Assimilation of N by heterotrophic soil microbial biomass is associate
d with decomposition of organic matter in the soil. The form of N assi
milated can be either low molecular weight organic N released from the
breakdown of organic matter (direct assimilation), or NH4+ and NO3- f
rom the soil inorganic N pool, into which mineralized organic N is rel
eased (mineralization immobilization turnover). The kinetics of C and
N turnover in soil is quantifiable by means of computer simulation mod
els. NCSOIL was constructed to represent the two assimilation schemes.
The rate of N assimilation depends on the rate of C assimilation and
microbial C/N ratio, thereby rendering it independent of the assimilat
ion scheme. However, if any of the N forms is labeled, a different amo
unt of labeled N assimilation will be simulated by the different schem
es. Experimental data on inorganic N and N-15 and on organic N-15 dyna
mics in soils incubated with N-15 added as NH4+ or organic N were comp
ared with data simulated by different model schemes. Direct assimilati
on could not account for the amount of N-15 assimilated in any of the
experimental treatments. The best fit of the model to experimental dat
a was obtained for the mineralizaton immobilization turnover scheme wh
en both NH4+ and NO3- were assimilated, in proportion to their concent
ration in the soil.