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Inst. of Soils and Water, ARO, The Volcani Center, Bet Dagan 50250, Israel
Dep. of Soil Science, Univ. of Minnesota, St. Paul, MN 55108
USDA-ARS, St. Paul, MN 55108
* Corresponding author.
ABSTRACT
Factors that control immobilization of inorganic N in soils not amended with organic C-rich materials have not been fully established. Different N flow schemes for N immobilization were tested by comparing the kinetics of CO2 evolution, NH+4-N, NO-3-N, inorganic 15N, and organic 15N excess, measured in soils incubated with 200 mg kg–1 of 15N-labeled NH+4-N, with data simulated by the computer model NCSOIL structured to representseveral pathways of C and N turnover. Estimates of those parameters most likely to induce or enhance N immobilization, namely the mineralizable soil organic matter content, its C/N ratio, and the efficiency with which C is assimilated by the soil microbial biomass were obtained by optimization. Cumulative N immobilization was up to 10% of the N added and was greater when NH+4 was added to dry soils than when added to preincubated soils. The immobilization was primarily due to the microbial biomass drawing N from the inorganic pool, rather than utilizing N directly from the decomposing soil organic matter. Nitrate formed by nitrification seemed to have also been immobilized. A microbial efficiency factor of 0.4 and a C/N ratio of 20 or more for mineralizable soil organic matter were needed to account for the observed rate of N immobilization.
Contribution from the ARO, The Volcani Center, Bet Dagan, Israel. no. 3320-E 1991 series. This research was supported by a grant from the U.S.-Israel (Binational) Agricultural Research and Development fund (BARD).
Received for publication August 6, 1991.
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