SOIL C AND N TURNOVER AFTER INCORPORATION OF CHOPPED MAIZE, BARLEY STRAW AND BLUE GRASS IN THE FIELD - EVALUATION OF THE DAISY SOIL-ORGANIC-MATTER SUBMODEL
T. Mueller et al., SOIL C AND N TURNOVER AFTER INCORPORATION OF CHOPPED MAIZE, BARLEY STRAW AND BLUE GRASS IN THE FIELD - EVALUATION OF THE DAISY SOIL-ORGANIC-MATTER SUBMODEL, Ecological modelling, 111(1), 1998, pp. 1-15
The DAISY soil-organic-matter submodel was evaluated against independe
nt data from a 1 year field study with incorporation (0-15 cm) of chop
ped barley straw, blue grass and maize into a sandy loam soil. Investi
gated parameters were soil respiration, soil mineral N, soil microbial
biomass-C and N (SMB-C and N) dynamics and the predicted decompositio
n of the added organic matter (AOM) measured as light particulate orga
nic matter (LPOM > 100 mu m, rho < 1.4 g cm(-3)). Significant differen
ces between values predicted from the model and measured values of soi
l respiration, soil mineral N, and soil microbial biomass-C and N were
observed in all treatments. However, the model predictions for the un
amended soil and for the soil receiving barley straw were better than
those for the two other treatments. Discrepancies, in the blue grass a
nd in the maize treatment, led to suggestions for model improvements.
A distinct short-term pulse of SMB growth observed immediately after i
ncorporation of the plant materials was not predicted fully. However,
the difference between the measured and the predicted SMB pools did no
t induce a complementary difference for the mineral N pool. Soil micro
bial residues (SMR), temporarily protected against recycling via the m
icrobial turnover and mineralisation, are discussed as a possible sink
for the N from SMB. The predicted dynamics of the less labile AOM1-po
ol (initialised as water inextractable AOM) was correlated with the me
asured amounts of LPOM from the added plant materials. A slight overes
timation of measured LPOM by AOM1 in the initial period after incorpor
ation of AOM was followed by a slight underestimation later on. This t
rend might be attributed to the assumed constant C/N-ratio and turnove
r rate during the simulated decay of AOM1, contrasting reality in whic
h LPOM is changing, e.g. C/N-ratio and lignin content. The simple init
ial partition of AOM into a water extractable part (AOM2) and a water
inextractable part (AOM1), both parameterised with predetermined turno
ver rates and utilisation efficiencies, calls for re-evaluation. Sugge
stions are made to include the concept of SMR and the changing composi
tion of LPOM into the DAISY model. (C) 1998 Elsevier Science B.V. All
rights reserved.