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경운에 따른 옥수수 근권에서의 질산태질소의 이동양상
Nitrate Movement in The Root Zone of Corn Fields with Different Tillage Systems 원문보기

韓國土壤肥料學會誌 = Korean journal of soil science & fertilizer, v.39 no.1, 2006년, pp.38 - 45  

김원일 (농업과학기술원 환경생태과) ,  정구복 (농업과학기술원 환경생태과) ,  이종식 (농업과학기술원 환경생태과) ,  김진호 (농업과학기술원 환경생태과) ,  이정택 (농업과학기술원 환경생태과)

초록
AI-Helper 아이콘AI-Helper

질산태 질소의 이동에 대한 토양 특성과 경운의 영향을 구명하기 위하여 1993년부터 1994년까지 2년 동안 미국 일리노이주 중부지방의 몇 개 토양통이 다른 옥수수 포장에서 질산태 질소의 함량을 조사하였다. 1993년 포장에는 무수암모니아 $225kg\;ha^{-1}$을, 1994년 포장에는 URAN $115kg\;ha^{-1}$을 시용하였다. 1993년 초기 포장에 질산태질소의 함량은 토양 깊이 100 cm 까지 $20mg\;kg^{-1}$ 정도의 농도를 보였으나, 시용후 옥수수 재배 초기에는 질산태질소의 하향이동을 확인할 수 있었다. 또한 수확 후 토양중의 질산태질소의 함량은 유기물 함량이 보다 많은 Flanagan 및 Ipava 토양통에서 Saybrook 및 Catlin 토양통에 비해 높은 경향을 보였으나 유의적인 차이는 없었고, 무경운 포장에서 경운 포장에 비하여 질산태질소의 함량이 높게 나타났다. 이는 무경운에 의한 질산태질소의 지하수로의 용탈 감소를 의미한다.

Abstract AI-Helper 아이콘AI-Helper

Movement of nitrate ($NO_3-N$) through a soil profile under no tillage (NT) or conventional tillage (CT) practices was monitored to identify the effects of tillage systems on nitrate leaching and retention in the soil profile at two commercial farms in central Illinois from 1993 through 1...

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제안 방법

  • In the experiments, soil samples with 3 or 4 replications were collected to a depth of 120 cm with a hydraulic core-sampling machine at periodic intervals for analysis. Soil core samples were systematically collected at the sampling sites within each plot : halfway between adjacent plant rows, and directly in the row to estimate spatial variability as a function of distance from path of the applicator knife.
  • In the experiments, soil samples with 3 or 4 replications were collected to a depth of 120 cm with a hydraulic core-sampling machine at periodic intervals for analysis. Soil core samples were systematically collected at the sampling sites within each plot : halfway between adjacent plant rows, and directly in the row to estimate spatial variability as a function of distance from path of the applicator knife.
  • This experiment represents a cooperative effort between ARS personnel and operational commercial farms using practices typical of those in the central corn belt. The cooperating farmers allowed USDA scientists unrestricted access to representative fields over the three-year experimental period reported in this study; the measurements reported here were designed to monitor the soil water balance and the fate of nutrients applied to the soil with a view to evaluating the contribution of typical farmers practices to environmental contamination.
  • Therefore, to find optimal N management practices for use with the different tillage systems and to minimize nitrate leaching losses, one must understand the fate of various N forms in soil, and how N availability to plants affects numerous parameters, especially soil water uptake. The objectives of this study were to monitor changes of soil water content, and nitrate concentrations under different tillage systems on commercial farms in Central Illinois, and to identify the effects of fertilizer, soil type, and tillage systems on nitrate leaching in soils following inorganic N fertilizer application, with a view to estimating optimal N fertilizer application rates and timing to minimize environmental hazards.

대상 데이터

  • The study was conducted in cooperation with two privately-owned commercial farms located in central Illinois near the city of Bloomington. The study was begun on farm A in 1993 and on farm B in 1994. The soil series in farm A consisted of (a) Flanagan silt loam (a fine, montmorillonitic, mesic, Aquic Argiudoll) and (b) Saybrook silt loam (a fine silty, mixed, mesic Typic Argiudoll).
  • A field study was initiated in the spring of 1993 and continued for two growing seasons. The study was conducted in cooperation with two privately-owned commercial farms located in central Illinois near the city of Bloomington. The study was begun on farm A in 1993 and on farm B in 1994.
  • Two tillage systems, conventional tillage (CT) and no tillage (NT), were used in this study. CT involved chiselplowing, leaving residue on the soil surface, while in the NT system, the soil surface was left undisturbed from one harvest to next.

데이터처리

  • Data reduction for statistical analysis of the nitrate concentration was done with the SAS system (SAS Institute, 1985) and Super ANOVA (Gagnon, et al., 1989). Separated analyses of variance for nitrate concentration were performed for each year.
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참고문헌 (22)

  1. Angle, J. S., C. M. Gross, R. L. Hill, and M. S. McIntosh. 1993. Soil nitrate concentrations under corn as affected by tillage, manure, and fertilizer applications. J. Environ. Qual. 22: 141-147 

  2. Bauder, J. W., and R. P. Schneider. 1979. Nitrate-nitrogen leaching following urea fertilization and irrigation. Soil Sci. Soc. Am. J. 43: 348-352 

  3. Eck, H. V., and O. R. Jones. 1992. Soil nitrogen status as affected by tillage, crops, and crop sequences. Agron. J. 84: 660-668 

  4. Gagnon, J., K. A. Haycock, J. M. Roth, D. S. Feldman, Jr. W. F. Finzer, R. Hoffman, and J. Simpson. 1989. SuperANOVA accessible general linear modeling. Abacus Concepts Inc. CA 

  5. Gaines, T. P., and S. T. Gaines. 1994. Soil texture effect on nitrate leaching in soil percolates. Commun. Soil Sci. Plant Anal. 25 (13 & 14): 2561-2570 

  6. Harris, G. H., O. B. Hesterman, E. A. Paul, S. E. Peters, and R. .R Janke. 1994. Fate of legume and fertilizer nitrogen-15 in a longterm cropping system experiment. Agron. J. 86: 910-915 

  7. Hauck, R. D. 1982. Nitrogen-isotope-ratio analysis. p 735-779 In Methods of soil analysis. part 2. (2nd ed.) Agronomy. ASA, Madison, WI 

  8. Illinois Soil Survey. series 1900-1996. University of Illinois at Urbana-Champaign, College of Agriculture, Cooperative Extension Service 

  9. Ismail, I., R. L. Blevins, and W. W. Frye. 1994. Long-term notillage effects on soil properties and continuous com yields. Soil Sci. Soc. Am. J. 58: 193-198 

  10. Kanwar, R, S., J. L. Baker, J. M. Laflen. 1985. Nitrate movement through the soil profile in relation to tillage system and fertilizer application method. Transactions of the ASAE. 28(6): 1802-1807 

  11. Kitur, B. K., S. R. Phillips, K. R. Olson, and S. A. Ebelhar. 1994. Tillage effects on selected chemical properties of Grantsburg silt loam. Commun. Soil Sci. Plant Anal. 25(3&4): 225-246 

  12. Kundler, P. 1970. Utilization, fixation, and loss of fertilizer nitrogen (review of international results of the last 10 years of basic research). Albrecht-Thaer-Arch. 14: 191-210 

  13. Lal, R., A. A. Mahboubi, and N. R. Fausey. 1994. Long-term tillage and rotation effects on properties of a central Ohio soil. Soil Sci. Soc. Am. J. 58: 517-522 

  14. Randall, G. W., and T. K. Iragavarapu. 1995. Impact of long-term tillage systems for continuous corn on nitrate leaching to tile drainage. J. Environ. Qual. 24: 360-366 

  15. Rao, S. C, and T. H. Dao. 1992. Fertilizer placement and tillage effects of nitrogen assimilation by wheat. Agron. J. 84: 1028-1032 

  16. Rice, C W., M. S. Smith, and R. L. Blevins. 1986. Soil nitrogen availability after long-term continuous no-tillage and conventional tillage com production. Soil Sci. Soc. Am. J. 50: 1206-1210 

  17. SAS Institute. 1985. SAS procedures guide for personal computers. Version 6 edition. SAS Institute Inc. NC 

  18. Sims, G. K., T. R. Ellsworth, and R. L. Mulvaney. 1995. Microscale determination of inorganic nitrogen in water and soil extracts. Commun. Soil Sci. Plant Anal. 26(1&2): 303-316 

  19. Stinner, B. R., G. D. Hoyt, and R. L. Todd. 1983. Changes in soil chemical properties following a 12-year fallow: A 2-year comparison of conventional tillage and no-tillage agroecosystems. Soil Tillage Res. 3: 277-290 

  20. Timmons, D. R. 1984. Nitrate leaching as influenced by water application level and nitrification inhibitors. J. Environ. Qual. 13: 305-309 

  21. Tisdale, S. L., W. L. Nelson, and J. D. Beaton. 1985. Soil fertility and fertilizers. Macmillan Publishing Company, New York 

  22. Wallace, A. 1994. Soil organic matter is essential to solving soil and environmental problems. Commun. Soil Sci. Plant Anal. 25(1&2): 15-28 

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