混凝模拟搅拌杯的设计

根据相似理论,结合水处理实际混凝工艺条件,设计出了1L方形模拟搅拌杯,并进行了初步试验分析,取得了满意结果。     

微污染水源水脱氮的强化混凝工艺

通过对机械搅拌桨桨板结构优化改造,实现在絮凝池内同步进行强化混凝及生物脱氮反应,分析桨板长度梯度、板间间距及其与固定挡板间夹角对絮凝池内溶解氧浓度梯度产生影响,设计出了一种搅拌时池内可以形成厌氧-缺氧-好氧环境的新型机械搅拌桨,Fluent流场分析进一步验证了池内横向、纵向都会产生溶解氧浓度梯度。新型搅拌桨与传统搅拌桨生物脱氮对比实验表明,当采用新型搅拌桨时,絮凝池对NH_4~+-N、TN去除效果远优于传统搅拌桨。进一步进行模拟微污染水源水的强化混凝生物脱氮应用实验,出水浊度为0.47 NTU,COD、NH_4~+-N和TN的浓度分别为10.54、5.01和5.84 mg·L~(-1),表现出良好的处理效果。对污泥粒径的研究表明,PAC投加可有效改善污泥絮体结构,为微污染水源水的处理提供了新思路。     

絮体性状实时图像检测系统的开发与应用

概述了水处理絮体性状(包括絮体粒度、分形维数及表观强度)在线图像检测系统的开发,结合实验室条件下的混凝实验考查了该实时图像检测系统的应用情况.结果表明,利用该图像检测系统获取的数据符合一般混凝实验的结果,且对混凝慢速搅拌时间、原水浊度及混凝剂投加量有不同程度的敏感性.在进一步研究的基础上,该图像检测系统可在水处理混凝过程的自动控制中加以应用.     

混凝沉淀去除丙烯酸丁酯废水浊度物质

采用混凝沉淀法去除丙烯酸丁酯废水中的浊度物质,比较6种混凝剂的去除效率,确定聚合氯化铝为适宜混凝剂,并选用阳离子型聚丙烯酰胺作为助凝剂。研究结果表明,聚合氯化铝和阳离子型聚丙烯酰胺的优化投加量分别为150 mg/L和20 mg/L,优化pH值为4～5,水温20～40℃,快速搅拌速度200～400 r/min,搅拌时间1～3 min,慢速搅拌速度50～80 r/min,搅拌时间5～15 min。在以上条件下,可使出水浊度从3 000 NTU左右降至1 NTU左右,同时也实现了废水中胶体物质的大量去除。     

钱江隧道盾构废弃泥浆的混凝分离

为了实现钱江隧道盾构废弃泥浆的无害化处理,对盾构废弃的砂土泥浆和粘土泥浆分别进行混凝分离的实验条件研究,结果表明:对于砂土泥浆,密度为1.20 g/cm3有利于实现高效的泥水分离;PAM作为絮凝剂的分离效果最好;混凝分离的最优化分离条件为:投药量为150 mg/L,pH为8左右,水力条件为以300 r/min搅拌1 min,再以80 r/min搅拌20 min。对于粘土泥浆,密度为1.10 g/cm3有利于实现高效的泥水分离;PAM作为絮凝剂的分离效果最好;混凝分离的最优化分离条件为:投药量为150 mg/L,pH为6左右,水力条件为以300 r/min搅拌1 min,再以80 r/min搅拌20 min。该实验为废弃泥浆的进一步处理奠定了基础。     

铁氧体强化低温低浊水的处理效果

在低温低浊水(T<10℃,浊度<40 NTU)处理中,采用常规处理流程难以达到理想效果。实验采用铁氧体(Fe3O4)配合聚合氯化铝(PAC)进行低温低浊水的实验研究。通过混凝沉淀烧杯实验,比较两者投加量对其处理效果的影响,实验结果表明PAC为30 mg/L,Fe3O4为0.004 mg时为最佳投药量。采用混凝沉淀过滤的常规处理工艺,并保证适当的混凝搅拌强度。     

城市污水纳米材料混凝强化一级处理研究

对nano-SiO2与PAC复配使用强化混凝处理城市污水进行了实验研究。探讨了nano-SiO2在水中的分散效果、nano-SiO2强化混凝的工艺条件及强化效果。实验表明，与常规PAC强化混凝相比，nano-SiO2强化混凝能有效提高城市污水的除污效果、改善矾花沉降性能、缩短沉淀时间、提高城市污水化学絮凝强化一级处理工艺的抗冲击能力。同时投加nano-SiO2（25mg／L）与PAC（75mg／L）后，先快速搅拌（250r／min）2min，然后慢速搅拌（60r／mln）8min，再沉淀3min，出水COD、TP及浊度去除率分别为50．47％、79．84％和90．93％，较单独投加PAC（75mg／L）分别提高28．43％、39．94％和62．18％。     

应用加载磁混凝处理微污染河水

实验对比考察了常规混凝和加载磁混凝工艺对微污染河水中COD、浊度和TP等污染物的去除效果,系统研究了混凝剂用量、磁种加载量、搅拌条件和药剂投加顺序等因素对加载磁混凝效果的影响。实验结果表明,加载磁种后沉淀颗粒的体积平均粒径为从常规混凝工艺的50.1μm显著增加到68.6μm;污染物去除效果明显优于常规混凝工艺,尤其对浊度和总磷的去除效果得到了显著的提升;在实验最优条件下COD、浊度和TP的去除率分别达到54.17%、99.28%和75.82%;并且加载磁种后可减少50%以上的混凝剂投加量,同时大大缩短沉淀时间。     

城市污水纳米材料混凝强化一级处理研究

对nano-SiO2与PAC复配使用强化混凝处理城市污水进行了实验研究.探讨了nano-SiO2在水中的分散效果、nano-SiO2强化混凝的工艺条件及强化效果.实验表明,与常规PAC强化混凝相比,nano-SiO2强化混凝能有效提高城市污水的除污效果、改善矾花沉降性能、缩短沉淀时间、提高城市污水化学絮凝强化一级处理工艺的抗冲击能力.同时投加nanoSiO2(25 mg/L)与PAC(75 mg/L)后,先快速搅拌(250r/min)2 min,然后慢速搅拌(60r/min)8 min,再沉淀3 min,出水COD、TP及浊度去除率分别为50.47%、79.84%和90.93%,较单独投加PAC(75 mg/L)分别提高28.43%、39.94%和62.18%.     

激光光散射在混凝研究中的应用评述

混凝研究的理论与实践近三十年来得到长足的发展，很大的原因在于现代检测技术与手段的大力运用，激光光散射为其中得力的方法之一。本文对其基本操作原理作了简要介绍，并对测定过程中存在的若干问题作了探讨。然后就其在混凝领域中诸层次的研究现状与发展趋势进行了若干概括。本文试图阐明其应用于混凝领域的研究所具有的巨大潜力及困难与局限所在，以期将来更大的进展     

Identification and characterization of coagulation inhibitor proteins derived from cyanobacterium Microcystis aeruginosa

The excess growth of cyanobacteria in semi enclosed water areas caused by eutrophication brings about coagulation inhibition in drinking water treatment processes. In this study, coagulation inhibitor proteins produced by Microcystis aeruginosa, a major cyanobacterium in algal bloom, were acquired by a phage display technique, an aluminum-immobilized affinity chromatography and a protein expression technique using Escherichia coli cells. Two cyanobacterial peptides with a high ratio of metallophilic amino acids were recovered, which were a part of homologues of a thiol oxidase enzyme Ero1p and a trans-acting repressor ArsR. It was also shown that the homologue of ArsR exhibited a stronger inhibitory effect on the coagulation of kaolin suspension with polyaluminum chloride than the control proteins. This is the first report to identify a cyanobacterial cell component to inhibit coagulation. The compositions of polar amino acids were critical to explain the strength of coagulation inhibition potential. Polar proteins from cyanobacteria could collectively consume coagulants or stabilize clay particles, which would be plausible explanations for causing coagulation inhibition. Meanwhile, results from the kaolin coagulation tests using the control proteins implied that the neutralization of positive charges of coagulant constituents by simple electrostatic interactions might not be the key mechanism on the protein-induced coagulation inhibition.     

不同工艺对含高浓度腐殖酸地下水处理的可行性

针对内蒙古农村地区高腐殖酸地下水的处理问题,分别对（pH调节）-PAC强化混凝、高锰酸钾预氧化／混凝、活性炭吸附／混凝、Fenton氧化等技术处理的可行性进行了研究,同时利用三维荧光和高效体积排阻色谱分析处理前后水中有机物的组成变化特征。有机分析结果显示,水中的有机物为腐殖酸类物质,分子量分别为1600和3500,腐殖酸类物质为水中色度的主要贡献者。原水PAC强化混凝、高锰酸钾预氧化／PAC混凝对有机物的去除效果不佳,处理前后水样DOC浓度无明显变化,而pH调节．PAC强化混凝、微米活性炭吸附和Fenton氧化均能有效去除有机物。将原水pH调节至6．5,经300mg／LPAC混凝后出水DOC降至5．99mg／L。活性炭投加量为0．6g／L时,DOC降至7．6mg／L,然后采用60mg／LPAC混凝出去高度分散而不易沉降的小颗粒活性炭。此外,当反应初始pH值为3,过氧化氢投加量为0．5％（v／v）,亚铁和双氧水摩尔比为0．05时,出水DOC降至5．6mg／L,氧化后有小分子有机物生成。     

不同来源高浓度有机废水的集中处理

按照水质情况,将多种来源于不同工业生产过程中的高浓度有机废水划分为高悬浮固体乳化液废水、难生化高浓度有机废水、高悬浮固体不含油有机废水、含铬有机废水和杂质含量较少的乳化液废水5类,分别采用酸化破乳/Fen-ton氧化/混凝/絮凝、Fenton氧化/混凝/絮凝、混凝/絮凝、还原/混凝/絮凝、震动膜过滤技术作为生化预处理技术,并通过小试和中试验证了各技术的效果。实验结果表明,按照上述分类结果,采用不同预处理技术可以得到良好的效果,废水水质明显改善,满足继续生化处理的基本条件。各预处理生产装置处理效果稳定,同时生化系统已经稳定运行120天以上,COD去除率超过90%,出水经过低剂量的Fenton试剂处理后可达到《污水排入城镇下水道水质标准》(CJ343-2012)。     

氯化镁复配硫酸铝混凝性能及絮体特性

在研究氢氧化镁混凝特性的基础上,复配氯化镁和硫酸铝作为混凝剂,以高岭土配水水样为研究对象,运用iPDA在线监测技术对混凝过程絮体形成进行监测,探讨了单独使用氯化镁和硫酸铝以及二者复配使用的混凝效果和絮体特性,确定复配使用的各种条件。结果表明,对于浊度20 NTU,pH 11.5的高岭土配水水样,氯化镁、硫酸铝最佳投加量分别为7.2 mg/L(Mg2+计)和3 mg/L(Al3+计);硫酸铝跟氯化镁复配使用时,先投加硫酸铝,间隔30 s后投加氯化镁,混凝效果较好;在镁离子最佳投加量7.2 mg/L时,铝和镁最佳质量比在1∶3~1∶2之间;镁铝复配时其FI值明显大于单独作用时,即絮体尺寸大小:二者复配硫酸铝氯化镁,而且复配条件下Zeta电位值在零电势左右浮动,浮动范围小,更利于聚集沉淀;镁铝复配时发生了协同效应,弥补了单独使用氯化镁混凝过程的不足。     

聚合氯化铝混凝强化新生态铁锰复合氧化物吸附去除水中的磷

采用氧化-共沉淀法制备出新生态铁锰复合氧化物(FMBO),研究了单独投加FMBO和聚合氯化铝(PACl)强化FMBO吸附除磷效能及吸附磷后的颗粒物特性。结果表明,单独投加FMBO后形成的颗粒物表面带负电荷,颗粒物聚集和沉淀性能较差。PACl的投加降低了颗粒物的表面电荷,促进了颗粒物的聚集,平均粒径明显增加,改善了颗粒物的沉淀性能;通过SEM-EDAX发现,投加PACl形成的复合颗粒物表面更为粗糙,Al元素在复合颗粒物表面相对富集。PACl的投加强化了FMBO的吸附除磷效果,在实验原水条件下FMBO和PACl最佳投量分别为12和30 mg/L,此时TDP去除率高达95.6%。并且出水中Fe、Mn、Al浓度均远低于《地表水环境质量标准》中规定的限值。PACl强化新生态FMBO易于实现原位投加,在水体和水处理除磷工艺中具有较好的应用潜力。     

Appropriate combination of physico-chemical methods (coagulation/flocculation and ozonation) for the efficient treatment of landfill leachates

An integrated technique consisted of ozonation and coagulation/flocculation processes was studied, aiming to provide an efficient method for the treatment of stabilized/biologically pre-treated leachates, in order to reduce the organic pollutants' content to concentration values lower than the corresponding limits, imposed by the legislation. Leachates were collected from a municipal landfill site; samples containing around 1000 mg l(-1) COD and BOD(5)/COD ratio about 0.17 were treated by using two different processes or combinations between them, i.e. ozonation, coagulation-flocculation, ozonation followed by coagulation/flocculation and coagulation/flocculation followed by ozonation. The application of single ozonation resulted to the efficient removal of color and organic loading, due to the respective oxidation, induced by ozonation; however, COD values lower than 200 mg l(-1) could be only achieved after prolonged reaction times and for high ozone production rates. The coagulation of leachate samples was studied by the addition of ferric chloride or poly-aluminum chloride agents at various dosages. Maximum COD removal rates (up to 72%) were achieved by the addition of 7 mM Fe, or of 11 mM Al respectively. However, final COD values higher than 200 mg l(-1) were obtained indicating the requirement of an additional treatment step. Pre-ozonation followed by coagulation/flocculation was not found to be an efficient treatment approach for this aim, but coagulation/flocculation followed by ozonation, was proved to be an efficient process for the reduction of COD to lower than 180 mg l(-1).     

Evaluation of Al30 polynuclear species in polyaluminum solutions as coagulant for water treatment

Polyaluminum coagulant with a content of 76.8% of Al30 (PACAl30) was prepared. Its coagulation behaviors were compared with high Al13 content polyaluminum coagulant (PACAl13) and AlCl3. The species stability was studied using Al-Ferron method and 27Al NMR. The coagulation performances were investigated by studying the rate of flocs development, the turbidity removal efficiency and charge neutralization capacity under fixed pH conditions and uncontrolled pH conditions. The effect of pH on coagulation was also studied. The results show that PACAl30 are stable for using as coagulant. PACAl30 causes less pH depression than PACAl13. The charge neutralization capacity of PACAl30 is slightly lower than that of PACAl13 at pH6.8 and higher at pH 6.5. PACAl30 achieves the most effective turbidity removal in these three coagulants. And it acts effectively within a much broader dosage range and a wider pH range when compared with PACAl13. PACAl30 achieves the highest turbidity removal due to its strong flocs formation capacity. The results verify that Al30 is another highly active coagulation/flocculation species for turbidity removal.     

Use of chemical coagulants to control fouling potential for wastewater membrane bioreactor processes.

Chemical coagulation with ferric chloride, alum, and an organic polymer were used to control the fouling potential of mixed liquors for submerged membrane bioreactor (MBR) processes in treating municipal wastewater. Their filterability was evaluated using a submerged hollow fiber ultrafiltration apparatus operated in constant permeate flux mode. The collected transmembrane pressures over filtration time were used to calculate the membrane fouling rates. The results showed that coagulation pretreatment can reduce fouling rates when MBRs were operated above the critical flux. Even though coagulation with the organic polymer formed larger mixed liquor suspended solids particles and had shorter time-to-filtration than those with ferric chloride and alum, the filterability for membrane filtration were similar, indicating that the membrane fouling in MBR systems was mainly controlled by the concentration of smaller colloidal particles.     

加药量和水力搅拌速度对雨水混凝效果的影响

为降低分流制雨水中悬浮颗粒物及其他污染物浓度,减轻城市景观河道的水体富营养化程度,对取自泵站的雨水进行混凝沉淀工艺优化实验。以PAC为混凝剂,采用Zeta电位仪、激光粒度仪和iPDA在线监测技术对混凝过程进行监测,考察了混凝剂投加量和水力搅拌速度对絮体形成和分流制雨水处理效果的影响,结果表明,混凝剂投加量和混合水力搅拌速度直接影响絮体Zeta电位和聚沉特性;混合搅拌速度控制混凝反应速率,絮凝速度梯度影响絮体形成粒径。FI曲线特征参数对控制混凝工艺具有指导意义。PAC投加量为35 mg/L,混合阶段搅拌速度800 r/min,搅拌30 s,絮凝阶段采用150、108和60 r/min的转速各自搅拌5 min,沉后水中剩余颗粒总数最少,浊度、COD和总磷去除效果最佳。     

磁混凝在水与废水处理领域的应用

磁技术作为一种高效的分离、净化方法在水与废水处理领域的作用和地位日益凸显,磁性接种、磁性吸附等水处理方法已受到了广泛关注;高场强、低能耗的磁分离器的相继问世和不断完善为高效稳定地进行磁分离提供了必要条件。基于上述考虑,将传统的混凝过程与磁技术有机结合而产生的磁混凝工艺将成为混凝发展的新方向之一。本文系统综述了磁混凝在水处理中的研究和应用,从颗粒物在磁场和重力场中的界面过程、相互作用机制,磁混凝在国内外的研究现状,以及磁分离器的研究进展等角度展开讨论,探讨了该技术面临的问题,并展望了其发展前景。