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Soil organic carbon storage in Southern Illinois woodland and cropland.

机译:伊利诺伊州南部林地和农田的土壤有机碳储量。

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Many factors including land use, management history, soil type, climate, and soil landscape processes affect the dynamics of soil organic C (SOC). The primary objective of this research was to compare the storage of SOC on sloping woodland and cropland landscapes of southern Illinois. The cropland area was previously cultivated between the 1880s and the 1930s, used for crop production with forages in crop rotation between the 1930s and the 1960s, and remained in hayland from the 1960s to 1989. Since 1989, row crops were grown on a yearly rotation system using conservation tillage practices. The woodland area was never cleared and farmed but part of the landscape was subjected to periodic grazing before the 1960s. The SOC concentration of various soil layers, to a depth of 1 m, was measured and expressed on both a gravimetric and volumetric basis. The woodland landscape had significantly higher SOC in the surface layer (0-0.05 m) on all 6 landscape segments; however, the 0.05- to 0.15-m layer in the cropland landscape contained significantly more SOC. The subsurface rooting zone SOC values varied by landscape segment for both land uses. Results suggested that the cropland landscape retained 95% of the total SOC on a volumetric basis during the last 130 years of agricultural use. The years with forages may have increased the SOC of the cropland site and help offset losses due to soil erosion and aeration as a result of tillage. The woodland and agricultural landscapes appear to have similar amounts of SOC when the crop rotations included forages, cover crops, conservation tillage, and contour farming. Results suggest that southern Illinois soils can be used for cropland with conservation practices and forages while still maintaining the SOC levels of woodland.
机译:土地使用,管理历史,土壤类型,气候和土壤景观过程等许多因素都会影响土壤有机碳(SOC)的动态。这项研究的主要目的是比较SOC在伊利诺伊州南部倾斜的林地和农田景观中的存储量。农田以前是在1880年代至1930年代之间耕种的,用于作物生产,并在1930年代和1960年代之间进行轮作牧草,从1960年代到1989年仍留在干草地。自1989年以来,大田作物每年轮作种植系统采用保护性耕作方法。林地面积从未被清除和耕种,但部分景观在1960年代之前曾定期放牧。测量了不同土壤层的SOC浓度,深度为1 m,并以重量和体积为单位表示。在所有6个景观区中,林地景观的表层SOC均较高(0-0.05 m);但是,农田景观中的0.05-0.15m层中的SOC明显更多。对于两种土地利用而言,地下生根区SOC值均随景观部分而变化。结果表明,在过去的130年的农业使用中,按体积计,农田景观保留了总有机碳的95%。牧草的年份可能增加了耕地的土壤有机碳,并有助于抵消耕作造成的土壤侵蚀和通气造成的损失。当农作物轮作包括饲草,覆盖作物,保护性耕作和等高线耕作时,林地和农业景观似乎具有相似的有机碳含量。结果表明,伊利诺伊州南部的土壤可用于耕地,具有保护作法和牧草,同时仍保持林地的SOC水平。

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