CN204973155U - Surface water drinking water purifies double -deck advection formula sedimentation tank - Google Patents
Surface water drinking water purifies double -deck advection formula sedimentation tank Download PDFInfo
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- CN204973155U CN204973155U CN201520221220.7U CN201520221220U CN204973155U CN 204973155 U CN204973155 U CN 204973155U CN 201520221220 U CN201520221220 U CN 201520221220U CN 204973155 U CN204973155 U CN 204973155U
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- 238000004062 sedimentation Methods 0.000 title claims abstract description 51
- 239000003651 drinking water Substances 0.000 title claims abstract description 15
- 235000020188 drinking water Nutrition 0.000 title claims abstract description 15
- 239000002352 surface water Substances 0.000 title claims abstract description 15
- 239000010802 sludge Substances 0.000 claims abstract description 39
- XLYOFNOQVPJJNP-UHFFFAOYSA-N water Substances O XLYOFNOQVPJJNP-UHFFFAOYSA-N 0.000 claims abstract description 39
- 239000011449 brick Substances 0.000 claims description 3
- 238000001556 precipitation Methods 0.000 claims description 2
- 238000007599 discharging Methods 0.000 claims 2
- 239000004568 cement Substances 0.000 claims 1
- 239000011505 plaster Substances 0.000 claims 1
- 239000004576 sand Substances 0.000 claims 1
- 239000013049 sediment Substances 0.000 claims 1
- 238000000746 purification Methods 0.000 abstract description 8
- 230000002706 hydrostatic effect Effects 0.000 abstract description 7
- 239000011083 cement mortar Substances 0.000 description 2
- 230000000694 effects Effects 0.000 description 2
- 238000005265 energy consumption Methods 0.000 description 2
- 230000009286 beneficial effect Effects 0.000 description 1
- 238000010276 construction Methods 0.000 description 1
- 230000007423 decrease Effects 0.000 description 1
- 238000005516 engineering process Methods 0.000 description 1
- 230000005484 gravity Effects 0.000 description 1
- 238000000034 method Methods 0.000 description 1
- 239000002245 particle Substances 0.000 description 1
- 230000021715 photosynthesis, light harvesting Effects 0.000 description 1
- 238000007790 scraping Methods 0.000 description 1
- 238000000926 separation method Methods 0.000 description 1
- 239000010865 sewage Substances 0.000 description 1
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- Treatment Of Sludge (AREA)
Abstract
本实用新型公开了一种地表水饮水净化双层平流式沉淀池,池体包括上下两层,下层池体右边的进水口位置设置有进水穿孔花墙,下层池体通过上层内部左侧的进水穿孔花墙与上层池体相通,下层池体设置有多排污泥斗,每排污泥斗之间的底部设置排泥管,排泥管上端与排泥总管相连;池体上层排泥区池底纵坡不小于0.01,上层排泥区右侧坡底设置单排污泥斗,在上层池体上设置有刮泥行车为上层池体底部去除污泥,上层池体右上方设置指形出水堰,指形出水堰末端设置有集水总管。克服现有平流式沉淀池采用静水压力排泥导致的排泥不畅问题、解决平流式沉淀池占地面积较大等问题。
The utility model discloses a double-layer advection sedimentation tank for surface water drinking water purification. The tank body includes upper and lower layers; The water perforated flower wall is connected with the upper pool body, the lower pool body is equipped with multiple rows of sludge hoppers, and the bottom of each row of sludge hoppers is equipped with a mud discharge pipe, and the upper end of the mud discharge pipe is connected with the mud discharge main pipe; the upper mud discharge area of the pool body The longitudinal slope at the bottom of the pool is not less than 0.01. A single row of sludge hoppers is installed at the bottom of the slope on the right side of the upper mud discharge area. A mud scraper is installed on the upper pool body to remove sludge from the bottom of the upper pool body. Outlet weir, the end of the finger-shaped outflow weir is provided with a water collection main pipe. It overcomes the problem of poor mud discharge caused by the hydrostatic pressure mud discharge in the existing advection sedimentation tank, and solves the problems such as the large floor area of the advection sedimentation tank.
Description
技术领域technical field
本实用新型属于给水和排水工程技术领域,涉及一种地表水饮水净化双层平流式沉淀池,适用于高浊度地表水源饮水净化的沉淀池,亦适用于污水处理系统中的初次沉淀池。The utility model belongs to the technical field of water supply and drainage engineering, and relates to a double-layer advection sedimentation tank for drinking water purification of surface water, which is suitable for a sedimentation tank for drinking water purification of surface water sources with high turbidity, and is also suitable for a primary sedimentation tank in a sewage treatment system.
背景技术Background technique
高浊度地表水饮水净化工程中沉淀池是整个净化系统中必不可少的构筑物,目前地表水人饮工程多采用的沉淀池型式有平流式、辐流式和竖流式等。其中,平流式沉淀池因构造简单、沉淀效果较好、性能稳定、对冲击负荷和温度变化的适应能力强等,是我国自来水厂应用最早、大中型水厂使用最广的泥水分离构筑物。然而,从排泥经济性考虑,绝大多数采用静水压力排泥的平流式沉淀池常常因静水压力过小导致排泥不畅;另外,平流式沉淀池占地面积一般较大,需要进一步提高沉淀效率以解决占地面积较大的问题。平流式沉淀池这些突出的问题是沉淀技术发展中急需研究和解决的问题。The sedimentation tank is an indispensable structure in the whole purification system in the drinking water purification project of high turbidity surface water. At present, the types of sedimentation tanks used in the surface water drinking water project are advection type, radial flow type and vertical flow type. Among them, the advection sedimentation tank is the earliest and most widely used mud-water separation structure in waterworks in my country due to its simple structure, good sedimentation effect, stable performance, and strong adaptability to impact loads and temperature changes. However, considering the economy of sludge discharge, most advection sedimentation tanks that use hydrostatic pressure for sludge discharge often have poor sludge discharge due to too low hydrostatic pressure; in addition, advection sedimentation tanks generally occupy a large area and need to be further improved. Sedimentation efficiency to solve the problem of large footprint. These outstanding problems in the advection sedimentation tank are urgently needed to be studied and solved in the development of sedimentation technology.
实用新型内容Utility model content
本实用新型的目的是提供一种地表水饮水净化双层平流式沉淀池,克服现有平流式沉淀池采用静水压力排泥导致的排泥不畅问题、解决平流式沉淀池占地面积较大等问题,该双层沉淀池可利用上下两层沉淀区的静水压力实现下层沉淀区顺畅排泥,上层沉淀区则通过加设刮泥行车,提高沉淀池工作效率,从而有效克服了常规平流式沉淀池占地面积较大的问题。The purpose of this utility model is to provide a double-layer advection sedimentation tank for surface water drinking water purification, which overcomes the problem of poor mud discharge caused by hydrostatic pressure in the existing advection sedimentation tank, and solves the problem that the advection sedimentation tank occupies a large area. and other problems, the double-layer sedimentation tank can use the hydrostatic pressure of the upper and lower sedimentation areas to realize the smooth discharge of mud in the lower sedimentation area, and the upper sedimentation area can improve the working efficiency of the sedimentation tank by adding mud scraping trucks, thus effectively overcoming the conventional advection. The problem that the sedimentation tank occupies a large area.
本实用新型所采用的技术方案是,一种地表水饮水净化双层平流式沉淀池,池体包括上下两层,下层池体右边的进水口位置设置有进水穿孔花墙,下层池体通过上层内部左侧的进水穿孔花墙与上层池体相通,下层池体设置有多排污泥斗,每排污泥斗之间的底部设置排泥管,排泥管上端与排泥总管相连;池体上层排泥区池底纵坡不小于0.01,上层排泥区右侧坡底设置单排污泥斗,在上层池体上设置有刮泥行车为上层池体底部去除污泥,上层池体右上方设置指形出水堰,指形出水堰末端设置有集水总管。The technical scheme adopted by the utility model is a double-layer advection sedimentation tank for surface water drinking water purification. The tank body includes upper and lower layers. The water inlet perforated flower wall on the left side of the interior is connected to the upper pool body, and the lower pool body is equipped with multiple rows of sludge hoppers, and the bottom of each row of sludge hoppers is equipped with a mud discharge pipe, and the upper end of the mud discharge pipe is connected to the mud discharge main pipe; The longitudinal slope of the pool bottom in the upper mud discharge area is not less than 0.01. A single row of sludge buckets is installed at the bottom of the slope on the right side of the upper mud discharge area. A mud scraper is installed on the upper pool to remove sludge from the bottom of the upper pool. A finger-shaped water outlet weir is arranged on the upper right, and a water collection main pipe is arranged at the end of the finger-shaped water outlet weir.
本实用新型的特征还在于,污泥斗边壁倾角为60°。The utility model is also characterized in that the inclination angle of the side wall of the sludge bucket is 60°.
集水总管上安装的出水总管。Outlet mains installed on water collection mains.
进水穿孔花墙采用砖砌或混凝土砌块砌筑,孔眼之外部分采用水泥砂浆抹面,进水穿孔花墙上下排进水孔眼错开布置,同时在沉淀面以上0.3m-0.5m处至池底部分的墙不设孔眼。The water inlet perforated flower wall is built with bricks or concrete blocks, and the parts outside the holes are plastered with cement mortar. The upper and lower water inlet holes of the water inlet perforated flower wall are arranged in a staggered manner, and at the same time, they are 0.3m-0.5m above the sedimentation surface to the pool bottom. The walls have no perforations.
池体的上层沉淀区、下层沉淀区的长宽比不小于4,长深比不小于10,沉淀区断面逐渐扩大。The aspect ratio of the upper sedimentation zone and the lower sedimentation zone of the pool body is not less than 4, and the aspect ratio is not less than 10, and the section of the sedimentation zone gradually expands.
指形出水堰的槽的深度为0.3~0.5m。The depth of the groove of the finger-shaped weir is 0.3-0.5m.
本实用新型的有益效果是:The beneficial effects of the utility model are:
1.结构简单、占地面积小、造价低、容易建造。该沉淀池虽采用双层布置,但上下层沉淀区构造简单,土建设施可现浇或预制,易于施工,排泥装置安装方便,双层结构实际上扩充了沉淀区域,总占地面积较小。1. Simple structure, small footprint, low cost and easy construction. Although the settling tank adopts double-layer arrangement, the structure of the upper and lower settling areas is simple, the civil facilities can be cast-in-place or prefabricated, which is easy to construct, and the mud discharge device is easy to install. The double-layer structure actually expands the settling area, and the total occupied area is small .
2.沉淀效率高。高浊度水首先进入下层沉淀区,经沉淀后再进入上层沉淀区,大大减轻了上层沉淀区的设计负荷,保障了上层沉淀区获得良好的出水水质。从整体上看,沉淀效率较高。2. High precipitation efficiency. High turbidity water first enters the lower sedimentation area, and then enters the upper sedimentation area after sedimentation, which greatly reduces the design load of the upper sedimentation area and ensures good effluent water quality in the upper sedimentation area. On the whole, the sedimentation efficiency is higher.
3.能耗低。该双层沉淀池下层排泥可资利用的静水压力较高,排泥顺畅,无需额外能耗。3. Low energy consumption. The hydrostatic pressure available for sludge discharge in the lower layer of the double-layer sedimentation tank is relatively high, and the sludge discharge is smooth without additional energy consumption.
附图说明Description of drawings
图1是本实用新型的平面示意图。Fig. 1 is a schematic plan view of the utility model.
图2是图1中A-A面剖视图。Fig. 2 is a sectional view of plane A-A in Fig. 1 .
图3是图1中B-B面剖视图。Fig. 3 is a sectional view of plane B-B in Fig. 1 .
图中,1-进水穿孔花墙;2-指形出水堰;3-集水总管;4-出水总管;5-刮泥行车;6-污泥斗;7-排泥管;i-池底坡度。In the figure, 1-water inlet perforated flower wall; 2-finger-shaped water outlet weir; 3-collection main pipe; 4-water outlet main pipe; 5-mud scraper driving; 6-sludge bucket; slope.
具体实施方式detailed description
下面结合附图和具体实施方式对本实用新型进行详细说明。The utility model will be described in detail below in conjunction with the accompanying drawings and specific embodiments.
一种地表水饮水净化双层平流式沉淀池的结构,如图1-3所示,由下层进水区、下层沉淀区、上层进水区、上层沉淀区、出水区、下层排泥区和上层排泥区组成。The structure of a double layer advection sedimentation tank for surface water drinking water purification, as shown in Fig. The upper mud discharge area is composed.
上层进水区、下层进水区均采用进水穿孔花墙1配水,起均匀补水与消能作用。进水穿孔花墙1采用砖砌或混凝土砌块砌筑,孔眼之外部分采用水泥砂浆抹面;花墙上下排进水孔眼错开布置,同时在沉淀面以上0.3~0.5m处至池底部分的墙不设孔眼,孔眼大小和数量根据进水流量可进行调整,控制孔口流速不大于0.15~0.2m/s。Both the upper water intake area and the lower water intake area use the perforated flower wall 1 for water distribution, which plays the role of uniform water replenishment and energy dissipation. The water inlet perforated flower wall 1 is built with bricks or concrete blocks, and the part outside the holes is plastered with cement mortar; the upper and lower water inlet holes of the flower wall are staggered, and at the same time, the wall from 0.3 to 0.5m above the sedimentation surface to the bottom of the pool is not Set holes, the size and number of holes can be adjusted according to the water flow rate, and the flow rate of the control holes is not greater than 0.15-0.2m/s.
为取得较好的排泥效果,下层排泥区采用多排污泥斗6排泥,污泥斗6边壁倾角采用60°,污泥斗6中设置排泥管7,排泥管7下端插入污泥斗6,排泥管7上端与排泥总管相连,利用上、下两层池水的静水压力排泥。上层排泥区池底纵坡i不小于0.01,采用单斗排泥,即在上层派排泥区坡底设置单排污泥斗6,由刮泥行车5将污泥刮入上层的污泥斗6,再由污泥泵吸排,实现排泥操作;沉淀区过水断面逐渐扩大,流速逐渐减小,颗粒在重力作用下发生自由沉淀。上层沉淀区、下层沉淀区可分别取较大和较小的表面水力负荷,以取得较好的沉淀效率。具体来说,池体的上层沉淀区、下层沉淀区的长宽比不小于4,长深比不小于10;沉淀区断面逐渐扩大,流速逐渐减小,颗粒在重力作用下发生自由沉淀,总沉淀时间控制在3h内;下层沉淀区可取较大的设计负荷,大大减轻上层沉淀池的设计负荷,以取得较好的沉淀效率。In order to obtain a better sludge discharge effect, the lower sludge discharge area adopts multiple rows of sludge hoppers 6 for sludge discharge, and the inclination angle of the side wall of the sludge hopper 6 is 60°. The sludge discharge pipe 7 is set in the sludge hopper 6, and the lower end of the sludge discharge pipe 7 Insert the sludge hopper 6, and the upper end of the sludge discharge pipe 7 is connected with the sludge discharge main pipe, and utilizes the hydrostatic pressure of the upper and lower two layers of pool water to discharge the sludge. The vertical slope i at the bottom of the upper sludge discharge area is not less than 0.01, and a single bucket is used for sludge discharge, that is, a single row of sludge buckets 6 is installed at the bottom of the slope of the upper sludge discharge area, and the sludge is scraped into the upper sludge by the scraper truck 5 Bucket 6 is then sucked and discharged by the sludge pump to realize the sludge discharge operation; the cross-section of the sedimentation zone gradually expands, the flow rate gradually decreases, and the particles are free to settle under the action of gravity. The upper sedimentation zone and the lower sedimentation zone can respectively take larger and smaller surface hydraulic loads to obtain better sedimentation efficiency. Specifically, the aspect ratio of the upper sedimentation zone and the lower sedimentation zone of the pool body is not less than 4, and the aspect ratio is not less than 10; The settling time is controlled within 3 hours; the lower settling area can take a larger design load, which greatly reduces the design load of the upper settling tank to achieve better settling efficiency.
出水区是通过设置指形出水堰2实现处理水收集的,指形出水堰2周边设置锯齿形自由溢流堰,指形出水堰2的槽的深度取0.3~0.5m,其长度和宽度则通过溢流堰负荷率控制,一般要求溢流堰负荷率不大于300m3/(m·d)。指形出水堰2将收集的清水汇入集水总管3,而后通过集水总管3上安装的出水总管4集中排出。The outlet area collects treated water by setting finger-shaped outlet weir 2, and a zig-zag free overflow weir is arranged around the finger-shaped outlet weir 2. Through the control of the load rate of the overflow weir, it is generally required that the load rate of the overflow weir is not greater than 300m 3 /(m·d). The finger-shaped water outlet weir 2 merges the collected clear water into the water collection main pipe 3, and then discharges it through the water outlet main pipe 4 installed on the water collection main pipe 3.
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Cited By (4)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
CN104784983A (en) * | 2015-04-14 | 2015-07-22 | 刘生宝 | Double-layer horizontal sedimentation tank for drinking water purification of surface water |
CN107158758A (en) * | 2016-03-08 | 2017-09-15 | 哈尔滨市多相水处理技术有限公司 | Bevel-type constrains spoil disposal individual layer lateral flow oblique plate sedimentation device |
CN111035972A (en) * | 2019-12-23 | 2020-04-21 | 宜兴华都琥珀环保机械制造有限公司 | Sedimentation tank of liquid drainage mode under liquid |
CN116550017A (en) * | 2023-04-10 | 2023-08-08 | 南通成亮再生资源有限公司 | Peripheral transmission mud sucking and scraping machine for sewage treatment |
-
2015
- 2015-04-14 CN CN201520221220.7U patent/CN204973155U/en not_active Expired - Fee Related
Cited By (5)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
CN104784983A (en) * | 2015-04-14 | 2015-07-22 | 刘生宝 | Double-layer horizontal sedimentation tank for drinking water purification of surface water |
CN107158758A (en) * | 2016-03-08 | 2017-09-15 | 哈尔滨市多相水处理技术有限公司 | Bevel-type constrains spoil disposal individual layer lateral flow oblique plate sedimentation device |
CN111035972A (en) * | 2019-12-23 | 2020-04-21 | 宜兴华都琥珀环保机械制造有限公司 | Sedimentation tank of liquid drainage mode under liquid |
CN111035972B (en) * | 2019-12-23 | 2020-11-13 | 宜兴华都琥珀环保机械制造有限公司 | Sedimentation tank of liquid drainage mode under liquid |
CN116550017A (en) * | 2023-04-10 | 2023-08-08 | 南通成亮再生资源有限公司 | Peripheral transmission mud sucking and scraping machine for sewage treatment |
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