Effects of acid,acid-ZVI/PMS,Fe(Ⅱ)/PMS and ZVI/PMS conditioning on the wastewater activated sludge(WAS)dewaterability and extracellular polymeric substances(EPS)

The effects of four conditioning approaches:Acid,Acid-zero-valent iron(ZVI)/peroxydisulfate(PMS),Fe(Ⅱ)/PMS and ZVI/PMS,on wastewater activated sludge(WAS) dewatering and organics distribution in supernatant and extracellular polymeric substances(EPS) layers were investigated.The highest reduction in bound water and the most WAS destruction was achieved by Acid-ZVI/PMS,and the optimum conditions were pH 3,ZVI dosage 0.15 g/g dry solid(DS),oxone dosage 0.07 g/g DS and reaction time 10.6 min with the reductions in capillary suction time(CST) and water content(Wc) as 19.67% and 8.49%,respectively.Four conditioning approaches could result in TOC increase in EPS layers and supernatant,and protein(PN) content in tightly bound EPS(TB-EPS).After conditioning,organics in EPS layers could migrate to supernatant.Polysaccharide(PS) was easier to migrate to supernatant than PN.In addition,Acid,Acid-ZVI/PMS or Fe(Ⅱ)/PMS conditioning promoted the release of some polysaccharides containing ring vibrations v P=O,v C-O-C,v C-O-P functional groups from TB-EPS.ESR spectra proved that both radicals of SO_4~-· and·OH contributed to dewatering and organics transformation and migration.CST value of WAS positively correlated with the ratios of PN/PS in LB-EPS and total EPS,while it negatively correlated with TOC,PN content and PS content in TB-EPS,as well as PS content in supernatant and LB-EPS.BWC negatively correlated to zeta potential and TOC value,PN content,and HA content in supernatant.     

碱性环境中臭氧破解污泥的效果研究

实验研究发现,在碱性环境中臭氧破解污泥的效果下降;将污泥pH调至11,24 h后,MLSS减少率=38.3%、MLVSS减少率=45.1%;通入臭氧18 min后,MLSS减少率=18.3%、MLVSS减少率=27.2%;污泥减量过程中pH呈下降趋势.     

脉冲电晕放电治疗有机废气的研究—放电反应器结构

对脉冲电晕法治理甲苯有机废气进行了实验，考察了放电反应器结构及参数对其性能的影响。结果表明，对线－筒式反应器，当直径较小时，去除率较高，但易发生火花放电，实验条件下直径２０ｍｍ的反应器效果较好。若采用陶瓷管反应器，其效果较金属管明显提高，脉冲峰值电压Ｖｐ为４２ｋＶ时，可使甲苯的去除率由４０％提高到６１％左右。对线－板式反应器，放电间隙越大，甲苯的去除率越低，使用陶瓷板反应器可使甲苯去除率明显提高，     

PW—W膜分离式活性污泥法处理中小规模高浓度有机废水

阐述ＰＷ－Ｗ膜分离式活性污泥法处理高浓度有机废水的原理、工艺流程及特点。处理系统集生化处理功能和固液分离于一体，对高浓度有机废水的处理取得了良好的效果，且剩余污泥量少，处理水质稳定，维护管理方便，运行费用低。     

超声波处理石化厂剩余活性污泥

采用超声波处理石化污水处理厂的剩余活性污泥。介绍了超声波对污泥的作用机理，初步研究了超声波处理污泥的影响因素。大功率超声波可以降解生物污泥，释放出其中的有机物。小功率超声波能够改善污泥的膨胀特性、提高污泥沉淀特性和脱水能力、降低污泥的含水率，达到减量的目的。经超声波处理并简单过滤的污泥滤液，COD达到4200mg／L左右，污泥含水率由94％降至85％左右。     

城市污水污泥堆肥化技术的研究进展

本文介绍了堆肥化技术发展的历史，以及国内外污泥堆肥化技术的研究进展，并介绍了国内的生产实例，可供大家初步了解污泥堆肥化技术。     

气浮--厌氧--生物接触氧化工艺处理屠宰废水

介绍了采用气浮-厌氧-生物接触氧化工艺处理屠宰废水的工程实例。当进水CODcr≤4500mg／L时，出水可达到国家《肉类加工工业污染物排放标准》(GB13457—1992)一级标准。     

序批式活性污泥法在炼油化工废水处理中的应用

炼油化工废水处理的传统处理工艺中存在一定的弊端。为此,玉门炼油化工总厂对其废水处理设施进行了改建和扩建,其生物处理系统采用了序批式活性污泥法处理工艺。经过 3年运行的结果表明:该系统运行效果良好,处理后的水质可达到《GB8978-1996》(石化)一级排放标准的要求;化学需氧量(COD)和生化需氧量(BOD)分别降低78.6%和91.2%,硫化物去除率为98.2%,挥发酚去除率为99.6%。而且该反应器具有较强的耐冲击负荷能力,进水中COD在600 mg/L以下且有大幅度波动时,该系统仍可稳定地运行,处理后的水可达标排放。     

Possible Utilization of Silica Gel Sludge for the Removal of Phenol from Aqueous Solutions: Laboratory Studies

This paper discusses the adsorption capacity of silica gel sludge for phenol removal from aqueous solution. Kinetic experiments showed that phenol adsorption was completed after 2 h. Adsorption isotherms were measured for phenol from aqueous solution onto silica gel sludge under various pHs and temperatures. Results showed that the adsorption capacities for phenol was increased as pH decreased from 6.5 to 2. Temperature also was found to affect the adsorption isotherm. As temperature increases from 30 to 50°C, the adsorption capacity increases. The adsorption equilibrium of phenol on silica gel sludge was described by the linear Freundlich and Langmuir models. Furthermore, results showed that the isotherm parameters fit both linearized Langmuir and Freundlich adsorption isotherms. The Freundlich and Langmuir parameters at optimum pH was found as K _f=2.89, 1/n=0.23 and K _d=22.0, q _m=7.98, respectively. Whereas, for those at optimum temperature it was observed as K _f=2.87, 1/n=0.16 and K _d=20.93, q _m=7.91, respectively.     

化学活化法制取污泥衍生吸附剂的实验研究

用有机污泥按照一定的工艺制作污泥衍生吸附剂。结果表明，氯化锌作为化学活化剂在吸附剂的生成过程中起到了关键作用，热解温度是影响吸附剂性能的最主要因素，750℃是最佳热解温度。