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Influence of liming and Topsoil Thickness on Vegetative Growth and Leachate Quality of Acidic Coal Refuse

机译:瑞穗和表土厚度对酸性煤矸石营养生长和渗滤液质量的影响

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Coal waste materials inhibit direct vegetation establishment due to adverse physical and chemical properties, particularly low water retention and high potential acidity. The Moss #1 coal refuse pile is located in Dickenson County, Virginia, and was idled in the late 1980's with little topsoil resource available for final closure. The refuse was acidic (Total-S = 0.38%; pH = 3.6), black, high (70%) in coarse fragments, and had a low water holding capacity (4.5% in < 2.0 mm fraction). A small plot experiment was established on the refuse pile to evaluate the influence of liming rates (50% and 100% of lime req.) and topsoil thickness (15, 30 and 60 cm) on vegetative growth and leachate quality. Liming and topsoil amendment increased the surface soil pH from < 4.0 to > 6.0 over a two-year period, which resulted in greater vegetative cover and biomass than the control plots. All topsoil treatments resulted in greater vegetative cover and biomass than plots treated with lime only due to improved surface soil physical and chemical properties. A topsoil treatment of 60 cm gave the thickest vegetative cover and biomass yield. Such a treatment, however, would be cost-prohibitive at this location. Application of 27 Mg ha~(-1) of lime to the refuse surface along with 15 cm of topsoil produced acceptable two-year vegetative cover and biomass, and appeared to be the optimal treatment for this particular situation. Both liming and topsoil had no affect on leachate pH and the electrical conductivity in leachates collected below the plots. This suggests that surface revegetation will have little effect on the quality of water draining through the pile, so long term water treatment requirements may not be reduced by successfully revegetating the pile surface.
机译:煤废料由于不利的物理和化学性质,特别是低水量和高潜在的酸度而抑制直接植被建立。苔藓#1煤矸石桩位于弗吉尼亚州迪克森县,在20世纪80年代后期闲置,有很少的表土资源可用于最终关闭。垃圾是酸性的(总-S = 0.38%; pH = 3.6),黑色,高(70%),粗碎片,水持续容量低(<2.0mm分数为4.5%)。在垃圾桩上建立了一个小的绘图实验,以评估估计率(50%和100%的石灰Req)的影响(50%和100%)和表土厚度(15,30和60cm)对营养生长和渗滤液质量。黎明和表土修正在两年期间将表面土壤pH从<4.0至> 6.0增加,导致比对照图更大的植物覆盖和生物量。所有表土治疗都会导致更大的植物覆盖和生物量,而不是由于改善的表面土壤物理和化学性质而用石灰处理的图。表土治疗60厘米,给出了较长的营养覆盖和生物质产量。然而,这种治疗将在这个位置是高昂的。在垃圾表面中施加27毫克HA〜(-1)的石灰以及15厘米的Topsoil生产可接受的两年营养覆盖和生物量,并且似乎是这种特殊情况的最佳处理。雷芬和甲虫均对渗滤液pH没有影响,渗滤液中收集的渗滤液中的电导率。这表明表面接收物对通过桩排出的水质量几乎没有影响,因此可以通过成功再培养桩表面来降低长期水处理要求。

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