CASE STUDY: EFFECTIVENESS OF COMMERCIAL COMPOST SOIL AMENDMENT IN MONTANA UPLAND AND RIPARIAN REVEGETATION 1

R. Prodgers
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Abstract

When using borrow dirt as cover-soil, revegetation often stagnates or declines in one decade or less, especially in cold, semiarid climates, due to infertility and lack of nutrient cycling. Fresh cover-soil is dirt; soil is distinguished by the organisms living in and on it. Compost amendment is intended to speed the conversion of dirt to soil by initiating an incipient soil food web. Compost provides microorganisms capable of degrading a wide variety of organic substances and the carbon and nutrients to sustain them until vascular plants provide fresh substrates and eventually a diverse array of food sources from root exudates to microbial cells. Or so it was thought when the two reclamation projects discussed in this paper began, one a Superfund remediation on Silver Bow Creek and the other waste dump reclamation at the Golden Sunlight Mine. The two projects are on opposite sides of the Continental Divide in southwest Montana. Applying and incorporating compost along Silver Bow Creek was easy; steep slopes at the gold mine limited both application and incorporation. One decade after seeding, microbiological analyses of composted and uncomposted soils failed to demonstrate greater diversity in composted cover- soils at the riparian Superfund site. Neither were short-term microbiological effects of compost amendment detectable at the hard-rock mine. Vascular plant cover likewise did not show a significant difference between composted and uncomposted treatments at the riparian site. This raises the question of whether introduced soil microbes drive revegetation or vice-versa, the vascular plants lead and soil microbiology follows. The microbiological activity that matters may be restricted mainly to the rhizosphere, at most a few percent of the bulk soil. Thermophilic microorganisms in moist compost simply may not survive in soils that dry and freeze. Soil biology may be one aspect of the recovery process that cannot be expedited using biologically active organic amendment. Compost specifications also are discussed.
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案例研究:商业堆肥土壤改良剂在蒙大拿州高地和河岸植被中的有效性
当使用借来的泥土作为覆盖土时,由于不育和缺乏养分循环,植被恢复往往在十年或更短的时间内停滞或下降,特别是在寒冷、半干旱气候中。新鲜的覆盖土是泥土;土壤是由生活在土壤里和土壤上的生物来区分的。堆肥改良剂的目的是通过启动一个早期的土壤食物网来加速污垢向土壤的转化。堆肥为能够降解多种有机物质的微生物提供了碳和营养物质,以维持它们的生存,直到维管植物提供新鲜的基质,并最终从根渗出物到微生物细胞提供各种各样的食物来源。当本文讨论的两个复垦项目开始时,人们是这样认为的,一个是超级基金对银弓溪的修复,另一个是金阳光矿的垃圾场复垦。这两个项目位于蒙大拿州西南部大陆分水岭的两侧。沿银弓溪施用和掺入堆肥很容易;金矿的陡坡限制了应用和合并。播种十年后,对堆肥和未堆肥土壤的微生物分析未能证明河岸超级基金遗址堆肥覆盖土壤的多样性更大。在硬岩矿中也没有检测到堆肥改良剂的短期微生物效应。同样,在河岸上,维管植物覆盖在堆肥处理和未堆肥处理之间也没有显着差异。这就提出了一个问题:是引入的土壤微生物驱动植被恢复,还是相反,是维管植物主导,土壤微生物紧随其后。重要的微生物活动可能主要局限于根际,最多占土壤总量的百分之几。潮湿堆肥中的嗜热微生物在干燥和冻结的土壤中根本无法生存。土壤生物学可能是恢复过程的一个方面,不能加速使用生物活性有机改剂。还讨论了堆肥规范。
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