DNDC模型在稻田生态系统中的研究进展及应用
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摘要
DNDC模型(De Nitrification-DeComposition model,反硝化-分解模型)是以模拟陆地生态系统中碳氮循环为目的,耦合生态环境驱动因子及其相应的生物地球化学过程的模型,在稻田生态系统中有较好的应用。以稻田生态系统中DNDC模型应用为研究对象,通过调研与查阅文献,针对模型中稻田作物参数、温室气体排放以及氮素流失等模块的优化改进情况进行了总结和分析。目前,模型虽然已经能较好地模拟稻田生态系统中作物生长、甲烷排放以及氮素流失等,但仍然存在着诸如水稻类型匮乏、管理措施输入参数较少、氧化亚氮再现性较弱等问题。在今后发展中,模型应丰富水稻类型、改进农田管理相应参数及优化氧化亚氮的模拟机理,为在稻田减排降污方向推广模型应用、建立可靠的评估方法提供理论支撑。
DNDC model( DeNitrification-DeComposition model) is a process-oriented model that predicts carbon and nitrogen dynamics via coupling of biogeochemistry processes to ecologic environmental factors,which also has a well prediction of greenhouse gas emissions from rice paddy. Advance and application of DNDC model in paddy ecosystem were reviewed,including crop growth,greenhouse gases emissions and nitrogen loss from paddy field. The results showed that modeled results of crop growth,methane emissions,and nitrogen loss fitted observed values well after years of improvement. However,DNDC model still has its disadvantages in rice varieties,management techniques,and nitrous oxide reproducibility. These findings have implication for model improvement on the variety of rice type,input data of agricultural management,and the mechanism of nitrous oxide emissions to provide theoretical support in greenhouse gases emissions mitigation and establish a reliable evaluation method on paddy ecosystem.
DNDC model( DeNitrification-DeComposition model) is a process-oriented model that predicts carbon and nitrogen dynamics via coupling of biogeochemistry processes to ecologic environmental factors,which also has a well prediction of greenhouse gas emissions from rice paddy. Advance and application of DNDC model in paddy ecosystem were reviewed,including crop growth,greenhouse gases emissions and nitrogen loss from paddy field. The results showed that modeled results of crop growth,methane emissions,and nitrogen loss fitted observed values well after years of improvement. However,DNDC model still has its disadvantages in rice varieties,management techniques,and nitrous oxide reproducibility. These findings have implication for model improvement on the variety of rice type,input data of agricultural management,and the mechanism of nitrous oxide emissions to provide theoretical support in greenhouse gases emissions mitigation and establish a reliable evaluation method on paddy ecosystem.
引文
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[39]王欣欣.生物炭施用对稻田温室气体排放的影响研究[D].南京:南京农业大学,2013.
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[41]张远,李颖,王毅勇,等.三江平原稻田甲烷排放的模拟与估算[J].农业工程学报,2011,27(8):293-298.
[42]张庆国,李鹏飞,徐丽,等.皖中沿江平原水稻田CH4和N2O排放估算及其影响因素分析[J].土壤通报,2012,43(1):212-218.
[43]HAYANO M,FUMOTO T,YAGI K,et al. National-scale estimation of methane emission from paddy fields in Japan:Database construction and upscaling using a process-based biogeochemistry model[J]. Soil Science and Plant Nutrition,2013,59(5):812-823.
[44]JIANG Z,YIN S,ZHANG X,et al. Research and Development of a DNDC Online Model for Farmland Carbon Sequestration and GHG Emissions Mitigation in China[J]. International Journal of Environmental Research and Public Health,2017,14:1493.
[45]SIMMONDS M,LI C,LEE J,et al. Modeling methane and nitrous oxide emissions from direct-seeded rice systems[J]. Journal of Geophysical Research-Biogeosciences,2015,120(10):2011-2035.
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[50]STONE E,HORNBERGER G. Impacts of management alternatives on rice yield and nitrogen losses to the environment:A case study in rural Sri Lanka[J]. Science of the Total Environment,2016,542:271-276.
[51]ZHANG H,SUN B,XIE X,et al. Simulating the effects of chemical and non-chemical fertilization practices on carbon sequestration and nitrogen loss in subtropical paddy soils using the DNDC model[J]. Paddy and Water Environment,2015,13(4):495-506.
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[2]中华人民共和国农业农村部. 2016年中国农业统计资料[M].北京:中国农业出版社,2017.
[3]国家发展和改革委员会应对气候变化司.中华人民共和国气候变化第二次国家信息通报[M].北京:中国经济出版社,2013.
[4]WANG H,ZHANG D,ZHANG Y,et al. Ammonia emissions from paddy fields are underestimated in China[J]. Environmental Pollution,2018,235:482-488.
[5]GAO S,XU P,ZHOU F,et al. Quantifying nitrogen leaching response to fertilizer additions in China’s cropland[J]. Environmental Pollution,2016,211:241-251.
[6]HOU X,ZHAN X,ZHOU F,et al. Detection and attribution of nitrogen runoff trend in China’s croplands[J]. Environmental Pollution,2018,234:270-278.
[7]ENGEL T,PRIESACK E. Expert-N,a building block system of nitrogen models as resource for advice,research,water management and policy:Integrated Soil and Sediment Research:A Basis for Proper Protection[C]. Dordrecht:Springer,1993.
[8]COLEMAN K,JENKINSON D. Roth C-26. 3:a model for the turnover of carbon in soil:Evaluation of Soil Organic Matter Models[C]. Berlin:Springer,1996.
[9]LI C. The DNDC mode:Evaluation of Soil Organic Matter Models[C]. Berlin:Springer,1996.
[10]李长生.生物地球化学:科学基础与模型方法[M].北京:清华大学出版社,2016.
[11]GILHESPY S,ANTHONY S,CARDENAS L,et al. First 20 years of DNDC(De Nitrification De Composition):model evolution[J]. Ecological Modelling,2014,292:51-62.
[12]LI C,MOSIER A,WASSMANN R,et al. Modeling greenhouse gas emissions from rice-based production systems:sensitivity and upscaling[J].Global Biogeochemical Cycles,2004,18(1):GB1043.
[13]ZHANG Y,NIU H. The development of the DNDC plant growth sub-model and the application of DNDC in agriculture:a review[J].Agriculture,Ecosystems&Environment,2016,230:271-282.
[14]ZHANG Y,LI C,ZHOU X,et al. A simulation model linking crop growth and soil biogeochemistry for sustainable agriculture[J]. Ecological Modelling,2002,151(1):75-108.
[15]PATHAK H,LI C,WASSMANN R. Greenhouse gas emissions from Indian rice fields:calibration and upscaling using the DNDC model[J].Biogeosciences,2005,2(2):113-123.
[16]LI C,QIU J,FROLKING S,et al. Reduced methane emissions from large-scale changes in water management of China’s rice paddies during1980-2000[J]. Geophysical Research Letters,2002,29(20):1972.
[17]ZHANG Y,LI C,TRETTIN C,et al. An integrated model of soil,hydrology,and vegetation for carbon dynamics in wetland ecosystems[J].Global Biogeochemical Cycles,2002,16(4):1061.
[18]FUMOTO T,KOBAYASHI K,LI C,et al. Revising a process-based biogeochemistry model(DNDC)to simulate methane emission from rice paddy fields under various residue management and fertilizer regimes[J]. Global Change Biology,2008,14(2):382-402.
[19] KATAYANAGI N,FURUKAWA Y,FUMOTO T,et al. Validation of the DNDC-Rice model by using CH4and N2O flux data from rice cultivated in pots under alternate wetting and drying irrigation management[J]. Soil Science and Plant Nutrition,2012,58(3):360-372.
[20]BABU Y,LI C,FROLKING S,et al. Field validation of DNDC model for methane and nitrous oxide emissions from rice-based production systems of india[J]. Nutrient Cycling in Agroecosystems,2006,74(2):157-174.
[21]BABU Y,LI C,FROLKING S,et al. Modelling of methane emissions from rice-based production systems in India with the denitrification and decomposition model:field validation and sensitivity analysis[J]. Current Science,2005,89(11):1904-1912.
[22]LI C,FARAHBAKHSHAZAD N,JAYNES D,et al. Modeling nitrate leaching with a biogeochemical model modified based on observations in a row-crop field in Iowa[J]. Ecological Modelling,2006,196(1):116-130.
[23] TONITTO C,DAVID M B,DRINKWATER L E,et al. Application of the DNDC model to tile-drained Illinois agroecosystems:model calibration,validation,and uncertainty analysis[J]. Nutrient Cycling in Agroecosystems,2007,78(1):51-63.
[24]DENG J,ZHU B,ZHOU Z,et al. Modeling nitrogen loadings from agricultural soils in southwest China with modified DNDC[J]. Journal of Geophysical Research Biogeosciences,2011,116:G02020.
[25]LI H,WANG L,QIU J,et al. Calibration of DNDC model for nitrate leaching from an intensively cultivated region of Northern China[J].Geoderma,2014,223-225:108-118.
[26]李虎,王立刚,邱建军. DNDC模型在农田氮素渗漏淋失估算中的应用[J].应用生态学报,2009,20(7):1591-1596.
[27]ZHAO Z,ZHANG H,LI C,et al. Quantifying nitrogen loading from a paddy field in Shanghai,China with modified DNDC model[J].Agriculture,Ecosystems&Environment,2014,197:212-221.
[28]赵峥.基于DNDC模型的稻田氮素流失及温室气体排放研究[D].上海:上海交通大学,2016.
[29]LI C. Modeling trace gas emissions from agricultural ecosystems[J]. Nutrient Cycling in Agroecosystems,2000,58:259-276.
[30]BALASUBRAMANIAN S,NELSON A,KOLOUTSOU-VAKAKIS S,et al. Evaluation of De Nitrification De Composition model for estimating ammonia fluxes from chemical fertilizer application[J]. Agricultural and Forest Meteorology,2017,237/238:123-134.
[31]CONGREVES K,GRANT B,DUTTA B,et al. Predicting ammonia volatilization after field application of swine slurry:DNDC model development[J]. Agriculture,Ecosystems&Environment,2016,219:179-189.
[32]DUTTA B,CONGREVES K,SMITH W,et al. Improving DNDC model to estimate ammonia loss from urea fertilizer application in temperate agroecosystems[J]. Nutrient Cycling in Agroecosystems,2016,106(3):275-292.
[33]张啸林.不同稻田轮作体系下温室气体排放及温室气体强度研究[D].南京:南京农业大学,2013.
[34]CHUN J,SHIM K,MIN S,et al. Methane mitigation for flooded rice paddy systems in South Korea using a process-based model[J]. Paddy and Water Environment,2016,14(1):123-129.
[35]PATHAK H,LI C,WASSMANN R,et al. Simulation of nitrogen balance in rice-wheat systems of the Indo-Gangetic Plains[J]. Soil Science Society of America Journal,2006,70(5):1612-1622.
[36]KATAYANAGI N,ONO K,FUMOTO T,et al. Validation of the DNDC-Rice model to discover problems in evaluating the nitrogen balance at a paddy-field scale for single-cropping of rice[J]. Nutrient Cycling in Agroecosystems,2013,95(2):255-268.
[37]李小礼.平原海岛地区稻麦轮作农田生态系统减量施用氮肥的环境效应研究[D].上海:华东理工大学,2012.
[38]刘欢欢,邵东国.节灌控排条件下稻田氮平衡模拟及利用效率分析[J].灌溉排水学报,2013,32(2):52-56.
[39]王欣欣.生物炭施用对稻田温室气体排放的影响研究[D].南京:南京农业大学,2013.
[40]ZHANG L,YU D,SHI X,et al. Simulation of global warming potential(GWP)from rice fields in the Tai-Lake region,China by coupling 1∶50 000 soil database with DNDC model[J]. Atmospheric Environment,2009,43(17):2737-2746.
[41]张远,李颖,王毅勇,等.三江平原稻田甲烷排放的模拟与估算[J].农业工程学报,2011,27(8):293-298.
[42]张庆国,李鹏飞,徐丽,等.皖中沿江平原水稻田CH4和N2O排放估算及其影响因素分析[J].土壤通报,2012,43(1):212-218.
[43]HAYANO M,FUMOTO T,YAGI K,et al. National-scale estimation of methane emission from paddy fields in Japan:Database construction and upscaling using a process-based biogeochemistry model[J]. Soil Science and Plant Nutrition,2013,59(5):812-823.
[44]JIANG Z,YIN S,ZHANG X,et al. Research and Development of a DNDC Online Model for Farmland Carbon Sequestration and GHG Emissions Mitigation in China[J]. International Journal of Environmental Research and Public Health,2017,14:1493.
[45]SIMMONDS M,LI C,LEE J,et al. Modeling methane and nitrous oxide emissions from direct-seeded rice systems[J]. Journal of Geophysical Research-Biogeosciences,2015,120(10):2011-2035.
[46]LI C,FROLKING S,XIAO X,et al. Modeling impacts of farming management alternatives on CO2,CH4,and N2O emissions:A case study for water management of rice agriculture of China[J]. Global Biogeochemical Cycles,2005,19:GB3010.
[47]LI C,SALAS W,DEANGELO B,et al. Assessing alternatives for mitigating net greenhouse gas emissions and increasing yields from rice production in china over the next twenty years[J]. Journal of Environmental Quality,2006,35(4):1554-1565.
[48]TIAN Z,NIU Y,FAN D,et al. Maintaining rice production while mitigating methane and nitrous oxide emissions from paddy fields in China:Evaluating tradeoffs by using coupled agricultural systems models[J]. Agricultural Systems,2018,159:175-186.
[49]CHEN H,YU C,LI C,et al. Modeling the impacts of water and fertilizer management on the ecosystem service of rice rotated cropping systems in China[J]. Agriculture Ecosystems&Environment,2016,219:49-57.
[50]STONE E,HORNBERGER G. Impacts of management alternatives on rice yield and nitrogen losses to the environment:A case study in rural Sri Lanka[J]. Science of the Total Environment,2016,542:271-276.
[51]ZHANG H,SUN B,XIE X,et al. Simulating the effects of chemical and non-chemical fertilization practices on carbon sequestration and nitrogen loss in subtropical paddy soils using the DNDC model[J]. Paddy and Water Environment,2015,13(4):495-506.
[52]ZHAO Z,SHA Z,LIU Y,et al. Modeling the impacts of alternative fertilization methods on nitrogen loading in rice production in Shanghai[J].Science of the Total Environment,2016,566:1595-1603.
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