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Management of table olive processing wastewater by an osmotic membrane bioreactor process

机译:渗透膜生物反应器工艺管理表橄榄处理废水

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摘要

The management of fermentation brines from the table olive processing is very complex due to its characteristics: high salinity and high organic matter concentration including phenolic compounds, which behave as slow degradable compounds when a biological process is performed. In this work, the management of these effluents by an osmotic membrane bioreactor has been assessed. This technique combines a biological reactor with forward osmosis membranes. For the study, a laboratory plant consisting of 1 L reactor and a forward osmosis module equipped with a membrane of 42 cm(2) of active surface has been used. Fermentation brine from table olive processing was fed to the system both as draw solution to set out the driving force for the membrane process and as a part of the feed to the reactor, mixing it with municipal wastewater. The experiments were carried out at a constant feed to microorganism ratio of 0.4 g COD.g SS-1.d(-1). Results indicated that the hypersaline effluent was able to produce the needed driving force by the process. Permeate fluxes ranged between 1 and 1.5 L.m(-2).h(-1) after the flux decay of the first operation days. Concerning the biological reaction, it has to be highlighted that phenols were eliminated after 24 days. Until that day, the biological process was jeopardized due to the quick increase of the conductivity in the reactor (ranging between 30 and 35 mS.cm(-1)), which was caused not only by the salinity of the influent but also by the reverse salt flux phenomenon. Soluble microbial products and extracted extracellular polymeric substances also increased in the reactor during the start-up.
机译:由于其特点:在进行生物过程时,从表橄榄化加工的发酵盐水管理的管理非常复杂,包括酚类化合物的高盐度和高有机物质浓度,其在进行生物过程时表现为缓慢可降解的化合物。在这项工作中,评估了通过渗透膜生物反应器对这些污水的管理。该技术将生物反应器与前渗透膜结合起来。对于研究,已经使用了由1L反应器和配备有42cm(2)的膜的前渗透模块组成的实验室植物。从表橄榄加工中发酵盐水被送到系统中,作为绘制溶液,以便向膜过程中的驱动力和作为反应器的进料的一部分,将其与城市废水混合。实验以恒定的进料进行,对微生物比为0.4g COD.G SS-1.D(-1)。结果表明,过氧碱流出物能够通过该方法产生所需的驱动力。在第一个操作天的磁通衰减后,渗透物助熔剂在1到1.5点(-2).h(-1)之间。关于生物反应,必须强调酚类在24天后被消除。直到那一天,由于反应器中的电导率的快速增加(在30到35 ms.cm(-1)之间的电导率的快速增加,因此不仅由流水的盐度而且由流动的盐度增加而受到危及逆盐通量现象。在启动期间,可溶性微生物产品和提取的细胞外聚合物物质也在反应器中增加。

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