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Treatment and Rehabilitation of Acidic Waste Rock and Tailings – A 14-year Case Study

机译:酸性废物岩石和尾矿的治疗和康复 - 一个14年的案例研究

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This paper presents a waste rock treatment and rehabilitation program conducted at a metaliferous mine site in northern New South Wales from 2000–2013. It updates findings from 2005 for Program #1 (which examined acidity, leachable metals and tree growth in a control and three treated areas of waste rock) and includes new results for Program #2 (which examined acidity, plant uptake of metals and trace elements and tree growth in a control and four treated areas compared to undisturbed background levels) and Program #3 (which examined the treatment and revegetation of submerged mine tailings and an exposed tailings beach).Program #1 showed low soil pH in the control area remained unchanged from years 1–14, and soil pH in the limed and capped areas was initially increased but fell back to starting levels within 12 months and remained low for 14 years. In contrast, soil pH in the Terra B area resulted in soil high pH immediately after treatment and increased in years six and 14 without further treatment. Tree height and density in 2005 and again in 2013 indicated acidity in the control, limed and capped areas suppressed tree height and density; however, in the Terra B area, revegetation in 2013 was comparable to undisturbed forest. Outcomes in the control, biosolids and three Terra B areas in Program #2 were similar to those observed in Program #1.Program #3 showed the submerged and exposed tailings initially had low pH and high concentrations of total and leachable metals before treatment, but these became non-leachable after treatment with Terra B. Revegetation was achieved on the tailings beach, with almost uniform colonisation of bulrush and common reed, along with bottlebrush and golden wattle; a variety of reptiles have also been observed on the revegetated tailings beach, along with migrating ducks, spoonbills and grebes.
机译:本文从2000 - 2013年开始,展示了在新南威尔士州北部北部的玻璃矿场的废弃岩石处理和康复计划。 IT更新2005年的调查结果,用于编程#1(检查控制中的酸度,可赤河金属和树生长和三个处理的废岩区域),并包括编程#2的新结果(其检查酸度,植物的金属和微量元素的植物摄取与未受干扰的背景水平相比的控制和四个处理区域的树木增长(检查了淹没矿山尾矿的治疗和再培养,露出的尾矿海滩)。编程#1显示了对照区域的低土壤pH值仍然存在从第1-14岁之间没有改变,跛行和凝固区域的土壤pH值最初增加,但恢复到12个月内的起始水平,持续14岁。相比之下,Terra B区域的土壤pH在治疗后立即产生土壤高pH,并在六年和14年内增加而没有进一步治疗。树高和密度在2005年,2013年再次指示控制中的酸度,跛行和盖子区域抑制了树高和密度;然而,在Terra B地区,2013年的重新植被与未受干扰的森林相当。对照中的结果,生物糖和程序#2中的三个Terra B区域类似于编程中观察到的编程#3.浸没和暴露的尾矿,最初在治疗前最初具有低pH和高浓度和可赤浸金属,但是在用Terra B治疗后,这些在尾巴海滩上取得了不可浸出的污垢,几乎造成了芦苇和常见的芦苇殖民,以及瓶装和金色的荆棘;在重新定位的尾矿海滩上也观察到各种爬行动物,以及迁移鸭,篦箱和格米。

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