GASEOUS NITROGEN LOSSES FROM ACID SULFATE SUGARCANE SOILS ON THE COASTAL LOWLANDS
By O.T. DENMEAD, B.C.T. MACDONALD, G. BRYANT, R.J. REILLY, D.W.T. GRIFFITH, W. STAINLAY, I.WHITE and M.D. MELVILLE
NITRIFICATION and denitrification are two important microbial processes in the
soil nitrogen cycle that result in the production and emission of gaseous N
compounds including the odd oxides of nitrogen NO and NO2, known collectively
as NOx, and nitrous oxide, N2O. Emissions of these gases to the atmosphere
represent a loss of N to agriculture and have important environmental effects. The
paper reports investigations of NOx and N2O emissions from fallow acid sulfate
soils (ASS) cultivated for sugarcane production on the coastal lowlands of
northern NSW. Two series of measurements were made, using chambers and
micrometeorological techniques. These allowed emissions to be measured
continuously and revealed their daily time-courses. The emission of NOx
appeared to be haphazard, with little time dependence, but there was a clear
diurnal cycle for N2O, emphasising the need for continuous measurement
procedures for both gases. In the first series, conducted in a field where a crop of
soybeans had been harvested previously, the water filled pore space, WFPS,
ranged from near 60% to near 80%. Emissions of NOx were high, amounting to as
much as 1.2 kg N/ha on the first day of measurement when the WFPS was close
to 60%. They decreased when the WFPS increased to around 80% following rain.
On the other hand, N2O emissions were high when the WFPS was near 80% (as
much as 0.8 kg N/ha/d) and declined rapidly as the WFPS fell to near 60%. In the
second series, conducted in a nearby field, the WFPS was <60%, and fluxes of
both gases were much smaller than in the first series even though urea was
applied at 50 kg N/ha halfway through the measurement period. We conclude that
emissions of both NOx and N2O from ASS are large when water contents are
high. We measured a combined loss of 5 kg N/ha over 13 days when the WFPS
was between 60% and 80%. When the WFPS was less than 60%, emissions were
markedly less, amounting to 0.9 kg N/ha over 10 days. When the soil was moist,
emissions of NOx were larger than those of N2O.