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EFFECTS OF COVER SOIL THICKNESS ON REVEGETATION OF ACIDIC APPALACHIAN COAL REFUSE

机译:覆盖土壤厚度对酸性阿巴拉契亚煤矸石植物的影响

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Appalachian coal processing wastes are typically acid forming with potential acidities in Virginia ranging from an average of 12 Mg CCE demand/1000 Mg waste up to > 50 Mg/1000 Mg where higher sulfur coal seams are cleaned. Direct seeding of these materials is further complicated by high rock fragment content, low water-holding capacity, and high summer surface soil temperatures. In Virginia, conventional revegetation protocols established by the Virginia Division of Mined Land Reclamation (DMLR) in the early 1980's required the return of 1.2 m of soil cover over all actively permitted coal wastes. Unfortunately, most active piles at the time had no available topsoil reserves, so the only alternative was to disturb adjacent properties via blasting to generate spoil derived topsoil substitutes. Between 1982 and 1990, we investigated a number of direct seeding and reduced topsoil cover alternatives in an effort to determine the optimal combination of soil amendments and cover soil thickness for the successful revegetation of varying coal waste acidity conditions. The centerpiece of this research effort was a series of topsoil wedge experiments established over three different coal waste materials where cover soil depth was varied from 0 to 125 cm, with and without lime (15 to 25 Mg/ha) at the soil/coal waste contact. Multi-year vegetation and soil sampling results indicated that a minimum of 45 to 75 cm of cover soil was required over highly acid-forming refuse (47 Mg CCE demand/1000 Mg), with the shallower depth sufficient when a lime layer was applied at the contact zone. Over moderately acid-forming materials (15 to 35 Mg CCE /1000 Mg), as little as 25 cm of cover soil was adequate as long as lime was added to the soil/waste contact zone. Coal waste materials that are < 15 Mg CCE/1000 Mg net acid forming can be direct seeded if high P applications are coupled with heavy mulch or organic amendments, especially when the fill faces are not south-facing. These results were implemented into permit review and oversight by Virginia DMLR in the early 1990's and over the past 15 years, a wide range of active coal waste piles have been successfully revegetated with soil covers of 50 cm or less.
机译:阿巴拉契亚煤炭处理废物通常是乙酸的酸形成,弗吉尼亚的潜在酸度范围为12毫克CCE需求/ 1000毫克浪费高达> 50mg / 1000mg,其中清洁了较高的煤层。这些材料的直接播种是通过高岩石片段含量,低水持量和高夏季表面土壤温度复杂化。在弗吉尼亚州,在20世纪80年代初,弗吉尼亚州弗吉尼亚州的弗吉尼亚州的弗吉尼亚州的常规接收协议要求返回1.2米的土壤覆盖物,所有积极允许的煤炭废物。不幸的是,当时最具活跃的桩没有可用的表土储备,因此唯一的替代方案是通过爆破使邻近的性能扰乱以产生弃土的表土替代品。在1982年至1990年期间,我们调查了许多直接播种和降低的表土覆盖替代品,以确定土壤修正案的最佳组合,并覆盖土壤厚度,以实现不同煤矸石条件的成功再培养。这项研究的核心是一系列表土楔形实验,建立了三种不同的煤矸石​​,其中覆盖土壤深度从0到125厘米变化,在土壤/煤炭废物中有和没有石灰(15至25 mg / ha)接触。多年植被和土壤采样结果表明,在高度酸性垃圾(47毫克CCE需求/ 1000mg)上需要至少45至75厘米的覆盖土壤,当施加石灰层时,较浅的深度就足够了。接触区。超过中度酸性形成材料(15至35mg CCE / 1000mg),只要向土壤/废物接触区加入石灰时,覆盖土壤的25厘米覆盖土壤就足够了。如果高P应用与重覆盖物或有机修改相结合,则<15mg CCE / 1000mg净酸形成的煤废料可以直接接种,特别是当填充面不朝南时,尤其是当填充面不朝南时。这些结果旨在审查和监督弗吉尼亚DMLR在1990年代初,在过去的15年里,各种活跃的煤炭废物桩已成功地植入50厘米或更小的土壤覆盖物。

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