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BIOREMEDIATION OF CONTAMINATED WATER SOURCES WITH SULPHATE-REDUCING BACTERIA

机译:硫酸盐还原细菌的受污染水源的生物修复

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Bioremediation of arsenic contaminated water by SRB could be a cost-effective process, especially if a suitable carbon source and support matrix were available. To these ends, the chemical composition of molasses was investigated as a candidate for the former purpose while pine bark, sand and polystyrene were assessed as support matrices. Batch culture studies were carried out to assess 1, 2.5 and 5 g l~(-1) molasses as suitable concentrations for SRB growth. The results show that all concentrations supported SRB growth, the response being dependent on the amount present; however, growth on molasses was not as good as that obtained when lactate was used. Biofilm formation on the matrices was evaluated in batch cultures in flasks containing Postgate medium B. The inherent ability of these matrices to support growth of the organisms was evaluated on the basis of pH and redox potential change and the levels of sulphate removal and sulphide production occurring. Environmental scanning electron microscopy (ESEM) was used to characterise the matrix surfaces. A consortium of SRB growing on polystyrene caused a 49% removal of the original sulphate present whereas on sand a 36% reduction occurred. With pine bark as support matrix no significant sulphate removal occurred. Polystyrene was further examined for its durability as a long-term support material for the growing of SRB in the presence of As(III) and/or As(V) at concentrations of 1, 5 and 20 mg l~(-1). An immobilised mixed culture of SRB with molasses as carbon source and polystyrene as support matrix was grown in laboratory-scale bioreactors to investigate the treatment of synthetic groundwater containing either As(III) or As(V) at initial concentration of 20, 10, 5 and 1 mg l~(-1). Percentage removal of As(III) improved from about 10% to 47% when the concentration was reduced from 20 to 1 mg l~(-1) whereas the corresponding improvement for As(V) was from 39% to 92% during the 14-day experiment.
机译:SRB的砷污染水的生物修复可能是一种成本效益的方法,特别是如果可获得合适的碳源和支持基质。对于这些末端,研究了糖蜜的化学成分作为前目的的候选者,而杉木树皮,砂和聚苯乙烯被评估为支持基质。进行分批培养研究以评估1,2.5和5g L〜(-1)糖蜜作为SRB生长的合适浓度。结果表明,所有浓度都支持SRB生长,响应依赖于存在的金额;然而,糖蜜的生长并不像使用乳酸时所获得的那样良好。在含有后介质B的烧瓶中的烧瓶中的批次培养物中的生物膜形成。基于pH和氧化还原潜在变化和发生的硫酸盐除去和硫化物产生的水平评估这些基质以支持生物体生长的固有能力。 。环境扫描电子显微镜(ESEM)用于表征基质表面。在聚苯乙烯上生长的SRB联盟引起了49%的原始硫酸盐存在,而在沙子上发生36%的减少。用松树吠叫作为支持基质,不会发生显着的硫酸盐去除。进一步检查聚苯乙烯,以耐久性,作为长期支持材料,用于在浓度为1,5和20mg L〜(-1)的浓度下的(III)和/或(v)中生长SRB。作为碳源和聚苯乙烯作为碳源和聚苯乙烯作为碳源的固定化的混合培养在实验室型生物反应器中,以研究含有(III)或(v)的合成地下水在20,10,5的初始浓度下的处理和1 mg l〜(-1)。当浓度从20至1mg L〜(-1)降低时,AS(III)的百分比从约10%降至47%,而AS(v)的相应改善是在14期间的39%至92%。 - 日试。

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