recovered
in the form added, suggesting that rapid conversion of nitrate to soluble
organic-N may be limited to C-rich organic horizons. The processes by which
this temperate forest soil transforms added nitrate to soluble organic-N c
annot be explained by established mechanisms, but appears to be due to abio
tic processes in the organic horizon.