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361.
采用普通小球藻(C.vulgaris)作为实验藻种,搭建缺氧MBR-微藻膜反应器(缺氧MBR-MMR)耦合系统处理海水养殖废水,前置缺氧MBR用于有机物、NO-3-N和NO-2-N的降解,释放的NH+4-N进入MMR用于微藻生长而得到去除,考察协同处理效能和微藻采收情况,探究膜污染行为.反应系统共运行91 d,对NO-3-N和NH+4-N的去除率分别达到90.0%和88.0%以上,对PO3-4-P和TOC的平均去除率分别为49.4%和84.7%.普通小球藻在进行连续采收的情况下,能以平均浓度为9×107个·mL-1的生物量稳定运行,实现了较好的去除效能和资源化利用.通过红外光谱和三维荧光光谱分析,MMR内造成膜污染的主要物质是色氨酸类蛋白质和腐殖酸类物质,与缺氧MBR内膜组件相比污染...  相似文献   
362.
采用空气隙膜蒸馏组件,采用美国进口膜,以自来水、伞盖3号原水和苦咸水为工质,实验分析了膜污染情况,结果显示:料液无旋转时,自来水间歇累计运行32 h后出现污染;质量分数分别为20%和50%的盐水8 h后传质通量降低到最初通量32%和12%;3号原水瞬时产生污染,经砂滤处理后为苦咸水,传质通量比原水提高4倍~5倍,运行8h后通量下降到初始通量的6%。削弱膜污染方法采用最优参数的三向旋转入流组件(α=70°、δ=2 mm、β=45°),自来水进入污染期由32 h推迟到65 h,传质通量比无旋转增大近20%;采用具有分水盘的并接式空气隙膜组件,开槽2 mm膜污染较严重,开槽3 mm的膜通量比无旋转入流传质通量平均增大60%,两种组件设计形式均可提高膜通量,一定程度缓解了膜污染的产生。  相似文献   
363.
一体式铝盐絮体-超滤膜净水效能与机制   总被引:1,自引:1,他引:0  
一体式膜工艺以其占地面积小、污染物去除效率高等优点在水处理工艺中逐渐应用.然而,长期运行后,传统颗粒性吸附剂存在加剧膜表面损伤的风险,同时大多数研究所用吸附剂价格较高,如纳米铁、碳纳米管等.针对上述问题,本文将铝盐混凝剂水解后形成的松散絮体直接注入膜池,基于腐殖酸(HA)和密云水库原水,考察了一体式絮体-超滤膜工艺运行效能及膜污染行为.结果表明,仅HA过膜时,第12 d跨膜压差(transmembrane pressure,TMP)急剧增至76. 4 k Pa,将膜组件取出经自来水清洗膜表面后TMP降为10. 1 k Pa (13 d),表明滤饼层是膜污染的主要形式,并且运行期间HA平均去除率仅为23. 3%.絮体注入频率、曝气强度及溶液pH能显著影响该工艺运行效能,尤其溶液pH.当采用连续投加方式将43. 2mmol·L-1铝盐絮体注入到pH为6. 0、曝气速率为0. 3 L·min-1膜池内时,膜污染程度显著降低,第12 d时TMP仅增长到19. 5 k Pa,清洗之后TMP降为5. 6 k Pa (13 d),此时HA平均去除率提高至61. 2%.此外,密云水库原水实验表明,当原水直接过膜时,TMP也急剧增加,运行12 d时TMP达到38. 0 k Pa,而清洗膜表面后TMP降低至3. 8 k Pa (13 d),滤饼层仍然为主要污染方式,同时有机质平均去除率为7. 5%.在上述最佳工艺条件下(曝气0. 3 L·min-1、溶液pH 6. 0)投加43. 2mmol·L-1铝盐絮体时,TMP增长也极其缓慢,12 d时仅增至6. 1 k Pa,膜表面清洗后TMP降至2. 3 k Pa (13 d),有机质平均去除率高达58. 6%.本研究表明一体式铝盐絮体-超滤膜在水处理中具有潜在的应用价值.  相似文献   
364.
Five negatively charged organic compounds with different structures, sodium methane sulfonate (MS), sodium benzene sulfonate (BS), sodium 6-hydroxynaphthalene-2-sulfonate (NSS), sodium dodecyl sulfate (SDS), and sodium dodecyl benzene sulfonate (SDBS), were used to examine the fouling of an anion exchange membrane (AEM) in electrodialysis (ED), to explore the effect of molecular characteristics on the fouling behavior on the AEM and changes in the surface and electrochemical properties of the AEM. Results indicated that the fouling degree of the AEM by the different organics followed the order: SDBS?>?SDS?>?NSS?>?BS?>?MS. SDBS and SDS formed a dense fouling layer on the surface of the AEM, which was the main factor in the much more severe membrane fouling, and completely restricted the transmembrane ion migration. The other three organics caused fouling of the AEM by adsorption on the surface and /or accumulation in the interlayer of the AEM, and exhibited almost no influence on the transmembrane ion migration. It was also concluded that the organics with benzene rings caused more severe fouling of the AEM due to the stronger affinity interaction and steric effect between the organics and the AEM compared with organics with aliphatic chains.  相似文献   
365.
Coagulation–ultrafiltration(C–UF) is widely used for surface water treatment. With the removal of pollutants, the characteristics of organic matter change and affect the final treatment efficiency and the development of membrane fouling. In this study, we built a dynamic C–UF set-up to carry out the treatment of micro-polluted surface water, to investigate the characteristics of dissolved organic matter from different units. The influences of poly aluminum chloride and poly dimethyldiallylammonium chloride(PDMDAAC) on removal efficiency and membrane fouling were also investigated. Results showed that the dosage of PDMDAAC evidently increased the UV254 and dissolved organic carbon removal efficiencies,and thereby alleviated membrane fouling in the C–UF process. Most hydrophobic bases(HoB)and hydrophobic neutral fractions could be removed by coagulation. Similarly, UF was good at removing HoB compared to hydrophilic substances(HiS) and hydrophobic acid(HoA)fractions. HiS and HoA fractions with low molecule weight accumulated on the surface of the membrane, causing the increase of transmembrane pressure(TMP). Membrane fouling was mainly caused by a removable cake layer, and mechanical cleaning was an efficient way to decrease the TMP.  相似文献   
366.
Membrane fouling is an obstacle impeding the wide applications of ceramic membranes and organics are responsible for most of the membrane fouling issues in wastewater treatment. In this study, Fenton cleaning strategy was firstly proposed to clean ceramic membrane fouling in wastewater treatment. Fe~(2+)efficiently catalyzed fouling cleaning with H_2O_2(1.5%) to recover the filterability of ceramic membrane. The maximum ΔTMP recovery(over 99%) was achieved at an optimal Fe~(2+)dosage of 124 mg/L after 6 hr of immersion cleaning. The total residual membrane fouling resistance decreased gradually from this optimum value as the Fe~(2+)dosage increased above 124 mg/L. The residual hydraulically reversible fouling resistance accounted for most of the membrane fouling and was basically removed(≤3.0 × 10~9 m~(-1)) when Fe~(2+)dosages higher than 124 mg/L were used. The foulants responsible for the formation of a residual hydraulically reversible fouling layer(DOC(dissolved organic carbon), proteins, polysaccharides, EEM(fluorescence excitationemission matrix spectra), SS(suspended solids), and VSS(volatile suspended solids)) were gradually removed as the Fe~(2+)dosage increased. These residual organic foulants were degraded from biopolymers(10–200 kDa) to low molecular weight substances(0.1–1 kDa),and the particle size of these residual foulants decreased significantly as a result. The strong oxidation power of hydrogen peroxide/hydroxy radicals towards organic foulants was enhanced by Fe~(2+). Fe~(2+)played a significant role in the removal of hydraulically reversible fouling and irreversible fouling from the ceramic membrane. However, Fe~(2+)(≥ 124 mg/L) increased the likelihood of forming secondary iron-organics aggregates.  相似文献   
367.
This study proposed a novel membrane filtration and dissolved ozone flotation integrated(MDOF) process and tested it at pilot scale. Membrane filtration in the MDOF process was operated in gravity-driven mode, and required no backwashing, flushing, or chemical cleaning. Because ozone was added in the MDOF process, ozonation, coagulation, and membrane filtration could occur in a single reactor. Moreover, in situ ozonation occurred in the MDOF process, which differs from the conventional pre-ozonation membrane filtration process. Significant enhancement of turbidity removal was further achieved through the addition of membrane filtration. Membrane fouling was mitigated in the MDOF process compared to the MDAF process. In situ ozonation in the MDOF process decreased the fluorescence intensity and transformed the high MW dissolved organics into small MW compounds. For the fouling layer, the extracellular polymeric substance(EPS) contents and cake layer morphology were analyzed. The results indicated that the contents of EPS decreased. Furthermore, a thinner and more loosely structured cake layer formed in the MDOF process. Because coagulation and ozonation occurred simultaneously in a single reactor, the generation of hydroxyl radicals was enhanced through the catalytic effect of Al-based coagulants on ozone decomposition, which further alleviated membrane fouling in the MDOF process.  相似文献   
368.
以粉末活性炭和硅藻土为涂膜材料,在聚醚砜超滤膜表面形成预涂动态膜,考察了预涂动态膜对海水中有机物的去除效果和作用机制,通过比较分析直接超滤和预涂动态膜过滤海水前后膜表面亲疏水性、形貌结构、粗糙度及膜阻力分布的变化,探讨了活性炭和硅藻土预涂覆对超滤膜污染的影响.结果表明,预涂动态膜可提高超滤膜对海水中溶解有机碳(DOC)和UV_(254)的去除率,活性炭预涂动态膜对海水中DOC和UV_(254)的去除率较直接超滤分别提高11.2%和11.3%.硅藻土预涂膜主要利用超滤膜表面形成的硅藻土滤饼层强化海水中蛋白质类有机物的截留,活性炭对海水中小分子有机物的额外吸附导致海水过滤过程中活性炭预涂膜对有机物的去除效果优于硅藻土预涂膜.与直接超滤相比,预涂动态膜过滤海水后膜表面亲水性更好,膜表面粗糙度更低,膜过滤阻力也更小,活性炭预涂动态膜净化海水时膜过滤总阻力较直接超滤降低50.3%.利用涂膜材料在超滤膜表面形成的滤饼层将超滤膜与有机物进行了"隔离",避免了超滤膜与有机污染物直接接触,降低了小分子有机物在膜孔内的吸附堵塞,能够有效减缓超滤膜的不可逆污染.  相似文献   
369.
膜污染是限制膜生物反应器大规模应用的关键所在,本文试图将现代清洁生产的思想应用到膜污染控制之中。采取从源头控制、过程控制以及末端治理相结合的全过程控制方法,最大限度地减缓膜污染,从而加快MBR在实际工程中的应用。  相似文献   
370.
1 IntroductionDuringthepastfewyears,membraneseparationshavebecomemorewidelyused,andreplacedsomeoftheconventionalconcentrationt?..  相似文献   
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