控制流域氮流失的最佳管理措施配置及效率评估

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摘要以潮河流域为研究对象，分别进行流域整体单一措施配置和氮流失分区综合措施配置，既采用负荷去除法从污染负荷削减率的角度对BMPs配置效率进行评价，也采用R-R-V （Reliability-Resilience-Vulnerability）指数法从可靠性、可修复性和脆弱性等角度对流域水质改善效果进行评价.结果表明，分区进行氮流失综合措施配置效果更为理想，研究年内流域出口总氮削减率为14.35%~31.65%，年平均削减率为24.98%，在地表水Ⅱ类评估标准下，年平均总氮R-R-V指数为0.37、0.24、95.78，而多项单一措施的年平均削减率为17.48%，月尺度平均总氮R-R-V指数为0.36、0.24、112.96.R-R-V指数法从可靠性、可修复性和脆弱性等角度反映消减效率，无论单一措施配置或分区综合措施配置，可靠性指数与脆弱性指数的改善效率较高（大于14%），而可修复性指数的改善效率较低.多数情况下可靠性指数与脆弱性指数的改善效率高于总氮削减率，可修复性指数的改善效率低于总氮削减率，表明流域总氮负荷虽然得到一定程度的削减且短期低于标准负荷，但其生态修复难度依旧较大.营养物标准负荷所对应浓度的设定是评估流域R-R-V指数改善效果的关键，且评估标准越严格，待评估营养物的R-R-V指数越趋于稳定.

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	郭英壮
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关键词 ：潮河流域, 氮流失, 最佳管理措施, 负荷去除法, R-R-V指数法

Abstract：In this paper, the single practice configuration and the comprehensive practices configuration were carried out respectively. Two evaluating methods including the load removal method, which was used to evaluate the configuration efficiency of BMPs from the perspective of pollution load reduction rate, and the R-R-V (Reliability-Resilience-Vulnerability) index method, which was used to evaluate the water quality improvement effect from the perspective of reliability, resilience and vulnerability, were both used in the Chaohe River Basin. The results showed that the effect of zoning comprehensive nitrogen loss practices was more ideal. The reduction rate of total nitrogen (TN) during the study year varied from 14.35% to 31.65%, and the average annual reduction rate was 24.98%. By the criteria for National surface water standard of Class II, the average annual R-R-V index of TN was 0.37, 0.24, and 95.78, respectively. The average annual reduction rate of multiple single practices was 17.48%, and the average monthly R-R-V index of TN was 0.36, 0.24, and 112.96, respectively. The R-R-V index reflected the reduction efficiency from multiple perspectives. Regardless of the configuration of single practices or the comprehensive practices, the improvement efficiency of reliability index and that of vulnerability index were higher (more than 14%), while the improvement efficiency of resilience index was lower. And in most cases, the improvement efficiency of reliability index and that of vulnerability index were higher than the TN reduction rate, while the improvement efficiency of resilience index was lower than the TN reduction rate. It shows that although the TN load has been reduced to a certain extent and is lower than the standard load in the short term, its ecological restoration is still difficult. The setting of the concentration corresponding to the standard load of nutrients is the key to evaluating the improvement efficiency of the R-R-V index. The stricter the evaluation standard, the more stable the R-R-V index of the nutrients to be evaluated.

Key words： Chaohe River Basin nitrogen loss best management practices load removal method R-R-V index method

收稿日期: 2020-07-06

PACS:

X52

基金资助:国家重点研发计划（2018YFD0800902）；北京市自然科学基金委员会-北京市教育委员会联合资助项目（KZ201810028047）；国家自然科学基金资助项目（41271495）

通讯作者: 王晓燕,教授,wangxy@cnu.edu.cn E-mail: wangxy@cnu.edu.cn

作者简介: 郭英壮(1996-),男,山东临沂人,首都师范大学硕士研究生,主要从事流域水环境污染控制与管理研究.发表论文2篇.

引用本文:

郭英壮, 王晓燕, 周丽丽, 郑文秀. 控制流域氮流失的最佳管理措施配置及效率评估[J]. 中国环境科学, 2021, 41(2): 860-871. GUO Ying-zhuang, WANG Xiao-yan, ZHOU Li-li, ZHENG Wen-xiu. Configuration and efficiency evaluation of the best management practices to control nitrogen loss in the watershed. CHINA ENVIRONMENTAL SCIENCECE, 2021, 41(2): 860-871.

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http://www.zghjkx.com.cn/CN/ 或 http://www.zghjkx.com.cn/CN/Y2021/V41/I2/860

[1]	Carpenter S R, Caraco N F, Correll D L, et al. Nonpoint pollution of surface waters with phosphorus and nitrogen[J]. Ecological Applications, 1998,8(3):559-568.
[2]	Ghebremichael L T, Veith T L, Hamlett J M. Integrated watershed-and farm-scale modeling framework for targeting critical source areas while maintaining farm economic viability[J]. Journal of Environmental Management, 2013,114:381-394.
[3]	Giri S, Qiu Z, Prato T, et al. An integrated approach for targeting critical source areas to control nonpoint source pollution in watersheds[J]. Water Resources Management, 2016,30(14):5087-5100.
[4]	马放,姜晓峰,王立,等.基于SWAT模型的阿什河流域非点源污染控制措施[J]. 中国环境科学, 2016,36(2):610-618.Ma F, Jiang X, Wang L, et al. Non-point source pollution control of Ashihe Basin based on SWAT Model[J]. China Environmental Science, 2016,36(2):610-618.
[5]	Panagopoulos Y, Makropoulos C, Mimikou M. Decision support for diffuse pollution management[J]. Environmental Modelling & Software, 2012,30:57-70.
[6]	Liu R, Zhang P, Wang X, et al. Assessment of effects of best management practices on agricultural non-point source pollution in Xiangxi River watershed[J]. Agricultural Water Management, 2013, 117:9-18.
[7]	Hanief A, Laursen A E. Meeting updated phosphorus reduction goals by applying best management practices in the Grand River watershed, southern Ontario[J]. Ecological Engineering, 2019,130:169-175.
[8]	Wu Y, Kerr P G, Hu Z, et al. Eco-restoration:Simultaneous nutrient removal from soil and water in a complex residential-cropland area[J]. Environmental Pollution, 2010,158(7):2472-2477.
[9]	Maringanti C, Chaubey I, Popp J. Development of a multiobjective optimization tool for the selection and placement of best management practices for nonpoint source pollution control[J]. Water Resources Research, 2009,45(6).
[10]	Cherry K A, Shepherd M, Withers P J A, et al. Assessing the effectiveness of actions to mitigate nutrient loss from agriculture:A review of methods[J]. Science of the Total Environment, 2008,406(1/2):1-23.
[11]	Hashimoto T, Stedinger J R, Loucks D P. Reliability, resiliency, and vulnerability criteria for water resource system performance evaluation[J]. Water Resources Research, 1982,18(1):14-20.
[12]	Naeem S. Species redundancy and ecosystem reliability[J]. Conservation Biology, 1998,12(1):39-45.
[13]	Mondal M S, Chowdhury J U, Ferdous M R. Risk-based evaluation for meeting future water demand of the Brahmaputra Floodplain within Bangladesh[J]. Water Resources Management, 2010,24(5):853-869.
[14]	Asefa T, Clayton J, Adams A, et al. Performance evaluation of a water resources system under varying climatic conditions:Reliability, Resilience, Vulnerability and beyond[J]. Journal of Hydrology, 2014, 508:53-65.
[15]	Hoque Y M, Tripathi S, Hantush M M, et al. Aggregate measures of watershed health from reconstructed water quality data with uncertainty[J]. Journal of Environmental Quality, 2016,45(2):709-719.
[16]	Hoque Y M, Tripathi S, Hantush M M, et al. Watershed reliability, resilience and vulnerability analysis under uncertainty using water quality data[J]. Journal of Environmental Management, 2012,109:101-112.
[17]	Hazbavi Z, Sadeghi S H R. Watershed health characterization using Reliability-Resilience-Vulnerability conceptual framework based on hydrological responses[J]. Land Degradation & Development, 2017, 28(5):1528-1537.
[18]	Zheng J K, Sun G, Li W H, et al. Impacts of land use change and climate variations on annual inflow into Miyun Reservoir, Beijing, China[J]. Hydrology and Earth System Sciences Discussions, 2016, 12(8):7785-7819.
[19]	Li D, Liang J, Di Y, et al. The spatial-temporal variations of water quality in controlling points of the main rivers flowing into the Miyun Reservoir from 1991 to 2011[J]. Environmental Monitoring and Assessment, 2016,188(1):42.
[20]	徐菲,王永刚,张楠,等.北京市白河和潮河流域生态健康评价[J]. 生态学报, 2017,37(3):932-942.Xu F, Wang Y, Zhang N, et al. Health assessment of watershed ecosystems:the Chao River and Bai River Basins as a case study[J]. Acta Ecologica Sinica, 2017,37(3):932-942.
[21]	Guo Y, Wang X, Zhou L, et al. Identification of critical source areas of nitrogen load in the Miyun Reservoir watershed under different hydrological conditions[J]. Sustainability, 2020,12(3):964.
[22]	Pennington D N, Dalzell B, Nelson E, et al. Cost-effective land use planning:Optimizing land use and land management patterns to maximize social benefits[J]. Ecological Economics, 2017,139:75-90.
[23]	Shen Z, Qiu J, Hong Q, et al. Simulation of spatial and temporal distributions of non-point source pollution load in the Three Gorges Reservoir Region[J]. Science of the Total Environment, 2014,493:138-146.
[24]	王晓燕,张雅帆,欧洋,等.最佳管理措施对非点源污染控制效果的预测——以北京密云县太师屯镇为例[J]. 环境科学学报, 2009, 29(11):2440-2450.Wang X, Zhang Y, Ou Y, et al. Predicting effectiveness of best management practices for control of nonpoint source pollution——a case of Taishitun Town, Miyun County, Beijing[J]. Acta Scientiae Circumstantiae, 2009,29(11):2440-2450.
[25]	耿润哲,王晓燕,庞树江,等.潮河流域非点源污染控制关键因子识别及分区[J]. 中国环境科学, 2016,36(4),1258-1267.Geng R, Wang X, Pang S, et al. Identification of key factors and zonation for nonpoint source pollution controlin Chaohe River watershed[J]. China Environmental Science, 2016,36(4):1258-1267.
[26]	Borrelli P, Robinson D A, Fleischer L R, et al. An assessment of the global impact of 21st century land use change on soil erosion[J]. Nature Communications, 2017,8(1).
[27]	Zhou X, Helmers M J, Asbjornsen H, et al. Nutrient removal by prairie filter strips in agricultural landscapes[J]. Journal of Soil and Water Conservation, 2014,69(1):54-64.
[28]	Sharpley A N, Kleinman P J, Jordan P, et al. Evaluating the success of phosphorus management from field to watershed[J]. Journal of Environmental Quality, 2009,38(5):1981-1988.
[29]	Diebel M W, Maxted J T, Nowak P J, et al. Landscape planning for agricultural nonpoint source pollution reduction I:A geographical allocation framework[J]. Environmental Management, 2008,42(5):789-802.
[30]	孟凡德.基于潮河流域非点源污染分布特征的BMPs优化配置研究[D]. 北京:首都师范大学, 2013.Meng F. Spatial optimal placement of BMPs based on nonpoint source pollution distribution characteristics in Chaohe River Basin[D]. Beijing:Capital Normal University, 2013.
[31]	卢少勇,张萍,潘成荣,等.洞庭湖农业面源污染排放特征及控制对策研究[J]. 中国环境科学, 2017,37(6):2278-2286.Lu S, Zhang P, Pan C, et al. Agricultural non-point source pollution discharge characteristic and its control measures of Dongtinghu Lake[J]. China Environmental Science, 2017,37(6):2278-2286.
[32]	Rothwell J J, Dise N B, Taylor K G, et al. Predicting river water quality across North West England using catchment characteristics[J]. Journal of Hydrology, 2010,395(3):153-162.
[33]	沈珍瑶.三峡库区农业非点源污染特征与控制技术[M]. 北京:科学出版社, 2015.Shen Z. Characteristics and control technology of agricultural non-point source pollution in the Three Gorges Reservoir area[M]. Beijing:Science Press, 2015.
[34]	Hoque Y M, Hantush M M, Govindaraju R S. On the scaling behavior of Reliability-Resilience-Vulnerability indices in agricultural watersheds[J]. Ecological Indicators, 2014,40:136-146.
[35]	Gao H, Li Z, Li P, et al. Quantitative study on influences of terraced field construction and check-dam siltation on soil erosion[J]. Journal of Geographical Sciences, 2012,22(5):946-960.
[36]	Gispert M, Pardini G, Colldecarrera M, et al. Water erosion and soil properties patterns along selected rainfall events in cultivated and abandoned terraced fields under renaturalisation[J]. Catena, 2017,155:114-126.
[37]	王晓,郝芳华,张璇.丹江口水库流域非点源污染的最佳管理措施优选[J]. 中国环境科学, 2013,33(7):1335-1343.Wang X, Hao F, Zhang X. Optimization of best management practices for non-point source pollution in Danjiangkou Reservoir Basin[J]. China Environmental Science, 2013,33(7):1335-1343.
[38]	Sharpley A N. The phosphorus paradox:Productive agricultural and water quality[J]. Journal of Environmental Indicators, 2015,(9):3-4.
[39]	Gathagu J, Mourad K, Sang J. Effectiveness of contour farming and filter strips on ecosystem services[J]. Water, 2018,10(10):1312.
[40]	Xin Y, Xie Y, Liu Y, et al. Residue cover effects on soil erosion and the infiltration in black soil under simulated rainfall experiments[J]. Journal of Hydrology, 2016,543:651-658.
[41]	Her Y, Chaubey I, Frankenberger J, et al. Implications of spatial and temporal variations in effects of conservation practices on water management strategies[J]. Agricultural Water Management, 2017, 180:252-266.
[42]	丁雪坤,王云琦,韩玉国,等.三峡库区人类活动净氮输入量估算及其影响因素[J]. 中国环境科学, 2020,40(1):206-216.Ding X, Wang Y, Han Y, et al. Evaluating of net anthropogenic nitrogen inputs and its influencing factors in the Three Gorges Reservoir Area[J]. China Environmental Science, 2020,40(1):206-216.
[43]	Yang F, Yang Y, Li H, et al. Removal efficiencies of vegetation-specific filter strips on nonpoint source pollutants[J]. Ecological Engineering, 2015,82:145-158.
[44]	耿润哲.流域非点源污染及管理措施优化配置研究[D]. 北京:首都师范大学, 2012.Geng R. Research on the optimal allocation of non-point source pollution and management measures in the watershed[D]. Beijing:Capital Normal University, 2012.
[45]	焦剑,朱少波,杨扬,等.密云水库上游流域水体营养物质现状及来源分析[J]. 水土保持通报, 2013,33(4):12-17.Jiao J, Zhu S, Yang Y, et al. Occurrences and sources of nutrients in upper-river basin of Miyun Reservoir[J]. Bulletin of Soil and Water Conservation, 2013,33(4):12-17.
[46]	李东青,梁籍,张立燕,等.密云库区1991~2011年水质变化趋势研究[J]. 中国环境科学, 2015,35(6):1675-1685.Li D, Liang J, Zhang L, et al. The research of water quality trend in the Miyun Reservoir from 1991 to 2011[J]. China Environmental Science, 2015,35(6):1675-1685.
[47]	Wang L, Robertson D M, Garrison P J. Linkages between nutrients and assemblages of macroinvertebrates and fish in Wadeable Streams:Implication to nutrient criteria development[J]. Environmental Management, 2007,39(2):194-212.