Nitrification and denitrification are two key links of nitrogen flow cycle in soil.N2O and N2,generated from biochemical process of nitrogen,can cause not only the nitrogen losses and reduction of nitrogen use efficie...Nitrification and denitrification are two key links of nitrogen flow cycle in soil.N2O and N2,generated from biochemical process of nitrogen,can cause not only the nitrogen losses and reduction of nitrogen use efficiency,but also the boosted concentration of greenhouse gases,severely endangering the environment.Accordingly,nitrification-denitrification has been more and more concerned from whether an agricultural view,or an environmental one.Referring to the related literatures published at home and abroad in recent years,we overviewed the denitrification-caused N loss and N2O emission in various agro-ecosystems,and based on which we put forward countermeasures to reduce the denitrification-caused N loss and N2O emission and its research prospects in the future.展开更多
The ratio of nitrous oxide(N2O)to N2O plus nitrogen gas(N2)emitted from soils(N2O/(N2O+N2))is regarded as a key parameter for estimating fertilizer nitrogen(N)loss via N2emission at local,regional or global scales.How...The ratio of nitrous oxide(N2O)to N2O plus nitrogen gas(N2)emitted from soils(N2O/(N2O+N2))is regarded as a key parameter for estimating fertilizer nitrogen(N)loss via N2emission at local,regional or global scales.However,reliable measurement of soil N2emissions is still difficult in fertilized soil-crop systems.In this study,the N loss via N2emission following basal urea application(with a dose of 150 kg N ha-1)to a calcareous soil cultivated with winter wheat was quantified using the helium-based gas-flow-soil-core technique.Emissions of N2and N2O from sampled fresh soils were measured under simulated field soil temperature and oxygen conditions.Our observation performed on the first day after irrigation and rainfall events showed the highest N2and N2O emissions,which amounted to approximately 11.8 and 3.8μg N h-1kg-1dry soil,corresponding to 3304 and 1064μg N m-2h-1,respectively.The N2O/(N2O+N2)molar ratios within about 10 days following fertilization ranged from 0.07 to 0.25,which were much larger than those at the other time.During the one-month experimental period,the urea-N loss via emissions of N2,N2O,and N2+N2O was 1.6%,0.6%,and 2.2%,respectively.Our study confirms that the widely applied acetylene-inhibition method substantially underestimates fertilizer N losses via N2emissions from calcareous soils cultivated with winter wheat.展开更多
Greenhouse gas emissions,nitrogen and phosphorous losses through ammonia volatilization,leaching and surface drainage from rice paddy under efficient irrigation and drainage were analyzed based on field experimental d...Greenhouse gas emissions,nitrogen and phosphorous losses through ammonia volatilization,leaching and surface drainage from rice paddy under efficient irrigation and drainage were analyzed based on field experimental data in order to reveal the eco-environmental impacts of efficient irrigation and drainage on rice paddy.The results showed that total methane emission from rice paddy under the controlled irrigation was reduced by more than 80% and total nitrous oxide emission increased by 15.9% compared with flooding irrigation.Seasonal comprehensive global warming potentials(GWP) of methane and nitrous oxide were 62.23 gCO2 m-2 for rice paddy under the controlled irrigation,reduced by 68.0% compared with flooding irrigation.Due to large reduction in seepage and surface drainages,nitrogen and phosphorous losses through leaching were reduced by 40.1% and 54.8%,nitrogen and phosphorous losses through surface drainage were reduced by 53.9% and 51.6% from rice paddy under efficient irrigation and drainage compared with traditional irrigation and drainage.Nitrogen loss through ammonia volatilization was reduced by 14.0%.Efficient irrigation and drainage management is helpful to mitigate greenhouse gases emission,nitrogen and phosphorus losses and their pollution on groundwater and surface water.展开更多
NOx and N2O emissions from coastal acid sulfate soils （CASS） cultivated for sugarcane production were investigated on the coastal lowlands of northern New South Wales, Australia. Two series of short-term measurement...NOx and N2O emissions from coastal acid sulfate soils （CASS） cultivated for sugarcane production were investigated on the coastal lowlands of northern New South Wales, Australia. Two series of short-term measurements were made using chambers and micrometeorological techniques. Series i occurred during the wet season, the water-filled pore space （WFPS） was between 60%-80% and the site flooded during the measurements. Measurements were made directly after the harvest of soybean crop, which fixed an estimated 100 kg N ha-1, and the emission amounted to 3.2 kg NOx-N ha-1 （12 d） and 1.8 kg N20-N ha-1 （5 d）. Series 2 was made towards the end of the dry season when the WFPS was less than 60%. In Series 2-1 after an application of 50 kg N ha-1, emissions were markedly less, amounting to 0.9 kg N ha 1 over 10 d. During both series when the soil was moist, emissions of NOx were larger than those of N2O. 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. These results suggest that agricultural production on CASS could be important sources of greenhouse gases and nitrogen practices will need to be optimised to reduce the offsite effects of atmospheric warming, acidification or nitrification. Many questions still remain unanswered such as the emissions during the soybean bean filling stage and crop residue decomposition, the longer-term losses following the fertiliser application and emissions from CASS under different land uses.展开更多
基金Supported by Key Natural Science Foundation of Fujian Province(2008J0120)Natural Science Foundation of Fujian Province(2006J0009)+1 种基金Non-profit Program from Science and Technology Department of Fujian Province(2009R10032-1 and 2010R1024-2)Special Fund for the Establishment of S&T Innovation Teams in Fujian Academy of Agricultural Sciences from Financial Department of Fujian Province(STIF-Y01)
文摘Nitrification and denitrification are two key links of nitrogen flow cycle in soil.N2O and N2,generated from biochemical process of nitrogen,can cause not only the nitrogen losses and reduction of nitrogen use efficiency,but also the boosted concentration of greenhouse gases,severely endangering the environment.Accordingly,nitrification-denitrification has been more and more concerned from whether an agricultural view,or an environmental one.Referring to the related literatures published at home and abroad in recent years,we overviewed the denitrification-caused N loss and N2O emission in various agro-ecosystems,and based on which we put forward countermeasures to reduce the denitrification-caused N loss and N2O emission and its research prospects in the future.
基金jointly supported by the National Key Research&Development Program [grant number 2017YFD0200100]the National Natural Science Foundation of China [grant numbers 41877333,41303060,and 41830751]
文摘The ratio of nitrous oxide(N2O)to N2O plus nitrogen gas(N2)emitted from soils(N2O/(N2O+N2))is regarded as a key parameter for estimating fertilizer nitrogen(N)loss via N2emission at local,regional or global scales.However,reliable measurement of soil N2emissions is still difficult in fertilized soil-crop systems.In this study,the N loss via N2emission following basal urea application(with a dose of 150 kg N ha-1)to a calcareous soil cultivated with winter wheat was quantified using the helium-based gas-flow-soil-core technique.Emissions of N2and N2O from sampled fresh soils were measured under simulated field soil temperature and oxygen conditions.Our observation performed on the first day after irrigation and rainfall events showed the highest N2and N2O emissions,which amounted to approximately 11.8 and 3.8μg N h-1kg-1dry soil,corresponding to 3304 and 1064μg N m-2h-1,respectively.The N2O/(N2O+N2)molar ratios within about 10 days following fertilization ranged from 0.07 to 0.25,which were much larger than those at the other time.During the one-month experimental period,the urea-N loss via emissions of N2,N2O,and N2+N2O was 1.6%,0.6%,and 2.2%,respectively.Our study confirms that the widely applied acetylene-inhibition method substantially underestimates fertilizer N losses via N2emissions from calcareous soils cultivated with winter wheat.
基金supported by the National Natural Science Foundation of China (Grant Nos 50839002 and 50809022)the National Key Tech-nologies R & D Program of China during the 11th Fiveyear Plan Period (Grant No 2006BAD11B09)
文摘Greenhouse gas emissions,nitrogen and phosphorous losses through ammonia volatilization,leaching and surface drainage from rice paddy under efficient irrigation and drainage were analyzed based on field experimental data in order to reveal the eco-environmental impacts of efficient irrigation and drainage on rice paddy.The results showed that total methane emission from rice paddy under the controlled irrigation was reduced by more than 80% and total nitrous oxide emission increased by 15.9% compared with flooding irrigation.Seasonal comprehensive global warming potentials(GWP) of methane and nitrous oxide were 62.23 gCO2 m-2 for rice paddy under the controlled irrigation,reduced by 68.0% compared with flooding irrigation.Due to large reduction in seepage and surface drainages,nitrogen and phosphorous losses through leaching were reduced by 40.1% and 54.8%,nitrogen and phosphorous losses through surface drainage were reduced by 53.9% and 51.6% from rice paddy under efficient irrigation and drainage compared with traditional irrigation and drainage.Nitrogen loss through ammonia volatilization was reduced by 14.0%.Efficient irrigation and drainage management is helpful to mitigate greenhouse gases emission,nitrogen and phosphorus losses and their pollution on groundwater and surface water.
基金Supported by the Australian Research Council,Australia (No. LP0219475)
文摘NOx and N2O emissions from coastal acid sulfate soils （CASS） cultivated for sugarcane production were investigated on the coastal lowlands of northern New South Wales, Australia. Two series of short-term measurements were made using chambers and micrometeorological techniques. Series i occurred during the wet season, the water-filled pore space （WFPS） was between 60%-80% and the site flooded during the measurements. Measurements were made directly after the harvest of soybean crop, which fixed an estimated 100 kg N ha-1, and the emission amounted to 3.2 kg NOx-N ha-1 （12 d） and 1.8 kg N20-N ha-1 （5 d）. Series 2 was made towards the end of the dry season when the WFPS was less than 60%. In Series 2-1 after an application of 50 kg N ha-1, emissions were markedly less, amounting to 0.9 kg N ha 1 over 10 d. During both series when the soil was moist, emissions of NOx were larger than those of N2O. 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. These results suggest that agricultural production on CASS could be important sources of greenhouse gases and nitrogen practices will need to be optimised to reduce the offsite effects of atmospheric warming, acidification or nitrification. Many questions still remain unanswered such as the emissions during the soybean bean filling stage and crop residue decomposition, the longer-term losses following the fertiliser application and emissions from CASS under different land uses.
