土壤剖面累积硝态氮的植物利用与消减潜力研究
详细信息    本馆镜像全文|  推荐本文 |  |   获取CNKI官网全文
摘要
氮素是人类提高粮食产量的巨大动力,然而经过长期不合理的氮肥投入,中国农田土壤已累积了大量的硝态氮,对地下水构成了严重威胁。如何解决土壤深层硝态氮高累积的问题备受人们专注。本研究分别采用外源15NO3--N注射法和硝态氮高累积剖面田间原位试验方法,通过不同根系植物和种植方式,设置田间微区试验和田间小区试验,对不同根系作物及种植方式对土壤中累积硝态氮的利用及残留运移趋势进行探讨,从而筛选出适宜的植物种类及种植方式,并且得出了以下结论:
     1在常规田间管理条件下,15N微注射微区中,当季苜蓿-无芒雀麦、苜蓿、春玉米、鸭茅及黑杨对深层标记15N利用率分别为18.4%,14.5%,11.0%,9.5%和7.0%;苜蓿-无芒雀麦显著高于玉米、鸭茅和黑杨;玉米显著高于鸭茅和黑杨。第二年对应为11.8%,8.9%,14.6%,2.8%和7.7%,小麦-玉米15N利用率显著大于苜蓿、黑杨和鸭茅,但与苜蓿-无芒雀麦无显著性差异。两年15N总利用率对应为30.2%,23.4%,25.6%,12.3%和11.4%,苜蓿-无芒雀麦显著高于其他处理,苜蓿和小麦-玉米显著高于鸭茅和黑杨。两年连作对标记15N利用率最大的是牧草间作,作物轮作及苜蓿连作对底土硝态氮也有较高量的吸收,而林木(黑杨)则较差。
     2硝态氮在土壤中移动性强,其空间有效性与作物根系的发育和分布关系密切。本试验研究发现,标记层区域作物的根长密度与作物对该区域的土壤标记硝态氮的利用率有很好的相关性。
     3在微区常规水肥管理条件下,一季后,鸭茅、黑杨15NO-3-N明显下移至130cm;苜蓿-无芒雀麦、苜蓿和春玉米未发生强淋洗,仅扩散20cm左右。连作两年,标记氮向下运移较向上强,鸭茅最为强烈(下移超过110cm)。结果表明可以利用牧草间作、作物轮作及苜蓿连作避免硝态氮进一步向深层迁移累积乃至向浅层地下水迁移。
     4硝态氮高累积剖面植物原位修复试验结果显示,连续种植两年总生物量黑杨、小麦-玉米、苇状羊茅、苜蓿-无芒雀麦和苜蓿分别为107.3,54.1,46.7 ,44.7和36.2kg/plot,黑杨显著高于其他处理,小麦-玉米显著高于苜蓿,三种牧草间无显著性差异。两年累计吸氮量对应为1053.4,595.4,902.3,854.3和826.1 g/plot;黑杨吸氮量显著高于其他处理,三种牧草之间没有明显差异,但显著高于小麦-玉米,在种植第二年吸氮量显著增加。本试验结果说明种植林木及牧草可以获得较高的生物量及吸氮量,牧草对土壤氮素吸收利用随种植年限而递增。
     5不同植物种类及土地利用方式对土壤剖面硝态氮分布的影响有差异,土层中硝态氮在一季后,0~100cm均有所降低,生草休闲和苇状羊茅消减能力较强;100~180cm(除苇状羊茅外)均高于种植前,说明种植当季有硝态氮淋洗。第二季后,苇状羊茅土壤剖面累积氮的表观损失量最高, 0~200cm土层硝态氮含量均低于5mg/kg,显著低于生草休闲和黑杨(0~20cm例外),黑杨有较强淋洗;苜蓿第二季较第一季对剖面硝态氮消减显著。
     6在通体高量积累硝态氮的土壤上,可以通过苇状羊茅、苜蓿-无芒雀麦及自然生草休闲的土地管理方式,实现土壤剖面硝态氮含量快速消减,但是自然生草仅在第一季效果较好。在必须考虑收获物经济利用条件下,故苇状羊茅和苜蓿-无芒雀麦为较优的选择,苜蓿在相对长期的修复中具有优势。
Nitrogen is the tremendous power of increaseing production, but after a long-term some farmers had unreasonably inputed application of nitrogen fertilizer. That would lead to accumulate a large amount of nitrate in soil,and that is a serious threat to groundwater. Some people has focus on the issue that how to solve the high accumulative nitrate of subsoil. This study separately set up the field micro-plot experiments by technique of external injection of labeled 15NO3- -N and the field plot of in-situ testing about the nitrate-nitrogen accumulation to investigate of the behavior of residue nitrate and its utilization by the different roots plants and planting patterns in agro-ecosystem , and main conclusions as following:
     (1) Under conventional field management condition,about 15N injection micro-plot experiments, in the first season ,the recovery of labeled of 15NO3--N by alfalfa- bromus inermis intercropping,alfalfa,spring maize,cocksfoot and black poplar were 18.4%, 14.5%, 11.0%, 9.5% and 7.0% respectively. The recovery of labeled of 15NO3--N by alfalfa - bromus inermis intercropping was significantly higher than that by corn, black poplar and cocksfoot; and corn was significantly higher than that by cocksfoot and black poplar. The second season, the recovery of labeled of 15NO3--N by alfalfa- bromus inermis intercropping,alfalfa,spring maize, cocksfoot and black poplar were 11.8 %, 8.9%, 14.6%, 2.8% and 7.7% respectively. Furthermore, the recovery of labeled of 15NO3--N by wheat-corn were significantly higher compared with alfalfa, black poplar and cocksfoot, but alfalfa - bromus inermis was no significant difference. In two years, the total 15N utilization rate of alfalfa- bromus inermis intercropping,alfalfa,spring maize, cocksfoot and black poplar were 30.2%, 23.4%, 25.6%, 12.3% and 11.4% respectively. Alfalfa - Bromus inermis’s 15N utilization rate were significantly higher than other treatments, 15N utilization rate of alfalfa and wheat - corn was significantly higher than cocksfoot and black poplar. In two years ,15N utilization rate of the forage intercropping systeme was the max-rate, wheat maize rotation system and continuous cropping alfalfa was the second rate, but the trees’s (black poplar) 15N utilization rate was mini-rate.
     (2)In the soil Nitrate-N transport had intimate correlation with crop root development and distribution. The pilot study found that in the labeled soil- region the density of crop’s root length and the utilization rate of the crop’s nitrate had good correlation.
     (3)Under the micro-conventional water management conditions,after the previous quarter,cocksfoot and black poplar about the 15NO3--N had significantly movement to 130 cm; Downward leaching of alfalfa - Bromus inermis, alfalfa and spring corn were weaker, only the spread of 20cm. In two years,the movement of the 15NO3--N was stronger downward than upward, and the strongest was cocksfoot (down more than 110cm). The results showed that the forage intercropping, crop rotation and cropping of alfalfa could be used to avoid downward leaching of the accumulation of NO3--N.
     (4) The results of in situ test showed that : in two years, the total biomass of black poplar, wheat - corn, fescue, alfalfa- bromus inermis intercropping and alfalfa were 107.3 kg/plot,54.1 kg/plot,46.7 kg/plot, 44.7 kg/plot and 36.2kg/plot respectively, and the total biomass of black poplar was significantly higher than other treatments, wheat - corn was significantly higher than the alfalfa,among total biomasses of the three forage plants were no significant difference.The total N uptake of black poplar, wheat - corn, fescue, alfalfa- bromus inermis intercropping and alfalfa were: 1053.4, 595.4,902.3,854.3 and 826.1 g / plot respectively,in two years. The N uptake of black poplar was significantly higher than other treatments;among total N uptakes the three forage plants, but they were significantly higher than wheat– corn’s, The test results indicated that planting trees and forage plants can be higher biomasses and N uptake, with the increaseing of cultivation period N uptaks of forage plants had increased production.
     (5) Different plant species and land uses were different their influences of nitrogen distribution on soil profile. After the fist term, in depth 0-100cm of the soil nitrogen was reduced,the catch grass and the fescue were strongerly. In depth 100-180cm of the soil (except fescue) were higher than the pre-cultivation ,which showed that had nitrate leaching in first season. The second season, in soil profile the apparent loss of nitrogen of the fescue was the highest In depth 0-200cm of the soil , NO3--N were lower than 5mg/kg, it was significantly lower than the catch grass and the fescue (except in depth 0-20cm),The NO3--N of the black poplar was strongly leaching; nitrate of the alfalfa was reducted on the section season more then the first.
     (6) In the high accumulate of nitrate-N of all soil layers, reducttion of the fescue, the alfalfa - bromus inermis and the catch grass was used to reducte nitrate-N that was effective of nitrate-N, in the soil.But the catch grass was used to reducted nitrate-N that was good only in the first season. Under the condiction of the economical and effective way , the fescue and alfalfa - Bromus inermis were better in effectiveness of nitrate-N;and in the long-term the alfalfa was showed better。
引文
[1]朱兆良.合理施用化肥充分利用有机肥发展环境友好的施肥体系[J].中国科学院院刊,2003.2:89-94.
    [2] FAO Fertilizer Yearbook,1998.
    [3]曹志鸿.科学施肥与我国粮食安全保障[J].土壤,1998,(2):57-63,69.
    [4]林葆,林继雄,李家康,等编.长期施肥的作物产量和土壤肥力变化[M].中国农业科技出版社,1996.
    [5]中国农业统计年鉴,2008.
    [6] FAO─Food and Agriculture Organization of the UnitedNations. FAOSTAT─FAO Statistical Databases,Agriculture Data (2008).
    [7]董伟,我国耕地逼近18亿亩红线[J],廉政燎望,2006,5:34.
    [8]农业部政府工作汇报,2008.
    [9]张晓松.人均耕地面积1.4亩传递三大替示信号[N].人民网,2006.4-17.
    [10]胡霭堂.植物营养学(下册).[M].北京.北京农业大学出版社. 1995.
    [11]彭琳.中国化肥施用与粮食生产的进程前景与布局.[J].西北农地学报,1999,8(6):1-5.
    [12] Tilman D, Farglone J, Wolff B ,et al. Forecasting agriculturally driven global environlnental change. Science. 2001,292:281-284.
    [13] Tilman D, Fargione J, Wolff B. Forecasting agriculturally driven globalen vironmental change[J]. Seienee,2002,292(13):281-284.
    [14] Tilman,D.,K.G.Cassman,P.A.Matson,et al .Agricultural sustainability and intensive Production Practices . Nature,2002,418:671-677.
    [15]中国农业统计年鉴,2007.
    [16] FAO─Food and Agriculture Organization of the UnitedNations. FAOSTAT─FAO Statistical Databases,Agriculture Data (2007).
    [17]中国农业年鉴资料,1981-2003.
    [18]杨俊刚,贺建德,陈新平.北京市作物施肥现状调查与测土配方施肥建议[J].北京农业,科技论文,2007.l:15-19.
    [19]寇长林,巨晓棠,张福锁.三种集约化种植体系氮素平衡及其对地下水硝酸盐含量的影响[J].应用生态学报,2005.16(4):660-667.
    [20]张福锁,马文奇.肥料投入水平与养分资源高效利用的关系[J].土壤与环境,2000.9(2):150-157
    [21]中国农业年鉴资料,2004.
    [22]孙世卫.小麦-玉米轮作区地下水硝态氮含量的研究[J].安徽农业科学,2007.35:
    [23]李晓欣,胡春胜,张玉铭,董文旭,欧阳志云.华北地区小麦-玉米种植制度下硝态氮淋失量研究[J].干旱地区农业研究,2006.24(6):7-10,28
    [24]邹国元,张福锁,巨晓棠,等.冬小麦/夏玉米轮作条件下氮素反硝化损失研究[J].中国农业科学, 2004,37(10):1492-1496.
    [25]朱兆良,文启孝.中国土壤氮素[M].南京江苏科技出版社,1992.
    [26]张福锁,等编著.我国肥料产业与科学施肥战略研究报告[M].北京:中国农业大学出版社,2008.
    [27] Van Dam A. Understanding the reduction of nitrogen leaching by catch crops.[J].Published PhD Thesis,Wageningen University,Wageningen, 2006,171:16-24
    [28] Cassman K G, Aehim D and Walters D T. Agroeeosystems,Nitrogen-use Efficiency,and Nitrogen Management[J]. Ambio,2003.31:132-140
    [29]朱兆良,沈善敏主编.中国土壤肥力-中国土壤的氮肥力与农业中的氮素管理.[M].北京.中国农业出版社. 1998.
    [30]王秋杰,寇长林等编著.黄泛平原沙区农业高效持续发展综合技术-砂质潮土冬小麦氮肥利用与土壤氮素平衡研究[M].黄河水利出版社,2000.
    [31]李世娟,周殿玺,兰林旺.不同水分和氮肥水平对冬小麦吸收肥料氮的影响[J].核农学报,2002.16(5):315-319.
    [32]刘学军,赵紫娟,巨晓棠,等.基施氮肥对冬小麦产量、氮肥利用率及氮平衡的影响[J].生态学报,2002.22(7):1121-1128.
    [33]巨晓棠,潘家荣,刘学军,等.北京郊区冬小麦/夏玉米轮作体系中氮肥去向研究[J].植物营养与肥料学报,2000.3:264-270.
    [34]沈善敏主编.中国土壤肥力[M]北京.中国农业出版社. 1998.
    [35] Ju X T, Liu X J, Zhang F S, et al. Nitrogen fertilization, soil nitrate accumulation, and policy recommendations in several agricultural regions of China[J]. Amibo, 2004, 33(5):330-305.
    [36]李晓欣,胡春胜,程一松.不同施肥处理对作物产量及土壤中硝态氮累积的影响[J].干旱地区农业研究, 2003.(3):38-42.
    [37] Zhang W L,Tian Z X,Zhang N,et al.Nitrate pollution of groundwater in nodhem China.Agriculttire[J].Ecosystems and Environment,1996,59:223-231.
    [38] Richer J,Roelcke M.The N-cycle as determined by intensive agriculture-example from central Europe and China [J].Nutrient Cycling in Agroecosystem,2000,57:33-6.
    [39]吴永成,周顺利,王志敏,等.华北地区夏玉米土壤硝态氮的时空动态与残留[J].生态学报,2005.25(7):1620-1625
    [40]张玉铭,毛任钊,胡春胜.太行山前平原土壤养分分布特征与肥料精准管理研究[J].中国生态农业学报,2005.13(4):116-120.
    [41] Ju X T, Liu X J, Zou G Y,et al. Evaluation of nitrogen loss way in winter wheat and summer maize rotation system,ScientiaAgricultura Sinica, 2002,35(2):1493-1499.
    [42] Ju X T,Kou C L, Zhang F S,Christie P. Nitrogen balance and groundwater nitrate contamination: Comparison among three intensive cropping systems on the North China Plain[J]. Environmental Pollution , 2006,143:117-125
    [43] Ju X.T et al., Interception of residual nitrate from a calcareous alluvial soil profile on the North China Plain by deep-rooted crops: A 15 N tracer study[J],Environmental Pollution ,2007, 146:534-542.
    [44] Agron J .REVIEW AND INTERPRETATION[R].Agron ,2002,94:53-171.
    [45]丁洪,蔡贵信,王跃思等.华北平原几种主要类型土壤的硝化及反硝化活性[J].农业环境保护,2001.20(6):390-393.
    [46]巨晓棠.冬小麦/夏玉米轮作体系中土壤一肥料氮的转化及去向[D].北京:中国农业大学,2000.
    [47] Ferguson.R.B.,GW.Hergent, et al.Site-speeific nitrogen management ofinrrigated maize:Yield and soil residual nittate effects[J].Soil Seience Society Ameriea. 2002,66:544-553.
    [48]李世清,李生秀.半干早地区农田生态系统中硝态氮的淋失闭.应用生态学报,2000.11(2):240-242.
    [49]邹国元.冬小麦/夏玉米轮作体系中肥料氮的硝化一反硝化作用研究[D].北京:中国农业大学,2001.
    [50] Zhu Z L,Chen D L. Nitrogen fertilizer use in China-contributions to food production,impacts on the environment and best management strategies [J].Nutrient Cycling in Agroecosystems,2002,63:117-127.
    [51]张瑞清.我国农田生态系统的养分平衡.1莱阳农学院硕士学位论文[D].莱阳:莱阳农学院,2002.
    [52]张玉良.地下水系统的污染控制[M].北京:中国环境科学出版社, 1991.
    [53]王智超.农田土壤硝态氮累积及干湿交替过程的影响[D].北京:中国农业大学, 2006.
    [54]党廷辉,蔡贵信,郭胜利,等.用15N标记肥料研究旱地冬小麦氮肥利用率与去向[J].核农学报,2003. 17(4):280-85.
    [55]巨晓棠,刘学军,邹国元,等.冬小麦/夏玉米轮作体系中氮素的损失途径分析[J].中国农业科学,2002.35(12):1493-1499.
    [56]李新慧.京郊粮田氮素损失机制与提高氮肥利用率[N].北京土壤学会简讯,1999.2(2):5
    [57] Bergstrom L,Brink N[J].Plant and soil,1986,93:333-345.
    [58]朱兆良,文启孝.中国土壤氮素[M].南京:江苏科学技术出版社,1990.267-276.
    [59] Cuello C L.Gastric cancer in Colombia,Cancert risk and suspect environmental agents.[J] Natl Cancer Inst , 1976,57:1015-1020.
    [60] Haenzel W.Stomach cancer in Japan.[J] Natl Cancer Inst,1976,56:265-274.
    [61] Fraser P.Nitrate and human cancer:A review of the evidence.Intern [J] Epidemiologe,1979,9(3):3-11
    [62] Cao L K, Chen G J and Lu Y T. Nitrogen Leaching in Vegetable Fields in the Suburbs of Shanghai[J]. Pedosphere,2005,15(5): 641-645.
    [63] Rodrigues M A, Coutinho J, M artins F. Efficacy and limitations of triticale as a nitrogen catch crop in a mediterranean environment[J]. European Journal of Agronomy, 2002,17: 155- 160.
    [64] Bouwman A F, Drecht G V and Hoek V D. Global and Regional Surface Nitrogen Balance in Intensive Agriculture Production Systems for the Period 1970-2030 [J].pedosphere, 2005,15(2):137-155.
    [65]张维理,徐爱国,冀宏杰,等.中国农业面源污染控制中存在问题分析[J].全国农业面源污染与综合防治学术研讨会论文集,2004.
    [66]巨晓棠,张福锁.中国北方土壤硝态氮的累积及其对环境的影响[J].生态环境,2003.12(l):24-28.
    [67] Ju X T,Kou C L,Zhang E S,et al.Nitrogen balance and groundwater nitrate contalnination comparison among three intensive cropping systems on the north China Plain[J].Environmental Pollution,2005,l-9.
    [68]巩建华,柯遵伟,李季.河北省奠城市蔬菜种植区化肥施用与地下水硝酸盐污染研究[J]农村生态环境,2004.(20):56-59.
    [69]董章杭,李季,孙丽梅.集约化蔬菜种植区化肥施用对地下水硝酸盐污染影响的研究一以“中国蔬菜之乡”山东省寿光市为例[J].农业环境科学学报,2005,24(6):1139-1144.
    [70] 2004年中国环境状况公报,2005.
    [71] Di H J and K C Cameron. Caleulating nitrogen leaching losses and critieal nitrogen applieation rates in dairy pastur esystems using a semiempirical model[J].New Zealand Journal of Agricultural Researeh,2000,43:139-147.
    [72] Di H J. and K. C. Cameron. Nitrate leaching in temperate agroecosystems: sources, factors and mitigating strategies [J].Nutrient Cycling Agroecosystems, 2002,46: 237-256.
    [73] Ramos C, A Agut,A L Lidon. Nitrate leaehing in important crops of the valencian Community region(spain)[J].EnviroentalPollution,2002,118:215-223.
    [74] Simmelsgaard S E. The effect of crop,N-level,soil type and drainage on nitrate leaehing from Danish soil.soil UseManagemeni,1998,14:30-36.
    [75] Simmelsgaard S E,and J Djurhuus. An empirieal model for estimating nitrate leaching as effected by crop type and the long-term N fertilizer rate[J].Soil Use Management,1998,14:37-43.
    [76] Oenema P C, M Boers, Van M M, et al. Leaching of nitrate from agriculture to groundwater:the effects of Polieies and meass in the Netherlands.[J].Environ.Pollut, 1998,102:471-478.
    [77] Stites W,and Kraft G J. Nitrate and chloride loading to groundwater from anirrigated north-central U·S·sand plain vegele fields[J].Environ.Qual,2001,30:1176-1184.
    [78] Townsend M A , R O Sleezer and S A Maeko. Effects of agrieultural praetiees and vadose zone stratigraphy on nitrate concentration in ground water in Kansas[J]. USA Vat Sei Tech,1996,33(3-4):219-226.
    [79] Thorbum P J,J S Biggs, K L Weie, et al. Nitrate in groundwaters of in tensive agrieultural areas in coastal Northeastern Australia.Agriculture[J].Eeosystems and Environment,2003,驶94:49-58.
    [80]金赞芳,叶红玉.氮同位素方法在地下水氮污染源识别中的应用[J].环境污染与防治, 2006.28(7):531-535.
    [81]袁新民,王周琼.硝态氮的淋洗及其影响因素.干早区研究,2000.17(4):46-52.
    [82]袁新民,同延安,杨学云等.灌溉与降水对土壤硝态氮累计的影响[J].水土保持学报,2000.14(3):71-74.
    [83]吴金水,郭胜利,党廷辉.半干旱区农田土壤无机氮积累与迁移机理[J].生态学报,2003.23(10):2041-2049.
    [84] Gathumbi S M.,G Cadiseh,R J Buresh, et al. Subsoil nitrogen capture in mixed legume stands as assessed by deep nitrogen-15 plaeement[J].Soil Seience Society America Journal,2003,67:573-582.
    [85] Wiesler F and W J Horst.Differences among maize cultivars in the utilization of soil nitrate and the related losses of nitrate through leaehing[J].Plant and soil,1993,151:193-203.
    [86] WieslerF.andW.J.Horst.1994.Root growth and nitrate utilization of maize cultivars under field conditions.[J].Plant and Soil,163(2):267-277.
    [87] Van Noordwijk M, Lawson G, Soumare A, Groot J J R and Hairiah K. Root distribution of trees and crops: Competition and/or complementarily[A]. C. K.Ong, P. Huxley(ed) Tree-crop interactions. CAB International. UK.Waallingford. 1996, 319-364.
    [88] Rowe E. C., K. Hairiah, K. E. Giller, M.V. Noordwijk , G. Cadisch, M. Noordwijk, and G. Cadisch. Testing the safety-net role of hedgerow tree roots by 15N placement at different soil depths.[J], Agroforestry Systems. 1999, 43: 81-93.
    [89] Kanwar R.S,T.S.colvin,J.M.Karlen.Ridge,moldboard,chisel,and no-till effects on tile water quelity beneath two cropping system.[J],Production Agricultrue,1997,10:227-234.
    [90] Randall,G W.,D.R.Huggins,M.P Russelle,D.J Fuches,W.W.Nelson and J.L.Anderson..Nitrate losses through subsurfaee tile drainage in conservation reserve program,alfafa,and row crops systems.[J].Environ.Qual. 1997,26:1240-1247.
    [91]吕殿青,同延安,孙本,Ove.Emteryd氮肥施用对环境污染影响的研究.[J],植物营养与肥料学报1998,4(l):8-15.
    [92]吕殿青,同延安,孙本华.氮肥施用对环境污染影响的研究[J].植物营养与肥料学报.1998,4:8-5
    [93]樊军,邵明安,郝明德,王全九.渭北旱塬苹果园土壤深层干燥化与硝酸盐累积[J],应用生态学报,2004, 15(7):1213-1216.
    [94] Brandi,Dohrn,F.M.,R.RDiek,S.M.Kauffinan,D.D.Hemphill and J.S.Selker.Nitrate Ieaching under a cereal rye eover crop[J],Environ.Qual. .1997,26:181-188.
    [95] Booltink H W G. 1995. Field monitoring of nitrate leaching and water flow in a structured clay soil. Agriculture, Ecosystems and Environment 52 :251-261.
    [96]王家玉,王胜佳,陈义等.稻田土壤中N的渗漏损失研究[J].应用生态学报,1995,6(增刊):62-66.
    [97] Hansen,E.M.,J.Djurhuus,Nitrate Leaching as affeeted by long-term N fertilization on a coarse sand. Siol Use and Manegement.1996,12(4):199-204.
    [98] Bergstrom L.The extraction of soil water by the suetion cup method.[J]. Environment.Quality. .1987,l6:11-8.
    [99]刘晓宏,郝明德.不同轮作施肥对土壤有机氮分解特征的影响[J].土壤与环境.2000,9(2):129-131.
    [100]刘晓宏,田梅霞,郝明德.黄土旱塬长期轮作施肥土壤剖面硝态氮的分布与累积[J].土壤肥料2001.(1):9-12.
    [101] Shen R P, Sun B, and Zhao Q G. 2005. Spatial and temporal variability of N, P and K balances for agroecosystems in China[J]. Pedosphere,15(3): 347-355.
    [102] Jolle,VD,W.H.Pierre.Profile acctunulation of fertilizer deived nitrate and total nitrogen recorvery in twolong-term nitrogen rate experimrnts with corn [J].Soil Sciene Society of Amer,1977,41:373-378.
    [103] Ferguson R B, Hergert G W, Schepers J S, et al. Site-specific nitrogen management of irrigated maize: Yield and soil residual nitrate effects[J]. Soil Science Society Journal of America, 2002, 66:544-553.
    [104] Varvel G E ,Peterson T A.Nitrogen fertilizer reeovery by grain sorghum in monoeulture and rotation systems[J].Agror,1991, 83:617-622.
    [105] Hartemink A E,R J Buresh,B H Jama, et al.Soil Nitrate and water dynamies in Sesbania fallows,weed fallows,and maize[J].Siol Seienc Socie Amerie Joual,1996, 60:568-574.
    [106] Randall G W, Huggins D R, Russelle M P, et al.Nitrate losses through subsurface tile drainage in conservation reserve program,alfalfa,and row crop systems [J]. Environ. Qual. 1997,26:1240-1247.
    [107] Van Es H M, Czymmek K J, Ketterings Q M. Management effects on nitrogen leaching and guide lines for a nitrogen leaching index in New York.[J].Journal of Soil and Water Conservation, 2002, 57(6):499-504.
    [108] Singh,B. and Sekhon G B. Some measures of redueing leaching loss of nitrates beyond poteniial rooting zone,ⅢProper crop rotation[J].Plant Siol,1977,47:585-591.
    [109] Schenk,M.,B.Heins and B. Steingrobe.The signifieanee of root development of spinach and kohlrabi for N fertilization[J].Plant Soil,1991,135:197-203.
    [110] Costa J M Bollero F G and Coale A.Early season nitrate accumulation in winter wheat.[J]. Journal of Plant Nutrition,2000,23(6):773-783.
    [111]王朝辉,宗志强,李生秀,陈宝明.蔬菜的硝态氮累积及菜地土壤的硝态氮残留[J].环境科学,2002.23(3):80-83.
    [112] Hofman G. Nutrient management legislation in European countries[N].Numalce Report.Concerted Aetion,1999,Fair6-CT98-4215.
    [113]刘学军,巨晓棠,张福锁.基施尿素对土壤剖面中无机氮动态的影响[J].中国农业大学学报.2001,6(5):63-68
    [114]张丽娟,巨晓棠,高强,张福锁.玉米对土壤深层标记硝态氮的利用.植物营养与肥料学报,2004,10(5):455-461.
    [115] Suprayogo D, Noordwijk M V, Hairiah K, et al.The inherent‘safety net of Aerisol: Measuring and modeling retarded leaching mineral nitrogen[J].Eurpean Journal Siol Seienee. 2002, 53:185-194.
    [116] Liu H B,Zhang Y G,Li Z H, et al. Nitrate contamination of deep groundwater in rural plainareas of Beijing.Acta Pedologica Sinica, 2005,42(3):411-418.
    [117] Macdonald A J, Poulton P R, Stockdale E A, et al. The fate of residual 15N-labelled fertilizer in arable soil: its availability to subsequent crops and retention in soil[J]. Plant and Soil, 2002, 246:123-127.
    [118] Kuldip K, Goh K M. Recovery of 15N-labelled fertilizer applied to winter wheat and perennial ryegrass crops and residual NO3- - N recovery by succeeding wheat crops under different crop residual management practices[J]. Nutrient Cycling in Agroecosystem, 2002, 46:123-130.
    [119]高强.土壤剖面不同位置累积硝态氮的作物有效性及去向[D].中国农业大学博士学位论文.北京:中国农业大学,2003.
    [120] Gathumbi S M,G Cadisch, et al. Subsoil nitrogen capture in mixed legume stands as assessed by deep nitrogen-15 placement. Soil Science Society America Journal,2003, 67:573-582.
    [121] Izaurralde R C,Y Feng,J A Robertson,et al.Long-term influence of cropping systems, tillage methods,and N sources on nitrate leaching[J].Can.J.Soil Sci,1995,75:497-505.
    [122] Papendick,R.I.,L.F.Elliot,andJ.F.Power.Alternative production systems to reduce nitrates in ground water[J].Am.J.Altern Agric,1987,2:19-24.
    [123] Campbell C A,G P Lafond,R P Zentner,andY W Jame. Nitrate leaching in a Udic Haploboroll as influenced by fertilization and legumes[J],Environ.Qual,1994.23:195C201.
    [124] Voorhees,W.B.,andR.F.Holt.Management of alfalfa to conserve soil moisture. Agric.Exp.Stn.Bull..Univ.of Minnesota, Muir,J.,J.S.Boyce,E.C.Seim,P.N.Mosher, E.J.Deibert, andR. A.St.Paul, 1969 ,494.
    [125] Schortemeyer M,Fei B,Stamp P.Root morphology and nitrogen uptake of maize simultaneously supplied with ammonium and nitrate in a split-root system[J].Annals of Botany,1993,72(2):107-115.
    [126] Zhang Y G, Liu H B, Li Z H, et al.Study of nitrate leaching potential from agricultural land in Northern China under long-term fertilization conditions[J]. Plant Nutrition and Fertilizer Science, 2005 ,11(6) :711-716.
    [127] Rowe E C, K Hairiah, K E Giller,et al. Testing the safety-net role of hedgerow tree roots by 15N placement at different soil depths[J]. Agroforestry Systems,1997, 43: 79-81.
    [128] Sehroth Gotz, Luciana Ferreira da Silva,Rosangela Seixas,et al.Subsoil aceumulation of mineral nitrogen under polyeulture and monoeulture plantations,fallow and primary forest in aferralitic Amazonnian upland Soil.Agriculture[J].Ecosystems and Environment,1999, 75:109-120.
    [129]陈培元,詹古宇,谢伯泰.冬小麦根系研究[J].陕西农业科学,1980.(6):1-6.
    [130]郭胜利.黄土旱塬农田土壤有机碳氮的演变与模拟[D].杨陵:中国科学院西北水土保持研究所,2001.
    [131] Huang Y, D H Rickerl and K D Kephart. Recovery of deep-point injected soil nitrogen-15by switchgrass, alfalfa, ineffective alfalfa and corn[J]. Journal Environmental Quality,1996, 25:1394-1400.
    [132] Menezes S C R, Gaseho G J, W Hanna,et al.Subsoil nitrate uptake by grain pearl millet[J].Agronomy Journal,1997,89:189-194.
    [133] Wiesler F and Horst W J. Differences between maize cultivars in Yield Formation Nitrogen uptake and assoeiated Depletion of Soil nitrate[J].Journal Agronomy and Crop Seienee,1992,168:226-237.
    [134]胡云才,G Reinhold SCHMIDHALTER Urs.从德国农业氮投入认识中国氮污染的严重性及应采取的对策[J].磷肥与复肥,2004.19(5):8-12.
    [135] Cai G X, Chen D L, Ding H.Nitrogen lossed from fertilizers applied to maize,wheat and rice in the North China Plain.[J],Nutrient Cycling in Agro-ecosystems,2002,63:187-195.
    [136] Andraski T W, Bundy L G and Brye K.R. Crop management and cornnitrogen rate effects on nitrate leaching.[J],Joumal of Environmental Quality,2000,29:1095-1103.
    [137]樊军,郝明德.旱地农田土壤剖面硝态氮累积的原因初探[J].农业环境科学学报,2003.22(3):263-266.
    [138]李世清,王瑞军,李紫燕,等.半干旱半湿润农田生态系统不可忽视的土壤氮库-土壤剖面中累积的硝态氮[J].干旱地区农业研究,2004.22(4):1-13.
    [139]鲍士旦.土壤农化分析[M].北京:中国农业出版社,2000.14-14.
    [140] Weed D A J and Kanwar R S. Nitrate and water present in and leaching from root-zone soil. Journal of Environmental Quality, 1996,25:709-719.
    [141] Rowe E C, Noordwijk M V, Suprayogo D, et al.Root distributions partially explain 15N uptake patterns in Gliricidia and peltophorum hedgerow ircropping stems[J]. Plant and Siol,2001,235:167-179.
    [142] Costa J L,H Massone, Martinez D, et al.Nitrate contamination of a rural aquifer and accumulation in the unsaturated zone[J].Agricultural Water Management,2002,57:33-47.
    [143] Christiansen J S, Thorup-Kristensen K and H L Kristensen. Root development of beetroot, sweet corn and celeriac, and soil N content after incorporation of green manure[J]. Journal of Horticultural Science & Biotechnology, 2006,81 (5) 831-838.
    [144] Guo Ruiying , Li Xiaolin , Peter Christie, et al. Influence of root zone nitrogen management and a summer catch crop on cucumber yield and soil mineral nitrogen dynamics in intensive production systems[J]. Plant Soil,2008,313:55-70.
    [145] Zhao Z L,F M Chandra,J Kaluli.Corn yield and fertilizer N recovery in warter-table-controlled corn-rye-grass. European Journal of Agronomy,2000,12:83-92.
    [146] Blumenthal J M, M P Russele and J F S Lamb. Subsoil Nitrate and Bromide Uptake by Contrasting Alfalfa Entries[J]. Agronomy Jouranl, 1999,91:269-275.
    [147]张劲松,孟平,尹昌君.果农复合系统果树根系空间分布特征[J].林业科学,2002.38(4):30-33.

© 2004-2018 中国地质图书馆版权所有 京ICP备05064691号 京公网安备11010802017129号

地址:北京市海淀区学院路29号 邮编:100083

电话:办公室:(+86 10)66554848;文献借阅、咨询服务、科技查新:66554700