CN204384990U - A kind of recirculated cooling water lime soften for sewage clarification filtration treatment system - Google Patents
A kind of recirculated cooling water lime soften for sewage clarification filtration treatment system Download PDFInfo
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- CN204384990U CN204384990U CN201420811978.1U CN201420811978U CN204384990U CN 204384990 U CN204384990 U CN 204384990U CN 201420811978 U CN201420811978 U CN 201420811978U CN 204384990 U CN204384990 U CN 204384990U
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- 239000000498 cooling water Substances 0.000 title claims abstract description 35
- 235000008733 Citrus aurantifolia Nutrition 0.000 title claims abstract description 24
- 235000011941 Tilia x europaea Nutrition 0.000 title claims abstract description 24
- 238000001914 filtration Methods 0.000 title claims abstract description 24
- 239000004571 lime Substances 0.000 title claims abstract description 24
- 238000005352 clarification Methods 0.000 title claims abstract description 13
- 239000010865 sewage Substances 0.000 title description 8
- 238000004062 sedimentation Methods 0.000 claims abstract description 47
- XLYOFNOQVPJJNP-UHFFFAOYSA-N water Substances O XLYOFNOQVPJJNP-UHFFFAOYSA-N 0.000 claims abstract description 45
- 239000010802 sludge Substances 0.000 claims abstract description 39
- 239000011148 porous material Substances 0.000 claims abstract description 26
- 238000002156 mixing Methods 0.000 claims abstract description 18
- 238000006243 chemical reaction Methods 0.000 claims description 23
- QAOWNCQODCNURD-UHFFFAOYSA-N Sulfuric acid Chemical compound OS(O)(=O)=O QAOWNCQODCNURD-UHFFFAOYSA-N 0.000 claims description 18
- 230000015271 coagulation Effects 0.000 claims description 10
- 238000005345 coagulation Methods 0.000 claims description 10
- 239000000701 coagulant Substances 0.000 claims description 7
- 239000008267 milk Substances 0.000 claims description 7
- 210000004080 milk Anatomy 0.000 claims description 7
- 235000013336 milk Nutrition 0.000 claims description 7
- 239000000645 desinfectant Substances 0.000 claims description 6
- 238000006477 desulfuration reaction Methods 0.000 claims description 6
- 230000023556 desulfurization Effects 0.000 claims description 6
- 239000002002 slurry Substances 0.000 claims description 6
- 238000005189 flocculation Methods 0.000 claims description 3
- 230000016615 flocculation Effects 0.000 claims description 3
- 238000005272 metallurgy Methods 0.000 abstract description 2
- 239000000463 material Substances 0.000 description 15
- 239000002245 particle Substances 0.000 description 9
- 229940037003 alum Drugs 0.000 description 6
- 239000007788 liquid Substances 0.000 description 5
- 238000000034 method Methods 0.000 description 5
- ODINCKMPIJJUCX-UHFFFAOYSA-N Calcium oxide Chemical compound [Ca]=O ODINCKMPIJJUCX-UHFFFAOYSA-N 0.000 description 4
- 238000003756 stirring Methods 0.000 description 4
- 230000032258 transport Effects 0.000 description 4
- 238000012545 processing Methods 0.000 description 3
- 239000007787 solid Substances 0.000 description 3
- 239000000126 substance Substances 0.000 description 3
- 238000005406 washing Methods 0.000 description 3
- VYPSYNLAJGMNEJ-UHFFFAOYSA-N Silicium dioxide Chemical group O=[Si]=O VYPSYNLAJGMNEJ-UHFFFAOYSA-N 0.000 description 2
- 239000005708 Sodium hypochlorite Substances 0.000 description 2
- QAOWNCQODCNURD-UHFFFAOYSA-L Sulfate Chemical compound [O-]S([O-])(=O)=O QAOWNCQODCNURD-UHFFFAOYSA-L 0.000 description 2
- 238000011001 backwashing Methods 0.000 description 2
- 235000012255 calcium oxide Nutrition 0.000 description 2
- 239000000292 calcium oxide Substances 0.000 description 2
- 239000012141 concentrate Substances 0.000 description 2
- 238000001816 cooling Methods 0.000 description 2
- 230000000694 effects Effects 0.000 description 2
- 239000010419 fine particle Substances 0.000 description 2
- 230000000855 fungicidal effect Effects 0.000 description 2
- 239000000417 fungicide Substances 0.000 description 2
- 238000012806 monitoring device Methods 0.000 description 2
- 229920002401 polyacrylamide Polymers 0.000 description 2
- 238000005201 scrubbing Methods 0.000 description 2
- SUKJFIGYRHOWBL-UHFFFAOYSA-N sodium hypochlorite Chemical compound [Na+].Cl[O-] SUKJFIGYRHOWBL-UHFFFAOYSA-N 0.000 description 2
- 239000000725 suspension Substances 0.000 description 2
- BVKZGUZCCUSVTD-UHFFFAOYSA-M Bicarbonate Chemical compound OC([O-])=O BVKZGUZCCUSVTD-UHFFFAOYSA-M 0.000 description 1
- BVKZGUZCCUSVTD-UHFFFAOYSA-L Carbonate Chemical compound [O-]C([O-])=O BVKZGUZCCUSVTD-UHFFFAOYSA-L 0.000 description 1
- 241000195493 Cryptophyta Species 0.000 description 1
- 229910019440 Mg(OH) Inorganic materials 0.000 description 1
- 239000006004 Quartz sand Substances 0.000 description 1
- 239000002253 acid Substances 0.000 description 1
- 230000005540 biological transmission Effects 0.000 description 1
- 238000013461 design Methods 0.000 description 1
- 238000011161 development Methods 0.000 description 1
- 238000009826 distribution Methods 0.000 description 1
- 239000003814 drug Substances 0.000 description 1
- 239000003344 environmental pollutant Substances 0.000 description 1
- 238000004519 manufacturing process Methods 0.000 description 1
- 230000004048 modification Effects 0.000 description 1
- 238000012986 modification Methods 0.000 description 1
- 230000035515 penetration Effects 0.000 description 1
- 231100000719 pollutant Toxicity 0.000 description 1
- 229910052573 porcelain Inorganic materials 0.000 description 1
- 230000002028 premature Effects 0.000 description 1
- 229910052761 rare earth metal Inorganic materials 0.000 description 1
- 150000002910 rare earth metals Chemical class 0.000 description 1
- 230000003134 recirculating effect Effects 0.000 description 1
- 239000004576 sand Substances 0.000 description 1
- 238000007873 sieving Methods 0.000 description 1
- 239000002352 surface water Substances 0.000 description 1
- 238000012546 transfer Methods 0.000 description 1
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- Separation Of Suspended Particles By Flocculating Agents (AREA)
Abstract
本实用新型涉及一种水处理系统,尤其是涉及适用于电力、石化、冶金等工业部门的一种循环冷却水石灰软化澄清过滤处理系统。其主要是解决现有技术所存在的占地面积较大,污泥排放量较大,过滤效率低等的技术问题。本实用新型包括可通入循环冷却水的高密度沉淀池(1),所述的高密度沉淀池(1)通过管路连接有混合池(2),混合池通过管路连接有变孔隙滤池(3),变孔隙滤池通过管路连接有清水池(4),并清水池连接循环冷却水池。
The utility model relates to a water treatment system, in particular to a circulation cooling water lime softening clarification and filtration treatment system suitable for electric power, petrochemical, metallurgy and other industrial sectors. It mainly solves the technical problems existing in the prior art, such as large occupied area, large sludge discharge, and low filtration efficiency. The utility model comprises a high-density sedimentation tank (1) that can be fed into circulating cooling water. The high-density sedimentation tank (1) is connected with a mixing tank (2) through a pipeline, and the mixing tank is connected with a variable pore filter through a pipeline. The pool (3) and the variable pore filter are connected to a clear water pool (4) through pipelines, and the clear water pool is connected to a circulating cooling water pool.
Description
技术领域 technical field
本实用新型涉及一种水处理系统,尤其是涉及适用于电力、石化、冶金等工业部门的一种循环冷却水石灰软化澄清过滤处理系统。 The utility model relates to a water treatment system, in particular to a circulation cooling water lime softening clarification and filtration treatment system suitable for electric power, petrochemical, metallurgy and other industrial sectors.
背景技术 Background technique
随着地表水资源的日益紧缺及污染的日益严峻,工业企业的发展越来越受水资源的制约。循环冷却水消耗水量较大,排污水量也较大。将循环冷却水软化处理,提高循环冷却水浓缩倍率,减少循环排污水量,减少污染物排放,具有广泛的应用前景。但提高循环冷却水浓缩倍率,需要去除循环冷却水中的暂时硬度及碱度。 With the increasing shortage of surface water resources and the increasingly severe pollution, the development of industrial enterprises is increasingly restricted by water resources. Circulating cooling water consumes a lot of water, and the amount of sewage is also large. Softening the circulating cooling water, increasing the concentration ratio of the circulating cooling water, reducing the amount of circulating sewage and reducing pollutant discharge have broad application prospects. However, to increase the concentration ratio of circulating cooling water, it is necessary to remove the temporary hardness and alkalinity in circulating cooling water.
中国专利公开了一种石灰软化、澄清、过滤的水处理装置(公开号:CN200820143211.0),其主要采用澄清、过滤工艺作为市政污水处理厂出水的深度处理工艺,去除暂时硬度、浊度等指标,作为循环冷却系统补充水。该方法存在澄清池排污量较大,澄清池占地面积较大,排污量较大,澄清池内未投加消毒剂易滋生藻类,影响出水水质;滤池内滤料采用石英砂滤料易造成因水力筛分作用造成的细滤料集中在滤层表面,影响过滤效率,出水水质不稳定,反洗水量大等问题。 A Chinese patent discloses a lime softening, clarification, and filtration water treatment device (publication number: CN200820143211.0), which mainly uses clarification and filtration processes as an advanced treatment process for effluent from municipal sewage treatment plants to remove temporary hardness, turbidity, etc. Indicator, as make-up water for recirculating cooling system. In this method, the clarifier has a large amount of sewage discharge, the clarifier occupies a large area, and has a large sewage discharge. If no disinfectant is added to the clarifier, it is easy to breed algae and affect the water quality of the effluent; the filter material in the filter is quartz sand. The fine filter material caused by hydraulic sieving is concentrated on the surface of the filter layer, which affects the filtration efficiency, the quality of the effluent is unstable, and the amount of backwash water is large.
实用新型内容 Utility model content
本实用新型是提供一种循环冷却水石灰软化澄清过滤处理系统,其主要是解决现有技术所存在的占地面积较大,污泥排放量较大,过滤效率低等的技术问题。 The utility model provides a circulating cooling water lime softening, clarification and filtration treatment system, which mainly solves the technical problems of the prior art, such as large floor area, large sludge discharge, and low filtration efficiency.
本实用新型的上述技术问题主要是通过下述技术方案得以解决的: The above-mentioned technical problems of the utility model are mainly solved by the following technical solutions:
本实用新型的一种循环冷却水石灰软化澄清过滤处理系统,包括可通入循环冷却水的高密度沉淀池,所述的高密度沉淀池通过管路连接有混合池,混合池通过管路连接有变孔隙滤池,变孔隙滤池通过管路连接有清水池,并清水池连接循环冷却水池。 A circulating cooling water lime softening, clarifying and filtering treatment system of the present invention includes a high-density sedimentation tank that can be fed into the circulating cooling water. The high-density sedimentation tank is connected with a mixing tank through a pipeline, and the mixing tank is connected through a pipeline. There is a variable pore filter, and the variable pore filter is connected to a clear water pool through pipelines, and the clear water pool is connected to a circulating cooling water pool.
循环冷却水输送到高密度沉淀池,高密度沉淀池具有特点:高密度沉淀池具有反应区、沉淀区组成。反应区分为两个部分:快速混凝搅拌反应区、慢速混凝推流式反应区。将原水引入到快速混凝搅拌反应池底板的中央,通过叶轮使反应区内水流均匀混合,反应区中悬浮絮状或晶状固体颗粒的浓度保持在最佳状态,通过来自沉淀区的浓缩污泥外部再循环系统使池中污泥浓度得以保障。慢速混凝推流式反应区,其作用就是连续不断地使矾花颗粒增大。矾花慢速地进入到沉淀区,这样可避免损坏矾花或产生旋涡,确保大量的悬浮固体颗粒在沉淀区内均匀沉积。矾花在沉淀区下部汇集成污泥并浓缩,部分浓缩污泥通过污泥回流泵循环至反应区入口,剩余污泥通过污泥输送泵输送至脱硫系统浆液箱。浓缩污泥的浓度至少为20g/l。沉淀区设置逆流式斜管,并将剩余的矾花沉淀,出水通过溢流堰自流到混合池。高密度沉淀池出水暂时硬度≤1mmol/L。具有运行稳定可靠,占地面积小,布置紧凑,节省药剂用量等特点。 The circulating cooling water is transported to the high-density sedimentation tank. The high-density sedimentation tank has characteristics: the high-density sedimentation tank has a reaction zone and a sedimentation zone. The reaction zone is divided into two parts: the fast coagulation stirring reaction zone and the slow coagulation plug-flow reaction zone. The raw water is introduced into the center of the bottom plate of the rapid coagulation stirring reaction tank, and the water flow in the reaction zone is uniformly mixed through the impeller, and the concentration of suspended flocculent or crystalline solid particles in the reaction zone is kept at an optimal state, and the concentrated sewage from the sedimentation zone is passed The sludge external recirculation system ensures the sludge concentration in the pool. The role of the slow coagulation plug-flow reaction zone is to continuously increase the size of the alum flower particles. The alum flowers enter the sedimentation zone at a slow speed, which can avoid damage to the alum flowers or generate vortices, and ensure that a large amount of suspended solid particles are evenly deposited in the sedimentation zone. The alum flower collects into sludge in the lower part of the sedimentation area and concentrates it. Part of the concentrated sludge is circulated to the entrance of the reaction area through the sludge return pump, and the remaining sludge is transported to the slurry tank of the desulfurization system through the sludge transfer pump. The concentration of the thickened sludge is at least 20 g/l. The settling area is equipped with a counter-current inclined pipe to settle the remaining alum flowers, and the effluent flows to the mixing tank by itself through the overflow weir. The temporary hardness of the effluent from the high-density sedimentation tank is ≤1mmol/L. It has the characteristics of stable and reliable operation, small footprint, compact layout, and saving the amount of chemicals.
通过加酸后的循环冷却水自流到变孔隙滤池,变孔隙滤池具有特点:在过滤过程中悬浮颗粒在滤层孔隙里发生同向絮凝作用,因而使小颗粒悬浮物变成大颗粒悬浮物,从而被滤料截留,提高了过滤效率。变孔隙滤池的滤料采用粗滤料(1.2~2.8mm)和细滤料(0.5~1.0mm)均匀填充。粗滤料依靠整个滤层进行过滤,避免普通滤池形成滤层的表面过滤,降低滤层阻力,也避免悬浮物颗粒的过早穿透,还可以提高滤速。细滤料的加入并在滤层中混匀极大地降低了粗滤料的局部孔隙率,提高了对循环水中细小颗粒的絮凝作用,更有利于对细小颗粒的去除,也极大地提高了滤池的截污能力。变孔隙滤池出水浊度≤3NTU。具有滤速高,截污量大,运行周期长,产水量提高,运行平稳简单,出水水质好,反洗效果好,反洗水耗量小等特点。 The circulating cooling water after adding acid flows into the variable pore filter by itself. The variable pore filter has the characteristics: during the filtration process, the suspended particles flocculate in the same direction in the pores of the filter layer, so that the small particle suspension becomes large particle suspension The material is intercepted by the filter material, which improves the filtration efficiency. The filter material of the variable pore filter is evenly filled with coarse filter material (1.2-2.8mm) and fine filter material (0.5-1.0mm). The coarse filter material relies on the entire filter layer to filter, avoiding the surface filtration of the filter layer formed by ordinary filters, reducing the resistance of the filter layer, avoiding premature penetration of suspended particles, and increasing the filtration rate. The addition of fine filter material and mixing in the filter layer greatly reduces the local porosity of the coarse filter material, improves the flocculation of fine particles in the circulating water, is more conducive to the removal of fine particles, and greatly improves the filtration efficiency. Pollution interception capacity. The turbidity of the variable pore filter effluent is ≤3NTU. It has the characteristics of high filtration rate, large sewage interception capacity, long operation period, increased water production, stable and simple operation, good effluent water quality, good backwashing effect, and low backwashing water consumption.
高密度沉淀池沉淀区采用中心悬挂式刮泥机,将沉淀区内污泥汇集到中心污泥斗,并通过部分污泥回流至反应区,剩余污泥输送到脱硫系统浆液箱。反应区采用快速混凝搅拌反应池、慢速混凝推流式反应池组合的方式,将池内PH值调整到10左右,使Ca2+和Mg2+分别以CaCO3和Mg(OH)2的形式从水中沉析出来,实现对循环水的软化处理。 The sedimentation area of the high-density sedimentation tank adopts a central hanging sludge scraper to collect the sludge in the sedimentation area to the central sludge hopper, and return part of the sludge to the reaction area, and the remaining sludge is transported to the slurry tank of the desulfurization system. The reaction area adopts the combination of fast coagulation stirring reaction tank and slow coagulation plug-flow reaction tank. The pH value in the tank is adjusted to about 10, so that Ca 2+ and Mg 2+ are separated by CaCO 3 and Mg(OH) 2 The form is precipitated from the water to realize the softening treatment of the circulating water.
变孔隙滤池设计配水均匀(保证滤料上面有一定的液位高度),为更好的保证处理效果,配水和进气方式设计成支母管方式,反洗采用水洗—气水混合擦洗—水洗的方式。变孔隙滤池阀门全部采用自动阀门,实现自动控制。 The variable pore filter is designed to distribute water evenly (to ensure a certain liquid level above the filter material). In order to better ensure the treatment effect, the water distribution and air intake method is designed as a branch pipe, and the backwash adopts water washing-air-water mixed scrubbing- The way of washing. The variable pore filter valves all adopt automatic valves to realize automatic control.
高密度沉淀池、混合池、变孔隙滤池等位置设置可监测浊度、电导率、温度、流量、pH值、污泥液位等指标的在线监测装置。 On-line monitoring devices that can monitor indicators such as turbidity, conductivity, temperature, flow, pH value, and sludge level are installed in high-density sedimentation tanks, mixing tanks, and variable pore filters.
作为优选,所述的高密度沉淀池底部部分污泥通过污泥回流泵将回流至高密度沉淀池反应区,剩余污泥由污泥输送泵送至脱硫系统石灰浆液箱。 As a preference, part of the sludge at the bottom of the high-density sedimentation tank is returned to the reaction zone of the high-density sedimentation tank through the sludge return pump, and the remaining sludge is sent to the lime slurry tank of the desulfurization system by the sludge transport pump.
作为优选,变孔隙滤池通过设置反洗水泵、反洗风机实现对变孔隙滤池滤料的水洗及气水混合擦洗,反洗后排水自流到反洗排水池,反洗排水通过反洗排水泵输送到高密度沉淀池进水管。 As a preference, the variable pore filter can realize water washing and air-water mixed scrubbing of the filter material of the variable pore filter by setting a backwash water pump and a backwash fan. The pump delivers to the inlet pipe of the high-density sedimentation tank.
作为优选,所述的高密度沉淀池前端反应区设置搅拌器,实现循环水与药剂的充分混合,高密度沉淀池沉淀区设置刮泥机,将污泥集中至泥斗区域,污泥回流及输送采用电动阀门,实现全自动控制。 As a preference, a stirrer is provided in the front-end reaction zone of the high-density sedimentation tank to realize sufficient mixing of circulating water and chemicals, and a sludge scraper is installed in the sedimentation zone of the high-density sedimentation tank to concentrate the sludge into the mud hopper area, and the sludge returns and The transmission adopts electric valves to realize fully automatic control.
作为优选,所述的变孔隙滤池的各阀门采用电动阀门。变孔隙滤池采用稀土瓷砂滤料,主滤料粒径1.2-2.8mm,附属滤料粒径0.5-1.0mm,各阀门采用电动阀门,实现全自动控制。 Preferably, each valve of the variable pore filter uses an electric valve. The variable pore filter adopts rare earth porcelain sand filter material, the particle size of the main filter material is 1.2-2.8mm, and the particle size of the auxiliary filter material is 0.5-1.0mm. The valves adopt electric valves to realize automatic control.
作为优选,所述的高密度沉淀池凝聚区、絮凝区连通有加药系统,加药系统包含石灰乳加药装置、助凝剂加药装置、消毒剂加药装置、絮凝剂加药装置。石灰乳采用有效含量80%的生石灰,助凝剂采用0.1-0.3%聚丙烯酰胺溶液,杀菌剂采用10%溶液次氯酸钠溶液,絮凝剂采用10%聚合硫酸铁液体。 Preferably, the coagulation area and the flocculation area of the high-density sedimentation tank are connected with a dosing system, and the dosing system includes a lime milk dosing device, a coagulant dosing device, a disinfectant dosing device, and a flocculant dosing device. The lime milk uses quicklime with an effective content of 80%, the coagulant aid uses 0.1-0.3% polyacrylamide solution, the fungicide uses 10% sodium hypochlorite solution, and the flocculant uses 10% polyferric sulfate liquid.
作为优选,所述的混合池通过加药管连接有硫酸加药装置。硫酸采用98%浓硫酸液体。 Preferably, the mixing tank is connected with a sulfuric acid dosing device through a dosing pipe. Sulfuric acid adopts 98% concentrated sulfuric acid liquid.
因此,本实用新型通过将物理化学方法,使得对循环冷却水处理的硬度、浊度、碱度去除率高,占地面积小,排泥量少,处理效率高,运行费用较低,全自动操作,满足了循环冷却系统冷却水的处理后的水质要求,提高了循环冷却水系统浓缩倍率,系统结构经济、合理。 Therefore, the utility model adopts physical and chemical methods to make the circulating cooling water have high removal rate of hardness, turbidity and alkalinity, small floor area, less sludge discharge, high processing efficiency, low operating cost, fully automatic The operation meets the water quality requirements of the treated cooling water in the circulating cooling system, improves the concentration ratio of the circulating cooling water system, and the system structure is economical and reasonable.
附图说明 Description of drawings
附图1是本实用新型的一种结构示意图。 Accompanying drawing 1 is a kind of structural representation of the utility model.
图中零部件、部位及编号:高密度沉淀池1、变孔隙滤池2、混合池3、清水池4、反洗排水池5、污泥回流泵6、污泥输送泵7、反洗水泵8、反洗排水泵9、反洗风机10、石灰乳加药装置11、助凝剂加药装置12、消毒剂加药装置13、絮凝剂加药装置14、硫酸加药装置15、搅拌器16、刮泥机17。 Parts, parts and numbers in the figure: high-density sedimentation tank 1, variable pore filter tank 2, mixing tank 3, clear water tank 4, backwash drainage tank 5, sludge return pump 6, sludge delivery pump 7, backwash water pump 8. Backwash drainage pump 9, backwash fan 10, lime milk dosing device 11, coagulant aid dosing device 12, disinfectant dosing device 13, flocculant dosing device 14, sulfuric acid dosing device 15, agitator 16. Mud scraper 17.
具体实施方式 Detailed ways
下面通过实施例,并结合附图,对本实用新型的技术方案作进一步具体的说明。 The technical solutions of the present utility model will be further specifically described below through the embodiments and in conjunction with the accompanying drawings.
实施例:本例的一种循环冷却水石灰软化澄清过滤处理系统,如图1,包括循环冷却水进入的高密度沉淀池1,高密度沉淀池出水至混合池2,混合池出水至变孔隙滤池3,其出水自流到清水池4,并溢流到循环冷却水池内。高密度沉淀池底部污泥通过污泥回流泵6将部分污泥回流至高密度沉淀池内反应区,剩余污泥通过污泥输送泵7输送至脱硫系统石灰浆液箱。变孔隙滤池通过设置反洗水泵8、反洗风机10实现对其水洗及气水空气擦洗,反洗后排水自流到反洗排水池5,并通过反洗排水泵9将反洗排水输送到高密度沉淀池进水管。加药系统包含石灰乳加药装置11、助凝剂加药装置12、消毒剂加药装置13、絮凝剂加药装置14、硫酸加药装置15。高密度沉淀池、混合池、变孔隙滤池等位置设置可监测浊度、电导率、温度、流量、pH值、污泥液位等指标的在线监测装置。 Embodiment: A circulating cooling water lime softening, clarifying and filtering treatment system of this example, as shown in Figure 1, includes a high-density sedimentation tank 1 where the circulating cooling water enters, the high-density sedimentation tank effluent to the mixing tank 2, and the mixing tank effluent to variable porosity Filter tank 3, its effluent flows to clear water pool 4 by itself, and overflows in the circulating cooling water pool. The sludge at the bottom of the high-density sedimentation tank returns part of the sludge to the reaction zone in the high-density sedimentation tank through the sludge return pump 6, and the remaining sludge is transported to the lime slurry tank of the desulfurization system through the sludge delivery pump 7. The variable pore filter can be washed by water and scrubbed with air, water and air by setting the backwash water pump 8 and the backwash fan 10. After backwash, the drainage flows to the backwash drainage pool 5 by itself, and the backwash drainage pump 9 is used to transport the backwash drainage to High-density sedimentation tank inlet pipe. The dosing system includes a lime milk dosing device 11 , a coagulant dosing device 12 , a disinfectant dosing device 13 , a flocculant dosing device 14 , and a sulfuric acid dosing device 15 . On-line monitoring devices that can monitor indicators such as turbidity, conductivity, temperature, flow, pH value, and sludge level are installed in high-density sedimentation tanks, mixing tanks, and variable pore filters.
石灰乳采用有效含量80%的生石灰,助凝剂采用0.1-0.3%聚丙烯酰胺溶液,杀菌剂采用10%溶液次氯酸钠溶液,絮凝剂采用10%聚合硫酸铁液体,硫酸采用98%浓硫酸液体。 The lime milk uses quicklime with an effective content of 80%, the coagulant aid uses 0.1-0.3% polyacrylamide solution, the fungicide uses 10% sodium hypochlorite solution, the flocculant uses 10% polyferric sulfate liquid, and the sulfuric acid uses 98% concentrated sulfuric acid liquid.
本例设计处理能力900吨/小时,循环冷却水系统经过循环泵将部分循环冷却水输送至高密度沉淀池。 In this example, the design processing capacity is 900 tons/hour, and the circulating cooling water system transports part of the circulating cooling water to the high-density sedimentation tank through the circulating pump.
进水水质:碳酸盐硬度≥3mmol/L,浊度≥50NTU,PH值:7~9。出水水质要求:暂时硬度≤1mmol/L,碱度≤1mmol/L,浊度≤3NTU,pH值:7~8。 Influent water quality: carbonate hardness ≥ 3mmol/L, turbidity ≥ 50NTU, PH value: 7~9. Outlet water quality requirements: Temporary hardness ≤ 1mmol/L, alkalinity ≤ 1mmol/L, turbidity ≤ 3NTU, pH value: 7~8.
其处理步骤为: Its processing steps are:
a.循环冷却水进入到高密度沉淀池1反应区底部,经后快速混凝搅拌反应区及慢速混凝推流式反应区后,矾花在沉淀区下部沉淀并浓缩。部分浓缩污泥经污泥回流泵6循环至反应池入口,剩余污泥通过污泥输送泵7输送至脱硫系统浆液箱。沉淀区上部出水通过溢流堰自流到混合池3。高密度沉淀池反应区内投加石灰乳加药装置11、助凝剂加药装置12、消毒剂加药装置13、絮凝剂加药装置14等药剂,实现对循环水的处理。 a. The circulating cooling water enters the bottom of the high-density sedimentation tank 1 reaction zone, and after passing through the post-rapid coagulation stirring reaction zone and the slow coagulation plug-flow reaction zone, the alum flowers are precipitated and concentrated in the lower part of the sedimentation zone. Part of the concentrated sludge is circulated to the inlet of the reaction tank through the sludge return pump 6, and the remaining sludge is transported to the slurry tank of the desulfurization system through the sludge transport pump 7. The effluent from the upper part of the sedimentation zone flows to the mixing tank 3 by itself through the overflow weir. Lime milk dosing device 11, coagulant dosing device 12, disinfectant dosing device 13, flocculant dosing device 14 and other medicaments are added to the reaction zone of the high-density sedimentation tank to realize the treatment of circulating water.
b.在混合池3内通过浓硫酸加药装置15投加浓硫酸,浓硫酸调节pH为7.5~8.3,去除出水中碳酸氢根。 b. Dosing concentrated sulfuric acid in the mixing tank 3 through the concentrated sulfuric acid dosing device 15, the concentrated sulfuric acid adjusts the pH to 7.5-8.3, and removes bicarbonate in the effluent.
c.经加浓硫酸后自流到变孔隙滤池4,进一步去除悬浮物,减低浊度,出水作为循环冷却水。变孔隙滤池设置反洗水泵8、反洗风机10,实现对滤池的水洗及气水空气擦洗。反洗出水自流到反洗排水池5,反洗排水通过反洗排水泵9输送到高密度沉淀池进水管。 c. After adding concentrated sulfuric acid, it flows to the variable pore filter 4 by itself to further remove suspended solids and reduce turbidity, and the effluent is used as circulating cooling water. The variable pore filter is equipped with a backwash water pump 8 and a backwash fan 10 to realize water washing and air-water air scrubbing of the filter. The backwash effluent flows to the backwash drainage tank 5 by itself, and the backwash drainage is transported to the water inlet pipe of the high-density sedimentation tank through the backwash drainage pump 9.
以上所述仅为本实用新型的具体实施例,但本实用新型的结构特征并不局限于此,任何本领域的技术人员在本实用新型的领域内,所作的变化或修饰皆涵盖在本实用新型的专利范围之中。 The above is only a specific embodiment of the utility model, but the structural features of the utility model are not limited thereto, and any changes or modifications made by those skilled in the art within the scope of the utility model are covered by the utility model. In the scope of the new patent.
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Cited By (4)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| CN111348756A (en) * | 2020-04-01 | 2020-06-30 | 广西广宇水资源技术开发有限公司 | Process for removing temporary hardness of water by chemical reaction |
| CN112062329A (en) * | 2020-08-25 | 2020-12-11 | 耒阳金悦科技发展有限公司 | Energy-saving cooling water recovery treatment method |
| CN113603271A (en) * | 2021-09-08 | 2021-11-05 | 云南省生态环境科学研究院 | Treatment method of heavy metal and nitrogen-phosphorus composite polluted water body |
| CN119330435A (en) * | 2024-11-20 | 2025-01-21 | 华能沁北发电有限责任公司 | A two-point dosing method for circulating water treatment in thermal power plants |
-
2014
- 2014-12-22 CN CN201420811978.1U patent/CN204384990U/en not_active Expired - Lifetime
Cited By (4)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| CN111348756A (en) * | 2020-04-01 | 2020-06-30 | 广西广宇水资源技术开发有限公司 | Process for removing temporary hardness of water by chemical reaction |
| CN112062329A (en) * | 2020-08-25 | 2020-12-11 | 耒阳金悦科技发展有限公司 | Energy-saving cooling water recovery treatment method |
| CN113603271A (en) * | 2021-09-08 | 2021-11-05 | 云南省生态环境科学研究院 | Treatment method of heavy metal and nitrogen-phosphorus composite polluted water body |
| CN119330435A (en) * | 2024-11-20 | 2025-01-21 | 华能沁北发电有限责任公司 | A two-point dosing method for circulating water treatment in thermal power plants |
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