Nitrate leaching from arable and horticultural land

被引:163
作者
Goulding, K [1 ]
机构
[1] AFRC, Inst Arable Crops Res, Dept Soil Sci, Harpenden AL5 2JQ, Herts, England
关键词
nitrate; leaching; arable farming; horticulture; nitrogen fertilizers; models; pollution; UK;
D O I
10.1111/j.1475-2743.2000.tb00218.x
中图分类号
S15 [土壤学];
学科分类号
0903 ; 090301 ;
摘要
Arable crops in the UK make a large contribution to nitrate leaching by virtue of the land area they cover (> 4.5 million ha). By contrast horticultural crops occupy only a small area (< 0.2 million ha) but can leach very large amounts of nitrogen. The application of nitrogen fertilizer to arable and horticultural crops is very cost-effective, stimulating its use. MAFF's Nitrate Research Programme for arable and horticultural crops aims to reduce nitrate leaching and maintain productive farming through Best Management Practice. The Programme has led to the development and testing of methods to measure nitrate leaching, the identification of 'leaky' crops, soils and practices, and strategies to optimize the use of fertilizer nitrogen. Data have been used to construct and test models of nitrate leaching, which in turn have been used to evaluate the leakiness of potential rotations. Current best practice to minimize nitrate leaching requires measures to improve the efficiency of nitrogen use by crops, combined with measures to protect soil nitrogen from leaching during the late autumn to spring drainage period. This involves consideration of many factors: an appropriate crop variety must be chosen; a green cover must be maintained for as much of the year as is practicable; crops should be drilled early; fertilizer requirements should be calculated using a recommendation system and allowing for soil mineral nitrogen and any manures applied; fertilizers should be spread evenly with a properly calibrated spreader, perhaps using split applications; starter fertilizers and banding of fertilizers should be used where appropriate to reduce losses from vegetables; pest and disease infestation must be minimized; any irrigation must be applied carefully with scheduling. Research is now moving on to study whole farm systems and the interactions between losses of nitrogen and other pollutants to the environment with the aim of minimizing total environmental impact.
引用
收藏
页码:145 / 151
页数:7
相关论文
共 118 条
[1]   PARTITIONING LOSSES OF NITROGEN-FERTILIZER BETWEEN LEACHING AND DENITRIFICATION [J].
ADDISCOTT, TM ;
POWLSON, DS .
JOURNAL OF AGRICULTURAL SCIENCE, 1992, 118 :101-107
[2]   Modelling concepts and their relation to the scale of the problem [J].
Addiscott, TM .
NUTRIENT CYCLING IN AGROECOSYSTEMS, 1998, 50 (1-3) :239-245
[3]  
ADDISCOTT TM, 1991, J ROY AGR SOC ENGL, V152, P133
[4]  
[Anonymous], 1994, FERT REC AGR HORT CR
[5]  
[Anonymous], 1991, Farming, fertilizers, and the nitrate problem
[6]  
Anthony S., 1996, Aspects of Applied Biology, P23
[7]  
ARCHER JR, 1992, ASPECTS APPL BIOL, V30
[8]  
ARMSTRONG AC, 1996, ANN GEOPHYS, V14, pC317
[9]   Comparison of methodologies for field measurement of net nitrogen mineralisation in arable soils [J].
Bhogal A. ;
Hatch D.J. ;
Shepherd M.A. ;
Jarvis S.C. .
Plant and Soil, 1999, 207 (1) :15-28
[10]   Fate of N-15-labelled fertilizer in a long-term field trial at Ropsley, UK [J].
Bhogal, A ;
Young, SD ;
SylvesterBradley, R .
JOURNAL OF AGRICULTURAL SCIENCE, 1997, 129 (01) :49-63