CN204417280U - The device of Biological Pretreatment and film coupling integral system process villages and small towns tap water - Google Patents
The device of Biological Pretreatment and film coupling integral system process villages and small towns tap water Download PDFInfo
- Publication number
- CN204417280U CN204417280U CN201420579637.6U CN201420579637U CN204417280U CN 204417280 U CN204417280 U CN 204417280U CN 201420579637 U CN201420579637 U CN 201420579637U CN 204417280 U CN204417280 U CN 204417280U
- Authority
- CN
- China
- Prior art keywords
- water
- biological
- membrane
- pipeline
- water outlet
- Prior art date
- Legal status (The legal status is an assumption and is not a legal conclusion. Google has not performed a legal analysis and makes no representation as to the accuracy of the status listed.)
- Expired - Fee Related
Links
- 230000008878 coupling Effects 0.000 title claims abstract description 8
- 238000010168 coupling process Methods 0.000 title claims abstract description 8
- 238000005859 coupling reaction Methods 0.000 title claims abstract description 8
- 230000026676 system process Effects 0.000 title abstract 2
- 239000008399 tap water Substances 0.000 title abstract 2
- 235000020679 tap water Nutrition 0.000 title abstract 2
- XLYOFNOQVPJJNP-UHFFFAOYSA-N water Substances O XLYOFNOQVPJJNP-UHFFFAOYSA-N 0.000 claims abstract description 89
- 239000012528 membrane Substances 0.000 claims abstract description 62
- 238000006243 chemical reaction Methods 0.000 claims abstract description 10
- 239000010802 sludge Substances 0.000 claims abstract description 9
- 239000003651 drinking water Substances 0.000 claims description 19
- 235000020188 drinking water Nutrition 0.000 claims description 19
- 239000012510 hollow fiber Substances 0.000 claims description 19
- 238000005273 aeration Methods 0.000 claims description 13
- 230000003750 conditioning effect Effects 0.000 claims 2
- 239000000835 fiber Substances 0.000 abstract description 7
- PXGOKWXKJXAPGV-UHFFFAOYSA-N Fluorine Chemical compound FF PXGOKWXKJXAPGV-UHFFFAOYSA-N 0.000 abstract description 5
- 229910052731 fluorine Inorganic materials 0.000 abstract description 5
- 239000011737 fluorine Substances 0.000 abstract description 5
- 241000894006 Bacteria Species 0.000 abstract description 4
- 201000010099 disease Diseases 0.000 abstract description 2
- 208000037265 diseases, disorders, signs and symptoms Diseases 0.000 abstract description 2
- 238000011010 flushing procedure Methods 0.000 abstract description 2
- 238000007906 compression Methods 0.000 abstract 4
- 230000001105 regulatory effect Effects 0.000 abstract 3
- 230000008595 infiltration Effects 0.000 abstract 2
- 238000001764 infiltration Methods 0.000 abstract 2
- 238000010992 reflux Methods 0.000 abstract 2
- 208000015181 infectious disease Diseases 0.000 abstract 1
- 230000002458 infectious effect Effects 0.000 abstract 1
- 238000000034 method Methods 0.000 description 15
- 230000008569 process Effects 0.000 description 12
- 238000005516 engineering process Methods 0.000 description 9
- 239000003344 environmental pollutant Substances 0.000 description 9
- 231100000719 pollutant Toxicity 0.000 description 9
- 239000005416 organic matter Substances 0.000 description 8
- 230000000694 effects Effects 0.000 description 7
- 239000002245 particle Substances 0.000 description 7
- 239000000126 substance Substances 0.000 description 7
- 238000001914 filtration Methods 0.000 description 6
- 244000052616 bacterial pathogen Species 0.000 description 5
- 238000011001 backwashing Methods 0.000 description 4
- 230000007246 mechanism Effects 0.000 description 4
- 244000005700 microbiome Species 0.000 description 4
- 239000011148 porous material Substances 0.000 description 4
- 238000000746 purification Methods 0.000 description 4
- 238000004659 sterilization and disinfection Methods 0.000 description 4
- 239000006227 byproduct Substances 0.000 description 3
- 239000000701 coagulant Substances 0.000 description 3
- 238000005345 coagulation Methods 0.000 description 3
- 230000015271 coagulation Effects 0.000 description 3
- 239000000084 colloidal system Substances 0.000 description 3
- 230000014759 maintenance of location Effects 0.000 description 3
- 230000004060 metabolic process Effects 0.000 description 3
- 230000000813 microbial effect Effects 0.000 description 3
- 239000002243 precursor Substances 0.000 description 3
- 238000004062 sedimentation Methods 0.000 description 3
- 238000003911 water pollution Methods 0.000 description 3
- QJZYHAIUNVAGQP-UHFFFAOYSA-N 3-nitrobicyclo[2.2.1]hept-5-ene-2,3-dicarboxylic acid Chemical compound C1C2C=CC1C(C(=O)O)C2(C(O)=O)[N+]([O-])=O QJZYHAIUNVAGQP-UHFFFAOYSA-N 0.000 description 2
- 230000009286 beneficial effect Effects 0.000 description 2
- 238000005660 chlorination reaction Methods 0.000 description 2
- 238000005189 flocculation Methods 0.000 description 2
- 230000016615 flocculation Effects 0.000 description 2
- 239000004021 humic acid Substances 0.000 description 2
- 239000007788 liquid Substances 0.000 description 2
- 239000011159 matrix material Substances 0.000 description 2
- 238000001471 micro-filtration Methods 0.000 description 2
- 238000006386 neutralization reaction Methods 0.000 description 2
- 239000002957 persistent organic pollutant Substances 0.000 description 2
- 238000000926 separation method Methods 0.000 description 2
- 238000001179 sorption measurement Methods 0.000 description 2
- 238000010408 sweeping Methods 0.000 description 2
- 239000002351 wastewater Substances 0.000 description 2
- 208000004429 Bacillary Dysentery Diseases 0.000 description 1
- ZAMOUSCENKQFHK-UHFFFAOYSA-N Chlorine atom Chemical compound [Cl] ZAMOUSCENKQFHK-UHFFFAOYSA-N 0.000 description 1
- 206010008631 Cholera Diseases 0.000 description 1
- 208000035473 Communicable disease Diseases 0.000 description 1
- 206010017915 Gastroenteritis shigella Diseases 0.000 description 1
- 239000004743 Polypropylene Substances 0.000 description 1
- 208000037386 Typhoid Diseases 0.000 description 1
- 241000700605 Viruses Species 0.000 description 1
- 239000003905 agrochemical Substances 0.000 description 1
- 230000004888 barrier function Effects 0.000 description 1
- 238000006065 biodegradation reaction Methods 0.000 description 1
- 230000008859 change Effects 0.000 description 1
- 229910052801 chlorine Inorganic materials 0.000 description 1
- 239000000460 chlorine Substances 0.000 description 1
- 230000007423 decrease Effects 0.000 description 1
- 230000003247 decreasing effect Effects 0.000 description 1
- 238000010586 diagram Methods 0.000 description 1
- 239000005446 dissolved organic matter Substances 0.000 description 1
- 230000007613 environmental effect Effects 0.000 description 1
- 238000003912 environmental pollution Methods 0.000 description 1
- 239000003337 fertilizer Substances 0.000 description 1
- 239000012467 final product Substances 0.000 description 1
- 230000004907 flux Effects 0.000 description 1
- 230000036541 health Effects 0.000 description 1
- 229910001385 heavy metal Inorganic materials 0.000 description 1
- 239000012535 impurity Substances 0.000 description 1
- 239000010842 industrial wastewater Substances 0.000 description 1
- 239000000463 material Substances 0.000 description 1
- 230000002503 metabolic effect Effects 0.000 description 1
- 229910021645 metal ion Inorganic materials 0.000 description 1
- 239000008239 natural water Substances 0.000 description 1
- 238000012856 packing Methods 0.000 description 1
- 239000012466 permeate Substances 0.000 description 1
- 239000000575 pesticide Substances 0.000 description 1
- 230000010287 polarization Effects 0.000 description 1
- 229920002492 poly(sulfone) Polymers 0.000 description 1
- -1 polypropylene Polymers 0.000 description 1
- 229920001155 polypropylene Polymers 0.000 description 1
- 238000001556 precipitation Methods 0.000 description 1
- 238000004886 process control Methods 0.000 description 1
- 230000000717 retained effect Effects 0.000 description 1
- 239000010865 sewage Substances 0.000 description 1
- 201000005113 shigellosis Diseases 0.000 description 1
- 238000007873 sieving Methods 0.000 description 1
- 239000007787 solid Substances 0.000 description 1
- 239000000758 substrate Substances 0.000 description 1
- 239000002352 surface water Substances 0.000 description 1
- 231100001234 toxic pollutant Toxicity 0.000 description 1
- 201000008297 typhoid fever Diseases 0.000 description 1
Landscapes
- Biological Treatment Of Waste Water (AREA)
- Separation Using Semi-Permeable Membranes (AREA)
Abstract
Description
技术领域 technical field
本实用新型属于环保技术领域,涉及含病菌、有机物和高氟村镇饮用水的净化技术,具体地说是一种生物预处理与膜联用一体化系统处理村镇饮用水的装置。 The utility model belongs to the field of environmental protection technology, and relates to the purification technology of drinking water in villages and towns containing germs, organic matter and high fluorine, in particular to a device for treating drinking water in villages and towns with an integrated system of biological pretreatment and membrane coupling.
背景技术 Background technique
水环境污染已成为当今世界范围内与水资源短缺并存的问题。大量工业废水和生活污水未经处理或只经简单处理便向天然水体持续排放,以及广大农村地区不合理地使用化肥、农药等农用化学物质对地表水造成的非点源污染,均导致我国水环境污染的不断加剧,水源水质不断下降。十九世纪欧美的一些城市多次爆发霍乱、伤寒、细菌性痢疾等传染病,为了有效地控制这种因水源污染而导致的疾病的蔓延,发展了过滤净水技术如慢滤技术。到二十世纪,净水技术由单一过滤逐渐发展成为混凝、沉淀、过滤和消毒的常规净水工艺。常规水处理工艺主要能去除水中悬浮固体、胶体物质和病菌;其处理工艺对水中的有机污染物有一定去除作用。常规饮用水处理工艺以出水的浊度、色度和细菌总数为工艺控制的主要目标。 Water pollution has become a problem that coexists with water shortage in the world today. A large amount of industrial wastewater and domestic sewage are continuously discharged to natural water bodies without treatment or only after simple treatment, and the non-point source pollution of surface water caused by the unreasonable use of chemical fertilizers, pesticides and other agricultural chemicals in vast rural areas has caused my country's water pollution. Environmental pollution continues to intensify, and water quality continues to decline. Cholera, typhoid, bacillary dysentery and other infectious diseases broke out in some European and American cities in the 19th century. In order to effectively control the spread of such diseases caused by water pollution, water purification technologies such as slow filtration technology were developed. By the 20th century, water purification technology has gradually developed from a single filtration to a conventional water purification process of coagulation, sedimentation, filtration and disinfection. The conventional water treatment process can mainly remove suspended solids, colloidal substances and germs in water; its treatment process has a certain effect on the removal of organic pollutants in water. In the conventional drinking water treatment process, the turbidity, color and total number of bacteria in the effluent are the main objectives of process control.
对于水质良好的水源,常规饮用水处理工艺可获得安全合格的饮用水;但随着水源水质的日益恶化,常规水处理工艺在的局限性就显示了出来。主要表现为受污染水源水经过常规混凝、沉淀以及过滤工艺只能去除水中有机物的20%~30%,而且由于溶解性有机物的存在,不利于破坏胶体的稳定性而使常规饮用水处理工艺对原水浊度去除效果也明显下降。用增加混凝剂投量的方式来改善处理效果,不仅使水处理成本上升,而且可能使水中金属离子浓度增加,不利于人体健康;常规饮用水处理工艺对水中微量有机污染物没有明显的去除效果,水中有机物数量,尤其是毒性污染物的数量,在处理前后变化不大;预氯化产生的卤代物在混凝、沉淀及过滤中不能有效去除。 For water sources with good water quality, safe and qualified drinking water can be obtained by conventional drinking water treatment processes; however, as the water quality of water sources deteriorates day by day, the limitations of conventional water treatment processes are revealed. The main manifestation is that the polluted source water can only remove 20%~30% of the organic matter in the water through conventional coagulation, sedimentation and filtration processes, and due to the presence of dissolved organic matter, it is not conducive to destroying the stability of the colloid, so that the conventional drinking water treatment process The removal effect of raw water turbidity also decreased significantly. Increasing the dosage of coagulant to improve the treatment effect will not only increase the cost of water treatment, but also may increase the concentration of metal ions in the water, which is not conducive to human health; conventional drinking water treatment processes have no obvious removal of trace organic pollutants in water As a result, the amount of organic matter in water, especially the amount of toxic pollutants, does not change much before and after treatment; halogenated substances produced by pre-chlorination cannot be effectively removed in coagulation, precipitation and filtration.
由上可见,在水源受污染情况下,由于常规饮用水处理工艺的局限性,处理后的生活饮用水安全性难以保证,已经不能与现有的水源和水质标准相适应,必须开发新的水处理工艺。为了对水源水进行安全有效处理,保证饮用水水质。 It can be seen from the above that when the water source is polluted, due to the limitations of the conventional drinking water treatment process, it is difficult to guarantee the safety of the treated drinking water, and it can no longer adapt to the existing water source and water quality standards. New water must be developed. Processing technology. In order to carry out safe and effective treatment of source water and ensure the quality of drinking water.
膜分离技术最大的特点是对水中微粒、胶体、细菌和部分病毒能彻底去除。膜分离主要是机械筛分,大于膜孔径的微粒及胶体物质不能透过,小于其孔径的物质能透过。有时,膜在阻止大于膜孔径的微粒及胶体物质时还会使它们在膜表面形成一个动态的滤层,他们对水中污染物有屏障作用,这也是膜有时能分离小于其孔径的物质的原理之一。鉴于此,膜对水中浊度和细菌有优良的去除,是取代常规给水处理非常有前景的方法之一。 The biggest feature of membrane separation technology is that it can completely remove particles, colloids, bacteria and some viruses in water. Membrane separation is mainly mechanical sieving. Particles and colloidal substances larger than the pore size of the membrane cannot pass through, while substances smaller than the pore size can pass through. Sometimes, when the membrane prevents particles and colloidal substances larger than the pore size of the membrane, they will also form a dynamic filter layer on the surface of the membrane. They have a barrier effect on pollutants in the water, which is also the principle that the membrane can sometimes separate substances smaller than its pore size. one. In view of this, the membrane has excellent removal of turbidity and bacteria in water, and is one of the very promising methods to replace conventional water treatment.
生物处理法是通过微生物的新陈代谢作用使水中污染物得以去除的技术,其优点是可以降低配水系统中微生物繁殖的有机基质、减少臭味、降低氯化消毒副产物的前体物,延长后续工艺的使用周期。缺点是基建投资大,微生物新陈代谢活性受水温影响。由于腐殖酸等天然有机物是生物分解的最终产物,不可生物降解,生物处理法往往不能单独用于去除腐殖酸。因此,迫切需要一种联用处理工艺。 Biological treatment is a technology that removes pollutants in water through the metabolism of microorganisms. Its advantages are that it can reduce the organic substrate for microbial reproduction in the water distribution system, reduce odor, reduce the precursors of chlorinated disinfection by-products, and prolong the follow-up process. life cycle. The disadvantage is that the infrastructure investment is large, and the metabolic activity of microorganisms is affected by the water temperature. Since natural organic matter such as humic acid is the final product of biodegradation and cannot be biodegraded, biological treatment often cannot be used alone to remove humic acid. Therefore, there is an urgent need for a combined treatment process.
发明内容 Contents of the invention
针对上述不足,本实用新型的目的在于提供一种生物预处理与膜联用一体化系统处理村镇饮用水的装置。由于中空纤维膜不用支撑体,有很大的填装密度,单位体积内能容纳很多的膜面积,所以本实用新型中选用HQM系列聚丙烯中空纤维膜和HQM系列改性聚砜中空纤维膜。该装置不但可以有效去除病菌、有机物和高氟等污染物,减少对村镇饮用水的污染,同时还利于装置的集约化和降低投资成本。 In view of the above shortcomings, the purpose of this utility model is to provide a device for treating drinking water in villages and towns with an integrated system of biological pretreatment and membrane coupling. Because the hollow fiber membrane does not need a support body, it has a large packing density and can accommodate a lot of membrane area per unit volume. Therefore, the utility model uses HQM series polypropylene hollow fiber membranes and HQM series modified polysulfone hollow fiber membranes. The device can not only effectively remove pollutants such as germs, organic matter and high fluorine, reduce the pollution of drinking water in villages and towns, but also facilitate the intensification of the device and reduce investment costs.
本实用新型提出的生物预处理与膜联用一体化系统处理村镇饮用水的装置,包括生物反应系统、截留回路和渗透回路,其中:生物反应系统包括进水口1、加药口2、生物转盘3、曝气管道4、污泥管道13、空气罩14和生物调节池15,所述生物调节池15顶部设有空气罩14,其内设有生物转盘3,底部设有污泥管道13和曝气管道4,从曝气管道4中释放出的压缩空气驱动空气罩14使生物转盘3转动;截留回路包括隔膜泵5、流量计6和回流管道12,渗透回路包括膜进水口7、膜出水口9和中空纤维膜外压式组件8,中空纤维膜外压式组件8底部依次通过膜进水口7、流量计6、隔膜泵5和管道连接生物调节池15顶部出水口,中空纤维膜外压式组件8顶部通过反冲洗出水口11和回流管道12连接生物调节池15,中空纤维膜外压式组件8一侧设有膜出水口9。 The utility model proposes a device for treating drinking water in villages and towns with an integrated system of biological pretreatment and membrane coupling, including a biological reaction system, an interception circuit and a permeation circuit, wherein: the biological reaction system includes a water inlet 1, a dosing port 2, and a biological turntable 3. Aeration pipeline 4, sludge pipeline 13, air cover 14 and biological adjustment tank 15, the top of the biological adjustment tank 15 is provided with air cover 14, in which a biological turntable 3 is provided, and the bottom is provided with sludge pipeline 13 and The aeration pipeline 4, the compressed air released from the aeration pipeline 4 drives the air cover 14 to rotate the biological turntable 3; the retention circuit includes a diaphragm pump 5, a flow meter 6 and a return pipeline 12, and the permeation circuit includes a membrane water inlet 7, a membrane The water outlet 9 and the hollow fiber membrane external pressure module 8, the bottom of the hollow fiber membrane external pressure module 8 is connected to the top water outlet of the biological adjustment tank 15 through the membrane water inlet 7, the flow meter 6, the diaphragm pump 5 and the pipeline, and the hollow fiber membrane The top of the external pressure module 8 is connected to the bioregulation tank 15 through the backwash water outlet 11 and the return pipe 12 , and a membrane water outlet 9 is provided on one side of the hollow fiber membrane external pressure module 8 .
本实用新型中,膜进水口7的管路上设有反冲洗进水口10,兼作出水管道。 In the utility model, the pipeline of the membrane water inlet 7 is provided with a backwash water inlet 10, which doubles as a water outlet pipeline.
本实用新型提出的生物预处理与膜联用一体化系统处理村镇饮用水的装置的操作方法,具体步骤如下: The operation method of the device for treating drinking water in villages and towns with the integrated system of biological pretreatment and membrane coupling proposed by the utility model, the specific steps are as follows:
将预处理后的村镇饮用水通过进水口流入生物调节池,根据实际运行条件调节曝气时间,通过微生物的新陈代谢作用和絮凝作用,降低配水系统中微生物繁殖的有机基质、减少臭味、降低氯化消毒副产物的前体物使水中污染物得以去除。并向生物调节池内投加混凝剂,通过压缩双电层、电性中和、网捕卷扫、吸附架桥等机理作用使水中胶体、悬浮颗粒等形成絮体,改变原水中悬浮颗粒的尺寸分布,使单独使用微滤膜无法截留的小颗粒和溶解性污染物得到有效去除,提高了处理效果和膜通量,强化去除效果,被去除的污染物沉淀到池子底部通过污泥管道排出。装置通过水泵对抽吸时间进行优化,使水样流经中空纤维膜进入下一个处理装置。为延长其使用寿命需对中空纤维膜定期进行反冲洗,收集反冲洗水回流入生物调节池,进一步处理。对中空纤维膜组件通过压力控制系统实现对运行状况的调节。 The pretreated drinking water of villages and towns flows into the bioregulation tank through the water inlet, and the aeration time is adjusted according to the actual operating conditions. Through the metabolism and flocculation of microorganisms, the organic matrix for microbial reproduction in the water distribution system is reduced, and the odor and chlorine are reduced. Precursors of disinfection by-products can be used to remove pollutants in water. And add coagulant to the biological adjustment tank, through the mechanism of compressing the double layer, electrical neutralization, net capture and sweeping, adsorption bridging and other mechanisms, the colloids and suspended particles in the water will form flocs, and the concentration of suspended particles in the raw water will be changed. The size distribution enables the effective removal of small particles and dissolved pollutants that cannot be retained by the microfiltration membrane alone, which improves the treatment effect and membrane flux, and strengthens the removal effect. The removed pollutants settle to the bottom of the pool and are discharged through the sludge pipeline. . The device optimizes the suction time through the water pump, so that the water sample flows through the hollow fiber membrane and enters the next processing device. In order to prolong its service life, the hollow fiber membrane needs to be backwashed regularly, and the backwashed water is collected and returned to the bioregulation tank for further treatment. The adjustment of the operating conditions of the hollow fiber membrane modules is realized through the pressure control system.
本实用新型中,废水的预处理是指:过滤、沉淀去除废水中的悬浮杂质。 In the utility model, the pretreatment of waste water refers to: filtering and sedimentation to remove suspended impurities in waste water.
本实用新型中,所述污染物是指病菌、有机物和高氟中的至少一种。 In the utility model, the pollutant refers to at least one of germs, organic matter and high fluorine.
本实用新型的有益效果在于:The beneficial effects of the utility model are:
本实用新型与现有技术相比,显著优点是:膜技术与生物预处理工艺结合联用,用以降低膜的处理负荷,提高对水中病菌、有机物和高氟等的去除效果,有效控制出水浊度,保障出水的生物安全性,有巨大的技术和经济优势。 Compared with the prior art, the utility model has the remarkable advantages that the combination of membrane technology and biological pretreatment process is used to reduce the processing load of the membrane, improve the removal effect of germs, organic matter and high fluorine in water, and effectively control the effluent Turbidity, ensuring the biological safety of the effluent, has huge technical and economic advantages.
附图说明 Description of drawings
图1为本实用新型的装置示意图。 Fig. 1 is the device schematic diagram of the present utility model.
图中标号:1为进水口,2为加药口,3为生物转盘,4为曝气管道,5为隔膜泵,6为流量计,7为膜进水口,8为中空纤维膜外压式组件,9为膜出水口,10为反冲洗进水口,11为反冲洗出水口,12为截留回路管道,13为污泥管道,14为空气罩,15为生物调节池。 Numbers in the figure: 1 is the water inlet, 2 is the dosing port, 3 is the biological turntable, 4 is the aeration pipe, 5 is the diaphragm pump, 6 is the flow meter, 7 is the membrane water inlet, 8 is the hollow fiber membrane external pressure type 9 is the membrane water outlet, 10 is the backwash water inlet, 11 is the backwash water outlet, 12 is the retention circuit pipe, 13 is the sludge pipe, 14 is the air cover, and 15 is the biological adjustment tank.
具体实施方式 Detailed ways
以下通过实施例进一步说明本实用新型: Below further illustrate the utility model by embodiment:
实施例1:如图1所示,所述装置包括生物反应系统、截留回路、渗透回路,其中生物反应系统包括进水口1,加药口2,生物转盘3,曝气管道4,污泥管道13,空气罩14和生物调节池15,从曝气管道4中释放出的压缩空气驱动空气罩14使生物转盘3转动。截留区包括隔膜泵5,流量计6和回流管道12,渗透区包括膜进水口7,膜出水口9和中空纤维膜外压式组件8,用于分离污染物,反冲洗出水口11,反冲洗进水口10,。膜系统运行时需要压力控制系统调节。 Embodiment 1: As shown in Figure 1, the device includes a biological reaction system, a retaining circuit, and a permeation circuit, wherein the biological reaction system includes a water inlet 1, a dosing port 2, a biological turntable 3, an aeration pipeline 4, and a sludge pipeline 13, the air cover 14 and the biological adjustment tank 15, the compressed air released from the aeration pipeline 4 drives the air cover 14 to make the biological turntable 3 rotate. The retention area includes a diaphragm pump 5, a flow meter 6 and a return pipeline 12, and the permeation area includes a membrane water inlet 7, a membrane water outlet 9 and a hollow fiber membrane external pressure module 8 for separating pollutants, backwashing water outlet 11, reverse Rinse the water inlet 10'. When the membrane system is running, it needs to adjust the pressure control system.
采用上述装置向反应系统中加入村镇饮用水: Use the above-mentioned device to add village and town drinking water to the reaction system:
村镇饮用水从进水口1流入生物调节池15,根据实际运行条件调节曝气管道4的曝气时间,从曝气管中释放出的压缩空气驱动空气罩14使生物转盘3转动,在生物转盘3上通过微生物的新陈代谢作用和絮凝作用,降低配水系统中微生物繁殖的有机基质、减少臭味、降低氯化消毒副产物的前体物使水中污染物得以去除,同时向加药口2投入混凝药剂,通过压缩双电层、电性中和、网捕卷扫、吸附架桥等机理作用使悬浮颗粒,小分子有机物,重金属等形成絮体沉积到池底通过污泥管道13排出。一段时间后打开出水阀和隔膜泵5,通过隔膜泵5推动装置中的循环流动,水样通过流量计6进入中空纤维膜外压式组件8,水样从膜进水口7经含6通道分布的中心管口进水,在中空纤维膜外压式组件8内呈平流状经膜表面错流,可滤过物质在压力差推动下透过中空纤维膜壁进入纤维内孔成为超滤液,再经集流从膜出水口9流出进入下一个处理装置,其余则被浓缩成浓缩液经组件壳体另一端含6孔道分布的中心分配管汇集口的截留回路管道12流出,进入生物反应区。由于纤维呈规则的自然集束,原液在纤维间流动时,在比较高的流速下呈高度错流状态,对克服膜表面滞流层的浓差极化更有利,耐污量(耐污空间)更大,能够适应更宽广的进水水质或进料条件,减少预处理工艺及其成本,微滤透过液无死角。并在该装置中为了解决堵塞和反冲洗的困难,配套设计了全自动的反冲洗装置,在膜进水口7处关闭左侧阀门,清水从反冲洗进水口10处自下而上流动,反冲洗水从上部出水口经回流管道12流入生物反应区系统,完成一次循环。 The drinking water in the villages and towns flows into the biological adjustment tank 15 from the water inlet 1, and the aeration time of the aeration pipe 4 is adjusted according to the actual operating conditions. The compressed air released from the aeration pipe drives the air cover 14 to rotate the biological turntable 3. 3. Through the metabolism and flocculation of microorganisms, the organic matrix for microbial reproduction in the water distribution system is reduced, the odor is reduced, and the precursors of chlorination disinfection by-products are reduced to remove pollutants in the water. Coagulants, through the mechanism of compressing the double layer, electrical neutralization, net capture and sweeping, adsorption bridging and other mechanisms, the suspended particles, small molecular organic matter, heavy metals, etc. form flocs and deposit to the bottom of the pool and are discharged through the sludge pipeline 13. After a period of time, open the water outlet valve and the diaphragm pump 5 to promote the circulating flow in the device through the diaphragm pump 5. The water sample enters the hollow fiber membrane external pressure module 8 through the flow meter 6, and the water sample is distributed from the membrane water inlet 7 through 6 channels. The water enters the central nozzle of the hollow fiber membrane external pressure module 8 and cross-flows through the surface of the membrane in an advection manner. The filterable material is driven by the pressure difference through the hollow fiber membrane wall and enters the fiber inner hole to become an ultrafiltrate. Then it flows out from the membrane outlet 9 and enters the next treatment device through the collection, and the rest is concentrated into a concentrated liquid, which flows out through the interception circuit pipeline 12 of the central distribution pipe confluence with 6 holes distributed on the other end of the module shell, and enters the bioreaction area . Due to the regular natural bundles of the fibers, when the raw liquid flows between the fibers, it is in a highly cross-flow state at a relatively high flow rate, which is more beneficial to overcome the concentration polarization of the stagnant layer on the membrane surface, and the pollution resistance (fouling resistance space) Larger, able to adapt to wider water quality or feed conditions, reduce pretreatment process and cost, and have no dead ends for microfiltration permeate. And in this device, in order to solve the difficulties of blockage and backwashing, a fully automatic backwashing device is designed, and the left valve is closed at the membrane water inlet 7, and the clean water flows from the bottom to the top of the backwashing water inlet 10. The flushing water flows into the biological reaction zone system through the return pipe 12 from the upper water outlet to complete a cycle.
Claims (2)
Priority Applications (1)
| Application Number | Priority Date | Filing Date | Title |
|---|---|---|---|
| CN201420579637.6U CN204417280U (en) | 2014-10-09 | 2014-10-09 | The device of Biological Pretreatment and film coupling integral system process villages and small towns tap water |
Applications Claiming Priority (1)
| Application Number | Priority Date | Filing Date | Title |
|---|---|---|---|
| CN201420579637.6U CN204417280U (en) | 2014-10-09 | 2014-10-09 | The device of Biological Pretreatment and film coupling integral system process villages and small towns tap water |
Publications (1)
| Publication Number | Publication Date |
|---|---|
| CN204417280U true CN204417280U (en) | 2015-06-24 |
Family
ID=53467667
Family Applications (1)
| Application Number | Title | Priority Date | Filing Date |
|---|---|---|---|
| CN201420579637.6U Expired - Fee Related CN204417280U (en) | 2014-10-09 | 2014-10-09 | The device of Biological Pretreatment and film coupling integral system process villages and small towns tap water |
Country Status (1)
| Country | Link |
|---|---|
| CN (1) | CN204417280U (en) |
Cited By (1)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| CN105461181A (en) * | 2016-01-19 | 2016-04-06 | 清华大学 | Sewage treatment system and application thereof |
-
2014
- 2014-10-09 CN CN201420579637.6U patent/CN204417280U/en not_active Expired - Fee Related
Cited By (1)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| CN105461181A (en) * | 2016-01-19 | 2016-04-06 | 清华大学 | Sewage treatment system and application thereof |
Similar Documents
| Publication | Publication Date | Title |
|---|---|---|
| CN101219847A (en) | Integrated ultrafiltration membrane coagulation/bioreactor water purification treatment method and device | |
| CN102838227A (en) | System and method for treating industrial park recycled water to form power plant boiler supplemental water | |
| CN102417273A (en) | Dynamic membrane purification reactor and method for removing ammonia nitrogen and organic matters in reclaimed water | |
| CN104492265A (en) | Ultrafiltration membrane device with on-line medicament backwashing and blowdown device | |
| CN105645663A (en) | A water treatment method combining flocculation, counter-current ozone air floatation and biofiltration in order and a device used in the method | |
| CN101700914A (en) | Sludge circulation flocculation-membrane filtration reactor | |
| CN102633394B (en) | Integrative coagulation ultrafiltration-immersion membrane module combination water purification system | |
| CN102086079B (en) | Method and system for zero-discharge treatment of domestic sewage | |
| CN201713415U (en) | Dye wastewater treatment device | |
| CN204588956U (en) | A kind of low turbidity micro-polluted surface water advanced treatment apparatus | |
| CN202865053U (en) | Processing device for wastewater form circulating cooling water and reverse osmosis concentrated water | |
| CN205603429U (en) | Micro -polluted water source water purification system | |
| CN210122529U (en) | A kind of reverse osmosis direct drinking water purification equipment | |
| CN104587727A (en) | Multistage kieselguhr filter and filter method thereof | |
| CN204412073U (en) | A kind of ultra-filtration membrane device with online medicament backwashing blowdown function | |
| CN104261603B (en) | The integrated drinking water advanced treatment device of a kind of electric coagulation-electro-flotation/immersion ultrafiltration | |
| CN101955301B (en) | Method and equipment for treating micropollution raw water based on biological bamboo charcoal contact oxidation method | |
| CN109081477B (en) | An integrated energy-saving and emission-reducing rural water supply and purification system based on quality | |
| CN201433151Y (en) | A device for treating slightly polluted surface water | |
| CN204417280U (en) | The device of Biological Pretreatment and film coupling integral system process villages and small towns tap water | |
| CN100357202C (en) | Liquid flow type capacitance pretreatment method for sea water desalination | |
| CN103395896B (en) | Water purification equipment of special medicament for removing hardness ions in underground water | |
| CN201380045Y (en) | Mine water desalination pretreatment device and reverse osmosis desalination equipment | |
| CN2848838Y (en) | Nano-filtering membrane composite deep water purification device | |
| CN204162533U (en) | The device of coagulation-microfiltration membrane integral system process villages and small towns tap water |
Legal Events
| Date | Code | Title | Description |
|---|---|---|---|
| C14 | Grant of patent or utility model | ||
| GR01 | Patent grant | ||
| CF01 | Termination of patent right due to non-payment of annual fee | ||
| CF01 | Termination of patent right due to non-payment of annual fee |
Granted publication date: 20150624 Termination date: 20171009 |