CROP NITROGEN-UTILIZATION AND SOIL NITRATE LOSS IN A LETTUCE FIELD

被引:89
作者
JACKSON, LE
STIVERS, LJ
WARDEN, BT
TANJI, KK
机构
[1] Department of Vegetable Crops, University of California, Davis, 95616, CA
[2] Department of Land, Air and Water Resources, University of California, Davis, 95616, CA
来源
FERTILIZER RESEARCH | 1994年 / 37卷 / 02期
关键词
EROSION PRODUCTIVITY IMPACT CALCULATOR (EPIC) MODEL; LEACHING; LETTUCE; NET-N MINERALIZATION; NITRATE; NITROGEN;
D O I
10.1007/BF00748550
中图分类号
S15 [土壤学];
学科分类号
0903 [农业资源与环境]; 090301 [土壤学];
摘要
Low N use efficiency and high nitrate (NO3-) pollution potentials are problems in intensive vegetable production systems. The purpose of this study was to quantify N utilization by lettuce (Lactuca sativa L. cv Salinas), and identify periods of NO3- loss in an on-farm study in the Salinas Valley in coastal California. During autumn and winter, surface moisture remained low, and NO3- concentrations increased, reflecting high net mineralizable N, as determined by anaerobic incubation, and nitrification potential, as determined by the chlorate inhibition method. At the onset of a large winter storm, tracer levels of (NO3-)-N-15 were injected in the top 5 mm of soil in 30 cm-deep cylinders. After two weeks, most of the N-15 was present as (NO3-)-N-15 at 10-30 cm depth. By difference, losses to denitrification accounted for approximately 25% of the surface-applied N-15. Leaching below 30 cm did not occur, since no N-15 enrichment of NO3--N was measured in anion-exchange resin membranes placed at the base of each cylinder. During the crop period, NO3- losses were most pronounced after irrigation events. Uptake of N by two crops of lettuce (above- and belowground material) was approximately equal to fertilizer inputs, yet simulation of N fates by the Erosion/Productivity Impact Calculator (EPIC) model indicated losses of 14.6 g-N m-2 by leaching and 2.5 g-N m-2 by denitrification during the 6-month crop period. The large NO3- losses can be attributed to accumulation of soil NO3- during winter that was leached or denitrified during the irrigated crop period.
引用
收藏
页码:93 / 105
页数:13
相关论文
共 37 条
[1]
Addiscott T.M., Whitmore A.P., Powlson D.S., Farming, Fertilizers and the Nitrate Problem, (1991)
[2]
Belser L.W., Mays E.L., The specific inhibition of nitrite oxidation by chlorate and its use in assessing nitrification in soils and sediments, Appl Environ Microbiol, 33, pp. 309-333, (1980)
[3]
Brooks P.D., Stark J.M., McInteer B.B., Preston T., Diffusion method to prepare soil extracts for automated Nitrogen-15 analysis, Soil Sci Am J, 53, pp. 1707-1711, (1989)
[4]
Burns I.G., Short- and long-term effects of a change in the spatial distribution of nitrate in the root zone on N uptake, growth and root development of young lettuce plants, Plant, Cell and Environment, 14, pp. 21-33, (1991)
[5]
Carlson R.M., Automated separation and conductimetric determination of ammonia and dissolved carbon dioxide, Anal Chem, 50, pp. 1528-1532, (1978)
[6]
Carlson R.M., Continuous flow reduction of nitrate to ammonium with granular zinc, Anal Chem., 58, pp. 1590-1591, (1986)
[7]
Doerge T.A., Roth R.L., Gardner B.R., Nitrogen Fertilizer Management in Arizona, (1991)
[8]
Feigin A., Letey J., Jarrell W.M., Nitrogen utilization efficiency by drip irrigated celery receiving preplant or water applied N fertilizer, Agronomy Journal, 74, pp. 978-983, (1982)
[9]
Follett R.W., Schimel D.S., Effect of tillage practices on microbial biomass dynamics, Soil Sci Soc Am J, 53, pp. 1091-1096, (1989)
[10]
Freund R.J., Littell R.C., Spector P.C., SAS System for Linear Models, (1986)