Spatial variability of symbiotic N-2 fixation in grass-white clover pastures estimated by the N-15 isotope dilution method and the natural N-15 abundance method
Jp. Hansen et Fp. Vinther, Spatial variability of symbiotic N-2 fixation in grass-white clover pastures estimated by the N-15 isotope dilution method and the natural N-15 abundance method, PLANT SOIL, 230(2), 2001, pp. 257-266
Aiming at estimating the spatial variability in N-2 fixation, and to evalua
te the appropriateness of the N-15 isotope dilution (ID) method and the nat
ural N-15 abundance (NA) method in reflecting spatial variability under the
influence of cattle grazing, the symbiotic N-2 fixation in grass-white clo
ver mixture was studied. At the Foulum site, where the ID method was used,
differences in the climatic conditions between the two years of investigati
ons caused a considerable difference in plant growth rates and proportion o
f clover. Consequently, the total N-2 fixation in ungrazed reference plots
was significantly less in 1998 than in 1997, being 5.9 and 12.5 g N m(-2),
respectively. In both years there was a wide range in concentration of inor
ganic N in the soil with coefficients of variance of approximately 60-190%
for ammonium and 70-340% for nitrate. Significant negative correlations bet
ween pNdfa, determined by the ID method, and the log-transformed values of
inorganic N and total N in grass were found. The NA method was applied on t
hree nearby commercial dairy farms. They also showed high coefficients of v
ariation. The coefficient of variance for NO3--N ranged from 37 to 282% and
for NH4+-N from 29 to 237%. Average estimates of pNdfa values, which in th
e NA method were calculated using apparent B values ranging from -2.10 to -
2.59 parts per thousand, were generally lower (0.7-0.87) for these farms th
an for the Foulum site (0.89-0.95) using the ID method. For the NA method t
he delta N-15 values, i.e. deviation in N-15 concentration from atmospheric
N-2, ranged from -7.0 to 5.7 parts per thousand for the grass N, which in
several cases was lower than for clover N. Due to this high variability of
the delta N-15 values, probably caused by deposition and plant assimilation
of N-15 depleted urinary N in the pastures, the NA method was marginal for
accurate determination of pNdfa. Consequently no significant correlation b
etween the pNdfa determined by this method, and the log-transformed values
of inorganic N in soil or total N in grass were found.