农业改良措施对畜禽径流灌溉盐碱土密度和水量的影响

Viktor Kopytovskiy
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摘要

本文讨论了利用牲畜径流灌溉多年生牧草的长期田间研究结果。本研究的目的是对土地复垦措施和利用养猪场径流灌溉土地时的无排水径流进行实验论证。实验研究是在维捷布斯克州奥尔沙地区的一个专门的开垦系统上进行的,那里的土壤覆盖是由灰化土壤土代表的。实验设计包括8个方案。研究发现,家畜径流灌溉会导致上层土壤的压实。在0 ~ 20 cm耕层,与对照相比,附加密度从1.26 g/cm3增加到1.32 g/cm3,增幅为4.8%,在采取灌排措施的变异中,压实量有所减少。在0-40 cm土层中,只有土壤深度松动4%的变异体失固结更大,施用秸秆的变异体失固结率为5.1%。在0 ~ 60 cm层,只有深度松动和引入秸秆的变异体的添加密度降低。研究还发现,土壤水分流失随时间的变化而变化。对于厚度为0.4-0.6 m的巨石,在前2-3小时内最剧烈,在10-18小时后几乎完全停止;对于厚度为1.0 m的巨石,在36-48小时后几乎完全停止。方案5、6和7的失水强度最高。最低的是控制方案和方案2,其中没有采取土地复垦措施。在备选方案5、6和7中,注意到按年计算的失水强度的减少。因此,在方案5中,2000年的失水量为0.9 mm/h, 2001年为0.87 mm/h, 2002年为0.85 mm/h。选项6和选项7也显示了类似的模式。在不采取农垦措施的控制方案和方案2中,水土流失强度也有所降低。多年来水土流失强度的降低与人为影响造成的土壤密度变化有关。首先,通过农业机械的压实和多年生草的持续灌溉。
本文章由计算机程序翻译,如有差异,请以英文原文为准。
Influence of agromeliorative measures on the density and water yield of sodpodzolic soil when irrigated with livestock runoff
The article discusses the results of long-term field research on irrigation of perennial grasses with livestock runoff. The aim of the research was the experimental justification of land reclamation measures and drainage-free run off during irrigation of land with runoff from pig-breeding complexes. Experimental studies were conducted on a specialized reclamation system in Orsha district of Vitebsk region, where the soil cover is represented by sod-podzolic loamy soils. The experimental design included 8 options. As a result of research, it was found out that irrigation with livestock runoff leads to compaction of the upper soil layers. In the arable layer of 0–20 cm, the additional density increased from 1.26 to 1, 32 g/cm3, or 4.8 %, compared to the control, and in variants with irrigation and drainage measures, the compaction was somewhat less. In the soil layer of 0–40 cm, deconsolidation was greater only in the variants with soil deepening and loosening by 4 %, and when applying straw – by 5.1 %.In the 0–60 cm layer, a decrease in the density of addition was observed only in the variants with deep loosening and the introduction of straw. It was also found out that soil water loss varies over time. It is most intense in the first 2–3 hours and almost completely stops after 10–18 hours for monoliths with a thickness of 0.4–0.6 m, and in monoliths of 1.0 m, after 36–48 hours. The highest intensity of water loss was registered in options 5, 6 and 7. The lowest was in the control variant and option 2, where no land reclamation measures were taken. In options 5, 6 and 7, a decrease in the intensity of water loss by years was noted. Thus, in option 5 in 2000, water loss amounted to 0.9 mm /h, in 2001 – 0.87 mm/h, and in 2002 – 0.85 mm/h. Similar patterns were revealed in options 6 and 7. In the control option and option 2 without agro-reclamation measures, the intensity of water loss also decreased. The decrease in the intensity of water loss over the years is associated with changes in the density of the soil caused by anthropogenic impact on it. First of all, with compaction by farm machines and ongoing irrigation of perennial grasses.
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