用户名: 密码: 验证码:
不同水质及膜材质平板膜—生物反应器运行特性研究
详细信息    本馆镜像全文|  推荐本文 |  |   获取CNKI官网全文
摘要
膜-生物反应器是将膜分离与生物技术结合起来的一种新型污水处理和回用技术,近年来在基础研究和实际工程应用领域都得到广泛的关注。
     为了促进平板膜-生物反应器在城市废水处理上的工程化应用,在课题组前期研究成果的基础上,受课题组研究工作的安排,针对不同膜孔径和不同无纺布开展了高通量平板膜材质的研究及高通量平板膜-生物反应器处理生活污水的研究,针对不同处理对象进行了平板膜-生物反应器处理微污染水源水及高浓度酒糟废水的实验研究,主要研究内容及实验结果如下:
     1)进行了高通量平板膜材质的中试研究。实验结果表明:不同膜孔径和不同无纺布的平板膜按高通量30L/m~2·h运行时其膜过滤性能有很大的差异,6~#膜(国产无纺布)、仿6~#(1)膜、2~#最新膜(进口无纺布)其运行特性好,适宜于MBR工程用膜的推广。国产MF膜由于在成膜过程中孔尺寸的控制精度还不能很好掌握,可能会导致相同无纺布的膜其过滤性能有很大的差别。在此基础上考察了高通量平板膜-生物反应器处理生活污水的中试研究,实验结果表明:系统对COD_(Cr)、NH_4~+-N有很好的去除效果,出水COD_(Cr)在50mg/L以下,COD_(Cr)去除率在85%~99%之间。由于系统的污泥浓度高,在控制适宜的DO下,系统实现了同步硝化反硝化效应,对总N有一定程度的去除效果,去除率在20%~70%之间,平均去除率为38.7%。
     2)进行了平板膜-生物反应器净化微污染水源水的研究。实验结果表明:水力停留时间(HRT)为1.5h,系统对水体中的污染物COD_(Cr)、COD_(Mn)、TOC及NH_4~+-N有很好的去除效果。出水COD_(Cr)低于15mg/L,平均去除率为78.7%;出水NH_4~+-N低于0.5mg/L,平均去除率为90.2%;UV_(254)的去除率较低,平均去除率为34.6%。
     3)考察了平板膜-生物反应器净化微污染水源水系统污泥混合液中胞外聚合物(EPS)浓度与膜污染的关系。结果表明:EPS浓度与膜污染没有线性关系,运行通量的选择是本研究三个工况膜污染程度相异的一个主要原因。
     4)考察了投加粉末活性炭对平板膜.生物反应器处理微污染水源水去除效果的影响。结果表明:由于活性炭的强吸附能力,活性炭的投加使得系统对水体中COD_(Mn)、TOC及UV_(254)的去除率有很大的提高,去除率分别提高了10.3%、6.8%及26.2%,而对COD_(Cr)和NH_4~+-N的去除效果影响不大。
     5)进行了好氧平板膜-生物反应器处理高浓度酒糟废水的初步研究。实验结果表明:系统对不同COD_(Cr)浓度进水的高浓度酒糟废水有很好的去除效果。在HRT为24.4h,进水COD_(Cr)分别为4000mg/L、2000mg/L、1000mg/L的情况下,出水COD_(Cr)分别介于30mg/L~180mg/L之间;介于10mg/L~100mg/L之间;介于40mg/L~100mg/L之间。平均出水分别为70.9mg/L、43.5mg/L、57.1mg/L。平均去除率分别为98.2%、98%、94.1%。在HRT为12.2h,进水COD_(Cr),分别为2000mg/L、1000mg/L的情况下,出水COD_(Cr)分别介于30mg/L~250mg/L之间;介于5mg/L~80mg/L之间。平均出水分别为117mg/L、35mg/L。平均去除率分别为96.8%、94.2%。
     6)好氧平板膜-生物反应器处理高浓度酒糟废水其污泥混合液性质与一般的好氧MBR处理生活污水的混合液性质有很大的差异,膜面污染物质的性质也不同。处理高浓度酒糟废水时,混合液中和膜面上的糖类含量相比处理生活污水时要高。粘度是本研究好氧平板膜-生物反应器处理高浓度酒糟废水系统膜污染的一大主要影响因素。
The membrane bioreactor (MBR) has received great attention in Wastewater treatment and reclamation for years, which combines membrane separation with biological technology.
    In order to speed the Wastewater treatment project application of flat-sheet membrane bioreactor, regard to different membrane aperture and non-woven fabrics, high flux flat-sheet membrane material with pilot-scale experiment is investigated in this study. Furthermore, micro-polluted source water purification and high strength lees Wastewater treatment by aerobic flat-sheet membrane bioreactor are also studied. The main studying content and result are shown as follows:
    1) high flux flat-sheet membrane material with pilot scale experiment was investigated. Test results indicated that the membrane filtration performance was greatly different for different membrane aperture and non-woven fabrics. No.6, No.2 membrane and simulated No.6 membrane with excellent operation characteristics are suitable to develop in the MBR project. It may lead to great difference of membrane filtration performance with same non-woven fabrics due to be incapable of grasping the precision well in the forming of membrane aperture. Based in above studied, domestic Wastewater treatment by flat-sheet membrane bioreactor with pilot scale was studied. Test results indicated that MBR owned excellent remove effect of pollutant. Effluent COD_(Cr) was lower than 50mg/L and COD_(Cr) removal rate was fluctuated between 85% and 99%. Due to the high sludge concentration, flat-sheet MBR system achieved the Simultaneous Nitrification/Denitrification with low dissoluble oxygen, and MBR owned a certain extent removal effects of total nitrogen. Total nitrogen removal rate was fluctuated between 20% and 70%, and the mean total nitrogen removal rate was 38.7%.
    2) Micro-polluted source water treatment by flat-sheet membrane bioreactor was studied. Test results indicated that MBR owned excellent removal effect of COD_(Cr), COD_(Mn), TOC and NH_4~+ -N with HRT 1.5h. Effluent COD_(Cr) was lower than 15mg/L and the mean COD_(Cr) removal rate was 78.7%. Effluent NH_4~+-N was lower than 0.5mg/L and the mean NH_4~+-N removal rate was 90.2%. The mean UV_(254) removal rate was 34.6%.
    
     3) The relation between EPS concentration and membrane fouling was investigation in this study. Test results showed that there was no notable correlation between EPS concentration of mixed liquor and membrane fouling. The selection of operational flux had significant effects on membrane fouling and operation of flat membrane bioreactor.
     4) With the addition of PAC, the effect on the removal effect of flat-sheet membrane bioreactor was studied. Test results shown that due to the strong adsorption capability, the removal rate of COD_(Mn), TOC and UV_(254) treatment by flat-sheet MBR had a great improvement, which improved 10.3%, 6.8% and 26.2%. However, it had no notable effect on the removal rate of COD_(Cr), NH_4~+-N.
     5) High strength lees wastewater treatment by aerobic flat-sheet membrane bioreactor was primarily studied. Test results shown that MBR owned excellent removal effect treatment different COD_(Cr) concentration of high strength lees wastewater. In the condition of HRT 24.4 and influent COD_(Cr) respectively was 4000mg/L, 2000mg/L and 1000mg/L, Effluent COD_(Cr) respectively was fluctuated between 30mg/L and 180mg/L, between 10mg/L and 100mg/L, between 40mg/L and 100mg/L, and the mean effluent COD_(Cr) were 70.9mg/L, 43.5mg/L and 57.1mg/L, respectively. The mean COD_(Cr) removal rate were 98.2%, 98% and 94.1%, respectively. In the condition of HRT 12.2 and influent COD_(Cr) respectively was 2000mg/L and 1000mg/L, Effluent COD_(Cr) respectively was fluctuated between 30mg/L and 250mg/L, between 5mg/L and 80mg/L, and the mean effluent COD_(Cr) were 117mg/L and 35mg/L, respectively. The mean COD_(Cr) removal rate were 96.8% and 94.2%, respectively.
     6) There was a great difference between mixed liquor characteristics of high strength lees organic wastewater treatment by aerobic flat-sheet membrane bioreactor and mixed liquor characteristics of domestic wastewater treatment by MBR. And the characteristics of pollutants on membrane also had great difference. Viscosity was the main effect factor on the membrane fouling in the MBR system treatment high strength lees organic wastewater.
引文
[1] 建设部科技司.中国2000年水工业可持续发展战略—水工业科技产业化.给水排水,1995.5:31-35.
    [2] 郭卫宏等.中水道应用—建筑给排水的发展趋势.给水排水,1999,25(12):41-45.
    [3] S Chaize. Membrane Bioreactor on Domestic Wastewater Treatment Sludge Production and Modeling, Approach. War. Sci. Tech.. 1991.23(7~9): 1591-160.
    [4] 李秀芳,傅学起,胡国臣.膜-生物反应器在废水处理中的优势.工业水处理,2001,21(8):7-10.
    [5] 彭跃莲,刘忠州.膜-生物反应器在废水处理中的应用.水处理技术,1999,25(2):63-69.
    [6] Byung, Kook Hwang, Woo-Nyoung Lee, et al. Effect of membrane fouling reducer on cake structure and membrane permeability in membrane bioreactor. Journal of Membrane Science, 2006, 11: 1-8.
    [7] Belfort G, Marx B. Artificial particulate fouling of hyperfiltration membranes Ⅱ. Analysis protection from fouling. Desalination, 1979, 28: 13-30.
    [8] 高以煊,叶凌碧.膜分离技术基础.北京:科学出版社,1989.3,p17.
    [9] S. Nakao, H. Osada, H. Kurata, T. Tsuru, et al. Separation of proteins by charged ultrafiltration membranes. Desalination, 1988, 13 (70): 191-205.
    [10] Shimizu Y. Effect of particle size distributions of activated sludges on crossflow microfiltration flux for submerged membranes. Ferment. Bioeng, 1997, 83(6): 583-589.
    [11] Reihanian H, Roberts C.R.A.S. Mechanisms of polarization and fouling of ultrafiltration membranes by proteins. Membr. Sci., 1983, 16: 20-37.
    [12] Futamura O, Masuo K, Koyosi T. Organic waste water treatment by activated sludge process using integrated type membrane separation. Desalination, 1994, 98:17-25.
    [13] Satoshi Miyashita. The principle of microfiltration of activated sludge in the membrane bioreactor process. China Japan International Symposiumon Membrane Hybrid System Applied to Water Treatment Proceedings, 1999: 68-73.
    [14] Choo K.H, Lee C.H. Effect of anaerobic digestion broth composition on membrane permeability. Wat. Sci. Tech., 1996, 34(9): 173-179.
    [15] Shoji M. Membrane filtration treatment for domestic waste water. Membr. Sci., 1990, 54: 269-300.
    [16] Namjung Jang, Xianghao Ren, Geontae Kim, et al. Characteristics of soluble microbial products and extracellular polymeric substances in the membrane bioreactor for water reuse. Desalination, 2007, 202: 90-98.
    [17] 吴金玲,黄霞.膜-生物反应器混合液性质对膜污染影响的研究进展.环境污染治理技术与设备,2006,2(2):16-24.
    [18] Defrance L, JaffrinM. Y, Fupta B, Paullier P, et al. Contribution of various constituents of activated sludge to membrane bioreactor fouling. Bioresource Technology, 2000, 73: 105-112.
    [19] Zoh K.D, Stenstrom, Michae K. Application of a membrane bioreactor for treating explosives process wastewater. Wat. Res.,2002, 36(4): 1018-1024.
    [20] Shimizu Y. Filtration characteristics of hollow fiber microfiltration membranes used in membrane bioreactor for domestic wastewater treatment. Wat. Res., 1996, 30(10): 2385-2392.
    [21] Halila H, Cumalib K, Ayhana U. Viability of microbialmass in a submerged membrane bioreactor. Desalination, 2002, 150(3): 263-268.
    [22] Rosenberger S, Kraume M. Filterability of activated sludge in membrane bioreactors. Desalination, 2003, 151(2): 195-200.
    [23] Hong S.P, Bae T.H, Tak T.M, et al. Fouling control in activated sludge submerged hollow fiber membrane bioreactors. Desalination, 2002, 143(3): 219-228.
    [24] Nagaoka H, Ueda S, Miya A. Influence of bacterial extracellular polymers on the membrane separation activated sludge process. War. Sci. Tech., 1996, 34(9): 165-172.
    [25] R. Shane Trussell, Rion P. Merlo, Slawomir W. Hermanowicz, et al. Influence of mixed liquor properties and aeration intensity on membrane fouling in a submerged membrane bioreactor at high mixed liquor suspended solids concentrations. Water Res., 2006, 12: 1-12.
    [26] Lee J, Ahn W.Y, Lee C.A. Comparison of the filtration characteristics between attached and suspended growth microorganisms in submerged membrane bioreactor. Wat. Res., 2001, 10(35): 2435-2445.
    [27] 柳根勇,桃井清至,小松俊哉.膜分离活性污泥法膜透过性能对生物代谢成分影响.水环境学会志,1997,20(7):473-480.
    [28] Lee Y, Cho J, Seo Y, Lee J.W, Ahn K.H. Modeling of submerged membrane bioreactor process for wastewater treatment. Desalination, 2002, 146(1.3): 451-457.
    [29] 罗虹,顾平,杨造燕.膜-生物反应器内泥水混合液可过滤性的研究.城市环境与城市生态,2000,13(1):51-53.
    [30] 迪莉拜尔.苏力坦,莫罹,黄霞.PAC2MBR组合工艺中膜污染及清洗方法的研究.给水排水,2003,29(5):1-5.
    [31] Schafer A.I, Schwicker U, et al. Microfiltration of colloids and natural organic matter. Journal ofMembrane Science, 2000, 171: 151-172.
    [32] Bruus J.H, et al. On the stability of activated sludge flocs with implications to dewatering. War. Res., 1992, 26(12): 1597-1604.
    [33] In S. Kim, Namjung Jang. The effect of calcium on the membrane biofouling in the membrane bioreactor (MBR). Water Reserch, 2006, 40: 2756-2764.
    [34] Ueda T, Hata K, Kikuoka Y. Treatment of domestic sewage from rural settlements by a membrane bioreactor. Wat. Sci. Tech., 1996, 34(9): 189-196.
    [35] 上田达己,端二,菊冈保人,清野修.膜分离活性污泥法溶解性代谢产物动态膜过性能.水环境学会志,1997,20(4):233-237.
    [36] Muller E.B, Stouthamber A.H, Verseveld H.W, Eikeboom D.H. Aerobic domestic wastewater treatment in a pilot plant with complete sludge retention by cross-flow filtration Wat. Res., 1995, 29(4): 1179-1189.
    [37] Shimizu Y, et al. Effect of particle size distributions of activated sludges on cross2flow microfiltration flux for submerged membranes. J. Ferment. Bioeng., 1997, 83 (6): 583-589.
    [38] 刘锐.一体式膜-生物反应器的微生物代谢特性及膜污染控制[博士学位论文].北京:清华大学.2000:1-96-100.
    [39] Kim J.S, Lee C.H, Chang I.S. Effect of pump shear on the performance of a crossflow membrane bioreactor. Wat. Res., 2001, 35(9): 2137-2144.
    [40] Mikkelsen L.H. The shear sensitivity of activated sludge Relations to filterability, rheology and surface chemistry. Colloids and Surfaces, 2001, 182: 1-14.
    [41] Lee W, Kang S, Shin H. Sludge characteristics and their contribution to microfiltration in submerged membrane bioreactors. Journal of Membrane Science, 2003, 216(12): 217-227.
    [42] Houghton J.I, Quarmby J, Stephenson T. Municipal wastewater sludge dewaterability and the presence of microbial extracellular polymer. Wat. Sci. Tech., 2001,44(2~3): 373-379.
    [43] Yiantsios S.G.Karabclas A.J. The effect of colloid stability on membrane fouling. Desalination, 1998, 118: 143-152.
    [44] 奥野佑一,瓜升腾嗣,清水康利,渡边敦夫.膜分离活性污泥法浸渍型中空系膜吸引滤过特性.第29回日本水环境学会年会演讲集,1995,1.C-15.4:146.
    [45] Bai R.F.Leow H. Microfiltration of activated sludge wastewater-The effect of system operation parameters. Separation and Purification Technology, 2002, 29(2): 189-198.
    [46] Mikkelsen L.H, Keiding K. Physics chemical characteristics of full scale sewage sludges with implications to dewatring. Wat. Res., 2002, 36:2451-2462.
    [47] Choo K.H, Lee C.H. Membrane fouling mechanisms in the membrane coupled anaerobic bioreactor. Wat. Res., 1996, 30(8): 1771-1780.
    [48] Ognier S. A, Wisniewski C. A, Grasmick A. Characterisation and modelling of fouling in membrane bioreactors. Desalination, 2002, 146(1~3): 141-147.
    [49] Kang I.J, Lee C.H, Kim K.J. Characteristics of microfiltration membranes in a membrane coupled sequencing batch reactor system. War. Res., 2003, 37(5): 1192-1197.
    [50] Choi G.B, Bae T.H, Tak T.M, Randall A.A. The behavior of membrane fouling initiation on the crossflow membrane bioreactor system. Journal of Membrane Science, 2002, 203(1~2): 103-113.
    [51] Yu-Lan Jin, Woo-Nyoung Lee, Chung-Hak Lee, et al. Effect of DO concentration on biofilm structure and membrane filterability in submerged membrane bioreactor. Water research, 2006, 40: 2829-2836.
    [52] Wang Y, Huang X, Sun Y, Wen X, Qian Y. Influence of filamentous bulking on membrane fouling in membrane bioreactor. Water Environment—Membrane Teehnology(WEMT), Korea, June, 2004: 7-10.
    [53] 刘锐,黄霞,王志强,钱易.一体式膜-生物反应器的水动力学特性.环境科学,2000,5(21):47-50.
    [54] Lei Ji, Jiti Zhou. Influence of aeration on microbial polymers and membrane fouling in submerged membrane bioreactors. Journal of Membrane Science, 2006, 276:168-177.
    [55] Hideke H. Application of anaerobic-UF membrane reactor for treatment of a wastewater containing high strength particulate organics. Wat. Sci. Tech., 1996, 30(12): 307-319.
    [56] Veda T, Hata K. Kikuoka Y. Treatment of domestic sewage from rural settlements by a membrane bioreactor, Wat. Sci. Tech., 1996, 34 (9): 189-196.
    [57] Visvanathan C, Yang B.S, Muttamara S, et al. Application of air baekflushing technique in membrane bioreactor. Water Sci. Technol., 1997, 36: 259-266.
    [58] R. Shane Trussell, Rion P. Merlo, Slawomir W. Hermanowicz et al. The effect of organic loading on process performance and membrane fouling in a submerged membrane bioreactor treating municipal wastewater. Water Reserch, 2006, 40: 2675-2683.
    [59] Zubair Ahmed, Jinwoo Cho, Byung-Ran Lira, et al. Effects of sludge retention time on membrane fouling and microbial community structure in a membrane bioreactor. Journal of Membrane Science, 2007, 287:211-218.
    [60] 彭跃莲,刘忠洲.稳定膜透水率的新方法—恒流控制.水处理技术,2001,27(4):214-216.
    [61] Katsuki Kimura, Nobuhiro Yamato, Hiroshi Yamamura,et al. Membrane Fouling in Pilot-Scale Membrane Bioreactors(MBRs) Treating Municipal Wastewater. Environ. Sci. Technol, 2005, 39(16): 6293-6299.
    [62] Magara Y. The effect of operational factors on solid/liquid separation by ultramembrane filtration in a biological denitrification systems for collected human excreta treatment plant. Wat Sci Tech. 1991, 23(12): 1583-1590.
    [63] 徐慧芳,樊耀波.气升循环分体式膜生物反应器再生回用厕所污水的研究.环境科学,2003,2(24):125-129.
    [64] Jinling Wu, Futai Chen, Xia Huang, et al. Using inorganic coagulants to control membrane fouling in a submerged membrane bioreactor. Desalination, 2006, 197: 124-136.
    [65] 罗虹等.应用投加粉末活性炭的膜-生物反应器处理生活污水的研究.重庆环境科学,2002,24(3):28-31.
    [66] Yamamoto K, Hissa M, Mahmood T, Matsuo T. Direct solid liquid separation using hollow fiber membrane in an activated sludge aeration tank. Water Sci. Technol., 1989, 21: 43-54.
    [67] Chiemchaisri C, Yamamoto K. Biological nitrogen removal under low temperature in a membrane separation bioreactor. Water Sci. Technol., 1993, 28: 325-333.
    [68] Bouhabila E.H, Aim R.B, Buisson. Fouling charaeterisation in membrane bioreactors. Sep. Purif. Technol., 2001, 22(23): 123-132.
    [69] Chiemchaisri C, Wong Y.K, Urase T, et al. Organic stabilisation and nitrogen removal in membrane separation bioreactor for domestic wastewater treatment. Water Sci. Technol., 1992, 25:231-240.
    [70] Choo K.H, Stensel H.D. Sequencing batch membrane reactor treatment: Nitrogen removal and membrane fouling evaluation. Water Environ. Res., 2000, 72: 490-498.
    [71] Parameshwaran K, Visvanathan C, Ben A R. Membrane as solid/liquid separator and air diffuser in bioreactor. J. Environ. Eng., 1999, 125(9): 825-834
    [72] Visvanathan C, Yang B S, Muttamara S, et al. Application of air backflushing technique in membrane bioreactor. Water Sci. Teehnol., 1997, 36: 259-266.
    [73] Byung-Kook Hwang, Woo-Nyoung Lee, Pyung-Kyu Park, et al. Effect of membrane fouling reducer on cake structure and membrane permeability in membrane bioreactor. Membr. Sci., 2006, 10: 1-8.
    [74] S.R Chae, H.S Shin. Effect of condensate of food waste (CFW) on nutrient removal and behaviours of intercellular materials in a vertical submerged membrane bioreactor (VSMBR). Bioresource Technology, 2007, 98: 373-379.
    [75] Kuo-Shing Lee, Ping-Jei Lin, Kai Fangchiang, et al. Continuous hydrogen production by anaerobic mixed microflora using a hollow-fiber mierofiltration membrane bioreactor. International Journal of Hydrogen Energy, 2006.
    [76] Federica Alberti, Barbara Bienati, Aldo Bottino, et al. Hydrocarbon removal from industrial wastewater by hollow-fibre membrane bioreactors. Desalination, 2007, 204: 24-32.
    [77] M. Brik, P. Schoeberl, B. Chamam, et al. Advanced treatment of textile wastewater towards reuse using a membrane bioreactor. Process Biochemistry, 2006, 41: 1751-1757.
    [78] Yeom I.T., Lee K.R., Choi Y.G., et al. A pilot study on accelerated sludge degradation by a high-concentration membrane bioreactor coupled with sludge pretreatment. Water Sci. Technol., 2005, 62(10-11): 201-210.
    [79] 曹效鑫,魏春海,黄霞.投加粉末活性炭对一体式膜-生物反应器膜污染的影响研究.环境科学学报,2005,25(11):1443-1447.
    [80] 隋鹏哲,文湘华,黄霞.厌氧膜-生物反应器中超声控制膜污染研究.环境污染治理技术与设备,2006,4(7):25-29.
    [81] 李娜,王光辉,张志凡,等.AO-MBR工艺处理城市污水的研究.化学与生物工程,2006,9(23):54-56.
    [82] 杨琦,尚海涛,杨春等.IMBR-AO工艺对生活污水脱氮除磷的研究.中国给水排水,2006,7(22):101-104.
    [83] 郑祥,刘俊新.厌氧反应器与好氧MBR组合工艺处理毛纺印染废水试验研究.环境科学,2004,5(25):102-105.
    [84] 王志伟,吴志超,顾国维,等.一体式厌氧平板膜-生物反应器处理酒厂废水的研究.给水排水,2006,2(32):51-53.
    [85] 许宜平,陈少华,陈明.厌氧膜-生物反应器处理垃圾渗滤液中多环芳烃的研究.环境化学,2004,6(23):691-694.
    [86] 吴志超,曾萍,顾国维.膜截留分子量对污水分置式好氧膜-生物反应器处理性能的影响.膜科学与技术,2001,21(4):21-24.
    [87] Klangduen Pochana, Jurg Keller. Study on factors affecting simultaneous nitrification and denitrification (SND). Wat Sci Tech, 1999, 39(6): 61-68.
    [88] 齐唯,李春杰,何义亮.浸没式膜-生物反应器的同步硝化反硝化效应.中国给水排水,2003,19(7):8-11.
    [89] 邹联沛,刘旭东,王宝贞,等.MBR中影响同步硝化反硝化的生态因子.环境科学,2001,22(4):51-55.
    [90] Klangduen Poehana, Jurg Keller. Model development for simultaneous nitrification and denitrification. Wat Sci Tech., 1999, 39(1): 235-243.
    [91] 高廷耀,周增炎.生物脱氮工艺中反硝化现象.城市给排水,1998,24(12):6-9.
    [92] Xiaoyan Li, HiuPing Chu. Membrane bioreactor for the drinking water treatment of polluted surface water supplies. Water Research, 2003, 37: 4781-4791.
    [93] A. M. Barreiros, C. M. Rodrigues, J. P. S. G. Crespo, et al. Membrane bioreactor for drinking water denitrification. Bioprocess and Biosystems Engineering, 1998, 4(18): 297-302.
    [94] 莫罹,黄霞.微滤膜处理微污染原水研究.中国给水排水,2002,18(4):40-43.
    [95] 张光辉,郝爱玲,张颖等.MBR与MCR处理微污染原水的效果.中国给水排水,2004,20(2):47-50.
    [96] 国家环境保护局.水和废水监测分析方法(第3版).北京:中国环境科学出版社,1989.
    [97] Chang In-Soung, Lee Chung-Hak. Membrane filtration characteristics in membrane-coupled activated sludge system the effect of physiological states of activated sludge on membrane fouling. Desalination, 1998, 120(3): 221-233.
    [98] 王占生,刘文君.微污染水源饮用水处理(第1版).北京:中国建筑工业出版社,1999.
    [99] 莫罹,黄霞,迪里拜尔.苏里坦.膜—生物反应器处理微污染水源水的运行特性.中国环境科学,2003,23(2):196-200.
    [100] 郝爱玲,张光辉,张颖等.MBR、MCR处理微污染水的膜污染比较.中国给水排水,2004,20(7):49-53.
    [101] Bura R, Cheung, et al. Composition of extracellular polymeric substances in the activated sludge matrix. Wat. Sci. Tech., 1998, 37(4~5): 325-333.
    [102] Chang I.S, Lee C.H. Membrane filtration characteristics in membrane coupled activated sludge system-the effect of physiological states of activated sludge on membrane fouling. Desalination, 1998, 120(3): 221-233.
    [103] Huang X, Liu R, QianY, et al. Behaviour of soluble microbial products in a membrane bioreactor. Process Biochem, 2001, 36(5): 401-406.
    [104] Katsuki Kimura, Nobuhiro Yamato, Hiroshi Yamamura, et al. Membrane Fouling in Pilot-Scale Membrane Bioreactors (MBRs) Treating Municipal Wastewater. Environ. Sci. Technol, 2005, 39(16): 6293-6299.
    [105] Nagaoka H, Yamanishi S, Miya A. Modeling of biofouling by extracellular polymers in a membrane separation activated sludge. Water Sci. Technol, 1998, 38 (4~5): 497-504.
    [106] Fengshen Fan, Hongde Zhou, Hadi Husain. Identification of wastewater sludge characteristics to predict critical flux for membrane bioreactor processes. Water Research, 2006, 40: 205-212.
    [107] MiaoMiao Zhang, Chun Li, Markrn Benjamin, et al. Fouling and Natural Organic Matter Removal in Adsorbent/Membrane Systems for Drinking Water Treatment. Environ. Sci. Technol., 2003, 37: 1663-1669.
    [108] M. Mazet, B. Farkhani, M. Baudu. Influence of heat or chemical treatment of activated carbon onto the adsorption of organic compounds. Water Research, 1994, 7(28): 1609-1617.
    [109] 王广智,李伟光,何文杰,等.活性炭性质对固定化生物活性炭净水效果的影响研究.环境科学,2006,27(10):129-133.
    [110] Adham S.S, Snoeyink V.L, Clark, M.M, et al. Predicting and verifying organics removal by PAC in an ultrafiltration system. Journal of the American Water Works Association, 1995, 83(12): 81-91.
    [111] Jack A.M, Clark M.M. Using PAC-UF to treat a low quality surface water. Journal of the American Water Works Association, 1998, 90(11): 83-95.
    [112] Lin C.F, Huang Y.J, Hao O.J. Ultraflltration processes for removing humic substances: effect of molecular weight fraction on PAC treatment. Water Res., 1999, 33(5): 1252-1264.
    [113] 李军,江定国,刘红,等.复合式膜-生物反应器处理生活污水.中国环境科学,2006,26(3):271-274.
    [114] 李耀中,贺延龄,刘永红,等.投加粉末炭对SMBR过滤性能的影响.中国给水排水,2004,20(10):10-13.
    [115] 曹效鑫,魏春海,黄霞.投加粉末活性炭对一体式膜-生物反应器膜污染的影响研究.环境科学学报,2005,25(11):1443-1447.
    [116] JaeSeok Kim, ChungHak Lee. Effect of powdered activated carbon on the performance of an aerobic membrane bioreactor comparison between crossflow and submerged membrane systems. Water Environment Research, 2003, 75: 300-307.
    [117] 黄学政,段耀广,黄廷林.用中空纤维膜-生物反应器处理高浓度有机废水.化工环保,2005,6(25):462-465.
    [118] 王雪梅,刘燕,华志浩,等.胞外聚合物对浸没式膜-生物反应器膜过滤性能的影响.环境科学学报,2005,12(25):1602-1607.
    [119] Nagaoka H, Ueda S, Miya A. Influence of bacterial extracelluar polymers on the membrane separation activated sludge process. War Sci Tech., 1996, 34(9): 165-172.
    [120] Rosenberger S, Ka'aume M. Filterability of activated sludge in membrane bioreactors Desalination, 2002, 146:373-379.
    [121] Chang I.S, Lee C.H. Membrane filtration characteristics in membrane coupled activated sludge system the effect of physiological states of activated sludge on membrane fouling.Desalination, 1998, 120(3): 221-223.
    [122] Lee W, Kang S, Shin H. Sludge characteristics and their contribution to microfiltration in submerged membrane bioreactors. Journal of Membrane Science, 2003, 216(122): 217-227.
    [123] Gao M.C, Yang M, Li H.Y, et al. Nitrification and sludge characteristics in a submerged membrane bioreaetor on synthetic in organic wastewater. Desalination, 2004, 170: 177-185.

© 2004-2018 中国地质图书馆版权所有 京ICP备05064691号 京公网安备11010802017129号

地址:北京市海淀区学院路29号 邮编:100083

电话:办公室:(+86 10)66554848;文献借阅、咨询服务、科技查新:66554700