台晓丽, 胡振琪, 陈超. 西部风沙区不同采煤沉陷区位土壤水分中子仪监测[J]. 农业工程学报, 2016, 32(15): 225-231. DOI: 10.11975/j.issn.1002-6819.2016.15.031
    引用本文: 台晓丽, 胡振琪, 陈超. 西部风沙区不同采煤沉陷区位土壤水分中子仪监测[J]. 农业工程学报, 2016, 32(15): 225-231. DOI: 10.11975/j.issn.1002-6819.2016.15.031
    Tai Xiaoli, Hu Zhenqi, Chen Chao. Monitoring soil moisture at different subsidence areas of mining in western windy and sandy region with neutron instrument[J]. Transactions of the Chinese Society of Agricultural Engineering (Transactions of the CSAE), 2016, 32(15): 225-231. DOI: 10.11975/j.issn.1002-6819.2016.15.031
    Citation: Tai Xiaoli, Hu Zhenqi, Chen Chao. Monitoring soil moisture at different subsidence areas of mining in western windy and sandy region with neutron instrument[J]. Transactions of the Chinese Society of Agricultural Engineering (Transactions of the CSAE), 2016, 32(15): 225-231. DOI: 10.11975/j.issn.1002-6819.2016.15.031

    西部风沙区不同采煤沉陷区位土壤水分中子仪监测

    Monitoring soil moisture at different subsidence areas of mining in western windy and sandy region with neutron instrument

    • 摘要: 为探究西部风沙区采煤沉陷对土壤水分的影响,选取大柳塔某工作面为研究对象,采用中子仪法,对沉陷盆地的盆底区、边缘区和未受开采影响的未开采区2 m以内土壤含水量进行为期2 a的定位动态监测(包括采前—采中—采后0.5 a—采后1 a—采后1.5 a—采后2 a)。研究表明: 1)研究区2 m内土壤含水量具有明显的分层特征,在10~60 cm内含水量呈线性增加,>60~200 cm内基本稳定;2)采煤沉陷对土壤水分的影响具有明显的分区分层特征,使盆底区土壤含水量在10~130 cm内减小,>130~200 cm内含水量增加,使边缘区含水量在2 m内均减小;整体而言,对边缘区的影响大于盆底区;3)采后盆底区土壤含水量呈现自我恢复现象,采后1 a土壤含水量便可恢复到采前水平,采后1.5 a和2 a,表现出高于未开采区的特点;边缘区含水量自我恢复效果不明显,采后2 a 10~130 cm土层内仍没达到未开采区的水平。因此,在对西部风沙区采煤沉陷地进行土地复垦和生态修复时,要分区治理,盆底区要充分依靠土壤水分的自我恢复能力,对边缘区要施以人工修复措施,使含水量及时恢复,满足植物生长的需要;这样尽量依靠自然的力量,有针对性、有重点的治理,既可以减小人工修复带来二次扰动的可能性,又可以减少生态修复成本。

       

      Abstract: In order to research the influence of mining subsidence on soil water content and the variation characteristics of soil water content in windy and sandy region, the authors selected a working face of Da Liuta mining district as the research object, which has the similar characteristics with other mining faces, such as working thickness and mining progress.We divided the subsidence area into pelvic floor area and marginal zone.The pelvic floor area has dynamic fractures which can be quickly closed in the cycle of 18 d.The marginal zone has marginal fractions and additional slopes.And when mining is finished, the marginal fractures are still existing.We used neutron probe method to monitor soil moisture of pelvic floor area, marginal zone and unexploited area.The monitoring depth was 10-200 cm.The monitoring lasted for 2 years.By comparing 2 subsidence areas’ soil water content with unexploited area, we could find the impact law of mining and give feasible advice for land reclamation and ecological rehabilitation in western windy and sandy region.The result showed that: 1) Before exploitation, the study area’s soil moisture content of 10-200 cm depth had obvious layered characteristic, and the depth could be divided into two layers based on the differences of soil water content variation.In 10-60 cm depth, water content increased linearly, and it was then stable and decreased slightly in 60-200 cm depth.2) Mining subsidence could exert influence on soil water content of both the pelvic floor area and the marginal zone.And the influence of mining subsidence on soil water content had obvious leveling and zoning characteristics.Pelvic floor area’s water content decreased in 10-120 cm and increased in 140-180 cm.Meantime, soil water content decreased in marginal zone.In general, the mining subsidence’s influence on marginal zone was greater than the pelvic floor area.3) After mining, the soil water contents of pelvic floor area presented the phenomenon of recovery.Just one year after mining, the water content could be recovered to the one before, and one and a half years or two years after mining, the water content showed the characteristic of being higher than unexploited area.The recovery effect of marginal area’s soil water content was not so obvious.The soil water content at 140 cm depth could recover to the level of unexploited area in one and a half years after mining, but the soil water content of 10-140 cm depth did not eliminate the impact of mining after 2 years.Therefore, while performing land reclamation and ecological rehabilitation on the west windy and sandy coal mining subsidence land, we should implement subarea management.We can make full use of self-reliant ability of pelvic floor area’s soil water content.At the same time, we should adopt artificial restoration measures to restore soil water content of marginal area in time in order to meet the water needs of plant growth.In this way, we can rely on the power of nature as far as possible and implement management purposefully.Not only can it reduce the possibility of secondary disturbance brought by the artificial restoration measures, but it can reduce the cost of ecological restoration.

       

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