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CN102976564B - Continuous rural domestic waste water treating device - Google Patents

Continuous rural domestic waste water treating device Download PDF

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Publication number
CN102976564B
CN102976564B CN201210565113.7A CN201210565113A CN102976564B CN 102976564 B CN102976564 B CN 102976564B CN 201210565113 A CN201210565113 A CN 201210565113A CN 102976564 B CN102976564 B CN 102976564B
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aerobic
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aerobic zone
anaerobic
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CN102976564A (en
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马建锋
杨彦
姚超
李定龙
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Jiangsu Hongye Testing Technology Co ltd
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Changzhou University
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Abstract

The invention discloses a continuous rural domestic waste water treating device, wherein the inner space of a rectangular shell is divided into an anaerobic zone, an anoxic zone, an aerobic zone and a biological filtering zone; the biological filtering zone is arranged at the upper part in the aerobic zone; biological stuffing is suspended in the aerobic zone; active carbon is filled in the biological filtering zone; a first float is arranged on the liquid level in the anoxic zone; one end of a first pump is connected to the middle lower part of the anoxic zone, while the other end of the first pump extends between the housing wall of the aerobic zone and the housing wall of the biological filtering zone from the top of the aerobic zone; the pipe end extending between the two housing walls comprises a venturi tube; the opening of the venturi tube is downwards; a baffle plate is arranged right under the opening; a flow guide plate is arranged right under the baffle plate, and put on a second floating ball floating on the liquid level of the aerobic zone; a second float further floats on the liquid level of the aerobic zone; and a second pump is arranged between the aerobic zone and the biological filtering zone. The continuous rural domestic waste water treating device integrates the anaerobic zone, the anoxic zone, the aerobic zone and the biological filtering zone into a whole, thus being small in floor area, high in treating rate and high in automation degree.

Description

一种农村生活污水废水连续处理装置 A continuous treatment device for domestic sewage and wastewater in rural areas

技术领域 technical field

本发明涉及废水处理装置,尤其涉及对农村生活污水废水进行连续处理的装置。 The invention relates to a waste water treatment device, in particular to a device for continuous treatment of rural domestic sewage and waste water.

背景技术 Background technique

当前,我国农村的大多数生活污水直接排放,造成河流、水塘污染,不仅影响村民居住环境,而且严重威胁了农民的身体健康。而目前,农村普遍存在基础设施建设薄弱、排水系统和污水处理建设不够完善等诸多问题。当前农村污水处理主要有两种工艺,一种为膜生物反应器(MBR)工艺,另一种为人工湿地工艺。膜生物反应器是是膜分离技术和活性污泥生物技术的结合,其高效的固液分离使出水水质良好,悬浮物和浊度接近于零,生活污水处理后可直接回用。污水首先经化粪池厌氧消化,降低有机物负荷。但也存在很多缺点,主要体现在膜的​​价格比较高,膜污染问题并没有得到彻底解决,如物理性的堵塞、化学性的结构及生物性的污染,从而造成更换周期短、运行维护成本高,另外就是MBR的生化功能并未改变生化本质。人工湿地工艺是农村生活污水经化粪池处理后,上清液通过集水管道进入进水井,经过格栅流入沉淀池,经沉淀的上清液用泵扬入一级人工湿地,而后再进入二级人工湿地,二级人工湿地的出水回流至清水池,可供绿化、灌溉,也可溢流至附近坑塘,但该工艺需要有较大的土地和相应的温度,比如在冬天,该工艺在使用上有很大的局限。 At present, most of the domestic sewage in rural areas of our country is directly discharged, causing pollution of rivers and ponds, which not only affects the living environment of villagers, but also seriously threatens the health of farmers. At present, there are many problems in rural areas such as weak infrastructure construction, inadequate drainage system and sewage treatment construction. At present, there are two main processes for rural sewage treatment, one is the membrane bioreactor (MBR) process, and the other is the constructed wetland process. Membrane bioreactor is a combination of membrane separation technology and activated sludge biotechnology. Its efficient solid-liquid separation makes the effluent water quality good, suspended solids and turbidity close to zero, and domestic sewage can be directly reused after treatment. Sewage is first anaerobically digested in a septic tank to reduce the load of organic matter. But there are also many shortcomings, mainly reflected in the relatively high price of the membrane, and the problem of membrane fouling has not been completely solved, such as physical clogging, chemical structure and biological pollution, resulting in short replacement cycles and poor operation and maintenance. The cost is high, and the biochemical function of MBR has not changed the biochemical essence. The constructed wetland process is that after the rural domestic sewage is treated in a septic tank, the supernatant enters the water inlet well through the water collection pipe, flows into the sedimentation tank through the grid, and the settled supernatant is pumped into the first-level constructed wetland with a pump, and then enters the Second-level constructed wetland, the effluent of the second-level constructed wetland returns to the clear water pond, which can be used for greening, irrigation, and can also overflow to nearby ponds, but this process requires large land and corresponding temperature. For example, in winter, the Technology has great limitations in use.

发明内容 Contents of the invention

本发明的目的是为克服现有技术的不足,提供一种农村生活污水废水连续处理装置,该装置运行过程中所需的能耗小、成本低、自动化程度高、无需人工操作且无污染。 The purpose of the present invention is to overcome the deficiencies of the prior art and provide a continuous treatment device for rural domestic sewage and wastewater. The device requires less energy consumption, low cost, high degree of automation, no manual operation and no pollution during operation.

本发明采用的技术方案是:包含一个长方形壳体,长方形壳体内隔有厌氧区、兼氧区、好氧区、生物过滤区四部分,厌氧区隔壁是兼氧区,好氧区呈L型,从厌氧区和兼氧区的底部延伸至兼氧区的旁侧,好氧区内的上部是生物过滤区,好氧区内悬挂有生物填料,生物过滤区内填充有活性炭;厌氧区和兼氧区之间有出水管道相连,兼氧区中的液面上放置第一浮标,第一浮标通过第一杠杆连接自动开关;第一泵一端通过管路连接于兼氧区的中下部、另一端通过管路从好氧区顶部伸在好氧区的壳体壁和生物过滤区的壳体壁之间,并且伸在两个所述壳体壁之间的该管路端包含一个文丘里管和一个连接文丘里管最窄区的空气管,空气管另一端伸到壳体外;文丘里管的开口朝向下方,该开口的正下部设有挡板,挡板的正下部设置高度低于生物过滤区底部的导流板,导流板一端活动连接好氧区的壳体内壁、另一端搭放在漂浮在好氧区液面上的第二浮球上;好氧区的液面上还漂浮有第二浮标,第二浮标通过第二杠杆连接自动延时开关;好氧区和生物过滤区之间设置第二泵,第二泵的出水管路伸在生物过滤区的顶部。 The technical solution adopted in the present invention is: it includes a rectangular shell, which is divided into four parts: anaerobic zone, facultative zone, aerobic zone, and biological filtration zone. L type, extending from the bottom of the anaerobic zone and the facultative zone to the side of the facultative zone, the upper part of the aerobic zone is a biological filtration zone, the aerobic zone is suspended with biological fillers, and the biological filter zone is filled with activated carbon; The anaerobic zone and the anaerobic zone are connected by an outlet pipeline, and the first buoy is placed on the liquid surface in the anaerobic zone, and the first buoy is connected to the automatic switch through the first lever; one end of the first pump is connected to the anaerobic zone through a pipeline The middle and lower part, the other end extends from the top of the aerobic zone through the pipeline between the shell wall of the aerobic zone and the shell wall of the biofiltration zone, and the pipeline stretched between the two shell walls One end contains a Venturi tube and an air tube connected to the narrowest area of the Venturi tube. The lower part is provided with a deflector whose height is lower than the bottom of the biological filtration zone. One end of the deflector is movably connected to the inner wall of the shell of the aerobic zone, and the other end is placed on the second floating ball floating on the liquid surface of the aerobic zone; the aerobic zone There is also a second buoy floating on the liquid surface of the zone, and the second buoy is connected to the automatic delay switch through the second lever; a second pump is set between the aerobic zone and the biofiltration zone, and the outlet pipe of the second pump extends in the biofiltration zone. top of the area.

本发明的有益效果是: The beneficial effects of the present invention are:

1、本发明设备是集厌氧、兼氧、好氧、生物过滤室于一体的污水处理装置,该设备占地面积小、处理率高、处理过程投资小、操作简单费用低、自动化程度高。 1. The equipment of the present invention is a sewage treatment device integrating anaerobic, facultative oxygen, aerobic, and biological filtration chambers. The equipment occupies a small area, has a high treatment rate, small investment in the treatment process, simple operation, low cost, and high degree of automation .

2、在好氧区不需要曝气装置,降低污水处理的成本。 2. No aeration device is needed in the aerobic zone, reducing the cost of sewage treatment.

3、所有过程全自动控制,有液位控制泵开关,无需人工操作。 3. All processes are fully automatic control, with liquid level control pump switch, without manual operation.

附图说明 Description of drawings

图1是本发明的结构示意图; Fig. 1 is a structural representation of the present invention;

图中:Ⅰ.厌氧区;Ⅱ.兼氧区;Ⅲ.好氧区;Ⅳ.生物过滤区; In the figure: Ⅰ. Anaerobic zone; Ⅱ. Facultative oxygen zone; Ⅲ. Aerobic zone; Ⅳ. Biological filtration zone;

1.壳体;2.进水管道;3.出水管道;4.排泥口;5.浮标;6.自动开关;7.杠杆;8.泵;9.管路;10.文丘里管;11.空气管;12.挡板;13.导流板;14.浮球;15.生物填料;16.浮标;17.自动延时开关;18.杠杆;19.泵;20.管路;21.活性炭;22.出口。 1. Shell; 2. Inlet pipe; 3. Outlet pipe; 4. Mud outlet; 5. Buoy; 6. Automatic switch; 7. Lever; 8. Pump; 9. Pipeline; 10. Venturi tube; 11. Air pipe; 12. Baffle; 13. Deflector; 14. Float; 15. Biological filler; 16. Buoy; 17. Automatic delay switch; 18. Lever; 21. Activated carbon; 22. Export.

具体实施方式 Detailed ways

如图1所示,处理设备包含一个长方形壳体1,长方形壳体1内用隔墙隔成四个部分,分别是厌氧区Ⅰ、兼氧区Ⅱ、好氧区Ⅲ、生物过滤区Ⅳ这四个部分,污水从进水管道2从厌氧区Ⅰ顶部进入到厌氧区Ⅰ,厌氧区Ⅰ有盖子呈半封闭状态,厌氧区Ⅰ在该四个区中,所占体积最大,废水停留时间最长,厌氧区Ⅰ隔壁是兼氧区Ⅱ,厌氧区Ⅰ和兼氧区Ⅱ之间用一隔墙隔开,好氧区Ⅲ呈L型,从厌氧区Ⅰ和兼氧区Ⅱ的底部延伸至兼氧区Ⅱ的旁侧,在好氧区Ⅲ内的上部位置隔成一个生物过滤区Ⅳ。 As shown in Figure 1, the processing equipment includes a rectangular shell 1, which is divided into four parts by a partition wall, which are anaerobic zone I, facultative zone II, aerobic zone III, and biological filtration zone IV. In these four parts, the sewage enters the anaerobic zone I from the top of the anaerobic zone I through the water inlet pipe 2. The anaerobic zone I has a cover and is in a semi-closed state. The anaerobic zone I occupies the largest volume among the four zones. , the residence time of wastewater is the longest, the next door of anaerobic zone I is facultative zone II, anaerobic zone I and facultative zone II are separated by a partition wall, aerobic zone III is L-shaped, from anaerobic zone I and facultative zone II The bottom of facultative zone II extends to the side of facultative zone II, and the upper part of aerobic zone III is separated into a biological filtration zone IV.

厌氧区Ⅰ和兼氧区Ⅱ之间有出水管道3相连,出水管道3位于厌氧区Ⅰ和兼氧区Ⅱ之间隔墙的中下部,利于污泥沉淀于厌氧区Ⅰ而不流向兼氧区Ⅱ,废水可以从厌氧区Ⅰ自动流向兼氧区Ⅱ。在厌氧区Ⅰ有一个排泥口4,污泥可以从排泥口4排出。兼氧区Ⅱ中的液面上放置浮标5,浮标5通过杠杆7连接自动开关6,当水位达到一定高度,浮标5带动杠杆7接通自动开关6。 Anaerobic zone I and facultative zone II are connected by outlet pipe 3, and outlet pipe 3 is located in the middle and lower part of the partition wall between anaerobic zone I and facultative zone II, which is beneficial for sludge to settle in anaerobic zone I instead of flowing to the anaerobic zone In the aerobic zone II, wastewater can automatically flow from the anaerobic zone I to the facultative zone II. There is a sludge outlet 4 in the anaerobic zone I, and the sludge can be discharged from the sludge outlet 4. A buoy 5 is placed on the liquid surface in the aerobic zone II, and the buoy 5 is connected to the automatic switch 6 through the lever 7. When the water level reaches a certain height, the buoy 5 drives the lever 7 to switch on the automatic switch 6.

在兼氧区Ⅱ和好氧区Ⅲ之间设置泵8,泵8一端通过管路9连接于兼氧区Ⅱ的中下部,另一端通过管路9连通好氧区Ⅲ顶部内。位于好氧区Ⅲ内的管路9伸在好氧区Ⅲ的壳体壁和生物过滤区Ⅳ的壳体壁之间,并且位于好氧区Ⅲ内的管路9这端包含一个文丘里管10和一个与文丘里管10相连接的空气管11,空气管11的一端连接在文丘里管10的最窄区,空气管11另一端伸到壳体1外,且比壳体1的上端略高。文丘里管10的开口朝向下方,在文丘里管10正下部设置挡板12,挡板12的正下部设置导流板13。挡板12的高度与生物过滤区Ⅳ的底部高度相当,导流板13的高度低于生物过滤区Ⅳ的底部,挡板12可固定在好氧区Ⅲ的壳体内壁上,导流板13一端活动连接在好氧区Ⅲ的壳体内壁上,导流板13另一端搭放在浮球14上,浮球14漂浮在好氧区Ⅲ的液面上。在好氧区Ⅲ的液面上还漂浮浮标16,浮标16通过杠杆18连接自动延时开关17,好氧区Ⅲ的液位由浮标16连接自动延时开关17控制,当水位达到一定高度,浮标16带动杠杆18接通自动延时开关17。在好氧区Ⅲ内悬挂生物填料15,供微生物附着生长。在好氧区Ⅲ和生物过滤区Ⅳ之间设置泵19,泵19的入水管路20伸至好氧区Ⅲ的最里端,以避免好氧区产生死角,同时也避免了好氧反应区水流短路,增加了水流流程。泵19的出水管路20伸在生物过滤区Ⅳ的顶部。在生物过滤区Ⅳ内填充有活性炭21,活性炭21表面生长有微生物。 A pump 8 is set between the facultative zone II and the aerobic zone III, one end of the pump 8 is connected to the middle and lower part of the facultative zone II through the pipeline 9, and the other end is connected to the top of the aerobic zone III through the pipeline 9. The pipeline 9 located in the aerobic zone III extends between the shell wall of the aerobic zone III and the shell wall of the biofiltration zone IV, and the end of the pipeline 9 located in the aerobic zone III contains a Venturi tube 10 and an air pipe 11 connected to the Venturi tube 10, one end of the air pipe 11 is connected to the narrowest area of the Venturi pipe 10, and the other end of the air pipe 11 extends out of the housing 1, and is lower than the upper end of the housing 1 slightly higher. The opening of the venturi tube 10 faces downward, and a baffle plate 12 is provided directly under the venturi tube 10 , and a deflector 13 is provided directly under the baffle plate 12 . The height of the baffle plate 12 is equivalent to the height of the bottom of the biological filtration zone IV, the height of the deflector 13 is lower than the bottom of the biological filtration zone IV, the baffle plate 12 can be fixed on the inner wall of the shell of the aerobic zone III, the deflector plate 13 One end is movably connected to the inner wall of the shell of the aerobic zone III, and the other end of the deflector 13 is placed on the floating ball 14, and the floating ball 14 floats on the liquid surface of the aerobic zone III. A buoy 16 is also floating on the liquid surface of the aerobic zone III, and the buoy 16 is connected to an automatic time-delay switch 17 through a lever 18. The liquid level of the aerobic zone III is controlled by the buoy 16 connected to the automatic time-delay switch 17. When the water level reaches a certain height, The buoy 16 drives the lever 18 to connect the automatic delay switch 17. The biological filler 15 is suspended in the aerobic zone III for the attachment and growth of microorganisms. A pump 19 is set between the aerobic zone III and the biological filtration zone IV, and the water inlet pipe 20 of the pump 19 extends to the innermost end of the aerobic zone III, so as to avoid dead ends in the aerobic zone and also avoid the aerobic reaction zone The water flow is short-circuited, increasing the flow of water flow. The outlet pipe 20 of the pump 19 extends at the top of the biological filtration zone IV. Activated carbon 21 is filled in the biological filtration zone IV, and microorganisms grow on the surface of the activated carbon 21 .

当污水从进水管道2进入到厌氧区Ⅰ,启动泵8,通过管路9将水排向好氧区Ⅲ,当泵8将水打入好氧区Ⅲ时,在文丘里管10产生负压,通过空气管11将空气带入水中,增加水中溶解氧浓度,当由于兼氧区Ⅱ水位下降而浮标5带动杠杆7断开自动开关6后,管路9可以形成虹吸,泵8继续将废水从兼氧区Ⅱ引入好氧区Ⅲ,当水从文丘里管10流出后,遇到挡板12,水在挡板12上撞击后增加溶解氧浓度,经过挡板12后,再流到导流板13,水通过导流板13流到远离兼氧区Ⅱ的部分,避免产生处理死角。当好氧区Ⅲ水位达到一定高度,浮标16带动杠杆18接通自动延时开关17,启动泵19,启动泵19,通过管路20将水排向生物过滤区Ⅳ,水流从生物过滤区Ⅳ上端淋下,活性炭21表面生长有微生物,通过生物填料15表面附着的生物处理后,溢流从出口22排出。 When the sewage enters the anaerobic zone Ⅰ from the water inlet pipe 2, the pump 8 is started, and the water is discharged to the aerobic zone Ⅲ through the pipeline 9. When the pump 8 pumps the water into the aerobic zone Ⅲ, an Negative pressure brings air into the water through the air pipe 11 to increase the dissolved oxygen concentration in the water. When the buoy 5 drives the lever 7 to disconnect the automatic switch 6 due to the drop in the water level of the aerobic zone II, the pipe 9 can form a siphon, and the pump 8 continues The waste water is introduced from the facultative zone II into the aerobic zone III. When the water flows out from the Venturi tube 10, it encounters the baffle 12. After the water hits the baffle 12, the concentration of dissolved oxygen increases. After passing through the baffle 12, it flows again. To the deflector 13, the water flows through the deflector 13 to the part away from the aerobic zone II, so as to avoid the generation of treatment dead angle. When the water level in the aerobic area III reaches a certain height, the buoy 16 drives the lever 18 to switch on the automatic delay switch 17, starts the pump 19, starts the pump 19, and discharges the water to the biological filtration area IV through the pipeline 20, and the water flows from the biological filtration area IV. When the upper end is poured down, there are microorganisms growing on the surface of the activated carbon 21 , and after the biological treatment attached to the surface of the biological filler 15 , the overflow is discharged from the outlet 22 .

Claims (3)

1. a domestic sewage in rural areas by using waste water apparatus for continous treatment, comprise a rectangle housing (1), it is characterized in that: in rectangle housing (1), be separated with anaerobic zone (I), aerobic area (II), aerobic zone (III), biofiltration district (IV) four parts, next door, anaerobic zone (I) is aerobic area (II), aerobic zone (III) is L-type, from anaerobic zone, the bottom of (I) and aerobic area (II) extends to the side of aerobic area (II), top in aerobic zone (III) is biofiltration district (IV), in aerobic zone (III), be hung with biologic packing material (15), in biofiltration district (IV), be filled with gac (21),
Between anaerobic zone (I) and aerobic area (II), have outlet conduit (3) to be connected, place the first buoy (5) on the liquid level in aerobic area (II), the first buoy (5) connects auto-switch (6) by the first lever (7);
Middle and lower part, the other end that the first pump (8) one end is connected in aerobic area (II) by pipeline by pipeline between the housing wall of Shen aerobic zone, top, aerobic zone (III) (III) and the housing wall of biofiltration district (IV), and this pipeline end of stretching between two described housing walls comprises a Venturi tube (10) is connected Venturi tube (10) Zhai district blast main (11) with one, and blast main (11) the other end reaches outside housing (1); The opening of Venturi tube (10) downward, the positive bottom of this opening is provided with baffle plate (12), the positive bottom of baffle plate (12) arranges height lower than the flow deflector (13) of biofiltration district (IV) bottom, and inner walls, the other end of flexible connection aerobic zone, flow deflector (13) one end (III) taken and be placed on the ball float (14) swimming on the liquid level of aerobic zone (III); Also floating on the liquid level of aerobic zone (III) have the second buoy (16), and the second buoy (16) connects Auto-delay switch (17) by the second lever (18); Between aerobic zone (III) and biofiltration district (IV), the second pump (19) is set, the top in the outlet pipeline Shen biofiltration district (IV) of the second pump (19).
2. a kind of domestic sewage in rural areas by using waste water apparatus for continous treatment according to claim 1, it is characterized in that: from inlet channel (2), from anaerobic zone, (I) top enters into anaerobic zone (I) to sewage, on anaerobic zone (I), be stamped lid, lid is semi-closed state, and anaerobic zone (I) shared volume in described four parts is maximum.
3. a kind of domestic sewage in rural areas by using waste water apparatus for continous treatment according to claim 1, is characterized in that: outlet conduit (3) is positioned at the middle and lower part between anaerobic zone (I) and aerobic area (II), and anaerobic zone (I) is provided with a mud discharging mouth (4).
CN201210565113.7A 2012-12-24 2012-12-24 Continuous rural domestic waste water treating device Expired - Fee Related CN102976564B (en)

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* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN2186239Y (en) * 1994-04-04 1994-12-28 孙乔良 Multifunction efficient aerobic pool
JP3214291B2 (en) * 1995-04-21 2001-10-02 日立化成工業株式会社 Sewage septic tank
CN1176860C (en) * 2002-10-31 2004-11-24 大连理工大学 An anaerobic-facultative-aerobic integrated sewage treatment equipment and method including reuse
CN2743884Y (en) * 2004-09-17 2005-11-30 周继春 Multifunctional liquid level controller
CN102701452B (en) * 2012-06-01 2013-10-30 华南理工大学 Closed-loop control system for treating landfill leachate in cooperation with partial nitrosation and denitrification and denitrifying and decarburizing method thereof

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