典型红壤区农田养分平衡估算及环境影响
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摘要
南方红壤区是我国最重要的农业生产地区之一,土地面积仅占全国的1/5,却养育了全国40%的人口。近年来,随着农业投入的不断增加,该区农业生产和农村生活造成的农业面源污染日益凸显。本文以湖南省祁阳县为例,在进行了大量的农户调查、农田区域实地访问及相关资料收集的基础上,采用野外取样和室内分析测定的方法,通过与当地长期定位试验的结果进行对比分析,探讨了红壤地区农田土壤有机质及养分变化、养分平衡状况,并通过估算养分损失量为农业面源污染的防控提供科学依据。本文主要结论如下:
     (1)第二次土壤普查以来,研究区农田耕作层的有机质、全氮、碱解氮、有效磷含量均有不同程度的提高,其中水稻土分别提高了约9.6%、17.4%、23.4%和46.5%,旱地分别提高了约13.2%、8.3%、6.1%和49.4%。而土壤速效钾含量下降较明显,水稻土和旱地分别降低了18.4%、24.1%。从土壤剖面中养分的变化来看,水稻土和旱地土壤剖面各层次的有机质和全氮含量均有所增加,全磷含量则呈现下降趋势,水稻土的耕作层和犁底层及旱地土壤的耕作层和心土层全钾含量下降,而水稻土的淀积层及旱地土壤的母质层全钾含量则有所提高。分析对比土壤剖面各土层的厚度变化情况;水稻土耕作层和犁底层分别变薄了9cm和8cm,旱地土壤耕作层厚度增加了5cm,但心土层减少了4cm。
     (2)祁阳县所有农田中,氮、磷均有盈余,且氮素的盈余量较大,而钾素则全面亏缺。根据相关结果计算得出,水田中氮素盈余量为194.63 kg·hm-2·a-1~243.44 kg·hm-2·a-1,平均盈余率为89.20%;旱地为50.96 kg·hm-2·a-1~150.84 kg·hm-2·a-1,盈余率为50.88%。水田磷素盈余量为2.86 kg·hm-2·a-1 ~32.35 kg·hm-2·a-1,平均盈余率为13.96%;旱地磷素盈余量为26.63 kg·hm-2·a-1 ~39.98 kg·hm-2·a-1,平均为27.75%。水田钾素亏缺量为69.07 kg·hm-2·a-1 ~137.52 kg·hm-2·a-1,平均亏缺率为34.55%;旱地亏缺量为10.32 kg·hm-2·a-1 ~164.69 kg·hm-2·a-1,平均亏缺29.07%。
     (3)在小麦-玉米一年两熟的轮作制度下,不施肥(CK)处理的土壤年均供氮、磷、钾能力分别为21.43 kg·hm-2·a-1、10.72 kg·hm-2·a-1和31.71 kg·hm-2·a-1,作物吸收养分数量逐年下降,土壤中氮磷钾养分损耗严重,处于严重亏缺状态。单施氮、磷、钾化肥处理,土壤中氮磷钾的养分平衡均上升,特别是氮素盈余量达211.88 kg·hm-2·a-1 ~254.17 kg·hm-2·a-1。在氮磷钾配施有机肥(NPKM)处理中,耕层土壤全量氮、磷、钾的含量均有增加,作物对养分的吸收量呈上升趋势,土壤养分收支平衡表现为基本处于平衡状态,是较理想的施肥模式。
     (4)根据相关方法估算,祁阳县农田土壤中氮素总损失量26933.10吨,其中淋失量362.72吨,氨挥发量为26141.6吨,硝化-反硝化损失量428.78吨。全县磷素损失量3.30吨,其中渗漏损失2.64吨,径流损失0.66吨。全县钾素损失量507.81吨,其中渗漏损失422.08吨,径流损失85.73吨。这些养分的损失不仅是有限资源的严重浪费,也在一定程度上提高了农业的生产成本,降低了农业的整体效益,更可能是导致农田面源污染的重要原因。
     综上所述,在祁阳县现有施肥和耕作管理模式下,针对土壤中氮磷盈余、钾素亏损和相应养分的损失情况,在施肥结构和用量上,应增加有机肥施用量,同时提倡作物秸秆还田,促进农田有机物质循环,提高土壤肥力和养分库容,减少氮磷素向环境流失,构建有利于作物优质高产和资源节约环境发展友好的农业发展模式。
Red soil region in southern China is an important agricultural production base, with land area only of 1/5, but raising 40% of the population. With the increase of modern agricultural inputs, the influence of non-point source pollution in the environment caused by agricultural production and rural life has become increasingly prominent. In Qiyang County, Hunan Province, we investigated farmland field area and collected related information, and collected a large number of soil samples by using GPS. Compared with the results of long-term fertilization experiment, we discussed the temporal- spatial variability of soil nutrient, nutrient balance and estimated the nutrient loss to provide a scientific basis for the prevention and control of agricultural non-point source pollution. The main conclusions of this paper were as follows:
     1) Compared with the results of the Second Soil Census, almost all nutrients contents including OM, TN, available N and available P have increased in different levels, in which paddy field increased by 9.6%, 17.4%, 23.4% and 46.5%, respectively, and upland field increased by 13.6%, 8.3%, 6.1% and 49.4%,respectively. Available K decreased sharply by 18.4% in paddy field and by 24.1% in upland field. In different soil profile, contents of OM and TN increased in all layers of paddy soil and upland soil; TP decreased in all layers of paddy and upland soil; TK decreased in cultivated horizon and plow pan in paddy field, and decreased in cultivated horizon and illuvial horizon in upland field. TK increased significantly in gley horizon of paddy field and parent material horizon of upland field. From thickness of soil layers, the depth of cultivated horizon and plow pan decreased 9cm and 8cm in paddy field, respectively, and in upland field, the depth of cultivated horizon decreased 5cm and illuvial horizon increased 4 cm .
     2) N and P were in surplus and K had a deficit in Qiyang county agroecosystem. Surplus amount of N was 194.63 kg·hm-2·a-1 ~243.44 kg·hm-2·a-1, and the average annual rate of profit is 89.20% in paddy soil. Surplus amount of N was 50.96 kg·hm-2·a-1 ~150.84 kg·hm-2·a-1 in upland field, and the rate of profit is 50.88%. Surplus amount of P was 2.86 kg·hm-2·a-1 ~32.35 kg·hm-2·a-1 and 26.63 kg·hm-2·a-1 ~39.98 kg·hm-2·a-1 in paddy soil and upland field,with the average annual rate of profit of 13.96% in paddy soil and 27.75% in upland soil, respectively. The deficit of K was 69.07 kg·hm-2·a-1 ~137.52 kg·hm-2·a-1 and10.32 kg·hm-2·a-1 ~164.69 kg·hm-2·a-1 in paddy soil and upland field,and the average annual rate of deficit is 34.55% and 29.07%, respectively.
     3) Through long-term different fertilization treatment test located in Qiyang County, we studied the effect of different fertilization treatment on the soil balance. In CK treatment, the supplying amount of N, P and K were 21.43 kg·hm-2·a-1, 10.72 kg·hm-2·a-1, 31.71 kg·hm-2·a-1, respectively. The amount of nutrients absorption declined year by year, and N, P and K nutrients in soils were depleted greatly. With inorganic chemical treatment, soil nutrition balance had increased, and surplus amount of N was 211.88 kg·hm-2·a-1 ~254.17 kg·hm-2·a-1. With NPKM treatment, the contents of soil TN, TP and TK in plough layer improved, and the amount of nutrients absorption increased and soil nutrients kept balance on the whole as an ideal fertilizer treatment.
     4) The amount of N loss in farmland at Qiyang County was 26933.10t,including leaching amount of 362.72t, ammonia volatilization of 26141.6t, and nitrification-denitrification loss of 428.78t. The amount of P loss was 3.30t, including leaching amount of 2.64t, and runoff amount of 0.66t. The amount of K loss was 507.81t, including leaching amount of 422.08t, and runoff amount of 85.73 t. The loss of these nutrients was not only a serious waste of limited resources, but also increased the production cost of agriculture, and reduced the overall efficiency of agriculture, which may be a major reason to non-point source pollution.
     From the above, we should reduce the use of chemical fertilizers,and increase the amount of organic manure fertilizer application to improve soil fertility and nutrient storage capacity, reducing the loss of Nitrogen and Phosphorus in the environment for building high-yield crops and resource-saving environment-friendly agricultural development mode.
引文
1蔡祖聪.尿素和KNO3对水稻土无机氮转化过程和产物的影响Ⅱ.NO2生成过程.土壤通报, 2003, 40(3): 414~419.
    2仓恒瑾,许炼峰,李志安,任海.农田氮流失与农业非点源污染.热带地理, 2004, 24(4): 332~336.
    3陈安磊,王凯荣,谢小立.长期有机养分循环利用对红壤稻田土壤供氮能力的影响.植物营养与肥料学报, 2007, 13(5): 838~843.
    4崔键,周静,马友华,何圆球.我国红壤旱地氮素平衡特征.土壤, 2008, 40(3): 372~376.
    5范茂攀,郑毅,李少明,毛昆明,尹胜鑫,周华波.保山市农田生态系统养分循环与平衡研究.云南农业大学学报, 2005, 20(30): 415~418.
    6范晓晖,孙永红,林德喜,孟爱民,钦绳武.长期试验地红壤与潮土的矿化和硝化作用特征比较.土壤通报, 2005, 36(5): 672~674.
    7范晓晖,朱兆亮.旱地土壤中的硝化-反硝化作用.土壤通报, 2005, 33(5): 385~391.
    8方玉东.农田养分收支平衡的研究进展.山东农业大学学报(自然科学版), 2008, 39(3): 492~494.
    9傅庆林,孟赐福.热带主要稻作制农田生态系统的养分平衡.生态学杂志, 1994, 13(3): 53~56, 34.
    10高菊生,徐明岗,王伯仁,秦道珠,文石林,申华平.长期有机无机肥配施对土壤肥力及水稻产量的影响.中国农学通报, 2005: 211~214.
    11高菊生,李菊梅,徐明岗,孙楠,秦道珠.长期施用化肥对红壤旱地作物和水稻产量影响.土壤肥料科学, 2003, 24(1): 286~292.
    12高菊生,曹卫东,李本荣,颜钧.充分利用冬闲稻田大力发展绿肥生产.耕作与栽培,2009, 2: 1~2.
    13高超,张桃林,孙波,吴蔚东,鲁如坤. 1980年以来我国农业氮素管理的现状与问题.南京大学学报(自然科学学报), 2002, 38(5): 716~721.
    14何园球,黄小庆.红壤农业生态系统养分循环、平衡和调控研究.土壤学报, 1998, 35(4): 501~509.
    15黄昌勇主编.土壤学.北京:国农业出版社, 1999: 38.
    16黄健,王爱文,张惠琳,肖延华.吉林省农田养分平衡的研究.吉林农业科学, 2001, 26(2): 36~40.
    17金继运,李家康,李书田.化肥与粮食安全.植物营养与肥料学报, 2006, 12(5): 601~609.
    18劳秀荣,孙伟红,王真,郝艳如,张昌爱.秸秆还田与化肥配合施用对土壤肥力的影响.土壤学报, 2003, 40(4): 618~622.
    19李菊梅,李冬初,徐明岗,申华平,秦道珠.红壤双季稻田不同施肥下的氨挥发损失及其影响因素.生态环境, 2008, 17(4): 1610~1613.
    20李菊梅,徐明岗,秦道珠,李东初,宝川靖和,八木一行.有机肥无机肥配施对稻田氨挥发和水稻产量的影响.植物营养与肥料学报, 2005, 11(1):51~56.
    21李强,张林秀.农户模型方法在实证分析中的运用-以中国加入WTO后对农户的生产和消费行为影响分析为例.南京农业大学学报(社会科学版), 2007, 7(1): 20, 25~31.
    22李忠芳,徐明岗,张会民,张文菊,高静.长期施肥下中国主要粮食作物产量的变化.中国农业科学, 2009, 42(7): 2407~2414.
    23李忠佩,唐永良,石华,高坤林.不同施肥制度下红壤稻田的养分循环与平衡规律.中国农业科学, 1998, (31)1: 46~54.
    24刘崇群,曹淑卿,陈国安.我国南亚热带闽、滇地区降雨中养分含最的研究.土壤学报,1984, 21(4): 438~442.
    25刘宏斌,李志宏,张云贵,张维理,林葆.北京平原农区地下水硝态氮污染状况及其影响因素研究.土壤通报, 2006, 43(3): 405~413.
    26刘绍贵,张桃林,王兴祥,潘剑君.江西省余江县土壤肥力变化和驱动因素与对策研究.土壤通报, 2006, 37(5): 869~874.
    27鲁如坤,刘鸿翔,闻大中,钦绳武,郑剑英,王周琼.我国典型地区农业生态系统养分循环和平衡研究Ⅰ.农田养分支出参数.土壤通报, 1996, 27(4): 145~151.
    28鲁如坤,刘鸿翔,闻大中,钦绳武,郑剑英,王周琼.我国典型地区农业生态系统养分循环和平衡研究Ⅱ.农田养分收入参数.土壤通报, 1996, 27(4): 151~154.
    29鲁如坤,刘鸿翔,闻大中,钦绳武,郑剑英,王周琼.我国典型地区农业生态系统养分循环和平衡研究Ⅲ.全国和典型地区养分循环和平衡现状.土壤通报, 1996, 27(5):193~196.
    30鲁如坤,刘鸿翔,闻大中,钦绳武,郑剑英,王周琼.我国典型地区农业生态系统养分循环和平衡研究Ⅳ.农田养分平衡的评价方法和原则.土壤通报, 1996, 27(5): 197~199.
    31鲁如坤,时正元,施建平.我国南方6省农田养分平衡现状评价和动态变化研究.中国农业科学, 2000, 33(2): 63~67.
    32鲁如坤.土壤-植物营养学原理和施肥.北京:化学工业出版社, 1998: 1~16.
    33欧阳友徽.祁阳县农业志(内部资料)第一卷, 2002: 1~61.
    34祁阳县统计局.祁阳县统计年鉴(内部资料), 1998~2007年.
    35祁阳县土壤普查办公室.祁阳县土壤志(内部资料), 1983: 1~146.
    36沈善敏.氮肥在中国农业发展中的贡献和农业中氮的损失.土壤学报, 39(增刊): 12~25.
    37沈善敏.中国土壤肥力.北京:中国农业出版社, 1998: 12.
    38孙波,潘贤章,王德建,韩晓增,张玉铭,郝明德,陈欣.我国不同区域农田养分平衡对土壤肥力时空演变的影响.地球科学进展, 2008, 23(11): 1201~1208.
    39谭宏伟,周柳强,谢如林.广西农田养分循环与平衡分析.广西科学院学报, 2000, 16(2): 82~86.
    40王伯仁,徐明岗,申华平.红壤旱地长期施肥下土壤肥力及肥料效益变化研究.植物营养与肥料学报, 2002, 8(增刊): 21~28.
    41王伯仁,徐明岗,文石林.长期施肥土壤氮的累积与平衡.植物营养与肥料学报, 2002, 8(增刊): 29~34.
    42王伯仁,徐明岗,文石林,李东初,黄晶.长期施肥对红壤旱地作物产量及肥料效益影响.土壤肥料科学, 2008, 24(10): 322~326.
    43王伯仁,徐明岗,文石林.有机肥和化学肥料配合施用对红壤肥力的影响.土壤肥料学科, 2005, 21(2): 160~163.
    44王火焰,周健民,陈小琴,杜昌文,李寿田,董彩霞.氮磷钾肥料在土壤中转化过程的交互作用Ⅱ.硫酸铵在水稻土中的转化.土壤学报, 2005, 42(1): 70~77.
    45王军,傅伯杰,邱扬,陈利顶,余莉.黄土高原小流域土壤养分的空间异质性.生态学报, 2002, 22(8): 1173~1177.
    46王绍强,朱松丽,周成虎.中国土壤土层厚度的空间变异性特征.地理研究, 2001, 20(2): 161~169.
    47王兴祥,张桃林,张斌.红壤旱坡地农田生态系统养分循环和平衡.生态学报, 1999, 19(3): 335~341.
    48吴晓晨,李忠佩,张桃林.长期不同施肥措施下红壤稻田的养分循环与平衡.土壤,2009, 41(3): 377~383.
    49徐翠云.地理信息系统的应用现状及发展趋势.地质找矿论丛. 2001, 16(l), 52~57.
    50徐华,邢光熹,蔡祖聪,鹤田冶雄.土壤质地对小麦和棉田N2O排放影响.农业环境保护, 2000, 19(1): 1~3.
    51徐明岗,文石林,高菊生.南方丘陵区水土流失控制的技术模式.农业环境与发展, 2008, 4: 71~75.
    52徐明岗,梁国庆,张夫道.中国土壤肥力演变.北京:中国农业出版社, 2006, 32.
    53闫湘,金继运,何萍,粱鸣早.提高肥料利用率技术研究进展.中国农业科学, 2008, 41(2): 450~459.
    54杨林章,孙波,刘健.农田生态系统养分迁移转化与优化管理研究.地球科学进展,2002, 17(3): 441~445.
    55杨林章,孙波.中国农田农田生态系统养分循环与平衡及其管理.北京:科学出版社,2008:24.
    56叶厚专,范业成,万美莲.南昌县农田养分平衡和循环研究.江西农业科技, 1999, 3: 23~25.
    57宇万太,姜子绍,李新宇,丁怀香.不同土地利用方式对潮棕壤有机碳含量的影响.应用生态学报, 2007, 8(12): 2760~2764.
    58曾希柏.红壤化学退化与重建.北京:中国农业出版社, 2003, 43~77.
    59曾希柏,胡学玉,胡清秀.我国肥料的施用现状及发展趋势.科技导报, 2002, 8: 36~39.
    60曾希柏,刘更另.化肥施用和秸秆还田对红壤磷吸附性能的影响研究.土壤与环境, 1999, 8(1): 45~49.
    61曾希柏,李菊梅,徐明岗,高菊生,孙楠.红壤旱地的肥力现状及施肥和利用方式的影响.土壤通报, 2006, 37(3): 434~437.
    62曾希柏,孙楠,高菊生,王伯仁,李莲芳.双季稻田改制对作物生长及土壤养分的影响.中国农业科学, 2007, 40(6): 1198~1205.
    63张爱君,马飞,张明普.黄潮土的钾素状况与钾肥效应的长期定位试验.江苏农业学报,2000, 16(4): 237~241.
    64张会民,徐明岗著.长期施肥土壤钾素演变.北京:中国农业出版社, 2008: 1.
    65张慧,高如泰,夏训峰,贾小红,刘树庆,许其功,姜甜甜.北京市房山区农田表观磷平衡分析.生态环境学报, 2009, 18(5): 1949~1955.
    66张维理,冀宏杰, Kolbe H,徐爱国.中国农业面源污染形势估计及控制对策Ⅱ.欧美国家农业面源污染状况及控制.中国农业科学, 2004, 37(7): 1018~1025.
    67张锡洲,刘岱,李廷轩,王昌全.资中县农田养分平衡与土壤养分变化初探.西南农业学报, 2001, 14(12): 21~25.
    68张玉铭,胡春胜,毛任钊,董文旭.华北太行山前平原农田生态系统中氮、磷、钾循环与平衡研究.应用生态学报, 2003, 14(11): 1863~1867.
    69赵士洞.国际长期生态研究网络(ILTER)—背景、现状和前景.植物生态学报, 2001, 25(4): 510~512.
    70甄兰,崔振岭,陈新平,张福锁,寇长林,巨晓棠. 25年来种植业结构调整驱动的县域养分平衡状况的变化-以山东惠民县为例.植物营养与肥料学报, 2007, 13(2): 213~222.
    71中华人民共和国国家统计局.中国统计年鉴2009.北京:中国统计出版社: 2009. 376.
    72周娟.基于WebGIS中国农田养分平衡与环境风险评价系统的研制与开发(硕士学位论文).南京:南京信息工程大学, 2008.1~7.
    73周杨明,于秀波,鄢帮有. 1949~2005年江西省农田养分平衡动态的宏观分析.江西农业大学学报, 2008, 30(5): 919~926.
    74朱兆良,孙波,杨林章,张林秀.我国农业面源污染的控制政策和措施.科技导报,2005, 23(4): 47~51.
    75 Bouwman, A. F. Nitrogen oxides and tropical agriculture. Nature, 1998, 392: 866~867.
    76 Cooke, G. W. The nations’s plant food larder. Journal of the Science of Food and Agriculture, 1958, 9: 716~722.
    77 Deigado, J. A., & Mosier, A. R. Mitigation alternatives to decrease nitrous oxides emissions and urea-nitrogen loss and their effect on methane flux. Journal of Environmental Quality,1999, 25(6): 1105~1111.
    78 Dodjic, F. L. B. Phosphorus losses from arable fields in Sweden-Effects of Field-specific factors and long-term trends. Environmental Monitoring and Assessment. 2005, 102: 103~117.
    79 Duan, S. W., Zhang, S. & Zhang, H. Y. Transport of dissolved inorganic nitrogen from the major rivers to estuaries in China. Nutrient Cycling In Agroecosystems, 2000, 57(1): 13~22.
    80 Fillery, R. P., & Datta, S. K. Ammonia volatilization from nitrogen volatilization as a N loss mechanism in flooded rice field. Fertilizer research, 1986, 9:78~98.
    81 Galloway, J. N. The global nitrogen cycle: past, present and future. Science in China Sciences C: life Sciences, 48 (special issue): 669~677.
    82 Giles, J. Nitrogen study fertilizes fears of pollution. Nature, 2005, 433: 791.
    83 Goodlass, G., Halberg, N., & Verschuur, G.. Input output accounting system in the European community-an appraisal of their usefulness in raising awareness of environmental problems. European Journal of Agronomy, 2003, 20(1-2): 17~24.
    84 Jenkinson, D. S., & Rayner, J. H. The turnover of organic matter in some of the Rothamsted classical experiments. Soil Science, 1977, 123: 298~305.
    85 Kobayashi, H., & Kubota T. A study on the spatial distribution of nitrogen and phosphorus balance, and regional nitrogen flow through crop production. Environmental Geochemistry and Health. 2004, 26(2): 187~198.
    86 Kolbe, H. L., & Nutzung, W. Land Use and Water Protection. Effects of nitrogen budget, Nmin -values, nitrate content and leaching in Germany. WLV Wissenschaftliches Lektorat & Verlag, Leipzig, Germany, 2000, ISBN, 3-9805495-7-7: 1.
    87 M?der, P., Fliessbach, A., Dubois, D., Gunst, L., Fried, P., & Niggli U. Soil fertility and biodiversity in organic Farming. Science, 2002, 296: 1694~1697.
    88 Matson, P. A., Parton, W. J., Power, A. G., & Swift, M. J. Agricultural intensification and ecosystem properties. Science, 1997, 277: 504~509.
    89 Moss, S. R., Storkey, J., Usans, J. W., Erryman, S. A. M., Hewitt M, V., Rasmussen, P. E., Goulding, K. W. T., Brown, J. R., & Grace, P. R. Janzen H H, Krschens M. Long-term agro-ecosystem experiments: assessing agricultural sustainability and global change. Science, 1998, 82: 893~896.
    90 Rasmussen, P. E., & Rohde, C. R. Long-term tillage and nitrogen fertilization effects on organic nitrogen and carbon in semiarid soil. Soil Science Society of America Journal, 1988, 52(4): 1114~1117.
    91 Shaffer, M. J., Wylie, B. K., & Hall, M. D. Identification and mitigation of nitrate leaching hot spots using NLEAP-GIS technology. Journal of Contaminant Hydrology, 1995, 20: 253~263.
    92 Sharpley, A, N. Identifying sites vulnerable to phosphorus loss in agriculture runoff. Journal of Environmental Quality, 1995, 24: 947~951.
    93 Sheldrick, W. F., Syers, J. K., & Lingard, J. A conceptual model for conducting nutrient audits at national, regional, and global scales. Nutrient Cycling In Agroecosystems, 2002, 62: 61~72.
    94 Smil, V. Nitrogen in crop production: an account of global flows. Global Biogeochemical Cycles, 1999, 13: 647~662.
    95 Stoorvogel, J., & Smaling, E. M. A. Research on soil fertility decline in tropical environments: integration of spatial scales. Nutrient Cycling In Agroecosystems, 1998, 50: 151~158.
    96 Syers, K. J, Sheldrick, W., & Lingard, J. Nutrient balance change as an indicator of sustainable agriculture.17th WCSS, 14-21 August 2002, Thailand.
    97 Wang, Y. Ch., Wang, E. L., & Wang, D. L. Crop productivity and nutrient use efficiency as affected by long-term fertilization in North China Plain, Nutrient Cycling In Agroecosystems, 2010, 86: 105~119.
    98 Watson, C. A, & Atkinson, D. Using nitrogen budgets to indicate nitrogen use efficiency and losses from whole farm systems: comparison of three methodological approaches. Nutrient Cycling In Agroecosystems, 1999, 53: 259-267.
    99 William, F., Sheldrick, J., & Keith, S. Soil nutrienta udits for China to estimate nutrient balancesand output/input relationships. Agriculture, Ecosystems and Environment, 2003, 94: 341~354.
    100 Xing, G. X., & Zhu, Z. L. An assessment of N loss from agricultural fields to the environment in China. Nutrient Cycling in Agroecosystems, 2000, 57: 67~73.
    101 Xing, G. X., & Zhu, Z. L. Regional nitrogen budgets for China and its major watersheds. Biogeochem, 2002, 57/58: 405~427.
    102 Zavattaro, L, Romani, M., & Sacco, D. Fertilization management of paddy fields in Piedmont (NW Italy) and its effects on the soil and water quality. Paddy and Water Environment, 2006, 4: 61~66.
    103 Zebarth, B. J., Paul, J. W., & Kleeck, R. V. The effect of nitrogen management in agricultural production on water and air quality: Evaluation on a regional scale. Agriculture, Ecosystems & Environment, 1999, 72: 35~52.
    104 Zhu, Z. L., & Chen, D. L. Nitrogen fertilizer use in China-Contributions to food production, impacts on the environment and best management strategies. Nutrient Cycling In Agroecosystems, 2002, 63(2): 117~127.

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