CN205575883U - Domestic sewage treatment device - Google Patents
Domestic sewage treatment device Download PDFInfo
- Publication number
- CN205575883U CN205575883U CN201620354651.5U CN201620354651U CN205575883U CN 205575883 U CN205575883 U CN 205575883U CN 201620354651 U CN201620354651 U CN 201620354651U CN 205575883 U CN205575883 U CN 205575883U
- Authority
- CN
- China
- Prior art keywords
- tank
- sewage
- aerobic
- domestic sewage
- pool
- 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
- 239000010865 sewage Substances 0.000 title claims abstract description 59
- 238000004659 sterilization and disinfection Methods 0.000 claims abstract description 24
- XLYOFNOQVPJJNP-UHFFFAOYSA-N water Substances O XLYOFNOQVPJJNP-UHFFFAOYSA-N 0.000 claims abstract description 24
- 239000010802 sludge Substances 0.000 claims description 26
- 238000004062 sedimentation Methods 0.000 claims description 20
- 239000007788 liquid Substances 0.000 claims description 19
- 230000001105 regulatory effect Effects 0.000 claims description 16
- 238000005276 aerator Methods 0.000 claims description 8
- 238000003860 storage Methods 0.000 claims description 8
- 238000000034 method Methods 0.000 abstract description 14
- 230000000694 effects Effects 0.000 abstract description 11
- IJGRMHOSHXDMSA-UHFFFAOYSA-N Atomic nitrogen Chemical compound N#N IJGRMHOSHXDMSA-UHFFFAOYSA-N 0.000 abstract description 6
- KZBUYRJDOAKODT-UHFFFAOYSA-N Chlorine Chemical compound ClCl KZBUYRJDOAKODT-UHFFFAOYSA-N 0.000 abstract description 3
- OAICVXFJPJFONN-UHFFFAOYSA-N Phosphorus Chemical compound [P] OAICVXFJPJFONN-UHFFFAOYSA-N 0.000 abstract description 3
- 229910052757 nitrogen Inorganic materials 0.000 abstract description 3
- 229910052698 phosphorus Inorganic materials 0.000 abstract description 3
- 239000011574 phosphorus Substances 0.000 abstract description 3
- 239000002957 persistent organic pollutant Substances 0.000 abstract description 2
- 230000009466 transformation Effects 0.000 abstract description 2
- 239000000945 filler Substances 0.000 description 14
- 238000005273 aeration Methods 0.000 description 8
- 239000002351 wastewater Substances 0.000 description 8
- 239000005416 organic matter Substances 0.000 description 6
- 239000000126 substance Substances 0.000 description 6
- 239000012535 impurity Substances 0.000 description 5
- 239000013013 elastic material Substances 0.000 description 4
- 238000006243 chemical reaction Methods 0.000 description 3
- 239000003344 environmental pollutant Substances 0.000 description 3
- 239000002657 fibrous material Substances 0.000 description 3
- 231100000719 pollutant Toxicity 0.000 description 3
- 238000000926 separation method Methods 0.000 description 3
- 239000006228 supernatant Substances 0.000 description 3
- QVGXLLKOCUKJST-UHFFFAOYSA-N atomic oxygen Chemical compound [O] QVGXLLKOCUKJST-UHFFFAOYSA-N 0.000 description 2
- 239000002131 composite material Substances 0.000 description 2
- 238000010586 diagram Methods 0.000 description 2
- 238000007726 management method Methods 0.000 description 2
- 239000000463 material Substances 0.000 description 2
- VNWKTOKETHGBQD-UHFFFAOYSA-N methane Chemical compound C VNWKTOKETHGBQD-UHFFFAOYSA-N 0.000 description 2
- 239000001301 oxygen Substances 0.000 description 2
- 229910052760 oxygen Inorganic materials 0.000 description 2
- 239000011148 porous material Substances 0.000 description 2
- 239000013049 sediment Substances 0.000 description 2
- 239000002699 waste material Substances 0.000 description 2
- 238000005054 agglomeration Methods 0.000 description 1
- 230000002776 aggregation Effects 0.000 description 1
- 230000002925 chemical effect Effects 0.000 description 1
- 238000005265 energy consumption Methods 0.000 description 1
- 239000007789 gas Substances 0.000 description 1
- 230000006698 induction Effects 0.000 description 1
- 229920002521 macromolecule Polymers 0.000 description 1
- 238000004519 manufacturing process Methods 0.000 description 1
- 239000012528 membrane Substances 0.000 description 1
- 244000005700 microbiome Species 0.000 description 1
- 235000015097 nutrients Nutrition 0.000 description 1
- 230000003647 oxidation Effects 0.000 description 1
- 238000007254 oxidation reaction Methods 0.000 description 1
- 230000000704 physical effect Effects 0.000 description 1
- 230000008092 positive effect Effects 0.000 description 1
- 238000005070 sampling Methods 0.000 description 1
- 150000003384 small molecules Chemical class 0.000 description 1
- 239000000725 suspension Substances 0.000 description 1
- 231100000331 toxic Toxicity 0.000 description 1
- 230000002588 toxic effect Effects 0.000 description 1
- 238000009280 upflow anaerobic sludge blanket technology Methods 0.000 description 1
- 238000004065 wastewater treatment Methods 0.000 description 1
- 238000003911 water pollution Methods 0.000 description 1
Landscapes
- Biological Treatment Of Waste Water (AREA)
- Purification Treatments By Anaerobic Or Anaerobic And Aerobic Bacteria Or Animals (AREA)
Abstract
本实用新型涉及厌氧/好氧/氯气消毒领域,具体为一种生活污水处理装置。该装置将ABR(厌氧折流板)装置、消毒装置和(厌氧/好氧)装置等水处理工艺的优点相结合并进行了合理的改造,具有处理效果高、出水水质稳定、操作简单、占地面积少、运行成本低等特点,对有机废水中的有机污染物、氮、磷等有很好的处理效果,同时对SS(固体悬浮物)、浊度、色度等也具有较好的去除效果。
The utility model relates to the field of anaerobic/aerobic/chlorine gas disinfection, in particular to a domestic sewage treatment device. The device combines the advantages of water treatment processes such as ABR (anaerobic baffle) device, disinfection device and (anaerobic/aerobic) device, and has carried out a reasonable transformation. It has high treatment effect, stable effluent water quality and simple operation. , small footprint, low operating cost, etc., it has a good treatment effect on organic pollutants, nitrogen, phosphorus, etc. Good removal effect.
Description
技术领域 technical field
本发明涉及厌氧/好氧/氯气消毒领域,具体为一种生活污水处理装置。 The invention relates to the field of anaerobic/aerobic/chlorine gas disinfection, in particular to a domestic sewage treatment device.
背景技术 Background technique
生活污水的处理主要是处理水质中的有机物,COD作为有机物相对含量的一项综合指标,所以测量水质的COD即可看出水质质量,COD越大,水体污染越严重。目前,生活污水处理方法主要有物化处理法和生物处理法。物化处理法是应用物理化学作用及其原理将废水中的污染物成分转化为无害物质,使废水得到净化的方法,如化学氧化法和膜分离法等;生物处理法是利用微生物降解水中的污染物质作为自身的营养和能源,同时使废水得到净化的方法。生物法处理生活污水的主要方法有厌氧生物处理、好氧生物处理。 The treatment of domestic sewage is mainly to deal with the organic matter in the water quality. COD is a comprehensive indicator of the relative content of organic matter. Therefore, the water quality can be seen by measuring the COD of the water quality. The greater the COD, the more serious the water pollution. At present, domestic sewage treatment methods mainly include physical and chemical treatment and biological treatment. Physicochemical treatment is a method of converting pollutants in wastewater into harmless substances by applying physical and chemical effects and principles, such as chemical oxidation and membrane separation; biological treatment is the use of microorganisms to degrade pollutants in water. Pollutants are used as their own nutrients and energy sources, while the wastewater is purified. The main methods of biological treatment of domestic sewage are anaerobic biological treatment and aerobic biological treatment.
厌氧折流板反应器(ABR)是上世纪80年代开发的一种高效厌氧反应器,ABR是一个由多隔室组成的高效新型反应器,ABR反应器是一种连续流的多隔室结构,污水依次流经各隔室而得到降解,反应器每个隔室都有一个厌氧污泥层,其功能与UASB反应区类似,不同的ABR反应器不设置三相分离器。其工艺既有生物截留能力强、运行管理方便、性能可靠等优点。但ABR反应器作为厌氧生物处理工艺的一种,具有厌氧生物处理的共性,即对有机物虽然有着较高的处理率,但反应器出水中仍就含有大量有机物,出水不能达到排放标准,往往在厌氧反应器后需要加好氧处理,进一步去除厌氧反应器出水的有机物。 Anaerobic Baffled Reactor (ABR) is a high-efficiency anaerobic reactor developed in the 1980s. ABR is a high-efficiency new reactor composed of multiple compartments. The structure of the chamber, the sewage flows through each compartment in turn to be degraded, each compartment of the reactor has an anaerobic sludge layer, its function is similar to that of the UASB reaction zone, different ABR reactors do not have a three-phase separator. The process has the advantages of strong biological interception capacity, convenient operation and management, and reliable performance. However, as a kind of anaerobic biological treatment process, the ABR reactor has the commonality of anaerobic biological treatment, that is, although it has a high treatment rate for organic matter, the effluent of the reactor still contains a large amount of organic matter, and the effluent cannot meet the discharge standard. It is often necessary to add aerobic treatment after the anaerobic reactor to further remove the organic matter in the effluent of the anaerobic reactor.
发明内容 Contents of the invention
本发明正是针对生活有机污水处理效果差、出水水质不稳定等问题,提供一种生活污水处理装置,该装置采用ABR(厌氧折流板)装置、消毒装置和厌氧/好氧装置相结合进行一体化处理,可有效提高处理效果和出水水质。 The present invention aims at the problems of poor treatment effect of domestic organic sewage and unstable effluent quality, etc., and provides a domestic sewage treatment device, which adopts ABR (anaerobic baffle) device, disinfection device and anaerobic/aerobic device Combined with integrated treatment, the treatment effect and effluent quality can be effectively improved.
本发明的具体技术方案如下: Concrete technical scheme of the present invention is as follows:
一种生活污水处理装置,包括生活污水池、污水输送泵、调节池、ABR反应器、好氧池、辐流式沉淀池、消毒池、污水排出泵、清水池、污水回流泵、固液分离机和污泥储槽,生活污水池的污水通过污水输送泵和带有阀门的进水管与调节池连接,调节池的上端与ABR反应器的上端连接,ABR反应器上端的一侧与好氧池连接,上端的另一侧通过污水回流泵与固液分离机连接,好氧池的上端与辐流式沉淀池连接,ABR反应器、好氧池和辐流式沉淀池的底端均通过带有阀门的排泥管与总排泥管连接后进入固液分离机,辐流式沉淀池的中上部通过导流管与消毒池连接,消毒池通过污水排出泵与清水池连接,固液分离机与污泥储槽连接。 A domestic sewage treatment device, including a domestic sewage tank, a sewage delivery pump, a regulating tank, an ABR reactor, an aerobic tank, a radial flow sedimentation tank, a disinfection tank, a sewage discharge pump, a clear water tank, a sewage return pump, and solid-liquid separation Machine and sludge storage tank, the sewage from the domestic sewage pool is connected to the regulating tank through the sewage pump and the inlet pipe with valves, the upper end of the regulating pool is connected to the upper end of the ABR reactor, and one side of the upper end of the ABR reactor is connected to the aerobic The other side of the upper end is connected to the solid-liquid separator through the sewage return pump, the upper end of the aerobic pool is connected to the radial flow sedimentation tank, and the bottom of the ABR reactor, the aerobic pool and the radial flow sedimentation tank are all passed through The mud discharge pipe with a valve is connected to the main mud discharge pipe and then enters the solid-liquid separator. The middle and upper part of the radial flow sedimentation tank is connected to the disinfection tank through the diversion pipe, and the disinfection tank is connected to the clean water tank through the sewage discharge pump. The separator is connected with the sludge storage tank.
在所述的消毒池上端设置真空加氯器。 A vacuum chlorinator is arranged at the upper end of the disinfection pool.
在所述的调节池中设置了潜水搅拌器。 A submersible mixer is set in the regulating pool.
在所述的ABR反应器上端的一侧设置排气管。 An exhaust pipe is arranged on one side of the upper end of the ABR reactor.
在所述的好氧池底部设置微孔曝气器,微孔曝气器置于底部中心对称处。 A microporous aerator is arranged at the bottom of the aerobic tank, and the microporous aerator is placed symmetrically at the center of the bottom.
生活污水处理装置的具体原理为:生活污水在生活污水池中进行静置处理,生活污水池的生活污水通过污水输送泵和带有阀门的进水管从左端进入调节池,再经潜水泵搅拌后,上下交替单向推流,厌氧池所用的填料为高效YDT型立体波形弹性材料,除进水管外,与厌氧池相连的有排泥管、排气管、排气口、取样口,用以排出处理过程厌氧产生的脱落生物膜(污泥)、微小固定杂质、甲烷气体等物质;出水由厌氧反应器右端溢流,沿导流板进入好氧池,好氧池内填充的填料为组合纤维材料,好氧池低部布置了微孔曝气装置,下端连有排泥管;出水由好氧池上部经导流板进入辐流式沉淀池,经沉淀后的上清液进入沉淀池;出水由沉淀池上部导流管进入消毒池,消毒池上端布置了真空加氯器,下端连有污水排出泵流入清水池;厌氧池、好氧池和沉淀池的下部均设有排泥口,用一根共通的总排泥管连接固液分离机,将各感应池脱落的生物膜、杂质沉降物送入厌氧池和污泥储槽。 The specific principle of the domestic sewage treatment device is as follows: the domestic sewage is treated statically in the domestic sewage tank, and the domestic sewage in the domestic sewage tank enters the regulating tank from the left end through the sewage pump and the inlet pipe with a valve, and then is stirred by the submersible pump. , alternate up and down one-way push flow, the filler used in the anaerobic tank is a high-efficiency YDT type three-dimensional wave elastic material, in addition to the water inlet pipe, there are mud discharge pipes, exhaust pipes, exhaust ports, and sampling ports connected to the anaerobic tank. It is used to discharge the exfoliated biofilm (sludge), tiny fixed impurities, methane gas and other substances produced by anaerobic treatment; the effluent overflows from the right end of the anaerobic reactor and enters the aerobic pool along the guide plate, and the aerobic pool is filled with The filler is a composite fiber material, and a microporous aeration device is arranged in the lower part of the aerobic tank, and a mud discharge pipe is connected to the lower end; the effluent enters the radial flow sedimentation tank from the upper part of the aerobic tank through the deflector, and the supernatant after sedimentation Enter the sedimentation tank; the effluent enters the disinfection tank from the upper diversion pipe of the sedimentation tank. A vacuum chlorinator is arranged at the upper end of the disinfection tank, and a sewage discharge pump is connected at the lower end to flow into the clear water tank; There is a sludge discharge port, and a common main sludge discharge pipe is used to connect the solid-liquid separator, and the biofilm and impurity sediment shed from each induction tank are sent to the anaerobic tank and the sludge storage tank.
厌氧池采用弹性填料作为填充物,弹性填料为高效YDT型立体波形弹性材料,梅花型垂直结构;好氧池采用弹性填料作为填充物,弹性填料为组合纤维材料。在好氧池底部采用微孔曝气装置进行曝气,微孔曝气装置布置于底部中心对称处,曝气时气流带动水流均匀向上旋转流动。 The anaerobic pool uses elastic fillers as fillers, and the elastic fillers are high-efficiency YDT type three-dimensional wave elastic materials, plum-shaped vertical structures; the aerobic tanks use elastic fillers as fillers, and the elastic fillers are composite fiber materials. At the bottom of the aerobic tank, a microporous aeration device is used for aeration. The microporous aeration device is arranged at the symmetrical center of the bottom. During aeration, the airflow drives the water flow to rotate upwards evenly.
本发明的积极效果体现在: The positive effects of the present invention are reflected in:
(一)、该工艺将多种常用的废水处理工艺相结合,结构新颖、紧凑,布置合理,操作简便,工作安全稳定,提高了出水水质的稳定性,节省了处理的能耗和日常运行的费用。 (1) The process combines a variety of commonly used wastewater treatment processes. It has a novel and compact structure, reasonable layout, easy operation, safe and stable work, improves the stability of effluent water quality, and saves energy consumption for treatment and daily operation. cost.
(二)、填料采用高效YDT型立体波形弹性材料和组合纤维材料,孔隙可变性大、不粘连结团、不堵塞、材质使用寿命长,可提高氧转移率,生产运行管理简便,适应能力强。ABR反应器的填料采用单侧固定式,好氧池的填料采用中轴固定式,这两种布置方式均为悬浮式与固定式的良好结合,在防止生物膜流动脱落的同时又能增加空气、生物膜、水流的接触面积,可提高处理效果。 (2) The filler adopts high-efficiency YDT type three-dimensional wave elastic material and combined fiber material, which has large pore variability, no sticking and agglomeration, no clogging, long service life of the material, can improve the oxygen transfer rate, easy production and operation management, and strong adaptability . The filling of the ABR reactor adopts the one-side fixed type, and the filling of the aerobic tank adopts the central axis fixed type. These two arrangements are a good combination of suspension type and fixed type, which can increase the air while preventing the biofilm from flowing and falling off. The contact area of , biofilm and water flow can improve the treatment effect.
(三)、污泥回流采用ABR反应器、好氧池、沉淀池下部均设排泥口,用一根共通的总排泥管连接固液分离装置将部分活性污泥回到ABR反应器,能促进调节池的预处理,增强厌氧池的反硝化能力。 (3) ABR reactor, aerobic tank, and sedimentation tank are all equipped with sludge discharge outlets for sludge return, and a common total sludge discharge pipe is used to connect the solid-liquid separation device to return part of the activated sludge to the ABR reactor. It can promote the pretreatment of the regulating tank and enhance the denitrification capacity of the anaerobic tank.
(四)、污泥排放量少,具有良好的生化性。在ABR反应器中,厌氧过程可以将大分子物质和难降解的物质分解为小分子和易降解的物质,同时也可以进行部分反硝化作用,对有毒、难降解的有机废水具有很好的处理效果;反应池在长污泥下运行,污泥排放量少。 (4) The amount of sludge discharge is small and has good biochemical properties. In the ABR reactor, the anaerobic process can decompose macromolecular substances and refractory substances into small molecules and easily degradable substances. At the same time, it can also perform partial denitrification, which has a good effect on toxic and refractory organic wastewater. Treatment effect; the reaction tank operates under long sludge, and the sludge discharge is small.
(五)、处理有机废水以及脱氮除磷的效果显著,可处理中浓度的生活污水或处理中低浓度难降解的有机废水,因而本工艺的应用范围十分广泛。 (5) The effect of treating organic wastewater and removing nitrogen and phosphorus is remarkable, and it can treat medium-concentration domestic sewage or treat medium-low concentration refractory organic wastewater, so the application range of this process is very wide.
附图说明 Description of drawings
图1本实用新型中生活污水处理装置的主体结构剖面示意图。 Fig. 1 is a schematic cross-sectional view of the main structure of the domestic sewage treatment device in the utility model.
图2为生活污水处理装置的P—P截面结构示意图。 Figure 2 is a schematic diagram of the P-P cross-sectional structure of the domestic sewage treatment device.
图3为生活污水处理装置的H—H截面结构示意图。 Figure 3 is a schematic diagram of the H—H cross-sectional structure of the domestic sewage treatment device.
其中,1——生活污水池,2——水输送泵,3——带潜水搅拌机调节池,4——ABR反应器,5——好氧池,6——辐流式沉淀池,7——消毒池,8——污水排出泵,9——清水池,10——微孔曝气器,11——真空加氯器,12——污水回流泵,13——固液分离机,14——污泥储槽,15——阀门,16——进水管,17——排泥管,18——排气管,19——潜水搅拌器,20——总排泥管。 Among them, 1——domestic sewage pool, 2—water delivery pump, 3—adjusting tank with submersible mixer, 4—ABR reactor, 5—aerobic pool, 6—radial flow sedimentation tank, 7— — Disinfection pool, 8 — Sewage discharge pump, 9 — Clean water pool, 10 — Microporous aerator, 11 — Vacuum chlorinator, 12 — Sewage return pump, 13 — Solid-liquid separator, 14 - sludge storage tank, 15 - valve, 16 - water inlet pipe, 17 - mud discharge pipe, 18 - exhaust pipe, 19 - submersible mixer, 20 - total mud discharge pipe.
具体实施方式 detailed description
为了使本发明的目的、技术方案及优点更加清楚明白,下面结合具体实施方式对本发明作进一步的详细描述,但不应将此理解为本发明上述主题的范围仅限于下述实施例。 In order to make the purpose, technical solutions and advantages of the present invention clearer, the present invention will be described in further detail below in conjunction with specific embodiments, but it should not be understood that the scope of the above subject matter of the present invention is limited to the following examples.
实施例1: Example 1:
一种生活污水处理装置,其为一种厌氧/好氧/氯气消毒处理综合处理生活污水的装置,具体包括生活污水池、污水输送泵、调节池、ABR反应器、好氧池、辐流式沉淀池、消毒池、污水排出泵、清水池、污水回流泵、固液分离机和污泥储槽,生活污水池的污水通过污水输送泵和带有阀门的进水管与调节池连接,调节池的上端与ABR反应器的上端连接,ABR反应器上端的一侧与好氧池连接,上端的另一侧通过污水回流泵与固液分离机连接,好氧池的上端与辐流式沉淀池连接,ABR反应器、好氧池和辐流式沉淀池的底端均通过带有阀门的排泥管与总排泥管连接后进入固液分离机,辐流式沉淀池的中上部通过导流管与消毒池连接,消毒池通过污水排出泵与清水池连接,固液分离机与污泥储槽连接。在消毒池上端设置真空加氯器。在调节池中设置了潜水搅拌器。在ABR反应器上端的一侧设置排气管。在好氧池底部设置微孔曝气器,微孔曝气器置于底部中心对称处。在ABR反应器上端的一侧设置排气管。 A domestic sewage treatment device, which is an anaerobic/aerobic/chlorine gas disinfection treatment device for comprehensive treatment of domestic sewage, specifically including a domestic sewage tank, a sewage delivery pump, a regulating tank, an ABR reactor, an aerobic tank, and a radial flow tank. Type sedimentation tank, disinfection tank, sewage discharge pump, clear water tank, sewage return pump, solid-liquid separator and sludge storage tank, the sewage in the domestic sewage tank is connected to the regulating tank through the sewage conveying pump and the inlet pipe with valves, and the adjustment The upper end of the pool is connected to the upper end of the ABR reactor, one side of the upper end of the ABR reactor is connected to the aerobic pool, the other side of the upper end is connected to the solid-liquid separator through the sewage return pump, and the upper end of the aerobic pool is connected to the radial flow sedimentation tank. Pool connection, the bottom of the ABR reactor, aerobic tank and radial flow sedimentation tank are all connected to the main mud discharge pipe through the sludge discharge pipe with valves and then enter the solid-liquid separator, and the middle and upper parts of the radial flow sedimentation tank pass through The diversion pipe is connected to the disinfection tank, the disinfection tank is connected to the clean water tank through the sewage discharge pump, and the solid-liquid separator is connected to the sludge storage tank. A vacuum chlorinator is installed at the upper end of the disinfection tank. A submersible mixer is installed in the regulating tank. An exhaust pipe is provided on one side of the upper end of the ABR reactor. A microporous aerator is arranged at the bottom of the aerobic tank, and the microporous aerator is placed at the symmetrical center of the bottom. An exhaust pipe is provided on one side of the upper end of the ABR reactor.
该装置的特点是:污水首先进入调节池经搅拌处理后,通过进水管,由厌氧池左侧壁上部进入,厌氧池所用填料为弹性填料,固定方式为单侧固定;在底部布置排泥管,用于排出厌氧池产生的生物膜(污泥);好氧池所用填料也为弹性填料,固定方式为中轴固定式;在上流式好氧池的底部布置了微孔曝气器,微孔曝气器由多空挡板固定,曝气时气流带动水流均匀上旋转流动;好氧处理后的废水从上部进入沉淀池,杂质得到充分沉淀,上清液进入上流式消毒池,截留了杂质的过滤废液从过滤废液出管流出。ABR反应器、好氧池和沉淀池主体的下部设有排泥口,共用一根共通的总排泥管连接固液分离机,部分活性污泥回到厌氧室,能促进调节池的预处理,增强厌氧池的反硝化能力,固液分离机可定期排出各反应池脱落的生物膜、杂质沉降物。 The characteristics of the device are: the sewage first enters the regulating tank and is stirred and treated, then enters from the upper part of the left side wall of the anaerobic tank through the water inlet pipe, the filler used in the anaerobic tank is elastic filler, and the fixing method is one-sided fixing; The mud pipe is used to discharge the biofilm (sludge) produced by the anaerobic tank; the filler used in the aerobic tank is also elastic filler, and the fixing method is a central axis fixed type; microporous aeration is arranged at the bottom of the upflow aerobic tank The microporous aerator is fixed by a multi-hole baffle, and the airflow drives the water flow to rotate upwards evenly during aeration; the waste water after aerobic treatment enters the sedimentation tank from the upper part, the impurities are fully precipitated, and the supernatant enters the upper flow disinfection tank , the filtered waste liquid with trapped impurities flows out from the filtered waste liquid outlet pipe. The lower part of the ABR reactor, aerobic tank and sedimentation tank is equipped with a sludge discharge outlet, and a common total sludge discharge pipe is connected to the solid-liquid separator, and part of the activated sludge returns to the anaerobic chamber, which can promote the preconditioning of the regulating tank. Treatment, enhance the denitrification capacity of the anaerobic tank, and the solid-liquid separator can regularly discharge the biofilm and impurity sediments that fall off from each reaction tank.
运行前,ABR反应器和好氧池按负荷从低到高进行生物膜挂膜培养,运行时,废水经调节池搅拌处理后进入ABR反应器左侧的折流板流室中,经厌氧处理的出水从ABR反应器右侧溢流沿导流板流入好氧池进行曝气好氧处理,有机物得到降解,出水从好氧池右侧溢流流入沉淀池,上清液流入消毒池,消毒后液体从出水管排出。 Before operation, the ABR reactor and the aerobic tank carry out biofilm hanging film cultivation according to the load from low to high. During operation, the wastewater is stirred and treated in the regulating tank and then enters the baffle flow chamber on the left side of the ABR reactor. The treated effluent overflows from the right side of the ABR reactor and flows into the aerobic tank along the guide plate for aeration and aerobic treatment. The organic matter is degraded, the effluent overflows from the right side of the aerobic tank into the sedimentation tank, and the supernatant flows into the disinfection tank. After disinfection, the liquid is discharged from the outlet pipe.
厌氧池弹性填料采用高效YDT型立体波形弹性材料,孔隙可变性大、不粘连结团、不堵塞、材质使用寿命长,可提高氧转移率,适应能力强。 The elastic filler of the anaerobic tank adopts high-efficiency YDT three-dimensional wave elastic material, which has large pore variability, no sticking, no clogging, long service life of the material, can improve the oxygen transfer rate, and has strong adaptability.
本实用新型将ABR(厌氧折流板)装置、消毒装置和(厌氧/好氧)装置等水处理工艺的优点相结合并进行了合理的改造,具有处理效果高、出水水质稳定、操作简单、占地面积少、运行成本低等特点,对有机废水中的有机污染物、氮、磷等有很好的处理效果,同时对SS(固体悬浮物)、浊度、色度等也具有较好的去除效果。 The utility model combines the advantages of water treatment processes such as ABR (anaerobic baffle) device, disinfection device and (anaerobic/aerobic) device, and carries out reasonable transformation. It is simple, occupies a small area, and has low operating costs. It has a good treatment effect on organic pollutants, nitrogen, phosphorus, etc. in organic wastewater. Better removal effect.
Claims (5)
Priority Applications (1)
| Application Number | Priority Date | Filing Date | Title |
|---|---|---|---|
| CN201620354651.5U CN205575883U (en) | 2016-04-26 | 2016-04-26 | Domestic sewage treatment device |
Applications Claiming Priority (1)
| Application Number | Priority Date | Filing Date | Title |
|---|---|---|---|
| CN201620354651.5U CN205575883U (en) | 2016-04-26 | 2016-04-26 | Domestic sewage treatment device |
Publications (1)
| Publication Number | Publication Date |
|---|---|
| CN205575883U true CN205575883U (en) | 2016-09-14 |
Family
ID=56860348
Family Applications (1)
| Application Number | Title | Priority Date | Filing Date |
|---|---|---|---|
| CN201620354651.5U Expired - Fee Related CN205575883U (en) | 2016-04-26 | 2016-04-26 | Domestic sewage treatment device |
Country Status (1)
| Country | Link |
|---|---|
| CN (1) | CN205575883U (en) |
Cited By (2)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| CN107176773A (en) * | 2017-07-27 | 2017-09-19 | 温州奇思科技有限公司 | A kind of domestic sewage processing system |
| CN107188297A (en) * | 2017-07-31 | 2017-09-22 | 宣城市飞诚环保科技有限公司 | A kind of sewage-treatment plant |
-
2016
- 2016-04-26 CN CN201620354651.5U patent/CN205575883U/en not_active Expired - Fee Related
Cited By (2)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| CN107176773A (en) * | 2017-07-27 | 2017-09-19 | 温州奇思科技有限公司 | A kind of domestic sewage processing system |
| CN107188297A (en) * | 2017-07-31 | 2017-09-22 | 宣城市飞诚环保科技有限公司 | A kind of sewage-treatment plant |
Similar Documents
| Publication | Publication Date | Title |
|---|---|---|
| CN102838205B (en) | External continuous flow aerobic granular sludge membrane bioreactor | |
| CN202131151U (en) | Efficient compound sewage treatment tower type bioreactor | |
| CN203866157U (en) | Integrated baffle type anaerobic/anoxic/aerobic membrane filtration high-concentration organic wastewater treatment device | |
| CN101205109A (en) | Apparatus for treating chemical fiber waste water by anaerobic method | |
| CN101074141A (en) | Low-concentration organic wastewater regeneration and reuse process | |
| CN204162570U (en) | A kind of light electrolysis/aerobic/anaerobic/membrane filtration treatment unit | |
| CN105347475B (en) | A kind of symmetrical built-in anaerobic membrane bioreactor | |
| CN203112655U (en) | Dispersive MBR (Membrane Bioreactor) water neutralizer | |
| CN201400630Y (en) | Chemical fiber wastewater treatment system | |
| CN203392979U (en) | Integrated treatment device for domestic wastewater | |
| CN101054234B (en) | upflow anaerobic reactor | |
| CN102050529B (en) | Immersed water treatment device of inner circulating membrane coagulation reactor | |
| CN103708618A (en) | Micro-power municipal sewage treatment equipment and process | |
| CN201136823Y (en) | An aerobic anaerobic cycle treatment device for waste water | |
| CN201817328U (en) | Aeration biological filter with hollow porous fiber filler and flow baffle plate | |
| CN205575883U (en) | Domestic sewage treatment device | |
| CN110342634A (en) | The micro- oxygen sludge bed process of membrane aeration biomembrane and its wastewater treatment method | |
| CN201648106U (en) | Coking wastewater flat-plate MBR treatment equipment | |
| CN212174718U (en) | Integrated equipment for decentralized sewage treatment | |
| CN201250160Y (en) | Energy-saving sewage treatment equipment | |
| CN106745708A (en) | A kind of compound type sludge bed reactor and its application | |
| CN202054668U (en) | Anaerobic reactor for treating wastewater containing emulsion | |
| CN206188490U (en) | Handle high concentration organic waste water's device | |
| CN205528260U (en) | Sewage treatment system | |
| CN105776652B (en) | A kind of residual sludge enhanced adsorption-membrane separation water treatment device and method |
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 |
Granted publication date: 20160914 Termination date: 20200426 |
|
| CF01 | Termination of patent right due to non-payment of annual fee |