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采用静态箱———气相色谱法对崇明岛稻麦轮作生态系统主要温室气体CO2、CH4和N2 O排放进行了田间原位观测,并分析了影响温室气体排放的主要因素。结果表明,崇明岛稻麦轮作生态系统中,CH4和N2 O的显著排放仅出现在水稻生长季,且透明箱与暗箱测得通量季节变化趋势具有高度一致性;水稻田是CH4和N2 O的排放源,是CO2的吸收汇;冬小麦生长季农田表现为CH4的吸收汇,是CO2和N2 O的排放源。整个稻麦轮作周期内,CH4、N2 O以及暗箱CO2(即呼吸排放CO2)通量与各温度因子呈现出显著或极显著正相关性;CH4通量与土壤含水率、土壤C/N比值均存在极显著正相关性。另外,稻田CH4通量与土壤有机质( SOM)含量之间存在极显著正相关性,与土壤NH+4?N含量呈显著正相关关系;而稻田N2 O通量与NO-3?N含量存在极显著正相关关系。

This paper used static chamber technique to investigate the emission and consumption of CO2 , CH4 and N2 O in rice?wheat rotation system, in Chongming Island. Based on one year data, the following conclusions were drawn: On the whole, rice field was the emission source of CH4 and N2 O, and the sink of CO2 . Wheat field was the sink of CH4 , and the emission source of CO2 . In rice?wheat rotation field period, the correlation between CH4 , N2 O, CO2 respiration emission flux ( opaque chamber ) and the temperature was significant or extremely significant; Extremely significant positive correlation between annual CH4 flux variation, soil moisture content, and C/N value was found. In rice field period, there was the significant positive correlation between CH4 flux and SOM( Soil organic matter) content, NH+4?N content;the significant positive correlation between N2 O flux and NO-3?N content also was found.

参考文献

[1] 蔡博峰;刘春兰;陈操操.城市温室气体清单研究[M].北京:化学工业出版社,2009:1,6-7.
[2] Solomon S;Qin D;Manning M.Climate Change 2007:The Physical Science Basis, Contribution of Working GroupⅠto the Fourth Assessment Report of the Intergovernmental Panel on Climate Change[M].Cambridge,UK and New York,USA:Cambridge University Press,2007:996.
[3] Hansen J E;Lacis A A .Sun and dust versus greenhouse gases:An assessment of their relative roles in global climate change[J].NATURE,1990,346:713-719.
[4] 侯玉兰,王军,陈振楼,王东启,许世远.崇明岛稻麦轮作系统稻田温室气体排放研究[J].农业环境科学学报,2012(09):1862-1867.
[5] 李晓密,伦小秀,陈琪,李佳慧,闫前江,宋晓梅.不同施肥处理下冬小麦-夏玉米轮作农田温室气体的排放[J].环境化学,2014(04):591-596.
[6] 彭世彰,杨士红,丁加丽,徐俊增.农田土壤N2O排放的主要影响因素及减排措施研究进展[J].河海大学学报(自然科学版),2009(01):1-6.
[7] 彭世彰,杨士红,徐俊增.控制灌溉对稻田CH4和N2O综合排放及温室效应的影响[J].水科学进展,2010(02):235-240.
[8] 蔡祖聪;颜晓元;鹤田治雄 等.丘陵区稻田CH4排放的空间分布[J].土壤学报,1995,32(s):151-159.
[9] Denmead O T;Freney J R;Simpson J R .Nitrous oxide emission during denitrification in a flooded field[J].Soil Society of America Journal,1979,43(4):716-718.
[10] Freney J R;Denmead O T;Watanable I et al.Ammonia and nitrous oxide losses following applications of ammonium su1fate to flooded rice[J].Australian Journal of Agricultural Research,1981,32(l):37-45.
[11] 郑循华;王明星;王跃思 等.稻麦轮作生态系统中土壤湿度对 N2O 产生与排放的影响[J].应用生态学报,1996,7(3):273-279.
[12] Huang Y;Jiang J;Zong L .Comparison of field measurement of CH4 emission from rice cultivation from Nanjing,China and in Texas,USA[J].ADVANCES IN ATMOSPHERIC SCIENCES,2001,18(6):1121-1130.
[13] 上官行健,王明星.稻田土壤中甲烷产生率的实验研究[J].大气科学,1993(05):604.
[14] 王丽媛,孙洁梅,徐荣.植物残体施用对土壤排放N2O的影响[J].新疆农业大学学报,2006(03):26-30.
[15] 蒋静艳,黄耀,宗良纲.稻田土壤理化特性对CH4排放的影响[J].土壤与环境,2001(01):27-29.
[16] Conrad R;Rothfuss F .Methane oxidation in the soil surface-layer of a flooded rice field and the effect of ammonium[J].Biology and Fertilization of Soils,1991,12(1):28-32.
[17] King G M;Schnell S .Effect of increasing atmospheric methane concentration on ammonium inhibition of soil methane consumption[J].NATURE,1994,370(6487):282-284.
[18] Xu X;Wang Y;ZhengX et al.Methane emission from a simulated rice field ecosystem as influenced by hydroquinone and dicyandiamide[J].The Science of the Total Environment,2000,263:243-253.
[19] 上官行键;王明星;陈德章 等.稻田土壤中CH4的产生[J].地球科学进展,1993,8(5):1-12.
[20] IPCC;Houghton J T;Ding Y .Climate Change 2001:The Scientific Basis[R].Cambridge,UK:Cambridge University Press,2001.
[21] 刘宏栋 .氮素形态对稻田土壤N<,2>O和CH<,4>排放影响研究[D].浙江大学,2007.
[22] 田光明,何云峰,李勇先.水肥管理对稻田土壤甲烷和氧化亚氮排放的影响[J].土壤与环境,2002(03):294-298.
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