Effect of Organic Fertilizers on Gas Emission from Lettuce-growing Soil in a Solar Greenhouse
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摘要: 采用静态箱-气相色谱法研究日光温室生菜地不施肥(CK)、施用腐熟鸡粪(H)、羊粪(S)、鸡粪+秸秆(HSt)、羊粪+秸秆(SSt)、羊粪+鸡粪+秸秆(SHSt)等6种处理的温室气体排放通量及增温潜势(GWP)。结果表明:(1)H、S、HSt处理的N2O排放通量在施肥前、中、后期呈近“V”型变化,CK、SSt、SHSt呈倒“V”型变化;S、SSt、SHSt处理的CH4排放通量呈倒“V”型变化;CO2排放通量均呈近“V”型变化(SSt除外);(2)施肥前期,HSt、S、H、SHSt、SSt处理的N2O排放通量分别较CK显著增加2.89、2.32、1.48、1.17、0.95倍;S、H的CH4排放通量显著高于CK处理1.91、1.11倍;H的CO2排放通量显著低于CK处理3.88倍。施肥中期,HSt的N2O排放通量显著低于CK处理1.93倍;SHSt的CH4排放通量显著高于CK处理1.34倍;各施肥处理的CO2排放通量与CK差异不显著。施肥后期,H的N2O排放通量显著高于CK处理1.10倍;SHSt、SSt、S的CH4排放通量显著低于CK处理3.76、5.25、5.58倍;HSt的CO2排放通量显著高于CK处理8.61倍;(3)全球增温潜势(GWP)按照S>SHSt>HSt>SSt>CK>H依次减小,建议施用腐熟鸡粪、鸡粪加秸秆及羊粪加秸秆。Abstract: Emission flux of greenhouse gases (GHGs) and global warming potential (GWP) of asolarlettuce-greenhouse using organic fertilizers were studied. A decomposed chicken manure (H), a sheep manure (S), a chicken manure/straw combination (HSt), a sheep manure/straw combination (SSt), a sheep manure, or a chicken manure/straw combination (SHSt) wasapplied on the soil. The atmospheric conditions in the greenhouse with each fertilization were monitored using the static chamber-gas chromatograph techniques. The results showed that (1) throughout the entire fertilization period, the N2O emissionsfrom H, S and HSt were in a V-shapemathematicfunction, whileCK, SSt and SHSt, an inverted V-shape function; the CH4 emissionsfrom S, SSt and SHSt were inan inverted V-shape trend; and, the CO2 emissionsfrom all, except SSt, were in aV-shape; (2) during the early stage of the fertilizations, the N2O emissionsfrom HSt, S, H, SHSt and SSt were 2.89, 2.32, 1.48, 1.17 and 0.95 times, respectively, greater than that of CK; the CH4 emissionsfrom S and H, 1.91 and 1.11 times, respectively, greater than that of CK; and, the CO2 emission from H, 3.88 times lower than that of CK; and, in the middle of the fertilizations, the N2O emission from HSt was 1.93 times lower than CK; the CH4 emission from SHSt, 1.34 times greater than CK; and, no significant differences onthe CO2 emissionsbetween CK and all other treatments; whereas, at the late stage of the fertilizations, the N2O emission from H was 1.10 times greater than CK; the CH4 emissionsfrom SHSt, SSt and S, 3.76, 5.25 and 5.58 times, respectively, lower than CK; and, the CO2 emission of HSt, 8.61 times greater than CK; and, (3) GWP for the various fertilization treatments decreased in the order of S > SHSt > HSt > SSt > CK > H. Consequently, H, SSt, orHSt was recommended for farmingapplicationsin light of their potentials in GHG emission reduction.
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Key words:
- decomposed manure /
- solar greenhouse /
- lettuce soil /
- greenhouse gas emission flux /
- GWP
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表 1 不同施肥处理肥料施用情况
Table 1. Application of different manures
处理 鸡粪 羊粪 鸡粪+
秸秆羊粪+
秸秆羊粪+鸡
粪+秸秆总碳含量/% 30 32 38.25 39.25 36.17 有机质含量/% 25.5 26 31.5 33.5 30 施肥用量/(t·ha-1) 25 25 25 25 25 注:表中各处理有机物料均为等体积混合,各有机物料在施用前均经过堆沤腐熟。 表 2 不同施肥处理N2O排放通量及方差分析结果
Table 2. Variance analysis results of N2O emission flux under different treatments
处理 4月19日/
(μg·m-2·h-1)5月1日/
(μg·m-2·h-1)5月18日/
(μg·m-2·h-1)CK b-38.91±25.35 c a 59.93±5.81 ab a 39.08±18.86 b H b 18.84±7.12 b b 22.24±3.31 b a 82.26±3.85 a S a 51.38±3.67 a a 38.3±11.34 ab a 33.08±6.86 b HSt a 73.61±16.40 a b-55.82±9.58 c a 47.38±11.63 b SSt b-2.11±4.55 b a 30.98±5.97 ab ab 15.57±13.97 b SHSt b 6.65±4.67 b a 66.89±21.61 a b 20.57±1.16 b 注:数字前同行不同小写字母表示同一处理不同时期在P=0.05水平上差异显著,数字后同列不同小写字母表示同一时期不同处理在P=0.05水平上差异显著。表 3、4同。 表 3 不同施肥处理CH4排放通量及方差分析结果
Table 3. Variance analysis results of CH4 emission flux under different treatments
处理 4月19日/
(μg·m-2·h-1)5月1日/
(μg·m-2·h-1)5月18日/
(μg·m-2·h-1)CK b-53.84±31.68 c a 56.14±4.8 b a 76.12±18.62 a H a 5.71±5.54 ab a 39.30±16.41 b a 22.04±17.51 ab S a 49.12±26.53 a a 36.46±18.68 b b-348.27±144.25 c HSt a-24.15±2.69 bc a-15.41±21.01 b a-59.21±24.30 ab SSt a-9.69±4.44 bc a 47.71±14.92 b a-323.25±134.25 c SHSt ab-19.73±10.28 bc a 131.42±42.58 a b-209.98±101.38 bc 表 4 不同施肥处理CO2排放通量及方差分析结果
Table 4. Variance analysis results of CO2 emission flux under different treatments
处理 4月19日/
(μg·m-2·h-1)5月1日/
(μg·m-2·h-1)5月18日/
(μg·m-2·h-1)CK a 142.04±52.88 ab b-291.24±69.23 ab b-120.64±8.95 b H b-409.19±41.24 c b-494.97±127.32 b a-5.85±44.41 b S a 497.33±67.17 a b-118.99±178.99 a b-266.74±74.76 b HSt b-26.05±5.24 bc c-481.06±90.75 b a 918.09±52.28 a SSt a 244.60±42.84 ab a 32.58±80.72 a b-263.45±124.88 b SHSt a 396.80±244.69 ab a-196.93±104.70 ab a-64.84±213.07 b 表 5 不同施肥处理温室气体排放量及全球增温潜势(GWP)
Table 5. GHG emission and GWP of variousfertilizations
[单位/ (kg·hm-2)]
处理N2O排放量 CO2排放量 CH4排放量 总GWP 累积排放量① CO2 当量 累积排放量① CO2 当量 CK 0.06 16.46 -353.45 0.08 2.09 -334.89 H 0.61 182.68 -5235.47 0.29 7.15 -5045.65 S 0.72 214.56 2606.83 -1.04 -26.07 2795.32 HSt 0.65 193.39 2290.46 -0.53 -13.23 2470.61 SSt 0.16 47.93 996.04 -1.39 -34.76 1009.20 SHSt 0.38 114.20 2399.75 -0.67 -16.71 2497.25 注:① 表中累积排放量为生菜从定植到收获整个生长季的温室气体排放总量。 -
[1] IPCC. The physical science basis. Working Group I Contribution to the Fifth Assessment Report of the IPCC[R]. UK:Cambridge University Press, 2013. [2] 葛全胜, 王芳, 王绍武, 等.对全球变暖认识的七个问题的确定与不确定性[J].中国人口资源与环境, 2014, 24(1):1-5. http://www.cnki.com.cn/Article/CJFDTOTAL-ZGRZ201401001.htm [3] 姜大膀, 福元海. 2℃全球变暖背景下中国未来气候变化预估[J].大气科学, 2012, 36(2):234-244. doi: 10.3878/j.issn.1006-9895.2011.11074 [4] 秦大河.气候变化科学与人类可持续发展[J].地理科学进展, 2014, 33(7):874-883. doi: 10.11820/dlkxjz.2014.07.002 [5] IPCC. Climate Change 2007-Impacts, Adaptation and Vulnerability[M]. Cambriage, UK and New York:Cambriage University Press, 2007:750-752. [6] THOMPSON AG, WAGNER-RIDDLE C, FLEMING R. Emissions of N2O and CH4 during the composting of liquid swine manure[J]. Environmental Monitoring and Assessment, 2004, 91(1/3):87-104. https://www.ncbi.nlm.nih.gov/pubmed/14969439/ [7] WEST T O, MARLAND G. Net carbon flux from agricultural ecosystems:Methodology for full carbon cycle analyses[J]. Environ Pollut, 2002. 116:439-444. doi: 10.1016/S0269-7491(01)00221-4 [8] 翟胜, 高宝玉, 王巨媛, 等.农田土壤温室气体产生机制及影响因素研究进展[J].生态环境, 2008, 17(6):2488-2493. http://www.cnki.com.cn/Article/CJFDTOTAL-TRYJ200806072.htm [9] 孙树臣, 翟胜, 王巨媛, 等.土壤CH4产生机理及其排放的影响因素[J].贵州农业科学, 2011, 39(1):135-138. http://kns.cnki.net/KCMS/detail/detail.aspx?filename=gate201101041&dbname=CJFD&dbcode=CJFQ [10] 邹建文, 黄耀, 宗良纲, 等.不同种类有机肥施用对稻田CH4和N2O排放的综合影响[J].环境科学, 2003, 24(4):7-12. http://kns.cnki.net/KCMS/detail/detail.aspx?filename=hjkz200304001&dbname=CJFD&dbcode=CJFQ [11] 沈仕洲, 王风, 薛长亮, 等.施用有机肥对农田温室气体排放影响研究进展[J].中国土壤与肥料, 2015, (6):2-8. http://www.cnki.com.cn/Article/CJFDTOTAL-TRFL201506001.htm [12] 郭腾飞, 梁国庆, 周卫, 等.施肥对稻田温室气体排放及土壤养分的影响[J].植物营养与肥料学报, 2016, 22(2):337-345. doi: 10.11674/zwyf.14557 [13] 马义虎, 顾道健, 刘立军, 等.玉米秸秆源有机肥对水稻产量与温室气体排放的影响[J].中国水稻科学, 2013, 27(5):520-528. http://www.cnki.com.cn/Article/CJFDTOTAL-ZGSK201305009.htm [14] 刘红江, 郭智, 郑建初, 等.不同栽培技术对稻季CH4和N2O排放的影响[J].生态环境学报, 2015, 24(6):1022-1027. [15] 翟振, 王立刚, 李虎, 等.有机无机肥料配施对春玉米农田N2O排放及净温室效应的影响[J].农业环境科学学报, 2013, 32(12):2502-2510. [16] 周鹏, 李玉娥, 刘利民, 等.施肥处理和环境因素对华北平原春玉米田N2O排放的影响[J].中国农业气象, 2011, 32(2):179-184. http://kns.cnki.net/KCMS/detail/detail.aspx?filename=zgny201102006&dbname=CJFD&dbcode=CJFQ [17] 吴家梅, 纪雄辉, 彭华, 等.不同种类有机肥施用对一季稻田CH4排放的影响[J].农业环境科学学报, 2011, 30(8):1688-1694. http://kns.cnki.net/KCMS/detail/detail.aspx?filename=nhbh201108034&dbname=CJFD&dbcode=CJFQ [18] 石生伟, 李玉娥, 李明德, 等.不同施肥处理下双季稻田CH4和N2O排放的全年观测研究[J].大气科学, 2011, 35(4):707-720. [19] 罗良国, 近藤始彦, 伊藤纯雄.日本长期不同施肥稻田N2O和CH4排放特征及其环境影响[J].应用生态学报, 2010, 21(12):3200-3206. http://kns.cnki.net/KCMS/detail/detail.aspx?filename=yysb201012030&dbname=CJFD&dbcode=CJFQ [20] 李波, 荣湘民, 谢桂先, 等.不同有机无机肥配施对双季稻田CH4排放的影响[J].生态环境学报, 2013, 22(2):276-282. http://adp.cnki.net/adfiles/ad/2017/0511/636301128184483750.jpg [21] 孙国峰, 郑建初, 陈留根, 等.配施猪粪对麦季CH4和N2O排放及温室效应的影响[J].生态与农村环境学报, 2012, 8(4):349-354. http://kns.cnki.net/KCMS/detail/detail.aspx?filename=ncst201204003&dbname=CJFD&dbcode=CJFQ [22] 邹建文, 黄耀, 宗良纲, 等.稻田不同种类有机肥施用对后季麦田N2O排放的影响[J].环境科学, 2006, 7(7):1264-1268. http://kns.cnki.net/KCMS/detail/detail.aspx?filename=hjkz200607001&dbname=CJFD&dbcode=CJFQ [23] 董玉红, 欧阳竹.有机肥对农田土壤二氧化碳和甲烷通量的影响[J].应用生态学报, 2005, 16(7):1303-1307. http://www.cnki.com.cn/Article/CJFDTOTAL-YYSB200507023.htm [24] 胡保安, 贾宏涛, 朱新萍, 等.不同水分条件下巴音布鲁克天鹅湖高寒湿地夏季N2O日排放特征[J].生态环境学报, 2015, 24(5):811-817. http://kns.cnki.net/KCMS/detail/detail.aspx?filename=tryj201505014&dbname=CJFD&dbcode=CJFQ [25] 史书, 木志坚, 吴波, 等.长期不同施肥处理对稻-麦轮作紫色土稻季CO2排放的影响[J].西南大学学报(自然科学版), 2015, 37(7):16-22. http://kns.cnki.net/KCMS/detail/detail.aspx?filename=xnnd201507003&dbname=CJFD&dbcode=CJFQ [26] 王浩成, 陈楠楠, 周超, 等.缓释氮肥对菊芋生长季土壤CH4和N2O排放的影响[J].生态与农村环境学报, 2012, 28(4):343-348. http://kns.cnki.net/KCMS/detail/detail.aspx?filename=ncst201204002&dbname=CJFD&dbcode=CJFQ [27] 万运帆, 李玉娥, 高清竹, 等.不同农业措施下冬小麦田N2O排放通量的特征[J].中国农业气象, 2008, 29(2):130-133. http://kns.cnki.net/KCMS/detail/detail.aspx?filename=zgny200802004&dbname=CJFD&dbcode=CJFQ [28] 邹建文. 稻麦轮作生态系统温室气体排放研究[D]. 南京: 南京农业大学, 2005, 43-46. [29] 张婧, 李虎, 王立刚, 等.京郊典型设施蔬菜地土壤N2O排放特征[J].生态学报, 2014, 34(14):4088-4098. http://adp.cnki.net/adfiles/ad/2017/0421/636283636114531250.jpg [30] 陈哲, 陈媛媛, 高霁, 等.不同施肥措施对黄河上游罐区油葵田土壤N2O排放的影响[J].应用生态学报, 2015, 26(1):129-139. http://kns.cnki.net/KCMS/detail/detail.aspx?filename=yysb201501019&dbname=CJFD&dbcode=CJFQ [31] 黄晶, 刘宏斌, 王伯仁.长期施肥下红壤旱地CO2、N2O排放特征[J].中国农学通报, 2009, 25(24):428-433. http://kns.cnki.net/KCMS/detail/detail.aspx?filename=zntb200924088&dbname=CJFD&dbcode=CJFQ [32] 姜宁宁, 李玉娥, 华珞, 等.不同氮源及秸秆添加对菜地土壤N2O排放的影响[J].土壤通报, 2012, 43(1):219-223. http://kns.cnki.net/KCMS/detail/detail.aspx?filename=trtb201201043&dbname=CJFD&dbcode=CJFQ [33] MENG L, DING W X, CAI Z C. Long term application of organic manure and nitrogen fertilizer on N2O emissions, soil quality and crop production in a sandy loam soil[J].Soil Biology & Biochemistry, 2005, 37(1):2037-2045. https://www.researchgate.net/publication/248447470_Long-term_application_of_organic_manure_and_nitrogen_fertilizer_on_N2O_emissions_soil_quality_and_crop_production_in_a_sandy_loam_soil [34] 付薇薇, 尹力初, 张蕾, 等.变更施肥管理对不同肥力水稻CH4排放影响[J].山东农业科学, 2015, 47(4):71-75. http://kns.cnki.net/KCMS/detail/detail.aspx?filename=agri201504019&dbname=CJFD&dbcode=CJFQ [35] 宋利娜, 张玉铭等.华北平原高产农区冬小麦农田土壤温室气体排放及其综合温室效应[J].中国生态农业学报, 2013, 21(3):297-307. http://www.cnki.com.cn/Article/CJFDTOTAL-ZGTN201303006.htm