Study on Vertical and Lateral Leaching of Nitrate from a Wheat Field in China

Vertical and lateral leaching of nitrate from a wheat field was studied through one season in a field in China by applying increasing amount of N fertilizers (e.g. 90, 180, 270 and 360 kg ha-1). Results showed that nitrate leaching was the dominating way of nitrate loss from wheat land during the first two month after sowing seeds. After irrigation, the nitrate concentration in the leachate of 30 cm soil layer was higher than that of 60 cm, while the concentration of nitrate leaching at the five N treatments through the two depth soil layer came into the same level with the value of 13.48 mg l-1 to 27.91 mg l-1 for 30 cm soil layer and 16.48 mg l-1 to 28.65 mg l-1 for 60 cm soil layer, respectively. As the plot scale (20 m2) concerned, the amount of nitrate loss varied from 101.13 mg l-1 to 209.35 mg l-1 for 30 cm and from 123.63 mg l-1 to 214.89 mg l-1 for 60 cm. Peak nitrate concentration was 3.47 mg l-1 during the third rainfall event. However, nitrate losing by lateral leaching in subsoil was less than that by vertical leaching. At the position that has 0.5 m distances from one side of each plot, the highest nitrate concentrations in lateral leachate among the plots was 10.75 mg l-1 and only has 13.43 mg l-1 the highest lose amount value. By comparison of nitrate concentration in two position of 0.5 m and 1.5 m from one side of each plot, it was not easy for nitrate that transported by lateral leaching from wheat land, in that, nitrate horizontal movement potential in shallow subsoil could be negative. Based on these results, it was suggested that the nitrate vertical leaching had a greater pollution potential to water body than the lateral leaching during the wheat growth period in the fields.

Study on Vertical and Lateral Leaching of Nitrate from a Wheat Field in China

Vertical and lateral leaching of nitrate from a wheat field was studied through one season in a field in China by applying increasing amount of N fertilizers (e.g. 90, 180, 270 and 360 kg ha-1). Results showed that nitrate leaching was the dominating way of nitrate loss from wheat land during the first two month after sowing seeds. After irrigation, the nitrate concentration in the leachate of 30 cm soil layer was higher than that of 60 cm, while the concentration of nitrate leaching at the five N treatments through the two depth soil layer came into the same level with the value of 13.48 mg l-1 to 27.91 mg l-1 for 30 cm soil layer and 16.48 mg l-1 to 28.65 mg l-1 for 60 cm soil layer, respectively. As the plot scale (20 m2) concerned, the amount of nitrate loss varied from 101.13 mg l-1 to 209.35 mg l-1 for 30 cm and from 123.63 mg l-1 to 214.89 mg l-1 for 60 cm. Peak nitrate concentration was 3.47 mg l-1 during the third rainfall event. However, nitrate losing by lateral leaching in subsoil was less than that by vertical leaching. At the position that has 0.5 m distances from one side of each plot, the highest nitrate concentrations in lateral leachate among the plots was 10.75 mg l-1 and only has 13.43 mg l-1 the highest lose amount value. By comparison of nitrate concentration in two position of 0.5 m and 1.5 m from one side of each plot, it was not easy for nitrate that transported by lateral leaching from wheat land, in that, nitrate horizontal movement potential in shallow subsoil could be negative. Based on these results, it was suggested that the nitrate vertical leaching had a greater pollution potential to water body than the lateral leaching during the wheat growth period in the fields.

___

  • Aggarwal, P.K., N. Kalra, S.K. Bandyopadyhay, H. Pathak, V.K. Sehgal, R. Kaur, T.B.S. Rajput, H.C. Joshi, R. Choudhary, R. Roetter, 1998. Exploring agricultural land use options for the state of Haryana: biophysical modeling. In: R.P. Roetter, H. Van Keulen and A.G. Laborte, Khanna Publishing, New Delhi, India.
  • Blackmore, S., 1994. Precision farming: an introduction. Outlook Agric. 23: 275-280.
  • Cassman, K.G., A. Dobermann and D.T. Walters, 2002. Agroecosystems, nitrogen-use efficiency and nitrogen management. Ambio 31: 132-140.
  • Chen, X., J.Q. Zhou, X.R. Wang and F.S. Zhang, 2000. A model selection on nitrogen fertilizer effects in wheat-maize rotation system: analysis of economical and environmental profit. Acta Pedol. Sinica 37: 346-354 (in Chinese with English abstract).
  • Craswell, E.T. and D.C. Godwin, 1984. The efficiency of nitrogen fertilizers applied to cereals in different climates. Adv. Plant. Nutr. 21: 51-55.
  • Delcourt, H., P.L. Darius and J.D. Bardemaeker, 1996. The spatial variability of same aspects of top soil fertility in two Belgium soils. Comput. Electron. Agric. 14: 179-182.
  • De Vos, J.A., D. Hesterberg and P.A.C. Raats, 2000. Nitrate leaching in tile-drained silt loam soil. Soil Sci. Soc. Am. J. 64: 517-527.
  • Drury, C.F., C.S. Tan, J.D. Gaynor, W.D. Reynolds, T.W. Welacky and T.O. Oloya, 2001. Water table management reduces tile nitrate loss in continuous corn and in a soybean-corn rotation. Scientific World Journal 1 Suppl 2: 163-169.
  • Earl, R., P.N. Wheeler, B.S. Blackmore and R.J. Godwin, 1996. Precision farming-the management of variability. J. Instit. Agric.14: 179-183.
  • Fixen, P.E. and F.B. West, 2002. Nitrogen fertilizers: Meeting contemporary challenges. Ambio 31: 169-173.
  • Fox, R.H, Y. Zhu, J.D. Toth, J.M. Jr. Jemison and J.D. Jabro, 2001. Nitrogen fertilizer rate and crop management effects on nitrate leaching from an agricultural field in central Pennsylvania. Scientific World Journal 1 Suppl 2: 181-186.
  • Gasser, M.O., J. Caron, R. Lagace and M.R. Laverdiere, 2003. Predicting nitrate leaching under potato crops using transfer functions. J. Environ. Qual. 32: 1464-1473.
  • Halitligil, M.B., A. Akin, N. Bilgin, Y. Deniz, K. Ögretir, B. Altmel and Y. Isik, 2000. Effect of nitrogen fertilization on yield and nitrogen and water use efficiencies of winter wheat (durum and bread) varieties grown under conditions found in Central Anatolia. Biol. Fertility Soils 31: 175-182.
  • Hernandez, H.H., D.E. Walsh and A. Bauer, 1974. Nitrate reductase of wheat. Its relation to nitrogen fertilization. Cereal Chem., 51: 330-336.
  • Kengi, L., G. Vachaud, J.L. Thony, R. Laty, B. Garino, H. Casabianca, P. Jame and R. Viscogliosi, 1994. Field measurements of water and nitrogen losses under irrigated maize, J. Hydrol.162: 23-26.
  • Kuo, S., B. Huang and R. Bembenek, 2001. Effect of winter cover crops on soil nitrogen availability, corn yield, and nitrate leaching. Scientific World Journal 1 Suppl 2: 22-29.
  • Ministry of Agriculture, 2001. China Agricultural Yearbook. Agricultural Publishing House, Beijing, China (in Chinese, pp. 35-40).
  • Randall, G.W. and D.J. Mulla, 2001. Nitrate nitrogen in surface waters as influenced by climatic conditions and agricultural practices. J. Environ. Qual. 30: 337-344.
  • Ren, L., J. Ma and R. Zhang, 2003. Estimating nitrate leaching with a transfer function model incorporating net mineralization and uptake of nitrogen. J. Environ. Qual. 32: 1455-1463.
  • Sanchez, L., J.A. Diez, A. Vallejo and M.C. Cartagena, 2001. Nitrification losses from irrigated crops in central Spain. Soil Biol. Bichem. 33: 1201-1203.
  • Spalding, R.F. and M.E. Exner, 1993. Occurrence of nitrate in groundwater: a review. J. Environ. Qual. 22: 2229-2236.
  • Xing, G.X. and Z.L. Zhu, 2000. An assessment of N loss from agricultural fields to the environment in China. Nutr. Cycl. Agroecosyst. 57: 67-73.
  • Yadav, R.L., 2004 Enhancing efficiency of fertilizer N use in rice-wheat systems of Indo-Gangetic Plains by intercropping Sesbania aculeata in direct seeded upland rice for green manuring. Bioresour. Technol. 93: 213-215.
  • Yu, Y.L., Y.X. Chen, Y.M. Luo, X.D. Pan, Y.F. He and M.H. Wong, 2003. Rapid degradation of butachlor in wheat rhizosphere soil. Chemosphere 50: 771-774.
  • Zhu, J.G., G. Liu, Y. Han, Y.L. Zhang and G.X. Xing, 2003. Nitrate distribution and denitrification in the saturated zone of paddy field under rice/wheat rotation. Chemosphere 50: 725-732.