Scientia Agricultura Sinica ›› 2018, Vol. 51 ›› Issue (3): 456-467.doi: 10.3864/j.issn.0578-1752.2018.03.006

• Nutrient Management in Soil-Crop-Animal Production System • Previous Articles     Next Articles

Nutrient Flow and Environmental Effects on Crop-Livestock System in Farming-Pastoral Transition Zone - A Case Study in Shanxi Province

ZHANG JianJie1, GUO CaiXia1, LI LianFen2, ZHANG Qiang1   

  1. 1Institute of Agricultural Environment and Resources, Shanxi Academy of Agricultural Sciences/Shanxi Province Key Laboratory of Soil Environment and Nutrient Resources, Taiyuan 030031; 2Institute of Animal Husbandry and Veterinary Sciences, Shanxi Academy of Agricultural Sciences, Taiyuan 030032
  • Received:2017-05-02 Online:2018-02-01 Published:2018-02-01

Abstract: 【Objective】The objective of this study is to explore the characteristics of nitrogen (N) flow of crop-livestock systems and its environmental effects on farming-pastoral transition zone in northwestern Shanxi Province, further to give scientific suggestions on the nutrient management and to speed up the adjustment progress of industrial structure in farming-pastoral transition zone in Shanxi Province.【Method】a systematic and quantitative analysis on the nutrient balance, nutrient losses of crop-livestock production in farming-pastoral transition zone (42 counties in total, mainly involving Datong, Shuozhou, Xinzhou, Lüliang, Linfen and Taiyuan) in Shanxi Province was reported using a coupled NUFER model (nutrient flows in food chains, environment and resources use) with GIS after collecting and sorting of data from statistical yearbooks data, literature, and field investigation.【Result】 In different counties, the N fertilizer application showed a great disparity, ranging from 6.7 to 253 kg·hm-2, which means a 38 times difference between the maxima and the minima. The N input structure of different counties also varied, due to the different N application habits and cropping systems. Crop N uptake ranged from 19.11 to 96.75 kg·hm-2, and the high amounts of crop N uptake were found in North and South regions, and low values in the middle regions. Crop N surplus ranged from -16 to 202 kg·hm-2, showing a coexistence of N sufficient and N surplus. There was a great difference in external N input by feed in livestock production system in the zone. In Shanyin county of Shuozhou City, the external N input by feed reached up to 9 400 t, whereas in Wuzhai of Xinzhou City and Xixian, Daning and Puxian of Linfen City, the demand of feed by livestock production system was met by local cropping system. This shows a great variation in the livestock production scale and farming-pastoral industrial structure among those counties. N uptake of animal main product per unit area of farming land was 1.51-27.50 kg·hm-2, with a range of 25.99 kg·hm-2, indicating a great disparity in the livestock productivity level among different counties. In the northern counties of Shanyin, Huairen and Datong, N uptake of animal main products was >13 kg·hm-2, showing a high N use efficiency of livestock production system in these counties. In the northern regions, the N load by manure was high (>50 kg·hm-2). There was an obvious spatial trend of N loss in crop-livestock production system. Grade I area (>200 kg·hm-2) was found in the north of the zone, Grade II area (120-200 kg·hm-2) was found in the north and south of the zone, and Grade III area (<120 kg·hm-2) mainly distributed in the middle of the zone. Therefore, N loss and environmental issues occur in the crop-livestock production process in the northern part of the zone should be paid close attention in the future. 【Conclusion】 Unreasonable agricultural production structure and the segregation of agricultural and animal husbandry systems were the main reasons for the low N use efficiency in the farming-pastoral transition zone in northwestern Shanxi Province. In the future management of farmland nutrient resources, apart from rational spatial allocation of N resources, not only N input by both chemical fertilizers and livestock excrement/urine should be taken into account, but also N input from the environment. Also, the coupling of farmland production system and animal husbandry production system should be emphasized. By these means the production of crop and animal products at the minimum environmental costs can be achieved.

Key words: farming-pastoral transition zone, NUFER model, crop-livestock production system, nitrogen flow, environmental effects, Shanxi Province

[1]    张卫峰, 马林, 黄高强, 武良, 陈新平, 张福锁. 中国氮肥发展、贡献和挑战. 中国农业科学, 2013, 46(15): 3161-3171.
ZHANG W F, MA L, HUANG G Q, WU L, CHEN X P, ZHANG F S. The development and contribution of nitrogenous fertilizer in China and challenges faced by the country. Scientia Agricultura Sinica, 2013, 46(15): 3161-3171. (in Chinese)
[2]    TILMAN D, CASSMAN K G, MATSON P A, NAYLOR R, POLASKY S. Agricultural sustainability and intensive production practices. Nature, 2002, 418(6989): 671-677.
[3]    蔡祖聪, 颜晓元, 朱兆良. 立足于解决高投入条件下的氮污染问题. 植物营养与肥料学报, 2004, 20(1): 1-6.
CAI Z C, YAN X Y, ZHU Z L. A great challenge to solve nitrogen pollution from intensive agriculture. Journal of Plant Nutrition and Fertilizer, 2014, 20(1): 1-6. (in Chinese)
[4]    LIU X J, ZHANG Y, HAN W X, TANG A H, SHEN J B, CUI Z L, VITOUSEK P, ERISMAN J W, GULDING K, CHRISTIE P, FANGMEIER A, ZHANG F S. Enhanced nitrogen deposition over China. Nature, 2013, 494(7438): 459-462.
[5]   CONELEY D J, PAERL H W, HOWARTH R W, BOESCH D F, SEITZINGER S P, HAVENS K E, LANCELOT C, LIKENS G E. Controlling eutrophication: nitrogen and phosphorus. Science, 2009, 323(5917): 1014-1015.
[6]    GUO J H, LIU X J, ZHANG Y, SHENG J L, HAN W X, ZHANG W F, CHRISTIE P, GOULDING K W T, VITOUSEK P M, ZHANG F S. Significant acidification in major Chinese croplands. Science, 2010, 327(5968): 1008-1010.
[7]    王方浩, 马文奇, 窦争霞, 马林, 刘小利, 许俊香, 张福锁. 中国畜禽粪便产生量估算及环境效应. 中国环境科学, 2006, 26(5): 614-617.
WANG F H, MA W Q, DOU Z X, MA L, LIU X L, XU J X, ZHANG F S. The estimation of the production amount of animal manure and its environmental effect in China. China Environmental Science, 2006, 26(5): 614-617. (in Chinese)
[8]    陈敏鹏, 陈吉宁. 中国种养系统的氮流动及其环境影响. 环境科学, 2007, 28(10): 2342-2349.
CHEN M P, CHEN J N. Nitrogen flow in farming-feeding system and its environmental impact in China. Environmental Science, 2007, 28(10): 2342-2349. (in Chinese)
[9]    张华芳. 河北省农牧生产体系氮磷养分流动特征及调控途径[D]. 保定: 河北农业大学, 2013.
ZHANG H F. Nitrogen and phosphorus flow in agro-livestock system and strategies of optimization in Hebei Province[D]. Baoding: Hebei Agricultural University, 2013. (in Chinese)
[10]   马林, 魏静, 王方浩, 马文奇, 张福锁. 中国食物链氮素资源流动特征分析. 自然资源学报, 2009, 24(12): 2104-2114.
MA L, WEI J, WANG F H, MA W Q, ZHANG F S. Analysis on the feature of nitrogen flow from food chain perspective in China. Journal of Natural Resources, 2009, 24(12): 2104-2114. (in Chinese)
[11]   黄和平, 毕军, 张炳, 李详妹, 杨洁, 石磊. 物质流分析研究述评. 生态学报, 2007, 27(1): 368-379.
HUANG H P, BI J, ZHANG B, LI X M, YANG J, SHI L. A critical review of material flow analysis (MFA). Acta Ecologica Sinica, 2007, 27(1): 368-379. (in Chinese)
[12]   MA L, MA W Q, VELTHOF G L, WANG F H, QIN W, ZHANG F S, OENEMA O. Modeling nutrient flows in the food chain of China. Journal of Environmental Quality, 2010, 39(4): 1279-1289.
[13]   BAI Z H, MA L, QIN W, CHEN Q, OENEMA O, ZHANG F S. Changes in pig production in china and their effects on nitrogen and phosphorus use and losses. Environmental Science & Technology, 2014, 48(21): 12742-12749.
[14]   ZHANG J J, GUO C X, ZHANG Y G, HAN P Y, ZHANG Q. Spatial characteristics of nitrogen flows in the crop and livestock production system of Shanxi Province, China. Acta Ecologica Sinica, 2016, 36(2): 99-107.
[15]   陈全功, 张剑, 杨丽娜. 中国农牧交错带的GIS表述//中国草业发展论坛论文集. 2006.
CHEN Q G, ZHANG J, YANG L N. GIS expression of ecotone between agriculture and animal husbandry//Symposium of China Grassland Development Forum. 2006. (in Chinese)
[16]   黄青, 辛晓平, 张宏斌. 基于生态系统服务功能的中国北方草地及农牧交错带区划. 生态学报, 2010, 30(2): 350-356.
HUANG Q, XIN X P, ZHANG H B. Ecosystem-service-based regionalization of the grassland and agro-pastoral transitional in Northern China. Acta Ecologica Sinica, 2010, 30(2): 350-356. (in Chinese)
[17]   刘耀宗, 张经元. 山西土壤. 北京: 科学出版社, 1992: 84-92.
LIU Y Z, ZHANG J Y. Shanxi Soil. Beijing: Science Press, 1992: 84-92. (in Chinese)
[18]   山西省人民政府. 畜牧产业规模化山西达到47%. 山西日报, (2015-11-16)[2017-05-02].
Shanxi Provincial People’s Government. The ratio of the intensive livestock industry in Shanxi Province reached 47%. Shanxi Daily, (2015-11-16)[2017-05-02]. (in Chinese)
[19]   山西省统计局. 山西统计年鉴. 北京: 中国统计出版社, 2013.
Shanxi Statistic Bureau. Shanxi Statistical Yearbook. Beijing: China Statistics Press, 2013. (in Chinese)
[20]   忻州市统计局, 国家统计局忻州调查队. 忻州统计年鉴. 北京: 中国统计出版社, 2013.
Xinzhou Statistic Bureau, Xinzhou investigation team of National Statistic Bureau. Xinzhou Statistical Yearbook. Beijing: China Statistics Press, 2013. (in Chinese)
[21]   太原统计局. 太原统计年鉴. 北京: 中国统计出版社, 2013.
Taiyuan Statistic Bureau. Taiyuan Statistical Yearbook. Beijing: China Statistics Press, 2013. (in Chinese)
[22]   朔州市统计局, 国家统计局朔州调查队. 朔州统计年鉴. 北京: 中国统计出版社, 2013.
Shuozhou Statistic Bureau, Shuozhou investigation team of National Statistic Bureau. Shuozhou Statistical Yearbook. Beijing: China Statistics Press, 2013. (in Chinese)
[23]   临汾市统计局. 临汾统计年鉴. 北京: 中国统计出版社, 2013.
Linfen Statistics Bureau. Linfen Statistical Yearbook. Beijng: China Statistics Press, 2013. (in Chinese)
[24]   张卫峰, 李亮科, 陈新平, 张福锁. 我国复合肥发展现状及存在的问题. 磷肥与复肥, 2009, 24(2): 14-16.
ZHANG W F, LI L K, CHEN X P, ZHANG F S. The present status and existing problems in China’s compound fertilizer development. Phosphate & Compound Fertilizer, 2009, 24(2): 14-16. (in Chinese)
[25]   毕于运, 高春雨, 王亚静, 李宝玉. 中国秸秆资源数量估算. 农业工程学报, 2009, 25(12): 211-217.
BI Y Y, GAO C Y, WANG Y J, LI B Y. Estimation of straw resources in China. Transactions of the Chinese Society of Agricultural Engineering, 2009, 25(12): 211-217. (in Chinese)
[26]   李书田, 金继运. 中国不同区域农田养分输入、输出与平衡. 中国农业科学, 2011, 44(20): 4207-4229.
LI S T, JIN J Y. Characteristics of nutrient input/output and nutrient balance in different regions of China. Scientia Agricultura Sinica, 2011, 44(20): 4207-4229. (in Chinese)
[27]   张建杰, 郭彩霞, 覃伟, 张强. 山西省畜禽业发展及粪尿养分时空变异. 应用生态学报, 2016, 27(1): 207-214.
ZHANG J J, GUO C X, QIN W, ZHANG Q. Temporal and spatial variability of livestock and poultry productions and manure nutrients in Shanxi Province, China. Chinese Journal of Applied Ecology, 2016, 27(1): 207-214. (in Chinese)
[28]   杜艳萍. 山西省农作物秸秆资源化利用现状及发展对策. 农业环境与发展, 2013(3): 38-41.
DU Y P. Current status of straw resource utilization in Shanxi Province and development strategies. Agro-Environment and Development, 2013(3): 38-41. (in Chinese)
[29]   张颖, 刘学军, 张福锁, 巨晓棠, 邹国元, 胡克林. 华北平原大气氮素沉降的时空变异. 生态学报, 2006, 26(6): 1633-1639.
ZHANG Y, LIU X J, ZHANG F S, JU X T, ZOU G Y, HU K L. Spatial and temporal variation of atmospheric nitrogen deposition in North China Plain. Acta Ecologica Sinica, 2006, 26(6): 1633-1639. (in Chinese)
[30]   刘平, 刘学军, 骆晓声, 吴庆华, 刘恩科,韩彦龙, 李丽, 白光洁, 武文丽, 张强.山西北部农村区域大气活性氮沉降特征. 生态学报, 2016, 36(17): 5353-5359.
LIU P, LIU X J, LUO X S, WU Q H, LIU E K, HAN Y L, LI L J, BAI G J, WU W L, ZHANG Q. The atmospheric deposition characteristics of reactive nitrogen (Nr) species in Shuozhou area. Acta Ecologica Sinica, 2016, 36(17): 5353-5359. (in Chinese)
[31]   山西省人民政府. 山西省人民政府关于印发《山西省主体功能区规划》的通知[EB/OL].(2014-04-10)[2017-05-02]. http: //www.shanxi. gov.cn/sxszfxxgk/sxsrmzfzcbm/sxszfbgt/flfg_7203/szfgfxwj_7205/201404/t20140410_145694.shtml.
The People’s Government of Shanxi Province. Notice of the People’s Government of Shanxi Province on the issuance of “Planning for Development Priority Zones of Shanxi Province” [EB/OL].(2014- 04-10)[2017-05-02]. http: //www.shanxi.gov.cn/sxszfxxgk/ sxsrmzfzcbm/sxszfbgt/flfg_7203/szfgfxwj_7205/201404/t20140410_145694.shtml. (in Chinese)
[32]   田良才, 牛天堂, 李晋川, 王宇宏, 任冻. 山西省水土流失治理的战略抉择. 山西农业科学, 2011, 39(1): 1-5, 20.
TIAN L C, NIU T T, LI J C, WANG Y H, REN D. Strategy choice for control of water loss and soil erosion in Shanxi. Journal of Shanxi Agricultural Sciences, 2011, 39(1): 1-5, 20. (in Chinese)
[33]   OENEMA O, KROS H, DE VRIES W. Approaches and uncertainties in nutrient budgets: implications for nutrient management and environmental policies. European Journal of Agronomy, 2003, 20(1/2): 3-16.
[34]   OENEMA O. Governmental policies and measures regulating nitrogen and phosphorus from animal manure in European agriculture. Journal of Animal Science, 2004, 82(suppl.): 196-206.
[35]   李宝堂. 山西岚漪河上游流域典型区段农业面源污染特征. 东北林业大学学报, 2010, 38(10): 85-87.
LI B T. Characteristics of the agricultural non-point source pollution in typical section of up stream Lanyi River in Shanxi. Journal of Northeast Forestry University, 2010, 38(10): 85-87. (in Chinese)
[36]   刘钦普. 中国化肥投入区域差异及环境风险分析. 中国农业科学, 2014, 47(18): 3596-3605.
LIU Q P. Distribution of fertilizer application and its environmental risk in different provinces of China. Scientia Agricultura Sinica, 2014, 47(18): 3596-3605. (in Chinese)
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