Quinone-mediated decolorization of sulfonated azo dyes by cells and cell extracts from Sphingomonas xenophaga

The effects of various quinone compounds on the decolorization rates of sulfonated azo dyes by Sphingomonas xenophaga QYY were investigated. The results showed that anthraquinone-2-sulfonate (AQS) was the most effective redox mediator and AQS reduction was the rate-limited step of AQS-mediated decolorization of sulfonated azo dyes. Based on AQS biological toxicity tests, it was assumed that AQS might enter the cells to kill them. In the cytoplasmic extracts from strain QYY, AQS effectively increased decolorization rates of sulfonated azo dyes than other quinone compounds. In addition, we found a NADH/FMN-dependent AQS reductase using nondenaturing polyacrylamide gel electrophoresis (Native-PAGE).     

Effectiveness of fluidized pellet bed for removing soluble contaminants

Fluidized pellet bed (FPB) has been successfully applied in water and wastewater treatment. However, the removal mechanism of contaminants especially the soluble ones, is still unclear. This study aimed to evaluate the e ectiveness of FPB reactor for removing soluble contaminants from synthetic wastewater. By only coagulation through jar test operation with addition of polyaluminium chloride (PACl) as primary coagulant and polyacryamide (PAM) as coagulant-aid, the removals of soluble chemical oxygen demand (COD), total phosphorus (TP), and NH4 +-N were found to be only 2.2%–7.5%, 5.7%–25.5%, and 9.9%–18.5%, respectively. However, by FPB operation under the same dosage of coagulants, these values increased to 82.7%, 37.2%, and 50%, indicating that the formation of pellets in the FPB e ectively enhanced the removal of soluble contaminants. By careful comparison of the settleablility and filterability of the pollutants after coagulation, the originally soluble contaminants could be divided into three groups, namely: (1) coagulated-andsettleable, (2) coagulated-but-nonsettleable, and (3) uncoagulable. It was found that not only the first two groups but also a large part of the third group could be e ectively removed by FPB operation. However, the mechanism for the removal of the uncoagulable pollutants by FPB operation still needs further investigation.     

包埋类脂的吸附剂制备及吸附POPs性能

用丙酮作溶剂将三油酸甘油酯分散到醋酸纤维(CA)基体中,采用悬浮聚合的方法制备出了一种兼具亲水性,又能高倍富集持久性有机污染物的球形复合吸附剂。通过对分散剂的种类及其用量、悬浮介质的种类及其用量的研究,获得了球形复合吸附剂的最佳合成路线与工艺.球形吸附剂粒径为1～2mm。通过荧光分析和电镜扫描分析,表明三油酸甘油酯已被包埋到醋酸纤维基体中,并得到了均匀分散。采用七氯、狄氏剂、异狄氏剂、灭蚁灵为代表性的持久性有机污染物(POPs)。动力学吸附实验表明,当初始浓度为1μg/L时,在快速吸附阶段,溶液中80%的氯、狄氏剂、异狄氏剂可得到有效去除,但并没有达到吸附平衡。快速吸附完后,还在持续地进行慢速吸附。而对于灭蚁灵,吸附速度远远低于其他几种POPs。实验证明了吸附速度不仅与辛醇/水系数有关,而且还与有机污染物的分子结构有关。     

对修订后《水污染防治法》第七十三、七十四条如何执行的疑惑与思考

本文主要介绍了在执行新修订的《水污染防治法》中遇到的一些疑惑,并对如何更好地执行提出了几点建议。     

可生物降解材料聚羟基脂肪酸酯（PHA）的合成与应用概述

聚羟基脂肪酸酯（polyhydroxyalkanoates,PHA）是很多微生物合成的一种细胞内聚酯,是一种天然的高分子生物材料。PHA具有良好的生物相容性能、生物可降解性和塑料的热加工等性能。文章主要综述了PHA的合成途径与有关应用方面的研究。     

聚丙烯酰胺与聚合氯化铝联合投加净化微污染水源水的试验研究

强化混凝是去除水中消毒副产物的最佳方法之一。文章针对强化混凝技术,从净化微污染水源水的角度出发,通过混凝搅拌试验,评价了联合投加聚丙烯酰胺与聚合氯化铝对原水中有机物的去除效果,考察了混凝剂投加量、投加方式等对去除效果的影响。结果表明,联合投加助凝剂和混凝剂有利于水中CODMn及浊度的去除,且可以节省药剂用量,具有进一步试验和推广的价值。     

静脉产业类生态工业园区的建设方法分析

静脉产业类生态工业园区运用先进的技术,将生产和消费过程中产生的废物资源化,是中国循环经济建设的重点领域之一。但是中国现有的静脉产业类生态工业园区尚处于创建阶段,没有形成规模化发展,因此可以在建设过程中借鉴日本、德国等发达国家的成功经验,探索适合中国国情的建设模式。本文通过分析静脉产业类生态工业因区在生产原料、生产过程和产品销售方面的主要影响因素以及其他国家采取的相应措施,为中国静脉产业类生态工业园区的建设提出建议。     

地震灾后重建中的多元化资金支持研究

本文以汶川地震为背景,针对灾后重建资金需求量大、持续时间长的特点,提出灾后重建资金来源应以财政资金为引导,走多元化的道路;并分别从财政资金支持、信贷资金支持、社会资金支持、国外资金支持、保险资金支持、证券市场资金支持的角度进行分析,提出了在财政资金引导下,切实可行的多元化资金支持建议.     

反硝化聚磷SBR与微动力曝气组合技术处理猪场废水的研究

在实验室模拟条件下,以猪场废水(粪尿及冲洗水等混合废水)为例,研究传统SBR(A/O模式)与反硝化聚磷(DNPAO)SBR在脱氮除磷及有机质降解方面的可行性及其功效.结果发现,采用传统SBR工艺直接处理猪场废水,其处理系统效率较低,处理效果不稳定,出水水质不佳,废水处理后出水TN、TP和BOD5的去除率分别为89.08%、86.04%和93.88%.而改用反硝化聚磷SBR,同时配以微动力曝气法,采用废水输入两步法与双循环"厌氧-缺氧/微氧"运行模式,可实现猪场废水TN、TP和BOD5去除率分别高达93.95%、99.26%和99.93%.由于其独特的工艺设计可使处理水NO-3浓度和输出负荷"双低".同时ORP、pH与DO 3项关键参数的动态变化可以间接地揭示微动力曝气SBR技术运行状态及出水水质,但在实际条件下的中试运行成效有待于进一步研究.     

EDTA催化Fe3+/H2O2降解水中孔雀石绿

以孔雀石绿(malachite green, MG)为目标物,在pH=7的中性条件下,考察EDTA对Fe3 /H2O2降解水中孔雀石绿的影响,发现EDTA很大程度地促进了Fe3 /H2O2对孔雀石绿的降解. EDRA的加入可以使MG的脱色率由43%升至98.3%.在本实验条件下, EDTA的投加量增加5倍时, MG的脱色率上升40%.随着H2O2投量的增加, MG的脱色率显著上升.随着温度的升高, MG的脱色率显著上升.叔丁醇的加入抑制了EDTA对Fe3 /H2O2降解孔雀石绿的催化效果.总量相同H2O2的多次投加并未获得明显优于一次投加的去除效果. EDTA催化Fe3 /H2O2降解水中孔雀石绿并不遵循简单的羟基自由基机理,同时存在的中间价态铁的物种起着主要的氧化作用.随着反应的进行, EDTA被部分降解.