The effect of soil inorganic N availability on the decomposition of ma
ize residues was tested under aerobic conditions in soil samples incub
ated for 125 days at 15 degrees C. Carbon residue were ground maize sh
oots applied at 4 g dry matter kg(-1) soil. The C-amended soils contai
ned five initial inorganic N concentrations (10, 30, 60, 80 and 100 mg
N kg(-1) soil). Gross N immobilization was calculated with a N-15 tra
cer, using changes in both the inorganic and organic N-15 pools. Inorg
anic N remained available in those soils having the three highest init
ial N concentrations. In this case the rates of C mineralization and N
immobilization were similar. Soil inorganic N completely disappeared
at the beginning of C decomposition in the soil samples with the two l
owest N contents, resulting in a marked decrease of C mineralization r
ate compared to the three highest N contents. Gross N immobilization a
mounted to 39 mg N g(-1) added C after 40 days (end of the net immobil
ization period) for the three highest N concentrations, indicating tha
t there was no luxury N consumption by the soil microflora. N immobili
zation was much lower in the two lowest-N treatments because decomposi
tion was slow and microbial N immobilization per unit of mineralized C
was reduced. The ratio N immobilized:C mineralized also decreased in
all treatments during decomposition due to changes in microbial N dema
nd with time or increasing contributions from other sources of N, such
as biomass-N recycling, to microbial N assimilation.