CN101633545B - Integrated bio-ecological collaborative sewage treatment method and reactor - Google Patents
Integrated bio-ecological collaborative sewage treatment method and reactor Download PDFInfo
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- 239000010865 sewage Substances 0.000 title claims abstract description 39
- 238000000034 method Methods 0.000 title claims abstract description 25
- 238000004659 sterilization and disinfection Methods 0.000 claims abstract description 36
- XLYOFNOQVPJJNP-UHFFFAOYSA-N water Substances O XLYOFNOQVPJJNP-UHFFFAOYSA-N 0.000 claims abstract description 33
- XEEYBQQBJWHFJM-UHFFFAOYSA-N Iron Chemical compound [Fe] XEEYBQQBJWHFJM-UHFFFAOYSA-N 0.000 claims abstract description 18
- 238000005273 aeration Methods 0.000 claims abstract description 14
- 239000010802 sludge Substances 0.000 claims abstract description 10
- 229910052742 iron Inorganic materials 0.000 claims abstract description 9
- 238000006243 chemical reaction Methods 0.000 claims description 20
- 239000000945 filler Substances 0.000 claims description 17
- IJGRMHOSHXDMSA-UHFFFAOYSA-N Atomic nitrogen Chemical compound N#N IJGRMHOSHXDMSA-UHFFFAOYSA-N 0.000 claims description 14
- OAICVXFJPJFONN-UHFFFAOYSA-N Phosphorus Chemical compound [P] OAICVXFJPJFONN-UHFFFAOYSA-N 0.000 claims description 14
- 229910052698 phosphorus Inorganic materials 0.000 claims description 14
- 239000011574 phosphorus Substances 0.000 claims description 14
- 238000005192 partition Methods 0.000 claims description 9
- 239000000758 substrate Substances 0.000 claims description 9
- 230000002195 synergetic effect Effects 0.000 claims description 9
- 229910052757 nitrogen Inorganic materials 0.000 claims description 7
- 239000005416 organic matter Substances 0.000 claims description 7
- 244000005700 microbiome Species 0.000 claims description 5
- OYPRJOBELJOOCE-UHFFFAOYSA-N Calcium Chemical compound [Ca] OYPRJOBELJOOCE-UHFFFAOYSA-N 0.000 claims description 4
- 239000011575 calcium Substances 0.000 claims description 4
- 229910052791 calcium Inorganic materials 0.000 claims description 4
- 239000000645 desinfectant Substances 0.000 claims description 4
- 230000001360 synchronised effect Effects 0.000 claims description 4
- 239000002131 composite material Substances 0.000 claims description 2
- 230000015556 catabolic process Effects 0.000 claims 1
- 238000010276 construction Methods 0.000 claims 1
- 238000006731 degradation reaction Methods 0.000 claims 1
- 239000003814 drug Substances 0.000 claims 1
- 229940079593 drug Drugs 0.000 claims 1
- 238000005265 energy consumption Methods 0.000 abstract description 7
- 238000000926 separation method Methods 0.000 abstract description 5
- 239000000725 suspension Substances 0.000 abstract description 2
- 241000196324 Embryophyta Species 0.000 description 6
- 238000001914 filtration Methods 0.000 description 3
- 238000004062 sedimentation Methods 0.000 description 3
- 238000005516 engineering process Methods 0.000 description 2
- 239000007788 liquid Substances 0.000 description 2
- 241000931336 Chloris truncata Species 0.000 description 1
- 240000001398 Typha domingensis Species 0.000 description 1
- QVGXLLKOCUKJST-UHFFFAOYSA-N atomic oxygen Chemical compound [O] QVGXLLKOCUKJST-UHFFFAOYSA-N 0.000 description 1
- 238000006065 biodegradation reaction Methods 0.000 description 1
- 230000007812 deficiency Effects 0.000 description 1
- 230000000694 effects Effects 0.000 description 1
- 230000002708 enhancing effect Effects 0.000 description 1
- 230000007613 environmental effect Effects 0.000 description 1
- 239000003344 environmental pollutant Substances 0.000 description 1
- 238000004519 manufacturing process Methods 0.000 description 1
- 230000000813 microbial effect Effects 0.000 description 1
- 230000001546 nitrifying effect Effects 0.000 description 1
- 229910052760 oxygen Inorganic materials 0.000 description 1
- 239000001301 oxygen Substances 0.000 description 1
- 238000012856 packing Methods 0.000 description 1
- 231100000719 pollutant Toxicity 0.000 description 1
- 238000001556 precipitation Methods 0.000 description 1
- 238000010992 reflux Methods 0.000 description 1
- 238000001179 sorption measurement Methods 0.000 description 1
- 238000003756 stirring Methods 0.000 description 1
- 230000032258 transport Effects 0.000 description 1
- 230000001228 trophic effect Effects 0.000 description 1
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- Y—GENERAL TAGGING OF NEW TECHNOLOGICAL DEVELOPMENTS; GENERAL TAGGING OF CROSS-SECTIONAL TECHNOLOGIES SPANNING OVER SEVERAL SECTIONS OF THE IPC; TECHNICAL SUBJECTS COVERED BY FORMER USPC CROSS-REFERENCE ART COLLECTIONS [XRACs] AND DIGESTS
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- Y02W—CLIMATE CHANGE MITIGATION TECHNOLOGIES RELATED TO WASTEWATER TREATMENT OR WASTE MANAGEMENT
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- Y02W10/10—Biological treatment of water, waste water, or sewage
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Abstract
Description
技术领域technical field
本发明属于污水处理、环境保护技术领域,具体涉及一种一体化生物生态协同污水处理反应器。The invention belongs to the technical fields of sewage treatment and environmental protection, and in particular relates to an integrated bio-ecological collaborative sewage treatment reactor.
背景技术Background technique
常规城市污水处理设施投资大、运行费用高、运行管理复杂,很难在小城镇推广。近年来,用于小城镇污水处理的反应器技术发展迅速,例如中国专利先后公开的CN2811278Y “六维三相生物处理工艺装置”、CN1552644“一种小城镇污水处理工艺”和CN2780751“折流湿地滤池+侧向潜流湿地床污水处理系统”等等,前两者为生物反应器,与本反应器的生物生态协同处理不同,为了达到较高的处理效能,其工艺流程较长,结构较复杂,且能耗较大,不利于小城镇污水处理反应器的运行管理;后者为连续流人工湿地处理系统,与本反应器中的间歇流生态处理池有较大不同,本生态处理池采用序批式运行方式并具有高效过滤沉淀区及除磷脱氮作用。此外,后者存在占地面积大的问题。而本生态处理池效能高,占地面积小,国内外尚未见有关于一体化生物生态协同污水处理反应器的报道。Conventional urban sewage treatment facilities require large investment, high operating costs, and complex operation and management, making it difficult to promote them in small towns. In recent years, the reactor technology for small town sewage treatment has developed rapidly, such as CN2811278Y "six-dimensional three-phase biological treatment process device", CN1552644 "a small town sewage treatment process" and CN2780751 "baffled wetland" published in Chinese patents filter + lateral subsurface flow wetland bed sewage treatment system" and so on, the first two are bioreactors, which are different from the biological and ecological synergistic treatment of this reactor. In order to achieve higher treatment efficiency, the process flow is longer and the structure is relatively It is complex and consumes a lot of energy, which is not conducive to the operation and management of small town sewage treatment reactors; the latter is a continuous flow artificial wetland treatment system, which is quite different from the intermittent flow ecological treatment pool in this reactor. It adopts the sequence batch operation mode and has the functions of high-efficiency filtration and precipitation area and phosphorus and nitrogen removal. In addition, the latter has the problem of occupying a large area. However, this ecological treatment pool has high efficiency and a small footprint, and there is no report about an integrated bio-ecological collaborative sewage treatment reactor at home and abroad.
发明内容Contents of the invention
针对现有小城镇污水处理工艺存在的不足,本发明的目的是提供一种一体化生物生态协同污水处理方法及反应器,将生物处理与生态处理有机结合,以达到简化处理工艺、减少投资、增强反应器处理效能、降低处理成本和减少占地的目的。In view of the deficiencies in the existing small town sewage treatment process, the purpose of the present invention is to provide an integrated bio-ecological synergistic sewage treatment method and reactor, which organically combines biological treatment and ecological treatment to simplify the treatment process, reduce investment, The purpose of enhancing the treatment efficiency of the reactor, reducing the treatment cost and reducing the land occupation.
本发明目的实现的技术方案如下:The technical scheme that the object of the present invention realizes is as follows:
一体化生物生态协同污水处理方法,所述方法过程为:An integrated bio-ecological collaborative sewage treatment method, the method process is:
(1)生物处理:利用具有多格结构的生物处理池,采用并联序批式运行方式,单格生物处理池周期运行方式为进水—反应—沉淀—出水,并联运行;首先将污水依次送入设置有悬浮填料和微孔曝气装置的生物处理池内,在间歇曝气环境下进行好氧缺氧厌氧交替运行,通过微生物对污水进行有机物降解、同步硝化反硝化脱氮及除磷生物处理;(1) Biological treatment: Utilize the biological treatment tank with multi-cell structure, adopt the parallel sequential batch operation mode, and the cycle operation mode of the single-cell biological treatment tank is water inlet-reaction-precipitation-water outlet, parallel operation; firstly, the sewage is sent to Enter the biological treatment tank equipped with suspended fillers and microporous aeration devices, and perform alternate aerobic and anoxic anaerobic operations in an intermittent aeration environment, and use microorganisms to degrade organic matter in sewage, synchronous nitrification and denitrification denitrification and phosphorus removal biological deal with;
(2)生态处理:上述序批式生物处理池的出水轮流进入设置富铁填料并种植水生植物的按序批式方式运行的生态处理池中,生态处理池也具有多格结构,多格生态池采用并联运行,每一格生态处理池的周期运行方式为进水—反应—出水—排空闲置,利用富铁富钙基质、基质上的微生物、水生植物进一步去除有机物并除磷脱氮;(2) Ecological treatment: the effluent of the above-mentioned sequential batch biological treatment tanks enters the ecological treatment tanks in sequence batch mode in which iron-rich fillers are set and aquatic plants are planted in turn. The ecological treatment tanks also have a multi-cell structure, and the multi-cell ecological The pools are operated in parallel, and the cycle operation mode of each ecological treatment pool is water intake-reaction-outlet-drainage, using iron-rich and calcium-rich substrates, microorganisms on the substrates, and aquatic plants to further remove organic matter and remove phosphorus and nitrogen;
(3)消毒处理:生态处理池的出水流入消毒接触池中,利用消毒药剂进行消毒,处理后的污水排放附近水体。(3) Disinfection treatment: the effluent from the ecological treatment pool flows into the disinfection contact pool, where it is disinfected with disinfectants, and the treated sewage is discharged into nearby water bodies.
实现上述方法的一体化生物生态协同污水处理反应器结构如下:它包括生物处理池、生态处理池、消毒池、管道系统及附属设备,所述生物处理池池体内设置隔墙,将池体分隔为多格:中心一格为鼓风机间,用于安置鼓风机;周围其余格为生物处理池,各反应池中设有悬浮填料。生物反应池各格均有独立的进、出水管和鼓风曝气系统,可使一体化生物生态协同污水处理反应器实现序批式运行方式,各池底部均设有排泥管,可定期从各反应池沉淀分离区排泥,出水排至所述生态处理池。所述生态处理池及消毒池环绕生物处理池且与其共壁,可实现序批式运行。生态处理池由隔墙分为至少两格,各格中设置富铁填料并种植水生植物,且池底设置生态处理池集水管;所述消毒接触池内由隔墙分隔为溶药投药区和消毒接触区,溶药投药区内设置折流挡墙,延长消毒接触时间,水流末端设置消毒接触池出水管,将处理后的污水排放附近水体。The structure of the integrated bio-ecological synergistic sewage treatment reactor that realizes the above method is as follows: it includes a biological treatment pool, an ecological treatment pool, a disinfection pool, a piping system and ancillary equipment, and a partition wall is set in the body of the biological treatment pool to separate the pool body There are multiple grids: the center grid is the blower room, which is used to place the blower; the rest of the surrounding grids are biological treatment tanks, and suspended fillers are installed in each reaction tank. Each compartment of the biological reaction tank has independent water inlet and outlet pipes and blast aeration system, which can make the integrated bio-ecological collaborative sewage treatment reactor realize the sequential batch operation mode. There are mud discharge pipes at the bottom of each tank, which can be used regularly Sludge is discharged from the sedimentation and separation area of each reaction tank, and the effluent is discharged to the ecological treatment tank. The ecological treatment pool and the disinfection pool surround the biological treatment pool and have the same wall as the biological treatment pool, so that batch operation can be realized. The ecological treatment pool is divided into at least two compartments by a partition wall, each compartment is provided with iron-rich filler and planted with aquatic plants, and the bottom of the pool is provided with an ecological treatment pool collection pipe; the disinfection contact pool is separated by a partition wall into a dissolving and dosing area and a disinfection area. In the contact area, baffle walls are set in the drug-dissolving and dosing area to prolong the disinfection contact time, and the outlet pipe of the disinfection contact pool is set at the end of the water flow to discharge the treated sewage into nearby water bodies.
与现有技术比较,本发明具有以下特点:Compared with the prior art, the present invention has the following characteristics:
①生物生态协同处理反应器处理效能高、出水水质稳定①Bio-ecological synergistic treatment reactor has high treatment efficiency and stable effluent quality
本反应器由于采用生物膜工艺方式(即池内设置悬浮填料),反应器具有较高的微生物浓度,耐冲击负荷及适应性强;通过在生物处理池中设置组合填料,并控制适宜的溶解氧水平,可以在生物膜内部形成好氧和缺氧微环境,易于实现高效的同步硝化反硝化脱氮。同时,反应器采用序批式运行,并且通过间歇曝气可在反应池中实现好氧缺氧厌氧交替运行,为生物膜除磷构建了良好的环境。此外,通过生态协同处理在人工湿地系统中利用富铁富钙基质、基质上的微生物、水生植物进一步除磷脱氮,并通过湿地基质层的过滤作用,保证了反应器获得较高的处理效能和稳定的出水水质。Because the reactor adopts the biofilm process (that is, the suspended filler is set in the tank), the reactor has a high microbial concentration, strong impact load resistance and adaptability; by setting the combined filler in the biological treatment tank and controlling the appropriate dissolved oxygen Level, aerobic and anoxic microenvironments can be formed inside the biofilm, and it is easy to realize efficient simultaneous nitrification and denitrification denitrification. At the same time, the reactor adopts sequential batch operation, and the aerobic-anoxic-anaerobic alternate operation can be realized in the reaction tank through intermittent aeration, which creates a good environment for biofilm phosphorus removal. In addition, through ecological synergistic treatment, iron-rich and calcium-rich substrates, microorganisms on the substrates, and aquatic plants are used to further remove phosphorus and nitrogen in the constructed wetland system, and through the filtration of the wetland substrate layer, the reactor can obtain higher treatment efficiency. and stable effluent quality.
②运行灵活,能耗低②Flexible operation and low energy consumption
通常污水处理过程中的能耗费用占其运行成本的比例较大,降低能耗是降低运行成本的关键所在。一般污水处理过程的能耗主要用于污水的提升、曝气、以及硝化液和污泥的回流。本反应器通过在生物池中设置悬浮填料,可实现高效的同步硝化反硝化,省去了混合液回流系统。同时,采用序批式运行方式和通过控制曝气方式在反应池内实现好氧缺氧厌氧交替运行,为生物膜法高效除磷构建了良好的环境,省去了一般除磷系统的污泥回流系统。并且,采用生物膜法构建该处理系统,省去了一般反应器在厌氧释磷和缺氧反硝化过程中所需的搅拌装置。此外,采用无能耗的生态协同处理进一步提升了处理效能,也为出水水质的稳定提供了保障。并且在温度高的季节,通过对生物池及生态池的工况调整,可以实现以生态处理为主,生物处理为辅,进一步减少运行能耗。因此该反应器具有高效低耗的特征。Usually, the energy consumption in the process of sewage treatment accounts for a relatively large proportion of its operating cost, and reducing energy consumption is the key to reducing operating costs. The energy consumption in the general sewage treatment process is mainly used for the lifting of sewage, aeration, and the return of nitrifying liquid and sludge. The reactor can realize high-efficiency synchronous nitrification and denitrification by setting suspended packing in the biological pool, and the mixed liquid reflux system is omitted. At the same time, aerobic-anoxic-anaerobic alternate operation is realized in the reaction tank by adopting the sequential batch operation mode and controlling the aeration mode, which builds a good environment for the efficient phosphorus removal by the biofilm method, and saves the sludge of the general phosphorus removal system Return system. Moreover, the biofilm method is used to construct the treatment system, which saves the stirring device required by the general reactor in the process of anaerobic phosphorus release and anoxic denitrification. In addition, the use of ecological collaborative processing without energy consumption further improves the processing efficiency and also provides a guarantee for the stability of the effluent water quality. And in seasons with high temperatures, by adjusting the working conditions of biological pools and ecological pools, it is possible to focus on ecological treatment, supplemented by biological treatment, and further reduce operating energy consumption. Therefore, the reactor has the characteristics of high efficiency and low consumption.
③剩余污泥量少③Less residual sludge
在生物处理池中设置悬浮填料形成稳定的由多个营养级组成的复合生态系统,减少了污泥产量。另一方面,生态协同处理部分几乎不产生剩余污泥。The suspended filler is set in the biological treatment tank to form a stable complex ecosystem composed of multiple trophic levels, which reduces the sludge production. On the other hand, the ecological co-processing part hardly produces excess sludge.
④工艺流程短、一体化设计、占地少、投资低④Short process flow, integrated design, less land occupation and low investment
本反应器集水量调节、有机物去除、生物除磷脱氮、污泥减量、沉淀及生态处理及消毒等工艺单元为一体,特别是利用反应器共壁,将鼓风机房与生物处理池构建成一体,将生态处理单元与生物处理池及消毒池构建成一体,大大减少了反应器的投资及占地。进出水可采间歇流及多组并联运行,具有操作管理灵活方便的特点。The reactor integrates process units such as water volume adjustment, organic matter removal, biological phosphorus and nitrogen removal, sludge reduction, sedimentation, ecological treatment, and disinfection. In particular, the blower room and the biological treatment pool are constructed by using the same wall of the reactor. Integrated, the ecological treatment unit is integrated with the biological treatment pool and disinfection pool, which greatly reduces the investment and land occupation of the reactor. Inlet and outlet water can adopt intermittent flow and multiple groups of parallel operation, which has the characteristics of flexible and convenient operation and management.
⑤集生物生态处理为一体,景观效果良好⑤ Integrating biological and ecological treatment into one, the landscape effect is good
附图说明Description of drawings
图1:一体化生物生态污水处理反应器平面图;Figure 1: Plane view of integrated bio-ecological sewage treatment reactor;
图2:一体化生物生态污水处理反应器剖面图;Figure 2: Sectional view of integrated bio-ecological sewage treatment reactor;
具体实施方式Detailed ways
参见图1、图2,反应器包括生物处理池1、生态处理池2、消毒接触池3、生物池处理池进水管4、生物处理池出水管5、生态处理池出水集水管6、消毒接触池出水管7、排泥管8和鼓风机9等。所述生物处理池1内竖向设置四面第一隔墙10,将生物处理池1分隔为五格,其中心一格作为鼓风机间11,其中布置鼓风机9,通过空气管12向生物处理池中的微孔曝气头15提供空气。其余四格为生物反应池,各池内设悬浮填料14(具体为球形半软性组合填料)。所述生物池处理池进水管4设于生物处理池1的上方分别通进各格生物反应池。各格生物反应池底部布置微孔曝气头15,且各池底部做下凹结构,形成泥斗16,并设有排泥管8,定期在各反应池沉淀分离一定时段后排泥。在所述四格生物池均有出水管5,将处理后的污水排入生态处理池2。所述生态处理池2与所述生物处理池1共壁,环绕于其外,且与其串联运行,该池内竖向设置第二隔墙17,将生态处理池2分隔为两格生态反应池,每格生态反应池填充基质,并栽种水生植物水香蒲、美人焦及风车草。各格生态反应池均设有生态处理池出水集水管6,将处理后的污水收集输送至消毒接触池3。所述消毒接触池3由第三隔墙19分隔为溶药投药区20和消毒接触区21,消毒药剂在溶药投药区20内溶解混合后通过投药管22将投加入消毒接触区21,消毒接触区21内设置折流导流墙防止短流,延长消毒接触时间,消毒接触区21的水流末端设置消毒接触池出水管7,将处理后的污水排放附近水体。Referring to Fig. 1 and Fig. 2, the reactor includes
本反应器的水处理过程如下:污水首先依次进入四格并联运行的生物处理池,每格生物处理池按序批式(进水—反应—沉淀—出水)方式周期运行;污水中的有机物、氮磷等污染物质通过生物降解、吸附作用得以去除。本发明采用生物膜处理技术,通过在反应器中设置悬浮球型半软性填料,可以在生物膜内部形成丰富的好氧缺氧微环境,易于实现高效的同步硝化反硝化脱氮。同时,反应器采用序批式运行,通过对工况的控制可在反应池中实现好氧缺氧厌氧交替运行,为生物膜除磷构建了良好的环境。生物处理池出水轮流进入外部的两格并联运行的生态反应池(即人工湿地系统),每格生态处理池按序批式(进水—反应—出水—排空闲置)方式周期运行;生态处理池利用富铁富钙填料、微生物及水生植物强化去除有机物和氮磷,并通过人工基质的过滤作用去除悬浮物保证了系统的处理效能。最后经生态处理池处理水还要流入消毒接触池,利用消毒药剂进行消毒,最后再排放附近水体。The water treatment process of this reactor is as follows: the sewage first enters the biological treatment tanks operated in parallel with four grids in turn, and each biological treatment tank is operated periodically in a sequential batch mode (water intake-reaction-precipitation-water outlet); the organic matter in the sewage, Pollutants such as nitrogen and phosphorus are removed through biodegradation and adsorption. The invention adopts the biofilm treatment technology, and by setting the suspended spherical semi-soft filler in the reactor, a rich aerobic and anoxic microenvironment can be formed inside the biofilm, and it is easy to realize efficient synchronous nitrification and denitrification denitrification. At the same time, the reactor adopts sequential batch operation. Through the control of the working conditions, the alternating operation of aerobic, anoxic and anaerobic can be realized in the reaction tank, which creates a good environment for biofilm phosphorus removal. The effluent of the biological treatment tank enters the two external ecological reaction tanks running in parallel in turn (that is, the artificial wetland system), and each ecological treatment tank operates periodically in a sequential batch mode (water intake-reaction-outlet-drainage); ecological treatment The pool uses iron-rich and calcium-rich fillers, microorganisms and aquatic plants to strengthen the removal of organic matter, nitrogen and phosphorus, and removes suspended matter through the filtration of artificial substrates to ensure the treatment efficiency of the system. Finally, the treated water in the ecological treatment pool also flows into the disinfection contact pool, where it is disinfected with disinfectants, and finally discharged into nearby water bodies.
主要技术参数:The main technical parameters:
COD容积负荷:生物处理池COD容积负荷为1.0kgCOD/m3.dCOD volume load: the COD volume load of the biological treatment tank is 1.0kgCOD/m 3 .d
结构参数:Structural parameters:
一体化反应器规格(L×B×H):(L、B、H分别代表长、宽、高)Integrated reactor specification (L×B×H): (L, B, H represent length, width and height respectively)
反应区有效水深H1=H-0.5(m)Effective water depth in reaction zone H 1 =H-0.5(m)
反应池有效容积V=Q/m×n×M(m3)(Q为Quantity的简写,即流量,单位:m3/d,m为排水比,n为单格生物反应池每天反应周期数,M为生物反应池格数)The effective volume of the reaction tank V=Q/m×n×M(m 3 ) (Q is the abbreviation of Quantity, that is, the flow rate, unit: m 3 /d, m is the drainage ratio, and n is the number of reaction cycles per day in the single-cell biological reaction tank , M is the number of cells in the biological reaction tank)
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CN102633366A (en) * | 2012-05-03 | 2012-08-15 | 重庆大学 | Mountainous urban artificial wetland sewage treatment system capable of controlling methane emission |
CN105060658B (en) * | 2015-09-17 | 2017-04-12 | 安徽省环境科学研究院 | Multistage combined ecological filter for treating domestic wastewater of villages and towns |
CN105174483B (en) * | 2015-10-21 | 2017-04-19 | 北京华凌时代科技发展有限公司 | Integrated biological sewage treatment system |
CN105601030B (en) * | 2015-12-19 | 2018-09-11 | 湖南科技大学 | A kind of sewage-treatment plant and technique of the operation of cycle sequence batch |
CN106007252A (en) * | 2016-07-28 | 2016-10-12 | 南京德磊科技有限公司 | Advanced oxidation and multistage biochemical combination waste water treatment system and technological method |
CN106082440A (en) * | 2016-07-28 | 2016-11-09 | 南京德磊科技有限公司 | A kind of biochemical sewage treatment device and multi-stage sewage processing system |
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Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
WO2003042114A1 (en) * | 2001-11-14 | 2003-05-22 | Dharma Living Systems, Inc. | Integrated hydroponic and fixed-film wastewater treatment systems and associated methods |
CN101037264A (en) * | 2007-02-12 | 2007-09-19 | 重庆大学 | Intermission type artificial marsh sewage treating method and sewage treating system |
CN101182070A (en) * | 2007-12-17 | 2008-05-21 | 宁波德安生态环保工程有限公司 | Biological-ecological composite sewage water treatment tank |
CN101264973A (en) * | 2008-04-15 | 2008-09-17 | 南京圣卡孚科技有限公司 | Biological composite bed technique for treating water |
CN201458913U (en) * | 2009-08-13 | 2010-05-12 | 重庆大学 | An integrated bio-ecological collaborative sewage treatment reactor |
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Publication number | Priority date | Publication date | Assignee | Title |
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CN101037264A (en) * | 2007-02-12 | 2007-09-19 | 重庆大学 | Intermission type artificial marsh sewage treating method and sewage treating system |
CN101182070A (en) * | 2007-12-17 | 2008-05-21 | 宁波德安生态环保工程有限公司 | Biological-ecological composite sewage water treatment tank |
CN101264973A (en) * | 2008-04-15 | 2008-09-17 | 南京圣卡孚科技有限公司 | Biological composite bed technique for treating water |
CN201458913U (en) * | 2009-08-13 | 2010-05-12 | 重庆大学 | An integrated bio-ecological collaborative sewage treatment reactor |
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