Effluent-irrigated tree plantations are becoming a popular alternative to t
he direct discharge of sewerage effluent into inland rivers. However, when
irrigated at the water-use rate of the plantation, nitrogen (N) applied in
the effluent often exceeds the demand of the trees both in the early stages
of growth and after canopy closure when much of the N is supplied from the
decomposition of litter. With the ample supply of water and large loadings
of N, conditions are conducive to significant N losses. The principal pote
ntial N loss mechanisms are leaching of nitrate-N to groundwater and biolog
ical denitrification. In 4 separate experiments between winter 1992 and sum
mer 1994, N-15-labelled N (total application of 2 g N/m(2); 30 atom%) was a
pplied to 1-m(2) subplots or small plastic (PVC) cylinders. In the first 2
experiments, using 1-m(2) subplots, the conservative tracer Br was applied
as KBr with the N-15 at a total application of 12.8 g Br-/m(2). In Expt 1,
the high recovery of the N-15-labelled N, and the comparable distribution o
f N-15 and Br- in the soil profile, implied that there was little loss of N
by denitrification, even though the soil was sufficiently wet for leaching
of both tracers. Although less conclusive, the other experiments also show
ed a high potential for leaching and minimal loss of applied N-15-labelled
N by denitrification. The small contribution to N loss of denitrification,
despite conditions being otherwise suitable for it, is attributed to the fr
ee-draining nature of the soil, which meant that aeration was rarely suffic
iently limited to encourage denitrification. Similar results are expected a
t other effluent irrigation sites on freely draining soils.