Gd. Bending et al., FATE OF NITROGEN FROM CROP RESIDUES AS AFFECTED BY BIOCHEMICAL QUALITY AND THE MICROBIAL BIOMASS, Soil biology & biochemistry, 30(14), 1998, pp. 2055-2065
Net mineralization of N from a range of shoot and root materials was d
etermined over a period of 6 months following incorporation into a san
dy-loam soil under controlled environment conditions. Biochemical ''qu
ality'' components of the materials showed better correlation with net
N mineralization than did gross measures of the respiration and N con
tent of the soil microbial community during decomposition. The quality
components controlling net N mineralization changed during decomposit
ion,with water-soluble phenolic content significantly correlated with
net N mineralization at early stages, and water-soluble N, followed by
cellulose at later stages. C-to-N and total N were correlated with ne
t N mineralization towards the end of the incubation only. Cumulative
microbial respir ation during the early stages of decomposition was co
rrelated with net N mineralizalion measured after 2 months, at which t
ime maximum net N mineralization was recorded for moat residues. Howev
er, there was no relationship between microbial-N and net N mineraliza
tion. Biochemical quality factors controlling the C and N content of t
he residue remaining at the end of the incubation as light fraction or
ganic matter (LFOM) were also investigated. Both C and N content of LF
OM derived from the residues were correlated with residue cellulose co
ntent, and the chemical characteristics of LFOM were highly correlated
with those of the original plant material. Incorporation of low cellu
lose, high water-soluble N-containing shoot residues resulted in more
N becoming mineralized than had been added in the residues, demonstrat
ing that net mineralization of native soil organic matter had occurred
. Large amounts of N were lost from the mineral-N pool during the incu
bation, which could not be accounted for by microbial immobilization.
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