CN204607814U - A kind of New Tail water extraction mark treatment system - Google Patents
A kind of New Tail water extraction mark treatment system Download PDFInfo
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- CN204607814U CN204607814U CN201520309370.3U CN201520309370U CN204607814U CN 204607814 U CN204607814 U CN 204607814U CN 201520309370 U CN201520309370 U CN 201520309370U CN 204607814 U CN204607814 U CN 204607814U
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Abstract
本实用新型公开了一种新型尾水提标处理系统,包括依次连通的粗栅格池、细栅格池、沉砂池、生化反应池、二沉池、中间水池和消毒出水池,中间水池和消毒出水池之间还依次连通有曝气生物滤池、高效沉淀池和用于去除悬浮固体的滤网式过滤器,曝气生物滤池的入水口与中间水池的出水口相连,滤网式过滤器的出水口与消毒出水池的入水口相连;滤网式过滤器的滤网精度为5~20um,流量为5~15m3/h。本实用新型能使提标处理后的尾水能稳定达到《地表水环境质量标准》(GB3838-2002)Ⅳ类水体要求,减少污水对环境的危害。
The utility model discloses a novel tail water standard-raising treatment system, which comprises a coarse grid pool, a fine grid pool, a grit chamber, a biochemical reaction pool, a secondary sedimentation pool, an intermediate pool, a disinfection outlet pool, and an intermediate pool The biological aerated filter, the high-efficiency sedimentation tank and the screen filter used to remove suspended solids are also connected in sequence between the disinfection outlet tank. The water outlet of the type filter is connected with the water inlet of the disinfection outlet pool; the filter mesh of the screen type filter is 5-20um in precision, and the flow rate is 5-15m 3 /h. The utility model can make the tail water after standard upgrading and treatment stably meet the requirements of Class IV water bodies in the "Environmental Quality Standard for Surface Water" (GB3838-2002), and reduce the harm of sewage to the environment.
Description
技术领域technical field
本实用新型涉及污水处理技术,尤其涉及一种新型尾水提标处理系统。The utility model relates to sewage treatment technology, in particular to a novel tail water standard raising treatment system.
背景技术Background technique
随着人口及社会经济的快速发展,工业废水与生活污水的排放量与日俱增,污水处理厂的建设和运行在一定程度上减轻了污废水对地表水的污染负荷。目前污水处理厂大多执行国家《城镇污水处理厂污染物排放标准》(GB18918-2002)中的一级B或一级A排放标准,且尾水基本直排纳污水体。而根据《地表水环境质量标准》(GB3838-2002)中水域功能和分类标准中规定,地表水最低标准为Ⅴ类水,主要适用于农业用水区及一般景观要求水域。两标准中主要指标对比可以看出,现行污水处理厂排放标准仍然劣于地表水Ⅴ类标准,仍然存在加重水体环境恶化的潜势。部分污水处理厂尾水排放水域属于饮用水水源地支流或上游水域,为确保水源地免受污染,保障居民的正常生活用水,提高部分敏感水域污水厂的尾水排放标准势在必行。With the rapid development of population and social economy, the discharge of industrial wastewater and domestic sewage is increasing day by day. The construction and operation of sewage treatment plants have reduced the pollution load of sewage and wastewater on surface water to a certain extent. At present, most sewage treatment plants implement the first-level B or first-level A discharge standards in the national "Pollutant Discharge Standards for Urban Sewage Treatment Plants" (GB18918-2002), and the tail water is basically discharged directly into the sewage body. According to the "Surface Water Environmental Quality Standards" (GB3838-2002), the water area function and classification standards stipulate that the minimum surface water standard is Class V water, which is mainly applicable to agricultural water areas and water areas with general landscape requirements. Comparing the main indicators in the two standards, it can be seen that the current discharge standard for sewage treatment plants is still inferior to the Class V standard for surface water, and there is still the potential to aggravate the deterioration of the water body environment. The tail water discharge waters of some sewage treatment plants belong to the tributaries or upstream waters of drinking water sources. In order to ensure that the water sources are free from pollution and ensure the normal living water of residents, it is imperative to improve the tail water discharge standards of sewage plants in some sensitive waters.
现有污水处理成熟工艺流程为:进水→粗格栅→细格栅→沉砂池(初沉池)→生化反应池→二沉池→滤池(一级A)→消毒出水,该工艺只能达到《城镇污水处理厂污染物排放标准》(GB18918-2002)中的一级B或一级A排放标准,无法满足进一步提标后的出水水质要求。而且,二级生化处理出水中污染物浓度较低,较难用常规生化处理方法去除。The existing mature process flow of sewage treatment is: water inlet→coarse grid→fine grid→grit chamber (primary sedimentation tank)→biochemical reaction tank→secondary sedimentation tank→filter (level A)→disinfected water, the process It can only meet the first-class B or first-class A discharge standard in the "Pollutant Discharge Standards for Urban Sewage Treatment Plants" (GB18918-2002), and cannot meet the effluent water quality requirements after further standardization. Moreover, the concentration of pollutants in the secondary biochemical treatment effluent is relatively low, and it is difficult to remove them by conventional biochemical treatment methods.
实用新型内容Utility model content
为了克服现有技术的不足,本实用新型的目的在于提供一种新型尾水提标处理系统,使提标处理后的尾水能稳定达到《地表水环境质量标准》(GB3838-2002)Ⅳ类水体要求,减少污水对环境的危害。In order to overcome the deficiencies of the prior art, the purpose of this utility model is to provide a new tail water standard treatment system, so that the tail water after the standard treatment can stably reach the Class IV of "Surface Water Environmental Quality Standard" (GB3838-2002) Water body requirements, reduce the harm of sewage to the environment.
本实用新型的目的采用以下技术方案实现:The purpose of this utility model adopts following technical scheme to realize:
一种新型尾水提标处理系统,包括依次连通的粗栅格池、细栅格池、沉砂池、生化反应池、二沉池、中间水池(原有滤池改造)和消毒出水池,中间水池和消毒出水池之间还依次连通有曝气生物滤池、高效沉淀池和用于去除悬浮固体的滤网式过滤器,曝气生物滤池的入水口与中间水池的出水口相连,滤网式过滤器的出水口与消毒出水池的入水口相连;滤网式过滤器的滤网精度为5~20um,流量为5~15m3/h。A new type of tail water upgrading treatment system, including a coarse grid tank, a fine grid tank, a grit chamber, a biochemical reaction tank, a secondary sedimentation tank, an intermediate tank (retrofitted from the original filter tank) and a disinfection effluent tank connected in sequence. The intermediate pool and the disinfection outlet pool are connected in turn with a biological aerated filter, a high-efficiency sedimentation tank, and a screen filter for removing suspended solids. The water inlet of the biological aerated filter is connected with the outlet of the intermediate pool. The water outlet of the strainer filter is connected with the water inlet of the disinfection outlet pool; the mesh precision of the strainer filter is 5-20um, and the flow rate is 5-15m 3 /h.
优选地,曝气生物滤池包括多个并联的向上流过滤池。Preferably, the biological aerated filter comprises a plurality of parallel upflow filter tanks.
优选地,新型尾水提标处理系统还包括反冲洗水排放水池,曝气生物滤池内置有反冲洗装置,该反冲洗装置的出水口与反冲洗水排放水池的入水口相连。Preferably, the novel tail water upgrading treatment system further includes a backwash water discharge tank, and the biological aerated filter has a built-in backwash device, and the outlet of the backwash device is connected to the water inlet of the backwash water discharge tank.
优选地,高效沉淀池包括用于机械搅拌的混合区和用于沉淀的沉淀区,混合区和沉淀区相互连通。Preferably, the high-efficiency sedimentation tank includes a mixing zone for mechanical stirring and a sedimentation zone for precipitation, and the mixing zone and the sedimentation zone are connected to each other.
优选地,沉淀区内置有多个并排设置的斜管。Preferably, the settling area is built with a plurality of inclined pipes arranged side by side.
相比现有技术,本实用新型的有益效果在于:Compared with the prior art, the beneficial effects of the utility model are:
(1)本实用新型对难去除的低浓度氨氮、有机物、总磷和细菌处理效果佳,出水水质稳定,通过曝气生物滤池、高效沉淀池和滤网式过滤器的结合,有效降低难以去除的低浓度BOD5、COD、TOC等污染物,兼具深度脱氮除磷,消毒杀菌的作用,出水水质能稳定达到《地表水环境质量标准》GB3838-2002Ⅳ类水体要求;(1) The utility model has a good treatment effect on the difficult-to-remove low-concentration ammonia nitrogen, organic matter, total phosphorus and bacteria, and the effluent water quality is stable. The low-concentration BOD 5 , COD, TOC and other pollutants removed have the functions of deep nitrogen and phosphorus removal, disinfection and sterilization, and the effluent water quality can stably meet the requirements of the "Surface Water Environmental Quality Standard" GB3838-2002 Class IV water body requirements;
(2)本实用新型仅针对污水处理工艺设备的后段修改,基本不涉及到原构筑物及管线的拆除,不影响污水厂的正常运行;(2) The utility model is only aimed at the rear section modification of the sewage treatment process equipment, basically does not involve the removal of the original structures and pipelines, and does not affect the normal operation of the sewage plant;
(3)本实用新型模块化、自动化程度高,效率高,且施工建造快,运行管理方便,而且使用寿命长,折旧费用低,性价比高。(3) The utility model has the advantages of modularization, high degree of automation, high efficiency, quick construction, convenient operation and management, long service life, low depreciation cost and high cost performance.
附图说明Description of drawings
图1为本实用新型一种新型尾水提标处理系统的连接示意框图;Fig. 1 is a connection schematic block diagram of a novel tail water labeling treatment system of the present invention;
图2为本实用新型中间水池与消毒出水池之间的连接示意图。Fig. 2 is a schematic diagram of the connection between the intermediate pool and the disinfection outlet pool of the present invention.
图中:1、中间水池;2、曝气生物滤池;21、向上流过滤池;3、高效沉淀池;31、混合区;32、沉淀区;33、斜管;4、滤网式过滤器;5、消毒出水池;6、反冲洗水排放水池。In the figure: 1. Intermediate pool; 2. Biological aerated filter; 21. Upflow filter; 3. High-efficiency sedimentation tank; 31. Mixing area; 32. Sedimentation area; 33. Inclined pipe; 4. Screen filter 5. Disinfection outlet pool; 6. Backwash water discharge pool.
具体实施方式Detailed ways
下面,结合附图以及具体实施方式,对本实用新型做进一步描述:Below, in conjunction with accompanying drawing and specific embodiment, the utility model is described further:
如图1~2所示的一种新型尾水提标处理系统,包括依次连通的粗栅格池、细栅格池、沉砂池、生化反应池、二沉池、中间水池(原有滤池改造)和消毒出水池,中间水池和消毒出水池之间还依次连通有曝气生物滤池、高效沉淀池和用于去除悬浮固体的滤网式过滤器,曝气生物滤池的入水口与中间水池的出水口相连,滤网式过滤器的出水口与消毒出水池的入水口相连;滤网式过滤器的滤网精度为5~20um,流量为5~15m3/h。As shown in Figure 1-2, a new type of tail water standardization treatment system includes a coarse grid tank, a fine grid tank, a grit chamber, a biochemical reaction tank, a secondary sedimentation tank, and an intermediate tank (the original filtration tank) connected in sequence. pool renovation) and the disinfection outlet pool, the intermediate pool and the disinfection outlet pool are connected in turn with a biological aerated filter, a high-efficiency sedimentation tank and a screen filter for removing suspended solids, and the water inlet of the biological aerated filter It is connected to the water outlet of the intermediate pool, and the water outlet of the strainer filter is connected to the water inlet of the disinfection outlet pool; the filter mesh precision of the strainer filter is 5-20um, and the flow rate is 5-15m 3 /h.
其中,高效沉淀池出水进入滤网式过滤器,其滤网精度优选为10um,流量优选为8m3/h,达到精密过滤效果。满足设计出水SS≤5mg/L,使之对于SS等悬浮物有极高的去除率。Among them, the effluent from the high-efficiency sedimentation tank enters the filter screen filter, the filter screen precision is preferably 10um, and the flow rate is preferably 8m 3 /h, so as to achieve the precision filtration effect. Meet the design water SS≤5mg/L, so that it has a very high removal rate for suspended solids such as SS.
在滤网式过滤器出水经消毒出水池消毒后,水质能达到《地表水环境质量标准》GB3838-2002Ⅳ类水体要求。After the effluent of the screen filter is sterilized by the disinfection effluent pool, the water quality can meet the requirements of the "Surface Water Environmental Quality Standard" GB3838-2002 Class IV water body requirements.
作为优选的实施方式,曝气生物滤池包括多个并联的向上流过滤池。本新型尾水提标处理系统还包括反冲洗水排放水池,曝气生物滤池内置有反冲洗装置(图中未标出),该反冲洗装置的出水口与反冲洗水排放水池的入水口相连。原有滤池改造成中间水池后,出水经中间水池泵站提升压力,先进入曝气生物滤池,通过该曝气生物滤池的多格并联运行,并采用上向流的形式,单格过滤面积35m2,控制平均上升流速为3.57m/h,滤料厚度为3.2m,反冲洗周期为24h。本曝气生物滤池充分借鉴了污水处理接触氧化池和给水快滤池的设计思路,使其集曝气、高滤速、截流悬浮物、定期反冲洗等特点为一体,是一种高效能、低成本、小体积的污水处理系统。污水通过滤料表面高浓度生物膜的强氧化降解能力快速净化去除COD和BOD5,并能够同步进行脱氮除磷。As a preferred embodiment, the biological aerated filter includes a plurality of parallel upward flow filter tanks. The new tail water standardization treatment system also includes a backwash water discharge pool, and a backwash device (not shown in the figure) is built in the biological aerated filter. The water outlet of the backwash device and the water inlet of the backwash water discharge pool connected. After the original filter is transformed into an intermediate pool, the outlet water passes through the pump station of the intermediate pool to increase the pressure, first enters the biological aerated filter, and runs through the multiple cells of the biological aerated filter in parallel, and adopts the form of upward flow, single cell The filtration area is 35m 2 , the average rising velocity is controlled to be 3.57m/h, the thickness of the filter material is 3.2m, and the backwash cycle is 24h. The biological aerated filter fully draws on the design ideas of the sewage treatment contact oxidation tank and the water supply fast filter tank, which integrates the characteristics of aeration, high filtration rate, interception of suspended solids, and regular backwashing. It is a high-efficiency , low-cost, small-volume sewage treatment system. The sewage can be quickly purified and removed from COD and BOD 5 through the strong oxidative degradation ability of the high-concentration biofilm on the surface of the filter material, and can simultaneously remove nitrogen and phosphorus.
作为另一个优选的实施方式,高效沉淀池包括用于机械搅拌的混合区和用于加入絮凝剂沉淀区,混合区和沉淀区相互连通。沉淀区内置有多个并排设置的斜管。曝气生物滤池出水进入该高效沉淀池,高效沉淀池根据原水情况必要时在混合区投加PAC 20mg/L,PAM 3mg/L,经机械搅拌充分混凝后进入沉淀区。沉淀区采用斜管式沉淀,控制表面负荷为6.0m3/m2·h。由于高效沉淀池絮体的循环使用,能显著提高絮凝剂的使用效果,节约10%~15%的药剂。斜管的布置提升了沉淀效果,具有较高沉淀速度,单位面积产水速率显著提高。污水经絮凝沉淀,能有效去除低浓度悬浮物,进而降低水中TP浓度。As another preferred embodiment, the high-efficiency sedimentation tank includes a mixing zone for mechanical stirring and a sedimentation zone for adding flocculant, and the mixing zone and the sedimentation zone are connected to each other. The settling area is built with multiple inclined pipes arranged side by side. The effluent from the biological aerated filter enters the high-efficiency sedimentation tank. According to the raw water conditions, the high-efficiency sedimentation tank will add PAC 20mg/L and PAM 3mg/L to the mixing area when necessary, and enter the sedimentation area after being fully coagulated by mechanical stirring. The sedimentation area adopts inclined tube sedimentation, and the surface load is controlled at 6.0m 3 /m 2 ·h. Due to the recycling of the flocs in the high-efficiency sedimentation tank, the use effect of the flocculant can be significantly improved, and 10% to 15% of the chemical agent can be saved. The arrangement of the inclined tube improves the sedimentation effect, has a higher sedimentation velocity, and the water production rate per unit area is significantly increased. Sewage flocculation and sedimentation can effectively remove low-concentration suspended solids, thereby reducing the concentration of TP in water.
对本领域的技术人员来说,可根据以上描述的技术方案以及构思,做出其它各种相应的改变以及形变,而所有的这些改变以及形变都应该属于本实用新型权利要求的保护范围之内。For those skilled in the art, various other corresponding changes and deformations can be made according to the technical solutions and ideas described above, and all these changes and deformations should fall within the protection scope of the claims of the present utility model.
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| CN201520309370.3U CN204607814U (en) | 2015-05-13 | 2015-05-13 | A kind of New Tail water extraction mark treatment system |
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Cited By (4)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| CN106348525A (en) * | 2016-08-31 | 2017-01-25 | 湖北山鼎环境科技股份有限公司 | Landscape ecological type city and down living sewage treatment method and system |
| CN107522312A (en) * | 2016-06-20 | 2017-12-29 | 南京梅山冶金发展有限公司 | A kind of weight, magnetic, floating beneficiation combined method produce useless water purification method |
| CN107643374A (en) * | 2017-02-10 | 2018-01-30 | 安聪聪 | A kind of high concentrated organic wastewater detecting system |
| CN114149138A (en) * | 2021-11-18 | 2022-03-08 | 高广辉 | A kind of urban sewage tail water treatment system and using method thereof |
-
2015
- 2015-05-13 CN CN201520309370.3U patent/CN204607814U/en not_active Expired - Lifetime
Cited By (5)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| CN107522312A (en) * | 2016-06-20 | 2017-12-29 | 南京梅山冶金发展有限公司 | A kind of weight, magnetic, floating beneficiation combined method produce useless water purification method |
| CN106348525A (en) * | 2016-08-31 | 2017-01-25 | 湖北山鼎环境科技股份有限公司 | Landscape ecological type city and down living sewage treatment method and system |
| CN107643374A (en) * | 2017-02-10 | 2018-01-30 | 安聪聪 | A kind of high concentrated organic wastewater detecting system |
| CN114149138A (en) * | 2021-11-18 | 2022-03-08 | 高广辉 | A kind of urban sewage tail water treatment system and using method thereof |
| CN114149138B (en) * | 2021-11-18 | 2024-11-22 | 高广辉 | A system for improving the treatment of urban sewage tail water and its use method |
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Granted publication date: 20150902 |