Establishment of Nitrogen surplus indicators in the main vegetable and orchard systems in Hainan

ZHANG Bofei; XIAO Yulin; ZHANG Chong; JU Xiaotang

doi:10.15886/j.cnki.rdswxb.20240030

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Volume 15 Issue 4

Jul. 2024

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Article Navigation > Journal of Tropical Biology > 2024 > 15(4): 391-399

ZHANG Bofei, XIAO Yulin, ZHANG Chong, JU Xiaotang. Establishment of Nitrogen surplus indicators in the main vegetable and orchard systems in Hainan[J]. Journal of Tropical Biology, 2024, 15(4): 391-399. doi: 10.15886/j.cnki.rdswxb.20240030

Citation:

ZHANG Bofei, XIAO Yulin, ZHANG Chong, JU Xiaotang. Establishment of Nitrogen surplus indicators in the main vegetable and orchard systems in Hainan[J]. Journal of Tropical Biology, 2024, 15(4): 391-399. doi: 10.15886/j.cnki.rdswxb.20240030

Establishment of Nitrogen surplus indicators in the main vegetable and orchard systems in Hainan

doi: 10.15886/j.cnki.rdswxb.20240030

School of Tropical Agriculture and Forestry, Hainan University, Haikou 570228

Received Date: 2024-02-24
Rev Recd Date: 2024-03-12
Publish Date: 2024-07-25

Abstract

This study aims to quantify the nitrogen （N） input and output of Hainan’s tropical vegetable and orchard cropping systems,establish N surplus indicators,and evaluate the environmental impacts.We collected 34 papers published in Hainan since 1980,including 72 samples of conventional and optimized N management of vegetables and orchards.The N inputs,outputs,and surpluses under conventional and optimized N management were analyzed based on the soil surface nitrogen balance method,and the N surplus under the optimized management was used as the N surplus benchmark.The life cycle assessment method （LCA） was used to quantify reactive N losses,greenhouse gas emissions,carbon and N footprints under conventional and optimized N management.Under conventional N management,the N surpluses were 290 kg·hm^-2 in vegetables and 432 kg·hm^-2 in orchards,respectively,the corresponding N surplus benchmarks under optimized N management were reduced by 39%and 49%,which were 176 and 222 kg·hm^-2,respectively.The reactive N emission,N footprint,greenhouse gas emissions（CO₂-eq）,and carbon footprint（CO₂-eq） under conventional N management of vegetables were 145 kg·hm^-2,4.5 kg·t^-1,9 444 kg hm^-2 and 295 kg·t^-1,respectively;under optimized N management,the above indicators were reduced by 26%,24%,19%and 19%,respectively.The active N emission,N footprint,greenhouse gas emission,and carbon footprint under conventional N management of orchards were 177 kg·hm^-2,4.5 kg·t^-1,14 758 kg·hm^-2 and 388 kg·eq t^-1,respectively;Optimizing N management can reduce the above indicators by 28%,33%,21%and 26%,respectively.In conclusion,the N surplus benchmarks of Hainan’s typical vegetable and orchard systems were 176 and 222 kg·hm^-2,respectively,using optimized N management （such as"4R Plus"nutrient management strategy,soil acid modification and organic carbon improvement,fertigation,etc.） can achieve the above N surplus benchmarks,and the current reactive N emissions,N footprint,greenhouse gas emissions,and carbon footprints can be reduced by 19%-33%.
- vegetable,
- orchard,
- nitrogen surplus benchmark,
- reactive nitrogen emission,
- greenhouse gas emission,
- Hainan

References

[1]	洪秀杨,钟于秀,李伟芳,等.海南农田养分平衡状况及环境风险评价[J].植物营养与肥料学报, 2022, 28(11):2070-2081.
[2]
[3]	ZHANG P, RUAN H, DAI P, et al. Spatiotemporal river flux and composition of nutrients affecting adjacent coastal water quality in Hainan Island, China[J]. Journal of Hydrology, 2020, 591:125293.
[4]	黄晖,陈竹,黄林韬,等,中国珊瑚礁状况报告2010-2019[M].北京:海洋出版社, 2021:1-127.
[5]	ZHANG C, JU X, POWLSON D, et al. Nitrogen surplus benchmarks for controlling N pollution in the main cropping systems of China[J]. Environmental Science&Technology, 2019, 53(12):6678-6687.
[6]	赵永鉴,张博飞,张翀,等.海南典型稻菜轮作区和香蕉园氮磷盈余及土壤硝态氮累积[J].中国农业科学,2023, 56(15):2954-2965.
[7]	中华人民共和国国家统计局.中国统计年鉴[M].北京:中国统计出版社, 2022.
[8]	海南省统计局.海南统计年鉴[M].北京:中国统计出版社, 2022.
[9]	武良,张卫峰,陈新平,等.中国农田氮肥投入和生产效率[J].中国土壤与肥料, 2016(4):76-83.
[10]	中华人民共和国农业农村部.中国农业农村统计摘要(2022)[M].北京:中国农业出版社, 2022.
[11]	肖玉林.中国蔬菜和果树氮素盈余指标的建立[D].海口:海南大学, 2023.
[12]	杨小林,贺梦微,陈艺晏,等.丹江口库区大气氮干湿沉降动态变化特征研究[J].人民长江, 2022, 53(5):62-68.
[13]	SMIL V. Nitrogen in crop production:an account of global flows[J]. Global Biogeochemical Cycles, 1999,13(2):647-662.
[14]	XU Z, ZHANG X, XIE J, et al. Total nitrogen concentrations in surface water of typical agro-and forest ecosystems in China, 2004-2009[J]. PLoS One, 2014, 9(3):e92850.
[15]	HE X, QIAO Y, LIU Y, et al. Environmental impact assessment of organic and conventional tomato production in urban greenhouses of Beijing city,China[J]. Journal of Cleaner Production, 2016, 134:251-258.
[16]	CHEN X H, MA C C, ZHOU H M,et al. Identifying the main crops and key factors determining the carbon footprint of crop production in China, 2001-2018[J]. Resources Conservation and Recycling, 2021, 72:105661.
[17]	ZHAO C, GAO B, WANG L, et al. Spatial patterns of net greenhouse gas balance and intensity in Chinese orchard system[J]. The Science of the Total Environment, 2021,779:146250.
[18]	王孝忠.我国蔬菜生产的环境代价、减排潜力与调控途径[D].北京:中国农业大学, 2018.
[19]	ZHAO H, LAKSHMANAN P, WANG X, et al. Global reactive nitrogen loss in orchard systems:a review[J].The Science of the Total Environment, 2022, 821:153462.
[20]	IPCC. N2O emissions from managed soils, and CO₂emissions from lime and urea application[C] //Agriculture, forestry and other land use. 2019 refinement to the 2006 IPCC guidelines for national greenhouse gas inventories, Geneva, Switzerland:IPCC,2019.
[21]	WANG X, DOU Z, SHI X, et al. Innovative management programme reduces environmental impacts in Chinese vegetable production[J]. Nature Food, 2021,2:47-53.
[22]	TEI F, DE NEVE S, DE HAAN J, et al. Nitrogen management of vegetable crops[J]. Agricultural Water Management, 2020, 240:106316.
[23]	ZHOU J, GU B, SCHLESINGER W H, et al. Significant accumulation of nitrate in Chinese semi-humid croplands[J]. Scientific Reports, 2016, 6:25088.
[24]	赵明炯,王孝忠,刘彬,等.长三角地区蔬菜生产的活性氮损失和温室气体排放估算[J].农业环境科学学报, 2020, 39(6):1409-1419.
[25]	赵环宇.我国柑橘生产的环境代价及氮素优化措施研究[D].重庆:西南大学, 2023.
[26]	ZHANG X, DAVIDSON E A, MAUZERALL D L, et al.Managing nitrogen for sustainable development[J].Nature, 2015, 528:51-59.
[27]	SOUZA E F C, SORATTO R P, SANDAÑA P, et al. Split application of stabilized ammonium nitrate improved potato yield and nitrogen-use efficiency with reduced application rate in tropical sandy soils[J]. Field Crops Research, 2020, 254:107847.
[28]	SAPKOTA T B, TAKELE R. Improving nitrogen use efficiency and reducing nitrogen surplus through best fertilizer nitrogen management in cereal production:The case of India and China[J]. Advances in Agronomy, 2023,178:233-294.
[29]	EU NITROGEN EXPERT PANEL. Nitrogen Use Efficiency(NUE)an indicator for the utilization of nitrogen in food systems[EB/OL]. 2015, https://research. wur. nl/en/publications/nitrogen-use-efficiency-nue-an-indicatorfor-the-utilisation-of-n.
[30]	SCHULTE-UEBBING L F, BEUSEN A H W,BOUWMAN A F, et al. From planetary to regional boundaries for agricultural nitrogen pollution[J]. Nature, 2022,610:507-512.
[31]	ZHU X, ZHOU P, MIAO P, et al. Nitrogen use and management in orchards and vegetable fields in China:challenges and solutions[J]. Frontiers of Agricultural Science and Engineering, 2022, 9:386-395.
[32]	HUDDELL A M, GALFORD G L, TULLY K L, et al.Meta-analysis on the potential for increasing nitrogen losses from intensifying tropical agriculture[J]. Global Change Biology, 2020, 26(3):1668-1680.

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通讯作者: 陈斌, bchen63@163.com

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沈阳化工大学材料科学与工程学院沈阳 110142

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Establishment of Nitrogen surplus indicators in the main vegetable and orchard systems in Hainan

School of Tropical Agriculture and Forestry, Hainan University, Haikou 570228

Received Date: 2024-02-24

Rev Recd Date: 2024-03-12

Publish Date: 2024-07-25

Key words:

Abstract: This study aims to quantify the nitrogen （N） input and output of Hainan’s tropical vegetable and orchard cropping systems,establish N surplus indicators,and evaluate the environmental impacts.We collected 34 papers published in Hainan since 1980,including 72 samples of conventional and optimized N management of vegetables and orchards.The N inputs,outputs,and surpluses under conventional and optimized N management were analyzed based on the soil surface nitrogen balance method,and the N surplus under the optimized management was used as the N surplus benchmark.The life cycle assessment method （LCA） was used to quantify reactive N losses,greenhouse gas emissions,carbon and N footprints under conventional and optimized N management.Under conventional N management,the N surpluses were 290 kg·hm^-2 in vegetables and 432 kg·hm^-2 in orchards,respectively,the corresponding N surplus benchmarks under optimized N management were reduced by 39%and 49%,which were 176 and 222 kg·hm^-2,respectively.The reactive N emission,N footprint,greenhouse gas emissions（CO₂-eq）,and carbon footprint（CO₂-eq） under conventional N management of vegetables were 145 kg·hm^-2,4.5 kg·t^-1,9 444 kg hm^-2 and 295 kg·t^-1,respectively;under optimized N management,the above indicators were reduced by 26%,24%,19%and 19%,respectively.The active N emission,N footprint,greenhouse gas emission,and carbon footprint under conventional N management of orchards were 177 kg·hm^-2,4.5 kg·t^-1,14 758 kg·hm^-2 and 388 kg·eq t^-1,respectively;Optimizing N management can reduce the above indicators by 28%,33%,21%and 26%,respectively.In conclusion,the N surplus benchmarks of Hainan’s typical vegetable and orchard systems were 176 and 222 kg·hm^-2,respectively,using optimized N management （such as"4R Plus"nutrient management strategy,soil acid modification and organic carbon improvement,fertigation,etc.） can achieve the above N surplus benchmarks,and the current reactive N emissions,N footprint,greenhouse gas emissions,and carbon footprints can be reduced by 19%-33%.

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Reference (32)

[1]	洪秀杨,钟于秀,李伟芳,等.海南农田养分平衡状况及环境风险评价[J].植物营养与肥料学报, 2022, 28(11):2070-2081.
[2]
[3]	ZHANG P, RUAN H, DAI P, et al. Spatiotemporal river flux and composition of nutrients affecting adjacent coastal water quality in Hainan Island, China[J]. Journal of Hydrology, 2020, 591:125293.
[4]	黄晖,陈竹,黄林韬,等,中国珊瑚礁状况报告2010-2019[M].北京:海洋出版社, 2021:1-127.
[5]	ZHANG C, JU X, POWLSON D, et al. Nitrogen surplus benchmarks for controlling N pollution in the main cropping systems of China[J]. Environmental Science&Technology, 2019, 53(12):6678-6687.
[6]	赵永鉴,张博飞,张翀,等.海南典型稻菜轮作区和香蕉园氮磷盈余及土壤硝态氮累积[J].中国农业科学,2023, 56(15):2954-2965.
[7]	中华人民共和国国家统计局.中国统计年鉴[M].北京:中国统计出版社, 2022.
[8]	海南省统计局.海南统计年鉴[M].北京:中国统计出版社, 2022.
[9]	武良,张卫峰,陈新平,等.中国农田氮肥投入和生产效率[J].中国土壤与肥料, 2016(4):76-83.
[10]	中华人民共和国农业农村部.中国农业农村统计摘要(2022)[M].北京:中国农业出版社, 2022.
[11]	肖玉林.中国蔬菜和果树氮素盈余指标的建立[D].海口:海南大学, 2023.
[12]	杨小林,贺梦微,陈艺晏,等.丹江口库区大气氮干湿沉降动态变化特征研究[J].人民长江, 2022, 53(5):62-68.
[13]	SMIL V. Nitrogen in crop production:an account of global flows[J]. Global Biogeochemical Cycles, 1999,13(2):647-662.
[14]	XU Z, ZHANG X, XIE J, et al. Total nitrogen concentrations in surface water of typical agro-and forest ecosystems in China, 2004-2009[J]. PLoS One, 2014, 9(3):e92850.
[15]	HE X, QIAO Y, LIU Y, et al. Environmental impact assessment of organic and conventional tomato production in urban greenhouses of Beijing city,China[J]. Journal of Cleaner Production, 2016, 134:251-258.
[16]	CHEN X H, MA C C, ZHOU H M,et al. Identifying the main crops and key factors determining the carbon footprint of crop production in China, 2001-2018[J]. Resources Conservation and Recycling, 2021, 72:105661.
[17]	ZHAO C, GAO B, WANG L, et al. Spatial patterns of net greenhouse gas balance and intensity in Chinese orchard system[J]. The Science of the Total Environment, 2021,779:146250.
[18]	王孝忠.我国蔬菜生产的环境代价、减排潜力与调控途径[D].北京:中国农业大学, 2018.
[19]	ZHAO H, LAKSHMANAN P, WANG X, et al. Global reactive nitrogen loss in orchard systems:a review[J].The Science of the Total Environment, 2022, 821:153462.
[20]	IPCC. N2O emissions from managed soils, and CO₂emissions from lime and urea application[C] //Agriculture, forestry and other land use. 2019 refinement to the 2006 IPCC guidelines for national greenhouse gas inventories, Geneva, Switzerland:IPCC,2019.
[21]	WANG X, DOU Z, SHI X, et al. Innovative management programme reduces environmental impacts in Chinese vegetable production[J]. Nature Food, 2021,2:47-53.
[22]	TEI F, DE NEVE S, DE HAAN J, et al. Nitrogen management of vegetable crops[J]. Agricultural Water Management, 2020, 240:106316.
[23]	ZHOU J, GU B, SCHLESINGER W H, et al. Significant accumulation of nitrate in Chinese semi-humid croplands[J]. Scientific Reports, 2016, 6:25088.
[24]	赵明炯,王孝忠,刘彬,等.长三角地区蔬菜生产的活性氮损失和温室气体排放估算[J].农业环境科学学报, 2020, 39(6):1409-1419.
[25]	赵环宇.我国柑橘生产的环境代价及氮素优化措施研究[D].重庆:西南大学, 2023.
[26]	ZHANG X, DAVIDSON E A, MAUZERALL D L, et al.Managing nitrogen for sustainable development[J].Nature, 2015, 528:51-59.
[27]	SOUZA E F C, SORATTO R P, SANDAÑA P, et al. Split application of stabilized ammonium nitrate improved potato yield and nitrogen-use efficiency with reduced application rate in tropical sandy soils[J]. Field Crops Research, 2020, 254:107847.
[28]	SAPKOTA T B, TAKELE R. Improving nitrogen use efficiency and reducing nitrogen surplus through best fertilizer nitrogen management in cereal production:The case of India and China[J]. Advances in Agronomy, 2023,178:233-294.
[29]	EU NITROGEN EXPERT PANEL. Nitrogen Use Efficiency(NUE)an indicator for the utilization of nitrogen in food systems[EB/OL]. 2015, https://research. wur. nl/en/publications/nitrogen-use-efficiency-nue-an-indicatorfor-the-utilisation-of-n.
[30]	SCHULTE-UEBBING L F, BEUSEN A H W,BOUWMAN A F, et al. From planetary to regional boundaries for agricultural nitrogen pollution[J]. Nature, 2022,610:507-512.
[31]	ZHU X, ZHOU P, MIAO P, et al. Nitrogen use and management in orchards and vegetable fields in China:challenges and solutions[J]. Frontiers of Agricultural Science and Engineering, 2022, 9:386-395.
[32]	HUDDELL A M, GALFORD G L, TULLY K L, et al.Meta-analysis on the potential for increasing nitrogen losses from intensifying tropical agriculture[J]. Global Change Biology, 2020, 26(3):1668-1680.

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Establishment of Nitrogen surplus indicators in the main vegetable and orchard systems in Hainan

doi: 10.15886/j.cnki.rdswxb.20240030

Abstract

References

Proportional views

通讯作者: 陈斌, bchen63@163.com

Proportional views

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