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

Citation
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
Citations number
24
Categorie Soggetti
Environment/Ecology
Journal title
PLANT AND SOIL
ISSN journal
0032079X → ACNP
Volume
230
Issue
2
Year of publication
2001
Pages
257 - 266
Database
ISI
SICI code
0032-079X(200103)230:2<257:SVOSNF>2.0.ZU;2-R
Abstract
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.