CN108975599A - Reed wetland sewage purification system and effluent purification method - Google Patents

Reed wetland sewage purification system and effluent purification method Download PDF

Info

Publication number
CN108975599A
CN108975599A CN201810660693.5A CN201810660693A CN108975599A CN 108975599 A CN108975599 A CN 108975599A CN 201810660693 A CN201810660693 A CN 201810660693A CN 108975599 A CN108975599 A CN 108975599A
Authority
CN
China
Prior art keywords
pool
sewage
wetland
water
pond
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.)
Pending
Application number
CN201810660693.5A
Other languages
Chinese (zh)
Inventor
裴绍峰
祝雅轩
叶思源
袁红明
丁喜桂
王锦
谢柳娟
Current Assignee (The listed assignees may be inaccurate. Google has not performed a legal analysis and makes no representation or warranty as to the accuracy of the list.)
Qingdao Institute of Marine Geology
Original Assignee
Qingdao Institute of Marine Geology
Priority date (The priority date 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 date listed.)
Filing date
Publication date
Application filed by Qingdao Institute of Marine Geology filed Critical Qingdao Institute of Marine Geology
Priority to CN201810660693.5A priority Critical patent/CN108975599A/en
Publication of CN108975599A publication Critical patent/CN108975599A/en
Pending legal-status Critical Current

Links

Classifications

    • CCHEMISTRY; METALLURGY
    • C02TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02FTREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02F9/00Multistage treatment of water, waste water or sewage
    • CCHEMISTRY; METALLURGY
    • C02TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02FTREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02F1/00Treatment of water, waste water, or sewage
    • C02F1/001Processes for the treatment of water whereby the filtration technique is of importance
    • CCHEMISTRY; METALLURGY
    • C02TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02FTREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02F2301/00General aspects of water treatment
    • C02F2301/08Multistage treatments, e.g. repetition of the same process step under different conditions
    • CCHEMISTRY; METALLURGY
    • C02TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02FTREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02F3/00Biological treatment of water, waste water, or sewage
    • C02F3/30Aerobic and anaerobic processes
    • CCHEMISTRY; METALLURGY
    • C02TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02FTREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02F3/00Biological treatment of water, waste water, or sewage
    • C02F3/32Biological treatment of water, waste water, or sewage characterised by the animals or plants used, e.g. algae

Landscapes

  • Life Sciences & Earth Sciences (AREA)
  • Hydrology & Water Resources (AREA)
  • Engineering & Computer Science (AREA)
  • Environmental & Geological Engineering (AREA)
  • Water Supply & Treatment (AREA)
  • Chemical & Material Sciences (AREA)
  • Organic Chemistry (AREA)
  • Purification Treatments By Anaerobic Or Anaerobic And Aerobic Bacteria Or Animals (AREA)

Abstract

The present invention relates to a kind of reed wetland sewage purification systems, including the first wetland pond, grille well, conditioning tank, anaerobic pond, anoxic pond, aerobic tank, sedimentation basin, the second wetland pond, the third wetland pond being sequentially connected;First wetland pond, grille well, conditioning tank are arranged from high to low;Anaerobic pond, anoxic pond, aerobic tank, sedimentation basin are arranged from high to low;Second wetland pond and third wetland pond are arranged from high to low.Setting mixes return pipe between the end of aerobic tank and the front end of anoxic pond, and the first water quality detection well is arranged between the water outlet in the second wetland pond and the water inlet in third wetland pond, and the second water quality detection well is arranged in the water outlet end in third wetland pond.Purification system of the invention reduces utilization and the site operation personnel of mechanical equipment, increases the design of reflux, improve Nitrogen/Phosphorus Removal using stepped design.

Description

芦苇湿地污水净化系统及污水净化方法Reed wetland sewage purification system and sewage purification method

技术领域technical field

本发明属于污水净化技术领域,具体涉及一种芦苇湿地污水净化系统及污水净化方法。The invention belongs to the technical field of sewage purification, and in particular relates to a reed wetland sewage purification system and a sewage purification method.

背景技术Background technique

近十几年来,我国沿海一些区域水体水质逐渐恶化,赤潮生态灾害频发,为海岸带经济发展和人民生活水平带来极大威胁。究其原因,城镇生活污水、工业废水和农田用水等携带的大量污染物质是导致水体富营养化及水质恶化的重要污染源。尤其废水中的氮、磷含量超标,可在春、夏季节刺激藻类爆发式生长,从而导致严重的水华问题,其危害已引起沿海人民的普遍关注。政府部门和科研工作者也正在为控制水体富营养化问题而付出诸多努力。In the past ten years, the water quality of some coastal areas in my country has gradually deteriorated, and red tide ecological disasters have occurred frequently, posing a great threat to the economic development of the coastal zone and people's living standards. The reason is that a large number of pollutants carried by urban domestic sewage, industrial wastewater and farmland water are important sources of pollution that lead to eutrophication of water bodies and deterioration of water quality. In particular, the excessive nitrogen and phosphorus content in wastewater can stimulate the explosive growth of algae in spring and summer, resulting in serious algal blooms, and its harm has aroused widespread concern among coastal people. Government departments and scientific researchers are also making great efforts to control the eutrophication of water bodies.

湿地与森林、海洋并列为全球三大生态系统类型,它是水陆相互作用形成的独特生态系统,具有极高的生物多样性和生物生产力,同时具有极强的自净能力和净化污水的能力,因此被称为“地球之肾”。如何利用“地球之肾”来净化城镇生活污水、工业废水和农田用水中的污染物质从而服务于社会已成为当今开发湿地服务功能的一个热点问题。Wetlands, forests, and oceans are listed as the three major types of ecosystems in the world. It is a unique ecosystem formed by the interaction of water and land. It has extremely high biodiversity and biological productivity, and has strong self-purification and sewage purification capabilities. Therefore, Known as the "kidney of the earth". How to use the "kidney of the earth" to purify urban domestic sewage, industrial wastewater and farmland water to serve the society has become a hot issue in the development of wetland service functions.

近年来,芦苇湿地开始被尝试用来进行污水处理,因其具有廉价、绿色环保等优点,而且避免了常规污水处理厂费用高、能源消耗高、运行管理复杂等缺陷,正逐渐成为一种高效的生物修复途径,受到科研人员和政府部门越来越多的重视。芦苇湿地污水处理技术利用人工或自然的湿地中陆上植被、土壤微生物、水体浮游生物等多圈层生态系统中的物理、化学、生物等多重过程协同作用,对污水中的杂质和有害元素进行处理,其作用机理包含滞留、过滤、吸附、氧化还原、沉淀、微生物分解、降解转化、植物吸收、残留物积累等各类生物化学作用,是一个极为复杂的过程。而该技术本身也需要与其他污水处理技术相结合才能发挥更好的效果。因此,芦苇湿地污水处理技术往往是综合的、多元的系统性技术,需要根据污水的来源、具体性质和污染状况而采用不同的设计方式。In recent years, reed wetlands have begun to be used for sewage treatment. Because of their advantages of low cost, green and environmental protection, and avoiding the defects of conventional sewage treatment plants, such as high cost, high energy consumption, and complicated operation and management, it is gradually becoming an efficient More and more attention has been paid by researchers and government departments to the bioremediation approach. Reed wetland sewage treatment technology utilizes the synergy of physical, chemical, biological and other multiple processes in multi-circle ecosystems such as terrestrial vegetation, soil microorganisms, and water plankton in artificial or natural wetlands to treat impurities and harmful elements in sewage. Treatment, its action mechanism includes various biochemical actions such as retention, filtration, adsorption, redox, precipitation, microbial decomposition, degradation transformation, plant absorption, residue accumulation, etc., is an extremely complex process. And the technology itself needs to be combined with other sewage treatment technologies to achieve better results. Therefore, the reed wetland sewage treatment technology is often a comprehensive and multivariate systemic technology, and different design methods need to be adopted according to the source, specific nature and pollution status of sewage.

调查发现,现有的湿地污水处理技术存在以下问题:(1)在湿地处理系统中过多采用机械设备,这样变相的增加了能源消耗,也增加了成本。比如以往设计往往使用很多污水泵,将污水从不同单元之间转换,而污水泵的操作即需要人员或自动系统,同时也消耗电力,这无疑增加了运营成本。(2)缺乏针对污水处理后的效果缺乏科学地监测,往往缺乏在处理过程中对水质进行检测的节点,因此究竟污水系统处理系统效果如何并不是非常明确。(3)缺乏针对脱氮除磷的回流设备。在污水处理中,“厌氧池—缺氧池—好氧池”(A/A/O)系统是脱氮除磷时的关键工艺,然而很多设计缺乏针对好氧池流出液体进行回流的设计,限制了“厌氧池—缺氧池—好氧池”工艺的效能发挥。(4)脱氮除磷以及污水处理效果不甚理想,且维护成本较高,需要人员长期在线场运营。The survey found that the existing wetland sewage treatment technology has the following problems: (1) Excessive use of mechanical equipment in the wetland treatment system increases energy consumption and costs in a disguised form. For example, in the past, many sewage pumps were often used to transfer sewage from different units, and the operation of sewage pumps required personnel or automatic systems, and also consumed electricity, which undoubtedly increased operating costs. (2) There is a lack of scientific monitoring of the effect of sewage treatment, and there is often a lack of nodes for testing water quality during the treatment process. Therefore, it is not very clear how effective the sewage system treatment system is. (3) Lack of reflux equipment for nitrogen and phosphorus removal. In sewage treatment, the "anaerobic tank-anoxic tank-aerobic tank" (A/A/O) system is a key process for nitrogen and phosphorus removal, but many designs lack the design for the reflux of the effluent from the aerobic tank , which limits the effectiveness of the process of "anaerobic pool - anoxic pool - aerobic pool". (4) The effect of nitrogen and phosphorus removal and sewage treatment is not ideal, and the maintenance cost is high, requiring personnel to operate on-site for a long time.

发明内容Contents of the invention

针对现有的湿地污水处理系统运营成本高、脱氮除磷以及污水处理效果不理想的上述问题,本发明提供一种芦苇湿地污水净化系统,具有结构简单、节省能源、占地面积小、效率高、适用范围广泛、使用寿命长、安全可靠的优点;本发明还提供利用芦苇湿地净化污水的方法,利用阶梯式设计,减少了机械设备的运用和现场操作人员,增加回流的设计,提高了脱氮除磷效果。In view of the above-mentioned problems of high operating cost, nitrogen and phosphorus removal and unsatisfactory sewage treatment effect of the existing wetland sewage treatment system, the present invention provides a reed wetland sewage purification system, which has the advantages of simple structure, energy saving, small footprint and high efficiency. High, wide application range, long service life, safe and reliable; the invention also provides a method for purifying sewage by using reed wetlands, using a stepped design, reducing the use of mechanical equipment and on-site operators, increasing the design of backflow, and improving Nitrogen and phosphorus removal effect.

本发明是通过以下技术方案实现的:The present invention is achieved through the following technical solutions:

一种芦苇湿地污水净化系统,包括依次相连的第一湿地池、格栅井、调节池、厌氧池、缺氧池、好氧池、沉淀池、第二湿地池、第三湿地池;A reed wetland sewage purification system, comprising a first wetland pool, a grid well, a regulating pool, an anaerobic pool, an anoxic pool, an aerobic pool, a sedimentation pool, a second wetland pool, and a third wetland pool;

所述第一湿地池设置入水口和出水口,出水口与格栅井的入水口相连,格栅井的出水口设置在格栅井的底部与调节池相连,调节池通过水管与厌氧池的前端相连,水管上设置第一污水泵;厌氧池的出水口与缺氧池的入水口相连,缺氧池的出水口与好氧池的入水口相连,好氧池的末端与缺氧池的前端之间设置混合回流管,混合回流管上设置第二污水泵;好氧池的出水口与沉淀池相连,沉淀池通过水管与第二湿地池的入水口相连,水管上设置第三污水泵;第二湿地池的出水口与第三湿地池的入水口相连,并且两者之间设置第一水质检测井,水质检测井内设置检测仪;第三湿地池的出水口端设置第二水质检测井,第二水质检测井连接出水管,出水管上设置阀门;The first wetland pool is provided with a water inlet and a water outlet, and the water outlet is connected to the water inlet of the grid well, and the water outlet of the grid well is set at the bottom of the grid well to connect with the regulating pool, and the regulating pool is connected to the anaerobic pool through a water pipe. The front end of the anoxic pool is connected, and the first sewage pump is installed on the water pipe; the outlet of the anaerobic pool is connected with the water inlet of the anoxic pool, the outlet of the anoxic pool is connected with the water inlet of the aerobic pool, and the end of the aerobic pool is connected with the anoxic pool. A mixing return pipe is arranged between the front ends of the pool, and a second sewage pump is arranged on the mixing return pipe; the outlet of the aerobic pool is connected to the sedimentation tank, and the sedimentation tank is connected to the water inlet of the second wetland pool through a water pipe, and a third sewage pump is installed on the water pipe. Sewage pump; the water outlet of the second wetland pool is connected to the water inlet of the third wetland pool, and the first water quality testing well is set between the two, and a detector is installed in the water quality testing well; the water outlet of the third wetland pool is equipped with a second The water quality testing well, the second water quality testing well is connected to the water outlet pipe, and the valve is set on the water outlet pipe;

所述第一湿地池、第二湿地池和第三湿地池内均设置生物基质,生物基质上生长芦苇,入水口和出水口分别设置在生物基质的上方和下方;The first wetland pool, the second wetland pool and the third wetland pool are all provided with biological substrates, reeds grow on the biological substrates, and the water inlet and water outlet are respectively arranged above and below the biological substrates;

第一湿地池、格栅井、调节池从高到低排布;厌氧池、缺氧池、好氧池、沉淀池从高到低排布;第二湿地池和第三湿地池从高到低排布。The first wetland pool, grid well, and regulating pool are arranged from high to low; the anaerobic pool, anoxic pool, aerobic pool, and sedimentation pool are arranged from high to low; the second wetland pool and the third wetland pool are arranged to low profile.

一种利用芦苇湿地净化污水的方法,包括以下步骤:A method for purifying sewage by using reed wetlands, comprising the following steps:

(1)将污水引入第一湿地池中,第一湿地池中种植芦苇,底部填充生物基质材料,污水从芦苇根部、基质表层流过,然后自动流入格栅井;(1) Introduce the sewage into the first wetland pool, plant reeds in the first wetland pool, fill the bottom with biological matrix materials, the sewage flows through the roots of the reeds and the surface of the matrix, and then automatically flows into the grid well;

(2)格栅井内布置有格栅,将水体中较大的悬浮体或颗粒截留,污水从格栅底部的出水管自动流入调节池;(2) A grid is arranged in the grid well to trap larger suspended solids or particles in the water body, and the sewage automatically flows into the regulating tank from the outlet pipe at the bottom of the grid;

(3)调节池与第一污水泵相连,第一污水泵将污水调流提升进入厌氧池;(3) The adjustment tank is connected to the first sewage pump, and the first sewage pump adjusts the flow of sewage and lifts it into the anaerobic tank;

(4)在厌氧池中,污水中的难降解的高分子有机物转变为易被降解的低分子有机物;(4) In the anaerobic tank, the refractory high-molecular organic matter in the sewage is transformed into a low-molecular organic matter that is easily degraded;

(5)污水从厌氧池的底部自动进入缺氧池中,污水在缺氧池中发生反硝化;(5) The sewage enters the anoxic pool automatically from the bottom of the anaerobic pool, and the sewage is denitrified in the anoxic pool;

(6)污水从缺氧池的底部自动进入好氧池中,污水中的有机物被进一步分解成无机物;好氧池末端的污水通过第二污水泵回流至缺氧池的前端;(6) The sewage enters the aerobic pool automatically from the bottom of the anoxic pool, and the organic matter in the sewage is further decomposed into inorganic matter; the sewage at the end of the aerobic pool is returned to the front end of the anoxic pool by the second sewage pump;

(7)污水从好氧池自动进入沉淀池进行初步沉淀,一些矿化物质或无法进行生化反应的污泥或颗粒物被沉淀;(7) Sewage from the aerobic tank automatically enters the sedimentation tank for preliminary precipitation, and some mineralized substances or sludge or particles that cannot undergo biochemical reactions are precipitated;

(8)沉淀后的污水通过第三污水泵提升至第二湿地池中,经过芦苇和生物基质的双重过滤和生化反应,污水中过量的氮、磷、硅和重金属的污染物质被去除;(8) The settled sewage is lifted to the second wetland pool through the third sewage pump, and through the double filtration and biochemical reaction of reeds and biological substrates, the excess nitrogen, phosphorus, silicon and heavy metal pollutants in the sewage are removed;

(9)第二湿地池中自动流出的污水,经过第一水质检测井,水质检测仪实时在线进行水质取样和检测;随后污水自动进入第三湿地池中,再次经过过滤和生化处理,最后自动流入第二水质检测井,经水质检测仪检测合格后流出。(9) The sewage that automatically flows out of the second wetland pool passes through the first water quality testing well, and the water quality detector performs real-time online water quality sampling and testing; then the sewage automatically enters the third wetland pool, undergoes filtration and biochemical treatment again, and finally automatically It flows into the second water quality testing well, and flows out after being tested by the water quality testing instrument.

进一步的,所述厌氧池中的溶解氧的含量控制在0.2mg/L以下,缺氧池中的溶解氧的含量控制在0.4mg/L-0.6mg/L,好氧池中的溶解氧的含量控制在2mg/L-5mg/L。Further, the dissolved oxygen content in the anaerobic pool is controlled below 0.2mg/L, the dissolved oxygen content in the anoxic pool is controlled at 0.4mg/L-0.6mg/L, and the dissolved oxygen in the aerobic pool The content is controlled at 2mg/L-5mg/L.

本发明提供的芦苇湿地污水净化系统及处理污水的方法具有以下有益效果:The reed wetland sewage purification system and the sewage treatment method provided by the present invention have the following beneficial effects:

(1)所有关键单元,均采用阶梯式设计,利用自然重力推动水流,减少了机械设备的运用,减少了现场操作人员,起到节能降耗、降低运营成本的效果。(1) All key units adopt a stepped design, using natural gravity to drive water flow, reducing the use of mechanical equipment and on-site operators, achieving the effect of saving energy, reducing consumption, and reducing operating costs.

(2)在以往格栅井前面,增加芦苇湿地池,有效减缓水流速度,同时利用芦苇自身的过滤作用和机械阻挡作用,将较大的污水杂质阻挡在格栅井外,降低格栅井的压力。(2) A reed wetland pool is added in front of the grid well to effectively slow down the water flow velocity. At the same time, the filter function and mechanical blocking effect of the reed itself are used to block the large sewage impurities outside the grid well and reduce the water flow rate of the grid well. pressure.

(3)采用“好氧池末端→缺氧池前端”的混合液回流设计,能达到更好的脱氮除磷效果。(3) The mixed liquid reflux design of "the end of the aerobic pool → the front end of the anoxic pool" can achieve better nitrogen and phosphorus removal effects.

(4)在两个湿地池之间和湿地池处理污水后端,分别增加了水质检测井,利用自动水质检测仪在线检测污水处理后的效果,确保污水处理结果符合排放标准。(4) Water quality testing wells were added between the two wetland pools and at the back end of the wetland pool for sewage treatment, and automatic water quality detectors were used to detect the effect of sewage treatment on-line to ensure that the sewage treatment results meet the discharge standards.

本发明充分利用人工/自然湿地中芦苇植被、土壤微生物、水体浮游生物等多圈层生态系统中的物理、化学、生物等多重过程协同作用,对污水中的杂质和有害元素进行处理;具有结构简单、巧妙利用重力节省能源、占地面积小、效率高、适用范围广泛等优点,实用寿命长,具有安全可靠的性能和作用。The present invention makes full use of the synergistic effect of physical, chemical, biological and other multiple processes in multi-circle ecosystems such as reed vegetation, soil microorganisms, and water body plankton in artificial/natural wetlands to process impurities and harmful elements in sewage; it has a structure Simple and ingenious use of gravity to save energy, small footprint, high efficiency, wide application range, etc., long practical life, safe and reliable performance and function.

附图说明Description of drawings

图1为实施例1芦苇湿地污水净化系统的结构示意图。Fig. 1 is a schematic structural diagram of the reed wetland sewage purification system in Embodiment 1.

图中:1、第一湿地池;2、格栅井;3、调节池;4、厌氧池;5、缺氧池;6、好氧池;7、沉淀池;8、第二湿地池;9、第三湿地池;10、第一污水泵;11、混合回流管;12、第二污水泵;13、第三污水泵;14、第一水质检测井;15、第二水质检测井;16、出水管;17、阀门;18、生物基质;19、芦苇。In the figure: 1. The first wetland pool; 2. Grid well; 3. Regulating pool; 4. Anaerobic pool; 5. Anoxic pool; 6. Aerobic pool; 7. Sedimentation pool; 8. Second wetland pool 9. The third wetland pool; 10. The first sewage pump; 11. The mixed return pipe; 12. The second sewage pump; 13. The third sewage pump; 14. The first water quality testing well; 15. The second water quality testing well ; 16, outlet pipe; 17, valve; 18, biological matrix; 19, reed.

具体实施方式Detailed ways

下面结合具体实施例及附图对本发明做进一步详细说明。The present invention will be described in further detail below in conjunction with specific embodiments and accompanying drawings.

实施例1Example 1

本实施例提供一种芦苇湿地污水净化系统,如图1所述,包括依次相连的第一湿地池1、格栅井2、调节池3、厌氧池4、缺氧池5、好氧池6、沉淀池7、第二湿地池8、第三湿地池9,图中的箭头表示水流方向。This embodiment provides a reed wetland sewage purification system, as shown in Figure 1, including a first wetland pool 1, a grid well 2, a regulating pool 3, an anaerobic pool 4, an anoxic pool 5, and an aerobic pool connected in sequence 6. Sedimentation pond 7, second wetland pond 8, and third wetland pond 9. The arrows in the figure indicate the direction of water flow.

第一湿地池、格栅井、调节池从高到低排布;厌氧池、缺氧池、好氧池、沉淀池从高到低排布;第二湿地池和第三湿地池也是从高到低排布。采用阶梯式设计,使得各单元具有一定的高度落差,这样可以利用重力来促使水流自动流动,从而减少了污水泵的使用频率。The first wetland pool, grid well, and regulating pool are arranged from high to low; the anaerobic pool, anoxic pool, aerobic pool, and sedimentation pool are arranged from high to low; the second wetland pool and the third wetland pool are also arranged from Arranged from high to low. The stepped design makes each unit have a certain height difference, so that gravity can be used to promote the automatic flow of water, thereby reducing the frequency of use of the sewage pump.

第一湿地池1设置入水口和出水口,底部设置生物基质18,生物基质18可满足芦苇基本生长,但氮磷含量并不丰富,生物基质上生长芦苇19,入水口设置在生物基质18的上方,出水口设置在生物基质18的下方,出水口与格栅井2的入水口相连。在格栅井2前面设置芦苇湿地池1,可有效减缓水流速度,同时利用芦苇自身的过滤作用和机械阻挡作用,将较大的污水杂质,比如泡沫塑料袋、较大的悬浮物等,阻挡在格栅井外,从而减轻格栅井的压力。The first wetland pool 1 is provided with a water inlet and a water outlet, and a biological matrix 18 is set at the bottom. The biological matrix 18 can satisfy the basic growth of reeds, but the nitrogen and phosphorus content is not rich. Reeds 19 grow on the biological matrix, and the water inlet is set at the bottom of the biological matrix 18. Above, the water outlet is set under the biological matrix 18 , and the water outlet is connected to the water inlet of the grid well 2 . The reed wetland pool 1 is set in front of the grid well 2, which can effectively slow down the water flow speed, and at the same time, use the filtering function and mechanical blocking function of the reed itself to block the larger sewage impurities, such as foam plastic bags and larger suspended solids. outside the grill well, thereby relieving the pressure on the grill well.

格栅井2的出水口设置在格栅井2的底部并与调节池3相连,调节池3通过水管与厌氧池4的前端相连,水管上设置第一污水泵10,厌氧池4的出水口与缺氧池5的入水口相连,缺氧池5的出水口与好氧池6的入水口相连,好氧池6的末端与缺氧池5的前端之间设置混合回流管11,混合回流管11上设置第二污水泵12。采用“好氧池末端→缺氧池前端”的混合液回流设计,能达到更好的脱氮除磷效果。The water outlet of the grid well 2 is set at the bottom of the grid well 2 and is connected with the adjustment tank 3. The adjustment tank 3 is connected with the front end of the anaerobic tank 4 through a water pipe, and the first sewage pump 10 is arranged on the water pipe. The water outlet is connected to the water inlet of the anoxic pool 5, and the water outlet of the anoxic pool 5 is connected to the water inlet of the aerobic pool 6, and a mixing return pipe 11 is set between the end of the aerobic pool 6 and the front end of the anoxic pool 5, A second sewage pump 12 is arranged on the mixing return pipe 11 . The mixed liquid reflux design of "the end of the aerobic pool → the front end of the anoxic pool" can achieve better nitrogen and phosphorus removal effects.

好氧池6的出水口与沉淀池7相连,沉淀池7内设置第三污水泵13,第三污水泵13通过水管与第二湿地池8的入水口相连,第二湿地池8的出水口与第三湿地池9的入水口相连。第二湿地池和第三湿地池的结构与第一湿地池相同,内部均设置生物基质和芦苇。在湿地池污水处理单元,采用多个湿地池相连的设计:前段湿地池充分利用芦苇湿地发育良好的根系及其根际大量增殖的微生物,快速降解污水中的有机质,使污水得以净化;后端湿地池的芦苇释放的氧气向水中扩散,使水体底部形成许多缺氧区和好氧区。在好氧区,通过附着在根系上的好氧微生物的作用,分解污水中的有机物,矿化后的一部分无机物(如氮和磷),可被植物利用;在缺氧区,可通过反硝化作用而脱氮,使污水得以净化。通过以上两次净化后,污水处理效果更加理想。The water outlet of the aerobic pool 6 is connected with the sedimentation tank 7, and the third sewage pump 13 is installed in the sedimentation tank 7, and the third sewage pump 13 is connected with the water inlet of the second wetland pool 8 through a water pipe, and the water outlet of the second wetland pool 8 It is connected with the water inlet of the third wetland pool 9. The structure of the second wetland pool and the third wetland pool is the same as that of the first wetland pool, and biological matrix and reeds are arranged inside. In the sewage treatment unit of the wetland pool, the design of connecting multiple wetland pools is adopted: the wetland pool in the front section makes full use of the well-developed root system of the reed wetland and the microorganisms proliferating in the rhizosphere to quickly degrade the organic matter in the sewage and purify the sewage; The oxygen released by the reeds in the wetland pool diffuses into the water, forming many anoxic and aerobic zones at the bottom of the water body. In the aerobic zone, through the action of aerobic microorganisms attached to the root system, the organic matter in the sewage is decomposed, and part of the mineralized inorganic matter (such as nitrogen and phosphorus) can be used by plants; Nitrification and denitrification, so that sewage can be purified. After the above two purifications, the sewage treatment effect is more ideal.

第二湿地池8的出水口与第三湿地池9的入水口之间设置第一水质检测井14,第一水质检测井内设置检测仪;第三湿地池9的出水口端设置第二水质检测井15,第二水质检测井连接出水管16,出水管上设置阀门17。在两个湿地池之间、湿地池末端,均设计了水质检测井,并利用自动水质在线检测仪对水质状况进行实时检测,从而减少了人力成本,使得污水处理效果得以保障。A first water quality testing well 14 is set between the water outlet of the second wetland pool 8 and the water inlet of the third wetland pool 9, and a detector is set in the first water quality testing well; a second water quality testing is set at the water outlet of the third wetland pool 9 The well 15 and the second water quality detection well are connected to a water outlet pipe 16, and a valve 17 is arranged on the water outlet pipe. Water quality detection wells are designed between the two wetland pools and at the end of the wetland pool, and the automatic water quality online detector is used to detect the water quality in real time, thereby reducing labor costs and ensuring the effect of sewage treatment.

实施例2Example 2

本实施例提供一种利用芦苇湿地净化污水的方法,包括以下步骤:This embodiment provides a method for purifying sewage by using reed wetlands, including the following steps:

(1)将污水引入第一湿地池1中,第一湿地池1中种植芦苇,底部填充生物基质材料,污水从芦苇根部、基质表层流过,然后自动流入格栅井2;(1) The sewage is introduced into the first wetland pool 1, reeds are planted in the first wetland pool 1, the bottom is filled with biological matrix materials, the sewage flows through the roots of the reeds and the surface of the matrix, and then automatically flows into the grid well 2;

(2)格栅井2内布置有格栅,将水体中较大的悬浮体或颗粒截留,污水从格栅井底部的出水管自动流入调节池3;(2) A grid is arranged in the grid well 2 to trap larger suspended solids or particles in the water body, and the sewage automatically flows into the regulating tank 3 from the outlet pipe at the bottom of the grid well;

(3)调节池3与第一污水提升泵10相连,第一污水泵10将污水调流提升进入厌氧池4;(3) The adjustment pool 3 is connected to the first sewage lifting pump 10, and the first sewage pump 10 lifts the sewage into the anaerobic pool 4;

(4)控制厌氧池4中的溶解氧的含量在0.1mg/L,污水中的难降解的高分子有机物转变为易被降解的低分子有机物;(4) control the content of dissolved oxygen in the anaerobic tank 4 at 0.1 mg/L, and the refractory high-molecular organic matter in the sewage is converted into an easily degradable low-molecular organic matter;

(5)污水从厌氧池4的底部自动进入缺氧池5中,控制缺氧池5中的溶解氧的含量在0.5mg/L,污水在缺氧池5中发生反硝化;(5) sewage enters in the anoxic pond 5 automatically from the bottom of the anoxic pond 4, controls the content of dissolved oxygen in the anoxic pond 5 at 0.5 mg/L, and denitrification occurs in the sewage in the anoxic pond 5;

(6)污水从缺氧池5的底部自动进入好氧池6中,好氧池6中的溶解氧的含量控制在4mg/L,污水中的有机物被进一步分解成无机物;好氧池6末端的污水通过第二污水泵12回流至缺氧池5的前端;(6) sewage enters in the aerobic pond 6 automatically from the bottom of the anoxic pond 5, and the content of dissolved oxygen in the aerobic pond 6 is controlled at 4mg/L, and the organic matter in the sewage is further decomposed into inorganic matter; the aerobic pond 6 The sewage at the end flows back to the front end of the anoxic pool 5 through the second sewage pump 12;

(7)污水从好氧池6自动进入沉淀池7进行初步沉淀,一些矿化物质或无法进行生化反应的污泥或颗粒物被沉淀;(7) The sewage enters the sedimentation tank 7 from the aerobic pool 6 for initial precipitation, and some mineralized substances or sludge or particles that cannot undergo biochemical reactions are deposited;

(8)沉淀后的污水通过第三污水泵13提升至第二湿地池8中,经过芦苇和生物基质的双重过滤和生化反应,污水中过量的氮、磷、硅和重金属的污染物质被去除;(8) The settled sewage is lifted to the second wetland pool 8 through the third sewage pump 13, and through double filtration and biochemical reaction of reeds and biological substrates, excess nitrogen, phosphorus, silicon and heavy metal pollutants in the sewage are removed ;

(9)第二湿地池8中自动流出的污水,经过第一水质检测井14,水质检测仪实时在线进行水质取样和检测;随后,污水自动进入第三湿地池9中,再次经过过滤和生化处理,最后自动流入第二水质检测井15,经水质检测仪检测合格后自出水管16流出。(9) The sewage automatically flowing out of the second wetland pool 8 passes through the first water quality detection well 14, and the water quality detector performs online water quality sampling and testing in real time; then, the sewage automatically enters the third wetland pool 9, and is filtered and biochemically processed again. processing, and finally automatically flows into the second water quality testing well 15, and flows out from the water outlet pipe 16 after the water quality testing instrument is qualified.

以上所述的实施例仅是对本发明的优选实施方式进行描述,并非对本发明的范围进行限定,在不脱离本发明设计精神的前提下,本领域普通技术人员对本发明的技术方案作出的各种变形和改进,均应落入本发明权利要求书确定的保护范围内。The above-mentioned embodiments are only descriptions of preferred implementations of the present invention, and are not intended to limit the scope of the present invention. Variations and improvements should fall within the scope of protection defined by the claims of the present invention.

Claims (3)

1.一种芦苇湿地污水净化系统,其特征在于,包括依次相连的第一湿地池、格栅井、调节池、厌氧池、缺氧池、好氧池、沉淀池、第二湿地池、第三湿地池;1. A reed wetland sewage purification system is characterized in that it comprises the first wetland pond, grid well, regulating pond, anaerobic pond, anoxic pond, aerobic pond, sedimentation pond, second wetland pond, The third wetland pool; 所述第一湿地池设置入水口和出水口,出水口与格栅井的入水口相连,格栅井的出水口设置在格栅井的底部与调节池相连,调节池通过水管与厌氧池的前端相连,水管上设置第一污水泵;厌氧池的出水口与缺氧池的入水口相连,缺氧池的出水口与好氧池的入水口相连,好氧池的末端与缺氧池的前端之间设置混合回流管,混合回流管上设置第二污水泵;好氧池的出水口与沉淀池相连,沉淀池通过水管与第二湿地池的入水口相连,水管上设置第三污水泵;第二湿地池的出水口与第三湿地池的入水口相连,并且两者之间设置第一水质检测井,水质检测井内设置检测仪;第三湿地池的出水口端设置第二水质检测井,第二水质检测井连接出水管,出水管上设置阀门;The first wetland pool is provided with a water inlet and a water outlet, and the water outlet is connected to the water inlet of the grid well, and the water outlet of the grid well is set at the bottom of the grid well to connect with the regulating pool, and the regulating pool is connected to the anaerobic pool through a water pipe. The front end of the anoxic pool is connected, and the first sewage pump is installed on the water pipe; the outlet of the anaerobic pool is connected with the water inlet of the anoxic pool, the outlet of the anoxic pool is connected with the water inlet of the aerobic pool, and the end of the aerobic pool is connected with the anoxic pool. A mixing return pipe is arranged between the front ends of the pool, and a second sewage pump is arranged on the mixing return pipe; the outlet of the aerobic pool is connected to the sedimentation tank, and the sedimentation tank is connected to the water inlet of the second wetland pool through a water pipe, and a third sewage pump is installed on the water pipe. Sewage pump; the water outlet of the second wetland pool is connected to the water inlet of the third wetland pool, and the first water quality testing well is set between the two, and a detector is installed in the water quality testing well; the water outlet of the third wetland pool is equipped with a second The water quality testing well, the second water quality testing well is connected to the water outlet pipe, and the valve is set on the water outlet pipe; 所述第一湿地池、第二湿地池和第三湿地池内均设置生物基质,生物基质上生长芦苇,入水口和出水口分别设置在生物基质的上方和下方;The first wetland pool, the second wetland pool and the third wetland pool are all provided with biological substrates, reeds grow on the biological substrates, and the water inlet and water outlet are respectively arranged above and below the biological substrates; 第一湿地池、格栅井、调节池从高到低排布;厌氧池、缺氧池、好氧池、沉淀池从高到低排布;第二湿地池和第三湿地池从高到低排布。The first wetland pool, grid well, and regulating pool are arranged from high to low; the anaerobic pool, anoxic pool, aerobic pool, and sedimentation pool are arranged from high to low; the second wetland pool and the third wetland pool are arranged to low profile. 2.一种利用芦苇湿地净化污水的方法,其特征在于,包括以下步骤:2. A method for utilizing reed wetlands to purify sewage, is characterized in that, comprises the following steps: (1)将污水引入第一湿地池中,第一湿地池中种植芦苇,底部填充生物基质材料,污水从芦苇根部、基质表层流过,然后自动流入格栅井;(1) Introduce the sewage into the first wetland pool, plant reeds in the first wetland pool, fill the bottom with biological matrix materials, the sewage flows through the roots of the reeds and the surface of the matrix, and then automatically flows into the grid well; (2)格栅井内布置有格栅,将水体中较大的悬浮体或颗粒截留,污水从格栅底部的出水管自动流入调节池;(2) A grid is arranged in the grid well to trap larger suspended solids or particles in the water body, and the sewage automatically flows into the regulating tank from the outlet pipe at the bottom of the grid; (3)调节池与第一污水泵相连,第一污水泵将污水提升调流进入厌氧池;(3) The adjusting tank is connected with the first sewage pump, and the first sewage pump lifts and regulates the sewage into the anaerobic tank; (4)在厌氧池中,污水中的难降解的高分子有机物转变为易被降解的低分子有机物;(4) In the anaerobic tank, the refractory high-molecular organic matter in the sewage is transformed into a low-molecular organic matter that is easily degraded; (5)污水从厌氧池的底部自动进入缺氧池中,污水在缺氧池中发生反硝化;(5) The sewage enters the anoxic pool automatically from the bottom of the anaerobic pool, and the sewage is denitrified in the anoxic pool; (6)污水从缺氧池的底部自动进入好氧池中,污水中的有机物被进一步分解成无机物;好氧池末端的污水通过第二污水泵回流至缺氧池的前端;(6) The sewage enters the aerobic pool automatically from the bottom of the anoxic pool, and the organic matter in the sewage is further decomposed into inorganic matter; the sewage at the end of the aerobic pool is returned to the front end of the anoxic pool by the second sewage pump; (7)污水从好氧池自动进入沉淀池进行初步沉淀,一些矿化物质或无法进行生化反应的污泥或颗粒物被沉淀;(7) Sewage from the aerobic tank automatically enters the sedimentation tank for preliminary precipitation, and some mineralized substances or sludge or particles that cannot undergo biochemical reactions are precipitated; (8)沉淀后的污水通过第三污水泵提升至第二湿地池中,经过芦苇和生物基质的双重过滤和生化反应,污水中过量的氮、磷、硅和重金属的污染物质被去除;(8) The settled sewage is lifted to the second wetland pool through the third sewage pump, and through the double filtration and biochemical reaction of reeds and biological substrates, the excess nitrogen, phosphorus, silicon and heavy metal pollutants in the sewage are removed; (9)第二湿地池中自动流出的污水,经过第一水质检测井,水质检测仪实时在线进行水质取样和检测;随后污水自动进入第三湿地池中,再次经过过滤和生化处理,最后自动流入第二水质检测井,经水质检测仪检测合格后流出。(9) The sewage that automatically flows out of the second wetland pool passes through the first water quality testing well, and the water quality detector performs real-time online water quality sampling and testing; then the sewage automatically enters the third wetland pool, undergoes filtration and biochemical treatment again, and finally automatically It flows into the second water quality testing well, and flows out after being tested by the water quality testing instrument. 3.根据权利要求2所述的净化污水的方法,其特征在于,所述厌氧池中的溶解氧的含量控制在0.2mg/L以下,缺氧池中的溶解氧的含量控制在0.4mg/L-0.6mg/L,好氧池中的溶解氧的含量控制在2mg/L-5mg/L。3. the method for purifying sewage according to claim 2, is characterized in that, the content of the dissolved oxygen in the described anaerobic pond is controlled below 0.2mg/L, and the content of the dissolved oxygen in the anoxic pond is controlled at 0.4mg /L-0.6mg/L, the content of dissolved oxygen in the aerobic pool is controlled at 2mg/L-5mg/L.
CN201810660693.5A 2018-06-25 2018-06-25 Reed wetland sewage purification system and effluent purification method Pending CN108975599A (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
CN201810660693.5A CN108975599A (en) 2018-06-25 2018-06-25 Reed wetland sewage purification system and effluent purification method

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
CN201810660693.5A CN108975599A (en) 2018-06-25 2018-06-25 Reed wetland sewage purification system and effluent purification method

Publications (1)

Publication Number Publication Date
CN108975599A true CN108975599A (en) 2018-12-11

Family

ID=64538692

Family Applications (1)

Application Number Title Priority Date Filing Date
CN201810660693.5A Pending CN108975599A (en) 2018-06-25 2018-06-25 Reed wetland sewage purification system and effluent purification method

Country Status (1)

Country Link
CN (1) CN108975599A (en)

Cited By (4)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN109970292A (en) * 2019-05-09 2019-07-05 中铁四川生态城投资有限公司 A rainwater storage and purification system
CN110040907A (en) * 2019-04-19 2019-07-23 徐州工程学院 The ecosystem of nitrogen phosphorus in a kind of removal aquiculture waste water
CN110330195A (en) * 2019-08-21 2019-10-15 贵州工业职业技术学院 A kind of drop wetland case treatment process of sewage
CN112299671A (en) * 2020-11-27 2021-02-02 西安建筑科技大学 System and method for treating and recycling rural sewage or black and odorous water body

Citations (11)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN101585642A (en) * 2008-05-20 2009-11-25 海斯博特(北京)科技有限公司 Sewage treatment systems based on artificial swamp
CN201722259U (en) * 2010-07-02 2011-01-26 北京特兰斯福生态环境科技发展有限公司 Two-stage descending flow type manpower wetland composite structure
CN202988927U (en) * 2012-12-27 2013-06-12 成都源创环保工程有限公司 Biological wetland treatment device for domestic sewage
CN103964649A (en) * 2014-05-26 2014-08-06 杨仲辉 Living sewage biologic wetland treatment device
CN203866154U (en) * 2014-05-06 2014-10-08 郑祖兰 Low-energy-consumption stepped sewage treatment device
CN203938558U (en) * 2014-01-10 2014-11-12 安徽锋亚环境技术有限公司 Rain, dirty dual-purpose landscape type ecological purification system
CN205473208U (en) * 2016-01-15 2016-08-17 江苏康源环保科技有限公司 Rural domestic sewage MBR of integral type and constructed wetland composite treatment device
CN106904792A (en) * 2017-03-06 2017-06-30 四川省登悦林木种植开发有限公司 For the artificial marsh sewage treatment system in city suburbs montane park
CN206359394U (en) * 2016-12-28 2017-07-28 绿地环保科技股份有限公司 Unpowered composite under-current artificial wetland sewage disposal system
CN207435269U (en) * 2017-10-30 2018-06-01 郑州源致和环保科技有限公司 A kind of bio-remediation system for being used to administer black and odorous water
CN207512045U (en) * 2017-11-17 2018-06-19 云南兆泓环境工程有限公司 A kind of rural scattered domestic sewage processing system

Patent Citations (11)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN101585642A (en) * 2008-05-20 2009-11-25 海斯博特(北京)科技有限公司 Sewage treatment systems based on artificial swamp
CN201722259U (en) * 2010-07-02 2011-01-26 北京特兰斯福生态环境科技发展有限公司 Two-stage descending flow type manpower wetland composite structure
CN202988927U (en) * 2012-12-27 2013-06-12 成都源创环保工程有限公司 Biological wetland treatment device for domestic sewage
CN203938558U (en) * 2014-01-10 2014-11-12 安徽锋亚环境技术有限公司 Rain, dirty dual-purpose landscape type ecological purification system
CN203866154U (en) * 2014-05-06 2014-10-08 郑祖兰 Low-energy-consumption stepped sewage treatment device
CN103964649A (en) * 2014-05-26 2014-08-06 杨仲辉 Living sewage biologic wetland treatment device
CN205473208U (en) * 2016-01-15 2016-08-17 江苏康源环保科技有限公司 Rural domestic sewage MBR of integral type and constructed wetland composite treatment device
CN206359394U (en) * 2016-12-28 2017-07-28 绿地环保科技股份有限公司 Unpowered composite under-current artificial wetland sewage disposal system
CN106904792A (en) * 2017-03-06 2017-06-30 四川省登悦林木种植开发有限公司 For the artificial marsh sewage treatment system in city suburbs montane park
CN207435269U (en) * 2017-10-30 2018-06-01 郑州源致和环保科技有限公司 A kind of bio-remediation system for being used to administer black and odorous water
CN207512045U (en) * 2017-11-17 2018-06-19 云南兆泓环境工程有限公司 A kind of rural scattered domestic sewage processing system

Cited By (4)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN110040907A (en) * 2019-04-19 2019-07-23 徐州工程学院 The ecosystem of nitrogen phosphorus in a kind of removal aquiculture waste water
CN109970292A (en) * 2019-05-09 2019-07-05 中铁四川生态城投资有限公司 A rainwater storage and purification system
CN110330195A (en) * 2019-08-21 2019-10-15 贵州工业职业技术学院 A kind of drop wetland case treatment process of sewage
CN112299671A (en) * 2020-11-27 2021-02-02 西安建筑科技大学 System and method for treating and recycling rural sewage or black and odorous water body

Similar Documents

Publication Publication Date Title
CN102464404B (en) Method and system for remediation and treatment of polluted river water
CN102557350A (en) Purification system for micro-polluted raw water and purification method thereof
CN108975599A (en) Reed wetland sewage purification system and effluent purification method
CN107352738B (en) A composite artificial ecological bed sewage treatment system and method for strengthening nitrogen and phosphorus removal
CN204848564U (en) Handle rural domestic sewage's domestic type system
CN203212433U (en) Rural sewage treatment system
CN111484206A (en) Simulate natural environment biological sewage treatment system
CN113003757A (en) Integrated rural water supply treatment device and method
CN206553350U (en) A kind of two-stage manual controlled infusion of intensified denitrification and dephosphorization
CN103159380A (en) Zero-energy-consumption sewage treatment system and method for constructed wetlands
CN101514068A (en) Method for employing anaerobic-aerobic combined biological filter to process domestic sewage
CN108996814B (en) Urban sewage and rainwater combined treatment process
CN108751600A (en) Utilize the sewage disposal system and sewage water treatment method of multiple muskeg group
CN203112657U (en) Constant-effluent variable-load SVBR (Steady outflow Variable load Biological Reactor) sewage treater
CN210438573U (en) Stifled oxygenation type constructed wetland system of inhibiting
CN209210593U (en) A kind of town sewage treatment system
CN205382060U (en) Villages and small towns domestic sewage ecologization oligodynamic treatment system
CN101279805A (en) Membrane drinking water treatment process and equipment
CN101333029A (en) Artificial aeration type compound subsurface flow wetland sewage purification process
CN212246689U (en) An intelligent treatment device for rural unconventional water
CN202492434U (en) Micro-pollution raw water purification system
CN109368941A (en) A kind of urban wastewater treatment device and its application
CN211255623U (en) Distributed rural domestic sewage treatment system
CN202175603U (en) Integrated non-point source sewage treatment system
CN210595462U (en) A dual-chamber artificial rapid infiltration sewage purification system

Legal Events

Date Code Title Description
PB01 Publication
PB01 Publication
SE01 Entry into force of request for substantive examination
SE01 Entry into force of request for substantive examination
RJ01 Rejection of invention patent application after publication
RJ01 Rejection of invention patent application after publication

Application publication date: 20181211