NITROUS OXIDE EMISSIONS FROM A SUGARCANE SOIL UNDER DIFFERENT FALLOW AND NITROGEN FERTILISER MANAGEMENT REGIMES
By WJ WANG; B SALTER; SH REEVES; TC BRIEFFIES; J PERNA
NITROUS OXIDE (N2O) EMISSIONS from a sugarcane soil at Mackay were monitored
during a fallow period and the subsequent sugarcane cropping year using both automatic
and manual gas sampling chambers to determine the effects of legume fallow, N
fertiliser application and a nitrification inhibitor (DMPP). Substantial N2O emissions
were observed from the bare fallow soil (5.3–6.0 kg N2O-N/ha in seven months),
although no nitrogen fertiliser was applied. Growing soybean during the fallow period
did not significantly affect N2O emissions but substantially increased the emissions in
the months after incorporation of the soybean biomass (2.5 t/ha without harvest of
grain). The cumulative N2O emissions from the unfertilised soil amounted to 6.3 kg
N2O-N/ha/year and 16.4 kg N2O-N/ha/year during the twelve-month sugarcane
cropping following bare fallow and soybean fallow, respectively. Application of N
fertiliser (urea) at 150 kg N/ha to the sugarcane grown on the bare-fallowed soil
increased N2O emissions by 6–9 kg N2O-N/ha/year. Addition of the nitrification
inhibitor in urea reduced N2O emissions by 4.2 kg N2O-N/ha/year from the fertilised
soil. Application of fertiliser at 75 kg N/ha to the sugarcane following soybean fallow
increased N2O emissions by 4.5–5.4 kg N2O-N/ha/year as compared to the no fertiliser
treatment. The high N2O emissions, particularly following soybean residue
incorporation and N fertiliser application, demonstrated the need for developing best
management strategies to reduce N losses and N2O emissions while increasing N use
efficiency by sugarcane crops. Further studies are required to ascertain the efficacy of
nitrification inhibitors in other soil and climate conditions and to investigate optimum
soybean residue management practices.