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Inducing Sulfate-Reducing Bacteria in the Saturated Zone Near a Nonferrous Industry

机译:在有色工业附近诱导饱和区的硫酸盐降低细菌

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To remediate three sites in the vicinity of a nonferrous industrial site, where groundwater was historically contaminated with metals, the best available technique should be selected. Because the groundwater contained not only high concentrations of metals (site 3 about 300 ppm Co, site 2 about 2000 ppm Zn and site 1 about 300ppm Zn) but also high sulfate concentrations (up to 2000 ppm), the feasibility of sulfate reduction and subsequent metal immobilization due to metalsulfide precipitation was examined in the lab before selecting an appropriate remediation technology. However, because of the very high metal concentrations in the groundwater and their potential toxic effects on microbial life, chemical reagents were selected in addition to biological substrates to immobilize the metals in situ. The first site (site 1) was characterized by a contamination of Zn (140ppm-3ppm) up to a depth of 130m-bg. A screening for inducibility of biological activity was performed at two depths I.e. 30m-bg and 65m-bg using microcosm experiments containing both aquifer and groundwater. Different electron-donors were selected including pure chemical agents like lactate and waste products like molasses and glycerol. Glycerol resulted in the most efficient metal and sulfate removal after about 106 days. Extremely high Zn concentrations were found in the groundwater of the second site (site 2), I.e., up to about 2000 ppm. Similar lab tests applied for site 1 were performed, but additionally chemical agents (NaS_2 and CaS_x) were used. Whereas the sulfide containing chemical agents immediately resulted in low Zn concentrations in the groundwater, it took > 140 days before biological activity in terms of sulfate removal started. Glycerol, lactate, and molasses resulted in efficient Zn removal. Site 3 was characterized by a relative shallow contamination ( < 10 m-bg) of mainly Co (30-300 ppm) and contained typical sulfate concentrations in the range of 300-1200 ppm. Rapid microbial sulfate reduction (within 50 days) was induced in the conditions containing nutrient amended lactate, cheese whey and soy oil. All data obtained will be used to decide which in situ application to implement for the pilot-scale demonstration and remediation. A more detailed presentation for site 3 is given in Van den Broeck et al. (2007).
机译:为了在一个有色的工业部位附近修复三个地点,地下水历史污染金属污染,应选择最佳的可用技术。因为地下水不仅含有高浓度的金属(Site 3约300ppm Co,部位2左右2000ppm Zn和位点1左右300ppm Zn),而且还具有高硫酸盐浓度(高达2000ppm),硫酸盐还原的可行性和随后的可行性在实验室中检查了由于金属硫化物沉淀而导致的金属固定在选择适当的修复技术之前。然而,由于地下水中的金属浓度非常高及其对微生物寿命的潜在毒性作用,除了生物基材之外还选择化学试剂以原位将金属固定。第一个位点(位点1)的特征在于Zn(140ppm-3ppm)的污染,其深度为130m-bg。在两个深度中进行生物活性诱导型的筛选。使用含有含水层和地下水的微观实验30m-Bg和65m-Bg。选择不同的电子供体,包括纯化学试剂,如乳酸盐和糖蜜和甘油等乳酸盐。甘油在约106天后导致最有效的金属和硫酸盐去除。在第二位点(位点2)的地下水中发现极高的Zn浓度,即,高达约2000ppm。进行类似的实验室测试,但是使用施加的位点1,但使用另外化学试剂(NAS_2和CAS_X)。虽然含有化学试剂的硫化物立即导致地下水中的低Zn浓度,但在生物活性在硫酸盐去除方面进行了140天。甘油,乳酸和糖蜜导致高效的Zn去除。遗址3的特征在于主要浅污染(<10m-BG),主要是CO(30-300ppm),并含有300-1200ppm的典型硫酸盐浓度。在含有营养修订的乳酸盐,奶酪乳清和豆油的条件下诱导快速微生物硫酸盐(50天内)。所获得的所有数据将用于决定哪种原位应用程序,以实现导频规范示范和修复。 Van Den Broeck等人提供了一个更详细的网站演示文稿。 (2007)。

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