• ISSN 1008-505X
  • CN 11-3996/S
同延安, 石维, 吕殿青, . 陕西三种类型土壤剖面硝酸盐累积、分布与土壤质地的关系[J]. 植物营养与肥料学报, 2005, 11(4): 435-441. DOI: 10.11674/zwyf.2005.0402
引用本文: 同延安, 石维, 吕殿青, . 陕西三种类型土壤剖面硝酸盐累积、分布与土壤质地的关系[J]. 植物营养与肥料学报, 2005, 11(4): 435-441. DOI: 10.11674/zwyf.2005.0402
TONG Yan-an, SHI Wei, L Dian-qing, Emteryd Ove. Relationship between soil texture and nitrate distribution and accumulation in three types of soil profile in Shaanxi[J]. Journal of Plant Nutrition and Fertilizers, 2005, 11(4): 435-441. DOI: 10.11674/zwyf.2005.0402
Citation: TONG Yan-an, SHI Wei, L Dian-qing, Emteryd Ove. Relationship between soil texture and nitrate distribution and accumulation in three types of soil profile in Shaanxi[J]. Journal of Plant Nutrition and Fertilizers, 2005, 11(4): 435-441. DOI: 10.11674/zwyf.2005.0402

陕西三种类型土壤剖面硝酸盐累积、分布与土壤质地的关系

Relationship between soil texture and nitrate distribution and accumulation in three types of soil profile in Shaanxi

  • 摘要: 研究了陕北黄绵土,关中土与陕南水稻土土壤剖面中硝酸盐的分布与累积,分析了硝酸盐淋移与土壤剖面粘粒含量的关系。结果表明,黄绵土由于粘粒含量少,土壤疏松,氮肥施入土壤后硝化作用速度快,氮素多以硝态氮存在于土壤中,遇到过量的灌溉或降水,容易引起硝酸盐淋失。在米脂的川道地,施肥2个月后,硝酸盐峰值在50cm左右,4个多月后,峰值下移至100cm左右,6个月后,该峰值下降到130cm左右,一年内,硝酸盐的峰值已经消失,分布在130至350cm之间。因此,在黄绵土地区可以灌溉的川道地,氮素损失的主要途径是硝酸盐淋失。关中土,粘粒含量相对较高,硝化作用速度快,但由于在80120cm有一粘化层,阻碍了水分与硝酸盐的向下淋移,使得大部分硝酸盐累积在0100cm土层,其累积量占到0400cm总累积量的64%~74%,而200400cm仅占到7%~13%。而且淋移到100cm以下的硝酸盐,也通过反硝化损失了。陕南水稻土,由于深层土壤水饱和,硝酸盐难以向下淋移,氮素主要累积在土壤表层。由于下层土壤长期处于厌气条件,即使淋移到下层的硝酸盐也通过反硝化作用而损失掉了。

     

    Abstract: Nitrate distribution and accumulation in soil profile in Entisol in northshaanxi, Anthrosol in Guanzhong plain, Paddy soil in southshaanxi, were studied and the relationship between soil texture and nitrate leaching was described in this paper. The results indicated that due to less clay content and looseness and a fast speed of nitrification, of Entisol, nitrogen input to the soil mostly presented as nitrate, in the bottom-land of Loess Plateau, 2 months later after fertilization, the peak of the nitrate content was located in 50 cm depth, and was moved down to 100 cm depth after 4 months, 130 cm after 6 months, the peak was disappeared after near one year and the nitrate was distributed between 130 and 350 cm depth. Therefore, nitrate leaching is the main way of N losses in bottom-land in Entisol area, where the irrigation could be carried out. However, in Anthrosol, Guanzhong plain, due to a higher clay content relatively and fast speed of nitrification, and a clay layer in 80-120 cm depth was found, which block the nitrate and water leaching through, so most of the nitrate was accumulated in 0-100 cm depth, which account for 64%-74% of total N accumulated in 0-400 cm depth, and N in 200-400 cm depth was only account for 7%-13%. Even some nitrate leached deeper than 100 cm depth, which would loss by denitrification. So, there was no nitrate peak movement could be seen in the soil profile. Since soil water saturated in deep layer, in Paddy soil in Southshaanxi, it isvery difficult for water and nitrate leaching down, so nitrate was mainly accumulated in top soil layer. Nitrate leached down to deeper layer where there is an anaerobic condition, losses through denitrification.

     

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