REVEGETATION TRENDS AND LESSONS AT TWO MONTANA COAL MINES BASED ON 20 YEARS OF MONITORING

R. Prodgers
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Abstract

Abstract: Bighorn Environmental Sciences monitored revegetation at Spring Creek Coal Mine (SCCM) and Decker Coal Mine (DCM) in semiarid southcentral Montana for 20 years using consistent transect locations and methods. Measurements include canopy coverage, air-dried peak standing crop (PSC), and shrub density. About 30 SCCM fields were old enough to evaluate temporal trends. Findings include: • Ten years after seeding, post-mine perennial productivity and canopy coverage were trending upward and exceeded both performance standards and pre-mine vegetation. • Shrub density declined in about 4/5s of fields. Meeting the shrub density standard of 5,740/ha for wildlife habitat, the primary post-mine land use, is a major revegetation challenge. • Rosana western wheatgrass tripled in relative cover by the conclusion of monitoring. It combines environmental suitability and vigorous rhizomatous spread. Introduced sheep fescue spread even more abundantly, quadrupling relative cover from the early years to one decade or more later, also spreading to adjacent fields. • Cheatgrass, which replaces annual forb weeds in unsatisfactory seedings, showed no net temporal trend. • The explosion of the first-year kochia impairs seeding success through interference competition. Prevention requires mine-wide effort. Seeding into annual weeds or litter has not worked, requiring chemical weed control and litter removal before interseeding. The first seeding opportunity is the best. • Shrub seedings are far more successful on suitable spoil than on topsoil. However, some spoil meeting the chemical-physical suitability criteria does not support satisfactory revegetation. Scoria can be a fine shrub and diversity substrate or disappointing. • Heavy-seeded Chenopod shrubs can be established through drill seeding even among vigorous, competitive grasses. • Light-seeded sagebrush establishes best when seeded apart from the heavy-seeded plants. • The most prevalent contribution of direct-haul coversoil to revegetation is weeds, not native perennials.
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基于20年的监测,蒙大拿州两个煤矿的植被恢复趋势和教训
摘要/ Abstract摘要:Bighorn Environmental Sciences采用一致的样带位置和方法对蒙大拿州中南部半干旱地区的Spring Creek Coal Mine (SCCM)和Decker Coal Mine (DCM)进行了20年的植被监测。测量包括冠层覆盖度,风干的直立峰作物(PSC)和灌木密度。大约有30个SCCM油田足够古老,可以评估时间趋势。结果表明:•播种后10年,矿区多年生生产力和冠层盖度均呈上升趋势,超过了矿区前植被的性能标准。•约4/5的林地灌木密度下降。满足野生动物栖息地5,740/ha的灌木密度标准是矿山后土地的主要利用方式,这是一个重大的植被挑战。•根据监测结论,Rosana西部小麦草的相对覆盖面积增加了两倍。它结合了环境适宜性和有力的根茎传播。引进的羊茅传播得更加丰富,从最初几年到十年或更久之后,相对覆盖率翻了两番,也蔓延到邻近的田地。•在不理想的苗种中取代一年生牧草的食草,没有表现出净时间趋势。•第一年kochia的爆发通过干扰竞争削弱了播种的成功。预防需要全矿区的努力。播种到一年生杂草或凋落物中没有效果,在播种前需要化学除草和清除凋落物。第一次播种的时机最好。灌木幼苗在合适的腐土上比在表土上成功得多。然而,一些满足化学-物理适宜性标准的破坏不能支持令人满意的植被恢复。山渣可以是优良的灌木和多样性基质或令人失望。•重种子藜科灌木可以通过钻播建立,甚至在旺盛的,竞争激烈的禾草。•轻种子山艾草与重种子植物分开播种时生长最好。•直接运输覆盖土壤对植被最普遍的贡献是杂草,而不是本地多年生植物。
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