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Passive Treatment of Coal-mine Drainage by a Sulfate-reducing Bioreactor: A Case Study from the Illinois Coal Basin, USA

机译:硫酸盐减少生物反应器的被动处理 - 硫酸盐减少生物反应器 - 伊利诺伊州煤炭盆地的案例研究

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The purpose of the study was to identify and monitor the geochemical and biogeochemical mechanisms that control the attenuation of coal-mine drainage during the first four years of treatment by an anaerobic sulfate-reducing bioreactor and associated oxidation ponds. This information is needed to investigate bioreactor design parameters, performance and longevity. The acid-mine drainage (AMD) at the case example site, the Tab-Simco Mine, had been highly acidic with an average pH of 2.9, a net acidity of 1,665 mg/L calcium carbonate equivalent-CCE, and high levels of dissolved SO42-, Al, Fe, and Mn. The severity of the AMD at this site may be considered as beyond the treatment capabilities of conventional passive treatment techniques. Nevertheless, the treatment system has increased the pH of the acid mine drainage (AMD) to ~6.0 and decreased the median acidity from 1,647 to 64.6 mg/L CCE, SO_4~(2-) from 2,995 to 1,691 mg/L, Fe from 443.3 to 4.6 mg/1, Al from 116.5 to 0.69 mg/L, and Mn from 36.5 to 23.5 mg/L. Geochemical modeling indicates that the bioreactor discharge is saturated with respect to the minerals alunite, gibbsite, siderite, rhodochrosite, jarosite, and iron hydroxide precipitates. The δ~(34)S value of SO_4~(2-) increased in the bioreactor from an average of +6.9%o to +9.2%o, suggesting the presence of bacterial sulfate reduction. Preliminary results of a bacterial community analysis show that DNA sequences corresponding to bacteria capable of sulfate reduction were present in the bioreactor outflow discharge, but were outnumbered by sequences similar to bacteria capable of re-oxidizing reduced sulfur species. The temporal trends include seasonal variation in SO_4~(2-) and metal concentration and a general decline in the amount of alkalinity. Recently, these declines have reduced the ability of the receiving stream to buffer the system discharge during dry seasons. Overall, this study illustrates the dynamic biogeochemical nature of the passive treatment systems.
机译:该研究的目的是识别和监测地球化学和生物地球织化学机制,可通过厌氧减少生物反应器和相关氧化池治疗的前四年来控制煤矿排水的衰减。需要此信息来调查生物反应器设计参数,性能和寿命。酸矿排出(AMD)在壳体实施例现场,标签-IMCO矿,平均pH值为2.9,净酸度为1,665mg / L碳酸钙等当量-CCE,以及​​高水平的溶解SO42-,Al,Fe和Mn。本网站的AMD的严重程度可被视为超出传统被动处理技术的治疗能力。然而,治疗系统增加了酸性矿氨流量(AMD)至〜6.0的pH,并从2,995到1,691 mg / L,Fe的2,995到1,691 mg / L,Fe,从1,695至1,691毫克/升,Fe减少443.3至4.6mg / 1,Al从116.5至0.69 mg / L,均为36.5至23.5 mg / L.地球化学建模表明,生物反应器放电相对于矿物学,Gibbsite,盐酸盐,罗地料,碱土和氢氧化铁沉淀物饱和。 SO_4〜(2-)的δ〜(34)S值在生物反应器中增加,平均值+ 6.9%〜+ 9.2%O,表明存在细菌硫酸盐的还原。细菌群落分析的初步结果表明,对应于能够减少硫酸盐的细菌的DNA序列存在于生物反应器流出子排出中,但是通过类似于能够重新氧化硫种类的细菌的序列数而寡不过谱。时间趋势包括SO_4〜(2-)和金属浓度的季节性变化,并且碱度量的一般下降。最近,这些下降减少了接收流在干燥季节缓冲系统放电的能力。总体而言,本研究说明了被动治疗系统的动态生物地球化学性质。

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