Hk. Bates et Rf. Spalding, AQUIFER DENITRIFICATION AS INTERPRETED FROM IN-SITU MICROCOSM EXPERIMENTS, Journal of environmental quality, 27(1), 1998, pp. 174-182
Denitrification of 40 mg L-1 NO3-N groundwater in the vicinity of Cent
ral City, NE was stimulated with ethanol in in situ microcosms that we
re vibrated into the aquifer sediment and, thus, filled with a relativ
ely undisturbed, saturated sand and gravel matrix, In microcosms recei
ving the 1.25 C/N ratio, nitrate disappeared within 40 h; however, NO2
-N accumulated and persisted after NO3-N was depleted, Nitrite has bee
n documented in groundwater redoxclines and is expected to be reported
more frequently with increased use of ion chromatography and dense sa
mpling networks. Dissolved oxygen was consumed to <2.0 mg L-1 within 1
5 h, and stoichiometric production of HCO3- occurred, Average denitrif
ication rate decreased from 28.5 to 19.3 and to 16 mg N L-1 d(-1) for
C/N ratios of 1.25, 2.5, and 5.0 mg L-1. Kinetic N-isotope effects res
ulted in the delta(15)N enrichment of residual nitrate as denitrificat
ion progressed, thus, causing the initial delta(15)N value of similar
to+6 parts per thousand to increase to >+20 parts per thousand. The da
ta support measuring additional parameters to prevent misinterpretatio
ns when using delta(15)N values in NO3- source identification investig
ations, Apparent isotope-enrichment factors, epsilon value, were deriv
ed from delta(15)N increases vs. NO3- and NO3- plus NO2- reduction, Th
ey ranged from -11 to -16 parts per thousand for delta(15)N vs. residu
al NO3- plus NO2- and from -2.5 to -9 parts per thousand for delta(15)
N vs. NO3- alone. Since NO3- could not be resolved from NO2- in the de
lta(15)N analysis, a delta(15)N depleted NO2- phase was not identified
, Nevertheless, isotopically light enrichment factors are consistent w
ith the presence of NO2-.