Nitrogen isotope fractionation in the fodder tree legume tagasaste (Chamaecytisus proliferus) and assessment of N-2 fixation inputs in deep sandy soils of Western Australia
Mj. Unkovich et al., Nitrogen isotope fractionation in the fodder tree legume tagasaste (Chamaecytisus proliferus) and assessment of N-2 fixation inputs in deep sandy soils of Western Australia, AUST J PLAN, 27(10), 2000, pp. 921-929
Nitrogen (N) isotope fractionation and symbiotic N fixation were investigat
ed in the shrub legume tagasaste, growing in the glasshouse and field. In a
pot study of effectively nodulated plants supplied with 0, 1, 5 and 10 mM
nitrate [stable isotope N-15 (delta(15)N) of 3.45 parts per thousand], the
delta(15)N of dry matter N of fully symbiotic cultures indicated a greater
isotope fractionation during distribution of N between nodules, stems, leav
es and roots than for N-2 fixation itself, with whole-plant delta(15)N bein
g near zero (-0.46 to 0.42 parts per thousand). Regardless of whether plant
s were field-grown, pot-cultured, fixing N-2 or utilising mineral N, woody
stems were depleted in N-15 relative to all other plant parts. The similar
orders of ranking of delta(15)N for plant components of the nitrate- treate
d and fully symbiotic plants, and a general increase in delta(15)N as plant
s were exposed to increasing concentrations of nitrate, indicated that N is
otope fractionation can be accounted for, and thus not undermine N-15 natur
al abundance as means of measuring N-2 fixation inputs in tagasaste trees.
In pot culture the percentage of plant N derived from the atmosphere (% Ndf
a) by symbiotic N-2 fixation fell from 85 to 37% when the nitrate supply wa
s increased from 1 to 10 mM, with evidence of nitrate N being preferentiall
y allocated to roots. delta(15)N natural abundance assessments of N-2 fixat
ion of 4-year- old trees of field-grown tagasaste in alley (550 trees ha(-1
)) or plantation (2330 trees ha(-1)) spacing were undertaken at a study sit
e at Moora, Western Australia, over a 2-year period of shoot regrowth (copp
icing). Cumulative N yields and %Ndfa were similar for trees of alley and p
lantation spacing, with much less coppice N accumulation in the first compa
red to the second year after cutting. Scaling values from a tree to plot ar
ea basis, and using a mean %Ndfa value of 83% for all trees at the site, in
puts of fixed N into current biomass plus fallen litter over the 2 years of
coppicing were calculated to be 83 kg N ha(-1) year(-1) for the alley and
390 kg N ha(-1) year(-1) for the plantation spacing. Although the plantatio
n tagasaste fixed 587 kg N ha(-1) in the second year, close to the maximum
value reported in the literature for any N-2-fixing system, this should not
be seen as typical where the trees are used for animal production, since g
razing and cutting management will substantially reduce productivity and N-
2 fixation input.