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Successful Treatment of Low PAH-Contaminated Sewage Sludge in Aerobic Bioreactors

机译:在好氧生物反应器中成功处理低PAH污染的污水污泥

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Background, Aims and Scope. Polycyclic Aromatic Hydrocarbons (PAHs) are known for their adverse and cumulative effects at low concentration. In particular, the PAHs accumulate in sewage sludge during wastewater treatment, and may thereafter contaminate agricultural soils by spreading sludge on land. Therefore, sludge treatment processes constitute the unique opportunity of PAH removal before their release in the environment. In this study, the ability of aerobic microorganisms to degrade light and heavy PAHs was investigated in continuous bioreactors treating trace-level PAH-contaminated sludge. Methods. Several aerobic reactors were operated under continuous and perfectly mixed conditions to simulate actual aerobic sludge digesters. Three sterile control reactors were performed at 35 deg C, 45 deg C or 55 deg C to assess PAH abiotic losses under mes-ophilic and thermophilic conditions. Three biological reactors were also operated at 35 deg C, 45 deg C or 55 deg C. Furthermore, 250 mM methanol were added in an additional mesophilic reactor (35 deg C). All reactors were fed with long-term PAH-contaminated sewage sludge, and PAH removal was assessed by inlet/outlet mass balance. In this study, PAH compounds ranged from 2 to 5-unsubstituted aromatic rings, i.e. respectively from Fluorene to Indeno(123cd)pyrene. Results and Discussion. Significant abiotic losses were observed for the lightest PAHs (fluorene, phenanthrene and anthracene), while biodegradation occurred for all PAHs. More than 80 percent of the lightest PAHs were removed. Biodegradation rates inversely correlated with the increasing molecular weight, and seemed limited by the low bioavailability of the heaviest PAHs (only 50 percent of removal). The enhancement of PAH bioavailability by increasing the process temperature or adding methanol was tested. A temperature increase from 35 deg C to 45 deg C and then to 55 deg C significantly enhanced the biodegradation of the heaviest PAHs from 50 percent to 80 percent. However, high abiotic losses were observed for all PAHs at 55 deg C, which was attributed to volatilization. Optimal conditions were found at 45 deg C considering the low abiotic losses and the high PAH biodegradation rates. Similar performances were achieved by addition of methanol in the sludge. It was concluded that increasing temperatures or addition of methanol favored PAH diffusion from solids to an aqueous compartment, and enhanced their bioavailability to PAH-degrading microorganisms. Conclusion. In this study, the use of long-term acclimated aerobic ecosystems showed the high potential of aerobic microorganisms to degrade a wide range of PAHs at trace levels. However, PAH biodegradation was likely controlled by their low bioavailability. Two aerobic processes have been finally proposed to achieve efficient decontamination of sewage sludge, at 45 deg C or in the presence of methanol. The PAH concentrations in reactor outlet were lower than the French requirements, and allow the treated sludge to be spread on agricultural land. Recommendations and Outlook. The two proposed aerobic processes used physical or chemical diffusing agents. The global ecological impact of using the latter agents for treating trace level contamination must be considered. Since methanol was completely removed during the process, no additional harm is expected after treatment. However, an increase of temperature to 45 deg C could drastically increase the energy demand in full-scale plants, and therefore the ecological impact of the process. Moreover, since bioavailability controls PAH biodegradation, efficiency of the processes could also be influenced by the hydraulic parameters, such as mixing and aeration rates. Further experimentations in a pilot scale are therefore recommended, as well as a final assessment of the global environmental benefit of using such aerobic processes in the bioremediation of trace level compounds.
机译:背景,目的和范围。多环芳烃(PAHs)在低浓度下会产生不利影响和累积影响而闻名。特别是,PAHs在废水处理期间会积聚在污水污泥中,此后可能会通过将污泥散布在土地上而污染农业土壤。因此,污泥处理过程构成了将PAH释放到环境中之前的独特机会。在这项研究中,在处理痕量PAH污染污泥的连续生物反应器中,研究了好氧微生物降解轻重PAH的能力。方法。几个好氧反应器在连续和完全混合的条件下运行,以模拟实际的好氧污泥消化池。在35°C,45°C或55°C下进行了三个无菌对照反应器,以评估在中温和嗜热条件下PAH非生物损失。三个生物反应器也分别在35℃,45℃或55℃下运行。此外,将250 mM甲醇添加到另一个中温反应器(35℃)中。给所有反应器喂长期污染PAH的污水污泥,并通过入口/出口质量平衡评估PAH的去除。在这项研究中,PAH化合物的范围为2至5个未取代的芳环,即分别从芴到茚并(123cd)re。结果与讨论。对于最轻的多环芳烃(芴,菲和蒽),观察到明显的非生物损失,而所有多环芳烃均发生了生物降解。去除了最轻的PAH的80%以上。生物降解率与分子量的增加成反比,并且似乎受到最重的PAH的低生物利用度的限制(仅去除50%)。测试了通过提高工艺温度或添加甲醇来提高PAH生物利用度。温度从35摄氏度升高到45摄氏度,然后升高到55摄氏度,将最重的PAH的生物降解率从50%大大提高到80%。但是,在55℃下,所有PAH的非生物损失都很高,这归因于挥发。考虑到低的非生物损失和高的PAH生物降解速率,发现了在45摄氏度的最佳条件。通过在污泥中添加甲醇获得类似的性能。结论是,升高温度或添加甲醇有利于PAH从固体向水室的扩散,并增强了PAH对降解PAH的微生物的生物利用度。结论。在这项研究中,长期适应性好氧生态系统的使用显示出好氧微生物在痕量水平上降解多种PAHs的巨大潜力。但是,PAH的生物降解很可能受到其低生物利用度的控制。最终提出了两种有氧工艺,以实现在45摄氏度或甲醇存在下对污泥的有效净化。反应器出口的PAH浓度低于法国的要求,并允许将处理后的污泥散布在农田上。建议和展望。提出的两种需氧工艺使用了物理或化学扩散剂。必须考虑使用后一种试剂处理痕量污染物对全球生态的影响。由于在此过程中甲醇被完全去除,因此处理后不会再有其他危害。但是,将温度升高到45摄氏度可能会大大增加大型工厂的能源需求,因此会增加该过程的生态影响。此外,由于生物利用度控制着PAH的生物降解,因此工艺效率也可能受到水力参数(例如混合和通气速率)的影响。因此,建议进行中试规模的进一步试验,以及对在痕量化合物的生物修复中使用此类好氧工艺的全球环境效益的最终评估。

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