双极性膜电渗析法在脱硫废液NaHSO3再生过程中的应用研究

介绍了用双极性膜电渗析法对烟气脱硫废液（ＮａＨＳＯ３）进行再生的方法,使用自制均相双极膜和上海产异相双极性膜,配以均阳相离子交换膜,均能以满意的转化率（８０％以上）实现再生,再行过程中电流效率的下降（由８０％左右下降到２０％左右）是由于酸室中氢离子浓度升高所致,脱硫废液中少量到钠的存在对再生过程无明显影响,目前障碍该法实际应用主要的问题是国内试制厝的寿命较短。     

胞外聚合物对MBR中改性无纺布过滤性能的影响

采用统计分析方法研究了胞外聚合物(extra-cellular polymeric sub6tances, EPS)对浸渍式膜生物反应器(submerged membrane bioreactor, SMBR)中聚乙烯醇改性聚丙烯无纺布过滤性能的影响.结果表明,无纺布膜组件表面污泥的溶解性EPS(soluble EPS, EPSs)、EPSs,组成(protein/carbohydrate, P/C)以及相对疏水性(relative hydrophobicity, RH)对膜的过滤性能有显著影响,与膜污染阻力的皮尔逊相关系数(rp)分别为:0.868、0.840、0.890;改性无纺布膜组件能有效抑制EPSs,的吸附、降低EPSs组分中P/C的比率、减少活性污泥的沉积.表明聚丙烯无纺布通过亲水改性后,过滤性能得到明显改善,表现出一定的耐污染性.     

生物除锰技术研究进展与应用

文章简要阐述了生物除锰的机理,重点介绍生物除锰的工艺流程和应用,包括以生物滤池为核心的单极/多级工艺、复合MF/UF中空纤维膜工艺以及用于处理矿山废水的人工湿地工艺;同时介绍了国内外生物除锰的研究动态,如:同时去除NH4+、Fe、Mn的研究、生物滤池运行模式的研究等。分析了目前存在的问题,并对今后生物除锰的研究方向提出了一点看法。     

粉末活性炭预处理对超滤膜通量的影响

研究了粉末活性炭预处理对改善超滤膜过滤通量的效果.试验采用了4种具有不同亲疏水性的水样,着重探讨粉末活性炭对有机物的疏水性和亲水性组分的去除效果以及所带来的通量改善.试验结果表明,对于4种水样,超滤膜直接过滤原水时,通量下降严重.虽然粉末活性炭预处理能在一定程度上提高通量,但通量下降的趋势仍未改善.对有机物各组分的分析表明,直接过滤原水时,膜主要截留疏水性有机物;粉末炭吸附主要去除亲水性有机物,而超滤膜过滤粉末炭处理水时,主要截留疏水性有机物.由此,超滤膜的通量下降主要是由疏水性有机物引起的,亲水性组分对通量的影响较小.     

Enhanced atrazine removal using membrane bioreactor bioaugmented with genetically engineered microorganism

Bioaugmentation with genetically engineered microorganisms (GEMs) in a membrane bioreactor (MBR) for enhanced removal of recalcitrant pollutants was explored. An atrazine-degrading genetically engineered microorganism (GEM) with green fluorescent protein was inoculated into an MBR and the effects of such a bioaugmentation strategy on atrazine removal were investigated. The results show that atrazine removal was improved greatly in the bioaugmented MBR compared with a control system. After a start-up period of 6 days, average 94.7% of atrazine was removed in bioaugmented MBR when atrazine concentration of influent was 14.5 mg/L. The volumetric removal rates increased linearly followed by atrazine loading increase and the maximum was 65.5 mg/(L·d). No negative effects were found on COD removal although carbon oxidation activity of bioaugmented sludge was lower than that of common sludge. After inoculation, adsorption to sludge flocs was favorable for GEM survival. The GEM population size initially decreased shortly and then was kept constant at about 10⁴–10⁵ CFU/mL. Predation of micro-organisms played an important role in the decay of the GEM population. GEM leakage from MBR was less than 10² CFU/mL initially and was then undetectable. In contrast, in a conventionally activated sludge bioreactor (CAS), sludge bulking occurred possibly due to atrazine exposure, resulting in bioaugmentation failure and serious GEM leakage. So MBR was superior to CAS in atrazine bioaugmentation treatment using GEM.     

好氧颗粒污泥膜生物反应器的研究进展

综述了好氧颗粒污泥膜生物反应器(MBR)在废水生物处理中的研究进展,着重介绍了MBR中好氧颗粒污泥的特性、好氧颗粒污泥对氨氮的去除特性及其对膜污染控制的特性,并在此基础上展望了好氧颗粒污泥MBR技术的发展方向。     

UF膜与混凝粉末活性炭联用处理微污染原水

采用混凝、粉末活性炭和UF膜分离的联用技术对黄浦江原水进行试验 ,结果表明 ,混凝、粉末活性炭可有效地去除溶解性有机物 .混凝处理主要去除大分子量的有机物 ,粉末活性炭主要去除低分子量的有机物 .混凝、粉末活性炭还能有效地去除三氯甲烷生成潜能 (THMFP) ,对于低分子量的THMFP ,混凝去除效果很差 ,而粉末活性炭去除很好 .试验还表明 ,混凝、粉末活性炭还可大大降低膜的滤饼层阻力 ,当混凝剂投加量为 4mg/L时 ,膜的滤饼层阻力最小 .     

膜萃取处理水溶液中镉、锌离子的工艺

以P204+正庚烷为萃取剂,将中空纤维膜萃取技术用于处理水溶液中镉离子、锌离子.研究了两相流速、初始浓度及溶液pH等因素对传质系数和萃取率的影响,计算了膜萃取器的传质单元高度(HTU)_w,同时还研究了萃取剂的再生问题.实验结果表明,在低浓度下(＜500 mg/L),平衡分配系数较大,传质阻力主要是在水相;在初始浓度较高时(＜2000mg/L),由于分配系数较小,三项传质阻力均不可忽略;在初始浓度很高时(＞2000mg/L),传质由有机相和膜相阻力控制.实验还表明通过膜器串联可以实现萃取剂的再生.对于稀溶液(＜200mg/L),中空纤维膜萃取可以使水溶液中金属离子浓度减小2个数量级,通过计算,中空纤维膜萃取器(HTU)_w在15～30cm之间,大大低于传统的萃取塔.     

醋酸纤维素小孔径超滤膜的研究

用醋酸纤维素(CA)为聚合物材料,研制出了截留分子量2000—10000、对PEG截留率为90％以上的小孔径超滤膜.并就铸膜液组成,制膜条件及膜的透过特性等进行了实验.     

Determination of organophosphorus pesticides and related compounds in water samples by membrane extraction and gas chromatography

A membrane extraction-gas chromatography method was developed fordetermination of organophosphorus pesticides and related compounds including methamidophos, DDVP, dimethoate, methyl parathion, parathion, thiophosphoric acid trimethyl ester, and thiophosphoramidic acid dimethyl ester in water samples. In thismethod, surface-modified acetic cellulose membranes were used to extract the target analytes in water samples, the extracted analytes were back-extracted into a small amount of methanol, andgas chromatography with pulsed flame photometric detector (GC-PFPD) was used to determine the concentrations of targetanalytes in the extracts. The recoveries obtained for thetarget analytes spiked into the water samples ranged from 66to 94%. The method detection limit for each target analyte was 0.05 g L^-1. The method developed in this study had shown the advantages of being cheap, simple, fast, and reliable. It had been used successfully to determine the concentrations of target analytes in river water samples.