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Bioremediation of aromatic compounds using municipal activated sludge.

机译:使用市政活性污泥对芳香族化合物进行生物修复。

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The activated sludge wastewater treatment system consists of a mixed community of aquatic microorganisms that transform organic and inorganic pollutants into environmentally acceptable end products. The objective of this research was to determine the potential of municipal activated sludge to biodegrade the model compound, sodium benzoate, and the recalcitrant compound, 2-chlorobenzoate, with and without microbial enhancement. Microbial enhancement included the addition to fresh municipal activated sludge of either municipal activated sludge adapted to these compounds or similarly adapted cultures of a wild type or a genetically engineered strain of Pseudomonas aeruginosa. The latter was the product of the use of Vitreoscilla hemoglobin technology.; Municipal activated sludge obtained directly from the water reclamation plant did have the ability to degrade both benzoate and 2-chlorobenzoate, and this could be enhanced by adapting the activated sludge to either compound. A 10% (v/v) addition of adapted activated sludge increased the benzoate degrading ability of fresh municipal activated sludge 3-fold. Adapting this municipal activated sludge to benzoate for more than 6 months increased its ability to degrade a 10 mg/L solution of benzoate 115-fold. Time to reach maximum enhancement (about 45-fold) for benzoate degradation was about five weeks. For 2-chlorobenzoate, projected time to maximum enhancement (20-fold) was about 25 weeks. The results suggest that significant enhancement for degradation of these aromatic compounds in wastewater could be achieved using such enricher technology.; Augmentation of benzoate and 2-chlorobenzoate degradation by addition of Pseudomonas aeruginosa, both wild type and engineered to contain the Vitreoscilla hemoglobin gene, was investigated. When grown on solid media for five weeks, PaWT and PaJC grew visibly only on benzoate, and not 2-chlorobenzoate, when each compound was provided as the sole carbon source. Both strains grew well on solid nutrient media containing 1 g/L 2-chlorobenzoate which indicated that these compounds were not toxic to either strain.
机译:活性污泥废水处理系统由水生微生物的混合群落组成,这些群落将有机和无机污染物转化为环境可接受的最终产品。这项研究的目的是确定市政活性污泥在不添加微生物的情况下生物降解模型化合物苯甲酸钠和难降解化合物2-氯苯甲酸盐的潜力。微生物强化包括在新鲜的市政活性污泥中添加适应于这些化合物的市政活性污泥或类似的野生型铜绿假单胞菌或基因工程菌株的培养物。后者是利用玻璃体血红蛋白技术的产物。直接从水再生厂获得的市政活性污泥确实具有降解苯甲酸盐和2-氯苯甲酸盐的能力,可以通过使活性污泥适应任何一种化合物来增强降解能力。添加10%(v / v)的适应性活性污泥可使新鲜市政活性污泥的苯甲酸酯降解能力提高3倍。使这种市政活性污泥适应苯甲酸盐的时间超过6个月,可提高其降解10毫克/升苯甲酸盐溶液的能力至115倍。苯甲酸酯降解达到最大增强(约45倍)的时间约为5周。对于2-氯苯甲酸酯,预计达到最大增强作用(20倍)的时间约为25周。结果表明,使用这种浓缩器技术可以显着增强废水中这些芳香族化合物的降解。研究了通过添加铜绿假单胞菌(Pseudomonas aeruginosa)来增强苯甲酸和2-氯苯甲酸酯的降解,这两种都是野生型的并且被改造成包含玻璃体血红蛋白基因。当在固体培养基上生长五周时,当每种化合物均作为唯一碳源提供时,PaWT和PaJC仅在苯甲酸酯上可见生长,而在2-氯苯甲酸酯上则不可见。两种菌株均在含有1 g / L 2-氯苯甲酸酯的固体营养培养基上生长良好,这表明这些化合物对任一菌株均无毒。

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