This experiment was conducted in Xinxiang, Henan from June 2013 to June 2014. Total four treatments were designed including farmers ’ common practice (F, 250 kg/hm^2), 80% F (LF, 200 kg/hm^2), 80% F+biochar (LF...This experiment was conducted in Xinxiang, Henan from June 2013 to June 2014. Total four treatments were designed including farmers ’ common practice (F, 250 kg/hm^2), 80% F (LF, 200 kg/hm^2), 80% F+biochar (LFC) and no fertilizer (CK) to measure the dynamic emissions of CO2 and N2O from a summer maize-winter wheat field by static chamber-gas chromatography method. The results showed that the soil CO2 emission was 21.8-1 022.7 mg/(m^2·h), and was mainly influenced by soil temperature and moisture content. During the growth of summer maize, the soil CO2 emission was more significantly affected by soil moisture con-tent; and in winter wheat growing season, it was more significantly affected by soil temperature in the top 5 cm. The LF and LFC treatments significantly reduced the soil cumulative CO2 emission, especial y during the growth of winter wheat. Fertiliza-tion and irrigation were the main factors influencing the soil N2O emission. The soil N2O emission during the fertilization period accounted for 73.9%-74.5% and 40.5%-43.6% of the soil cumulative N2O emission during the summer maize-and winter wheat-growing season, respectively. The peak of emission fluxes was determined by fertilization amount, while the occurrence time of emission peak and emission re-duction effect were influenced by irrigation. The LF treatment reduced the soil cu-mulative N2O emission by 15.7%-16.8% and 18.1%-18.5% during the growth period of summer maize and winter wheat, respectively. Reduced nitrogen fertilization is an effective way for reducing N2O emission in intensive high-yielding farmland. Under a suitable nitrogen level (200 kg/hm^2), the application of biochar showed no significant effect on the soil N2O emission in a short term. The N2O emission factors of the L and LF treatments were 0.60% and 0.56%, respectively. ln the intensive high-yield-ing farmland of North China, reducing the nitrogen application amount is an appro-priate measure to mitigate greenhouse gas emissions without crop yield loss.展开更多
Black carbon is a by-product of incomplete combustion of carbon containing fuels. It can alter atmos-pheric radiation property and make adverse impacts on human health. The energy consumption in Beijing City depends l...Black carbon is a by-product of incomplete combustion of carbon containing fuels. It can alter atmos-pheric radiation property and make adverse impacts on human health. The energy consumption in Beijing City depends largely on coal burning. Recently,Beijing City has been performing the municipal energy structure adjustment as a tool for air pollution abatement,aiming at the air quality goal for the Beijing 2008 Olympic Games. Based on Beijing energy use data in 2000,combined with emission fac-tors of major sources of black carbon,the emission of black carbon in Beijing City is estimated to be 7.77 Gg. Coke,raw coal and biomass as non-commercial energy are the main contributors to municipal black carbon emissions. Based on Beijing energy planning in the year 2008,the emission of black carbon in 2008 will be 2.97 Gg if the contribution from biomass is not taken into account. Assuming that the black carbon emission from rural biomass in 2008 is the same as that in 2004,the biomass burning will be the largest emitter of black carbon to Beijing City in 2008.展开更多
基金Supported by National Key Technology Research and Development Program(2013BAD11B03)National Natural Science Foundation(31272249,31071865,41505100)~~
文摘This experiment was conducted in Xinxiang, Henan from June 2013 to June 2014. Total four treatments were designed including farmers ’ common practice (F, 250 kg/hm^2), 80% F (LF, 200 kg/hm^2), 80% F+biochar (LFC) and no fertilizer (CK) to measure the dynamic emissions of CO2 and N2O from a summer maize-winter wheat field by static chamber-gas chromatography method. The results showed that the soil CO2 emission was 21.8-1 022.7 mg/(m^2·h), and was mainly influenced by soil temperature and moisture content. During the growth of summer maize, the soil CO2 emission was more significantly affected by soil moisture con-tent; and in winter wheat growing season, it was more significantly affected by soil temperature in the top 5 cm. The LF and LFC treatments significantly reduced the soil cumulative CO2 emission, especial y during the growth of winter wheat. Fertiliza-tion and irrigation were the main factors influencing the soil N2O emission. The soil N2O emission during the fertilization period accounted for 73.9%-74.5% and 40.5%-43.6% of the soil cumulative N2O emission during the summer maize-and winter wheat-growing season, respectively. The peak of emission fluxes was determined by fertilization amount, while the occurrence time of emission peak and emission re-duction effect were influenced by irrigation. The LF treatment reduced the soil cu-mulative N2O emission by 15.7%-16.8% and 18.1%-18.5% during the growth period of summer maize and winter wheat, respectively. Reduced nitrogen fertilization is an effective way for reducing N2O emission in intensive high-yielding farmland. Under a suitable nitrogen level (200 kg/hm^2), the application of biochar showed no significant effect on the soil N2O emission in a short term. The N2O emission factors of the L and LF treatments were 0.60% and 0.56%, respectively. ln the intensive high-yield-ing farmland of North China, reducing the nitrogen application amount is an appro-priate measure to mitigate greenhouse gas emissions without crop yield loss.
基金Supported by the National Natural Science Foundation of China (Grant No. 20637001)Project Comprehensive Impact of Atmospheric Brown Clouds and Strategies in China (Phase I), Ministry of Science and Technology, China
文摘Black carbon is a by-product of incomplete combustion of carbon containing fuels. It can alter atmos-pheric radiation property and make adverse impacts on human health. The energy consumption in Beijing City depends largely on coal burning. Recently,Beijing City has been performing the municipal energy structure adjustment as a tool for air pollution abatement,aiming at the air quality goal for the Beijing 2008 Olympic Games. Based on Beijing energy use data in 2000,combined with emission fac-tors of major sources of black carbon,the emission of black carbon in Beijing City is estimated to be 7.77 Gg. Coke,raw coal and biomass as non-commercial energy are the main contributors to municipal black carbon emissions. Based on Beijing energy planning in the year 2008,the emission of black carbon in 2008 will be 2.97 Gg if the contribution from biomass is not taken into account. Assuming that the black carbon emission from rural biomass in 2008 is the same as that in 2004,the biomass burning will be the largest emitter of black carbon to Beijing City in 2008.