CN106976930B - Hydrocyclone separator for sludge water, and treatment system and method for synchronous dissolution of sludge water concentration/coagulant - Google Patents
Hydrocyclone separator for sludge water, and treatment system and method for synchronous dissolution of sludge water concentration/coagulant Download PDFInfo
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- 239000000701 coagulant Substances 0.000 title claims abstract description 129
- XLYOFNOQVPJJNP-UHFFFAOYSA-N water Substances O XLYOFNOQVPJJNP-UHFFFAOYSA-N 0.000 title claims abstract description 99
- 238000004090 dissolution Methods 0.000 title claims abstract description 77
- 239000010802 sludge Substances 0.000 title claims abstract description 62
- 238000000034 method Methods 0.000 title claims abstract description 26
- 230000001360 synchronised effect Effects 0.000 title claims description 10
- 239000007788 liquid Substances 0.000 claims abstract description 83
- 238000000926 separation method Methods 0.000 claims abstract description 59
- 239000003795 chemical substances by application Substances 0.000 claims abstract description 37
- 239000003814 drug Substances 0.000 claims abstract description 8
- 238000002360 preparation method Methods 0.000 claims description 10
- 230000003068 static effect Effects 0.000 claims description 10
- 239000008399 tap water Substances 0.000 claims description 8
- 235000020679 tap water Nutrition 0.000 claims description 8
- 239000007787 solid Substances 0.000 claims description 6
- 239000002253 acid Substances 0.000 claims description 2
- 238000011084 recovery Methods 0.000 abstract description 23
- 230000000694 effects Effects 0.000 abstract description 9
- 230000018044 dehydration Effects 0.000 abstract description 8
- 238000006297 dehydration reaction Methods 0.000 abstract description 8
- 230000008569 process Effects 0.000 abstract description 8
- 239000000706 filtrate Substances 0.000 abstract description 5
- 229940079593 drug Drugs 0.000 abstract 1
- 238000006243 chemical reaction Methods 0.000 description 11
- 239000007790 solid phase Substances 0.000 description 10
- 239000007791 liquid phase Substances 0.000 description 7
- 238000002156 mixing Methods 0.000 description 7
- 239000002245 particle Substances 0.000 description 6
- 230000009471 action Effects 0.000 description 4
- 230000008901 benefit Effects 0.000 description 4
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- 238000001125 extrusion Methods 0.000 description 3
- 230000005012 migration Effects 0.000 description 3
- 238000013508 migration Methods 0.000 description 3
- 239000000203 mixture Substances 0.000 description 3
- 239000000243 solution Substances 0.000 description 3
- AZDRQVAHHNSJOQ-UHFFFAOYSA-N alumane Chemical class [AlH3] AZDRQVAHHNSJOQ-UHFFFAOYSA-N 0.000 description 2
- 229910052782 aluminium Inorganic materials 0.000 description 2
- 230000009286 beneficial effect Effects 0.000 description 2
- 238000010586 diagram Methods 0.000 description 2
- 230000010354 integration Effects 0.000 description 2
- 238000004064 recycling Methods 0.000 description 2
- 229910018626 Al(OH) Inorganic materials 0.000 description 1
- 239000003513 alkali Substances 0.000 description 1
- 239000002585 base Substances 0.000 description 1
- 239000004927 clay Substances 0.000 description 1
- 238000005345 coagulation Methods 0.000 description 1
- 230000015271 coagulation Effects 0.000 description 1
- 238000010276 construction Methods 0.000 description 1
- 238000005516 engineering process Methods 0.000 description 1
- 238000000605 extraction Methods 0.000 description 1
- 239000010419 fine particle Substances 0.000 description 1
- 239000008394 flocculating agent Substances 0.000 description 1
- 238000013467 fragmentation Methods 0.000 description 1
- 238000006062 fragmentation reaction Methods 0.000 description 1
- 238000005469 granulation Methods 0.000 description 1
- 230000003179 granulation Effects 0.000 description 1
- 230000005484 gravity Effects 0.000 description 1
- 230000007062 hydrolysis Effects 0.000 description 1
- 238000006460 hydrolysis reaction Methods 0.000 description 1
- 230000006872 improvement Effects 0.000 description 1
- 239000012535 impurity Substances 0.000 description 1
- 238000002347 injection Methods 0.000 description 1
- 239000007924 injection Substances 0.000 description 1
- 229910052500 inorganic mineral Inorganic materials 0.000 description 1
- 238000009434 installation Methods 0.000 description 1
- 238000005342 ion exchange Methods 0.000 description 1
- 238000002386 leaching Methods 0.000 description 1
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- 230000001151 other effect Effects 0.000 description 1
- 230000020477 pH reduction Effects 0.000 description 1
- 239000000047 product Substances 0.000 description 1
- 238000000746 purification Methods 0.000 description 1
- 239000008213 purified water Substances 0.000 description 1
- 238000007789 sealing Methods 0.000 description 1
- 239000013049 sediment Substances 0.000 description 1
- 239000002904 solvent Substances 0.000 description 1
- 239000000126 substance Substances 0.000 description 1
- 239000006228 supernatant Substances 0.000 description 1
- 238000009210 therapy by ultrasound Methods 0.000 description 1
- 231100000331 toxic Toxicity 0.000 description 1
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- C—CHEMISTRY; METALLURGY
- C02—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F1/00—Treatment of water, waste water, or sewage
- C02F1/38—Treatment of water, waste water, or sewage by centrifugal separation
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- C—CHEMISTRY; METALLURGY
- C02—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F1/00—Treatment of water, waste water, or sewage
- C02F1/34—Treatment of water, waste water, or sewage with mechanical oscillations
- C02F1/36—Treatment of water, waste water, or sewage with mechanical oscillations ultrasonic vibrations
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- C—CHEMISTRY; METALLURGY
- C02—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F1/00—Treatment of water, waste water, or sewage
- C02F1/52—Treatment of water, waste water, or sewage by flocculation or precipitation of suspended impurities
- C02F1/5281—Installations for water purification using chemical agents
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- C—CHEMISTRY; METALLURGY
- C02—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F11/00—Treatment of sludge; Devices therefor
- C02F11/12—Treatment of sludge; Devices therefor by de-watering, drying or thickening
- C02F11/121—Treatment of sludge; Devices therefor by de-watering, drying or thickening by mechanical de-watering
- C02F11/127—Treatment of sludge; Devices therefor by de-watering, drying or thickening by mechanical de-watering by centrifugation
-
- C—CHEMISTRY; METALLURGY
- C02—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F11/00—Treatment of sludge; Devices therefor
- C02F11/12—Treatment of sludge; Devices therefor by de-watering, drying or thickening
- C02F11/14—Treatment of sludge; Devices therefor by de-watering, drying or thickening with addition of chemical agents
-
- C—CHEMISTRY; METALLURGY
- C02—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F2303/00—Specific treatment goals
- C02F2303/06—Sludge reduction, e.g. by lysis
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- Chemical & Material Sciences (AREA)
- Hydrology & Water Resources (AREA)
- Life Sciences & Earth Sciences (AREA)
- Environmental & Geological Engineering (AREA)
- Water Supply & Treatment (AREA)
- Mechanical Engineering (AREA)
- Organic Chemistry (AREA)
- Chemical Kinetics & Catalysis (AREA)
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Abstract
本发明公开了一种自来水厂排泥水同步浓缩与混凝剂回收的方法及其装置。本发明以水力旋流固液分离为核心,包括泥泵(3)、混凝剂溶出药剂投加系统(I)、水力旋流系统(II)和离心分离机(8)。泥泵抽吸的自来水厂排泥水与来自混凝剂溶出药剂投加系统(I)的溶出药剂混合后,在水力旋流系统(II)同步完成排泥水的固液分离和混凝剂溶出过程;富含混凝剂的清液以溢流清液形式排出,底流浓缩污泥排至离心脱水机(8)脱水,产生的泥饼外运处置,脱水滤液与溢流清液合并后送至自来水厂原水井直接回用。本发明是一种占地面积小、固液分离效果好、混凝剂回收效率高、药耗低的同步实现排泥水固液分离和混凝剂回收的方法及其装置。
The present invention discloses a method and device for simultaneous concentration of sludge water and coagulant recovery in a waterworks. The present invention is centered on hydrocyclone solid-liquid separation and comprises a mud pump (3), a coagulant dissolution agent dosing system (I), a hydrocyclone system (II) and a centrifuge (8). After the sludge water from the waterworks pumped by the mud pump is mixed with the dissolution agent from the coagulant dissolution agent dosing system (I), the solid-liquid separation and coagulant dissolution process of the sludge water are simultaneously completed in the hydrocyclone system (II); the clear liquid rich in coagulant is discharged in the form of overflow clear liquid, the bottom flow concentrated sludge is discharged to a centrifugal dewatering machine (8) for dehydration, the generated mud cake is transported out for disposal, and the dehydrated filtrate is combined with the overflow clear liquid and sent to the raw water well of the waterworks for direct reuse. The present invention is a method and device for simultaneous solid-liquid separation and coagulant recovery of sludge water with a small footprint, good solid-liquid separation effect, high coagulant recovery efficiency and low drug consumption.
Description
技术领域technical field
本发明涉及一种自来水厂排泥水的处理领域,具体为排泥水浓缩和混凝剂同步溶出的装置以及该装置的应用方法。The invention relates to the field of treatment of muddy water in a waterworks, in particular to a device for concentrating muddy water and synchronously dissolving a coagulant and an application method of the device.
背景技术Background technique
自来水厂净水工艺产生的排泥水水量约占水厂总净水量的1.5%~4%,含水率在99.7%左右;其主要成分包括无机矿物(如粘土)、混凝剂水解产物(如Al(OH)3、Fe(OH)3),以及少量有机物和微生物等杂质。排泥水不经处理直接排放至水体,不仅浪费了宝贵的水资源,同时也会污染水体。对于采用铝盐作为絮凝剂的自来水厂,其排泥水中含有大量铝盐,还会对收纳水体中的水生生物造成一定的毒害作用。对自来水厂排泥水开展回用处理,一方面能节约大量水资源,大幅降低对收纳水体的污染;一方面还可以回收排泥水中的部分混凝剂,从而有效降低自来水厂的混凝剂消耗量。The amount of sludge produced by the water purification process in the water plant accounts for about 1.5% to 4% of the total purified water in the water plant, and the moisture content is about 99.7%; its main components include inorganic minerals (such as clay), coagulant hydrolyzates (such as Al(OH) 3 , Fe(OH) 3 ), and a small amount of impurities such as organic matter and microorganisms. The sludge water is directly discharged into the water body without treatment, which not only wastes precious water resources, but also pollutes the water body. For water plants that use aluminum salts as flocculants, the sludge water contains a large amount of aluminum salts, which will also cause certain toxic effects to aquatic organisms in the receiving water bodies. On the one hand, it can save a lot of water resources and greatly reduce the pollution to the receiving water body; on the other hand, it can also recover part of the coagulant in the muddy water, thereby effectively reducing the consumption of coagulant in the water plant. quantity.
当前,国内外关于自来水排泥水的回用处理技术方案,可以分为2大类。一类是基于排泥水高浓度悬浮物特性,进行的以固液分离为主要目的的回用处理;一类是针对排泥水中残留的混凝剂水解产物,开展的以混凝剂回收为主要目的的回用处理。其中,前者的核心在于排泥水浓缩效率的提高,可供采用的技术方法与设备包括传统的重力浓缩池、造粒流化床浓缩技术、污泥浓缩脱水一体化设备等;后者的关键则在于排泥水固相中Al、Fe的溶出或提取,常用的方法包括酸化、碱化、离子交换等。At present, domestic and foreign technical solutions for the reuse and treatment of tap water and muddy water can be divided into two categories. One is the reuse treatment with solid-liquid separation as the main purpose based on the characteristics of high-concentration suspended solids in the muddy water; the other is for the coagulant hydrolysis product remaining in the muddy water, and the main purpose is to recover the coagulant. purpose of reuse. Among them, the core of the former is to improve the concentration efficiency of sludge drainage, and the available technical methods and equipment include traditional gravity concentration tank, granulation fluidized bed concentration technology, sludge concentration and dehydration integrated equipment, etc.; the key of the latter is For the dissolution or extraction of Al and Fe in the solid phase of the sludge water, the commonly used methods include acidification, alkalization, ion exchange, etc.
排泥水固液分离的主要技术问题在于排泥水浓缩效率较低,导致工艺复杂、占地面积大,建设运行成本高。尽管通过混凝预处理可以提高浓缩效率,但增加了混凝剂的消耗量。中国发明专利(CN201210343711.X)公开了一种排泥水的高效浓缩装置,该装置通过向排泥水中投加PAM和设置分离塔的技术方案实现了排泥水浓缩效率的提高,但无法实现排泥水中混凝剂的回收。The main technical problem of solid-liquid separation of sludge-draining water is that the concentration efficiency of sludge-draining water is low, resulting in complicated process, large area and high construction and operation cost. Although the concentration efficiency can be improved by coagulation pretreatment, it increases the consumption of coagulant. Chinese invention patent (CN201210343711.X) discloses a high-efficiency concentrating device for muddy water. The device realizes the improvement of the concentration efficiency of muddy water through the technical scheme of adding PAM to the muddy water and setting up a separation tower, but it cannot realize the muddy water concentration. Recovery of coagulants.
排泥水中混凝剂回收处理的主要技术问题在于仍然需要增设后续排泥水的处理处置过程。经混凝剂回收处理后,富含Al、Fe的清液可以与自来水厂原水混合进行回用,剩余的大部分泥水混合物,仍然需要进一步进行固液分离,才能实现排泥水的妥善处理处置。此外,采用酸碱法回收混凝剂时,因为大量投加了酸或碱,在进行回用前还需要调整pH。The main technical problem of the recovery and treatment of coagulant in the sludge water is that it is still necessary to add a subsequent treatment and disposal process for the sludge water. After the coagulant recovery treatment, the clear liquid rich in Al and Fe can be mixed with the raw water of the water plant for reuse. Most of the remaining mud-water mixture still needs further solid-liquid separation to realize the proper treatment and disposal of the muddy water. In addition, when the coagulant is recovered by the acid-base method, since a large amount of acid or alkali is added, the pH needs to be adjusted before recycling.
总之,迄今为止,尚未见有关于自来水厂排泥水同步固液分离和混凝剂回收方法与装置的公开报道。In conclusion, so far, there has been no public report on the method and device for simultaneous solid-liquid separation and coagulant recovery of sludge and water in waterworks.
发明内容SUMMARY OF THE INVENTION
本发明第一目的在于,提供一种用于排泥水的水力旋流分离器;旨在实现排泥水中泥沙等固体与水的分离,以及混凝剂的同步溶出。The first objective of the present invention is to provide a hydrocyclone separator for sludge drainage; it aims to realize the separation of solids such as sediment and water in sludge drainage, and the simultaneous dissolution of coagulant.
本发明第二目的在于,提供一种包含所述的水力旋流分离器的排泥水浓缩以及混凝剂同步溶出的系统。The second object of the present invention is to provide a system for concentrating sludge water and synchronously dissolving coagulant comprising the hydrocyclone separator.
本发明第三目的在于,提供了一种所述系统的应用方法,旨在提供一种体积小、占地面积小、浓缩效率高,同时实现混凝剂溶出回收的自来水厂排泥水同步浓缩与混凝剂回收的方法。The third object of the present invention is to provide an application method of the system, aiming to provide a small volume, small footprint, high concentration efficiency, and at the same time realize the coagulant dissolution and recovery of synchronous concentration and concentration of sludge from a tap water plant. Methods of coagulant recovery.
一种排泥水同步浓缩与混凝剂回收的水力旋流分离器,为一容器,容器内部包括位于上部的圆柱形腔体和位于下部的圆锥型腔体,圆柱形腔体和圆锥型腔体相互连通;所述的圆柱形腔体顶部设置有溢流管,所述的圆柱形腔体侧壁设置有进料管;所述的圆锥型腔体底部设置有底流管;圆柱形腔体的上部侧壁设置有超声波发生器。The utility model relates to a hydrocyclone separator for synchronous concentration of sludge drainage and recovery of coagulant, which is a container. The interior of the container includes a cylindrical cavity located at the upper part and a conical cavity located at the lower part, and the cylindrical cavity and the conical cavity. The top of the cylindrical cavity is provided with an overflow pipe, the side wall of the cylindrical cavity is provided with a feeding pipe; the bottom of the conical cavity is provided with an underflow pipe; The upper side wall is provided with an ultrasonic generator.
作为优选,所述的容器壳体包括由上向下依次密封连接的顶盖板、上直筒段、下直筒段、圆锥段和带底流管的底板;顶盖板、上直筒段、下直筒段围成所述的圆柱形腔体;所述的圆锥段和带底流管的底板围成所述的圆锥型腔体;所述的顶盖板带有溢流管;所述的进料管沿上直筒段外壁切线方向设置;所述的超声波发生器设置在上直筒段的外壁。Preferably, the container shell comprises a top cover plate, an upper straight cylinder section, a lower straight cylinder section, a conical section and a bottom plate with an underflow tube which are sealed and connected sequentially from top to bottom; a top cover plate, an upper straight cylinder section, and a lower straight cylinder section The cylindrical cavity is enclosed; the conical section and the bottom plate with the underflow pipe are enclosed to form the conical cavity; the top cover plate is provided with an overflow pipe; The tangential direction of the outer wall of the upper straight tube section is arranged; the ultrasonic generator is arranged on the outer wall of the upper straight tube section.
本发明中,上直筒段设置有超声波发生器,有助于实现料液在旋流分离阶段同步辅助进行超声处理。In the present invention, the upper straight cylinder section is provided with an ultrasonic generator, which is helpful to realize the simultaneous auxiliary ultrasonic treatment of the material and liquid in the cyclone separation stage.
作为优选,所述的超声波发生器为相对设置的2套;所述的超声波发生器呈轴瓦状,通过栓接方式相连、并固定于上直筒段的外壁。Preferably, the ultrasonic generators are arranged in two opposite sets; the ultrasonic generators are in the shape of a bearing pad, are connected by bolting, and are fixed on the outer wall of the upper straight cylinder section.
作为优选,溢流管沿水力旋流分离器的中轴线设置。Preferably, the overflow pipe is arranged along the central axis of the hydrocyclone.
所述的溢流管穿过顶盖板插入水力旋流分离器的腔室内。也即是,所述的溢流管的输入端设置在圆柱形腔体腔室内,输出端设置在圆柱形腔体腔室外。The overflow pipe is inserted into the chamber of the hydrocyclone through the top cover plate. That is, the input end of the overflow pipe is arranged inside the cylindrical cavity cavity, and the output end is arranged outside the cylindrical cavity cavity.
溢流管的输入端设置在下直筒段围成的腔室内。The input end of the overflow pipe is arranged in the chamber enclosed by the lower straight cylinder section.
所述的溢流管插入水力旋流分离器的腔室的长度与上直筒段、下直筒段的高度相等。也即是,溢流管输入端设置在接近下直筒段的腔体底部。The length of the overflow pipe inserted into the chamber of the hydrocyclone is equal to the height of the upper straight cylinder section and the lower straight cylinder section. That is, the input end of the overflow pipe is arranged near the bottom of the cavity of the lower straight cylinder section.
作为优选,所述的顶盖板、上直筒段、下直筒段、圆锥段和底板通过法兰(密封)连接。Preferably, the top cover plate, the upper straight cylinder section, the lower straight cylinder section, the conical section and the bottom plate are connected by flanges (sealing).
所述的水力旋流分离器(5)自上向下依次为带溢流管(9)的顶盖板(10)、上直筒段(11)、下直筒段(12)、圆锥段(13)和带底流管(15)的底板(14)组成,各部分采用法兰连接;上直筒段(11)围成的区域为直筒段混凝剂溶出反应区(A),下直筒段(12)围成的区域为直筒段固液分离区(B)、圆锥段围成的区域为圆锥段固液分离区(C)。The hydrocyclone (5) is, from top to bottom, a top cover plate (10) with an overflow pipe (9), an upper straight cylinder section (11), a lower straight cylinder section (12), and a conical section (13). ) and a bottom plate (14) with an underflow tube (15), each part is connected by flanges; the area enclosed by the upper straight section (11) is the straight section coagulant dissolution reaction zone (A), the lower straight section (12 ) is the solid-liquid separation area of the straight cylinder section (B), and the area enclosed by the conical section is the solid-liquid separation area of the conical section (C).
进一步优选:所述的溢流管(9)插入水力旋流分离器(5)内的深度为直筒段混凝剂溶出反应区(A)高度与直筒段固液分离区(B)高度之和。Further preferably: the depth at which the overflow pipe (9) is inserted into the hydrocyclone (5) is the sum of the height of the straight cylinder section coagulant dissolution reaction zone (A) and the height of the straight cylinder section solid-liquid separation zone (B) .
作为优选,所述的圆锥段锥角为8°。Preferably, the cone angle of the cone segment is 8°.
本发明所述的水力旋流分离器优选应用于自来水厂的排泥水的同步浓缩与混凝剂回收。The hydrocyclone separator of the present invention is preferably applied to the simultaneous concentration and coagulant recovery of the sludge drainage in the waterworks.
本发明还提供了一种自来水厂排泥水浓缩以及混凝剂同步溶出的系统,包括所述的水力旋流分离器、混合器、泥泵、混凝剂溶出药剂配制桶和离心脱水机;所述的混凝剂溶出药剂配制桶的出口和泥泵的出口分别或合并后与混合器的入口连接;所述的混合器的出口与所述的水力旋流分离器的进料管连接;所述的混合器的底流管与离心脱水机的入口连接;离心脱水机的液体出口和溢流管分别或合并后接入自来水回用系统。The invention also provides a system for concentrating sludge drainage and coagulant synchronous dissolution in a waterworks, including the hydrocyclone separator, mixer, mud pump, coagulant dissolution agent preparation barrel and centrifugal dehydrator; The outlet of the coagulant dissolution agent preparation barrel and the outlet of the mud pump are respectively or combined with the inlet of the mixer; the outlet of the mixer is connected with the feed pipe of the hydrocyclone; the The underflow pipe of the mixer is connected with the inlet of the centrifugal dehydrator; the liquid outlet and the overflow pipe of the centrifugal dehydrator are connected to the tap water reuse system separately or after being combined.
本发明提供的自来水厂排泥水浓缩以及混凝剂同步溶出的系统,包括混凝剂溶出药剂投加系统和水力旋流分离系统。水力旋流分离系统为核心,水力旋流分离系统包括水力旋流分离器以及与水力旋流分离器的进料管连接的混合器;水力旋流分离器中增设混凝剂溶出反应区;也即是设置有超声波发生器的上直筒段;水力旋流分离器的底流管(底部出口)与离心脱水机相连。自来水厂的排泥水与来自混凝剂溶出药剂投加系统的溶出药剂混合后,进入水力旋流分离系统进行同步浓缩和混凝剂溶出反应,浓缩后的浓缩污泥排入离心脱水机脱水,溶出的混凝剂则随溢流清液直接回用到自来水厂。The system for concentrating sludge water from a tap water plant and synchronously dissolving a coagulant provided by the invention includes a coagulant dissolution agent dosing system and a hydrocyclone separation system. The core of the hydrocyclone separation system is the hydrocyclone separation system, which includes a hydrocyclone separator and a mixer connected to the feed pipe of the hydrocyclone separator; a coagulant dissolution reaction zone is added to the hydrocyclone separator; That is, the upper straight cylinder section provided with the ultrasonic generator; the underflow pipe (bottom outlet) of the hydrocyclone is connected to the centrifugal dehydrator. After the sludge discharge from the water plant is mixed with the dissolution agent from the coagulant dissolution agent dosing system, it enters the hydrocyclone separation system for simultaneous concentration and coagulant dissolution reaction, and the concentrated sludge is discharged into the centrifugal dehydrator for dehydration. The dissolved coagulant is directly recycled to the water plant with the overflow clear liquid.
作为优选,所述的混凝剂溶出药剂配制桶通过混凝剂溶出药剂投加泵与所述的混合器的入口连接。Preferably, the coagulant dissolution medicament preparation barrel is connected to the inlet of the mixer through a coagulant dissolution medicament dosing pump.
所述的混凝剂溶出药剂配制桶的出口与所述的混凝剂溶出药剂投加泵的输入端连接,混凝剂溶出药剂投加泵的输出端直接与混合器的入口连接,或者接入泥泵与混合器入口连接的管路上。The outlet of the coagulant dissolution medicament preparation barrel is connected with the input end of the coagulant dissolution medicament dosing pump, and the output end of the coagulant leaching medicament dosing pump is directly connected with the inlet of the mixer, or is connected to the inlet of the mixer. On the pipeline connecting the mud pump and the mixer inlet.
作为优选,所述的混合器为管式静态混合器。Preferably, the mixer is a tubular static mixer.
作为优选,所述的溢流管上设置有溢流清液排放阀门。Preferably, the overflow pipe is provided with an overflow clear liquid discharge valve.
作为优选,所述的底流管上设置有底流浓缩污泥排放阀门。Preferably, the underflow pipe is provided with an underflow concentrated sludge discharge valve.
本发明还提供了一种利用所述的系统同步进行排泥水浓缩和混凝剂溶出回收的方法,将所述的混凝剂溶出药剂在所述的配制桶中溶解;在混合器中与排泥水混合,随后转移至所述的水力旋流分离器中旋流分离,以及同步进行超声辅助混凝剂溶出;富含混凝剂的清液由溢流管连续排出;底流浓缩污泥由底流管转移至离心脱水机中固液分离;固液分离得到的固体部分为泥饼,液体部分和/或溢流的清液回用。The present invention also provides a method for synchronously concentrating sludge drainage and coagulant dissolution recovery by utilizing the system, wherein the coagulant dissolution agent is dissolved in the preparation barrel; The mud and water are mixed, and then transferred to the hydrocyclone for cyclone separation, and ultrasonic-assisted coagulant dissolution is carried out simultaneously; the clear liquid rich in coagulant is continuously discharged from the overflow pipe; the underflow thickened sludge is discharged by the underflow The tube is transferred to a centrifugal dehydrator for solid-liquid separation; the solid part obtained from the solid-liquid separation is mud cake, and the liquid part and/or the overflowed clear liquid are reused.
具体地,来自自来水厂的排泥水在泥泵抽吸作用下,与来自混凝剂溶出药剂投加系统的溶出药剂在所述的管式静态混合器进行充分混合;混合液沿切线方向进入水力旋流系统后,首先在混凝剂溶出反应区、在混凝剂溶出药剂以及超声辅助下实现混凝剂自固相向液相的溶出过程,之后继续进行水力旋流固液分离;分离得到的溢流清液富含混凝剂,送至自来水厂原水井与原水直接混合,实现排泥水和混凝剂的回收利用,高浓度的浓缩污泥则进入离心脱水机进行离心脱水。Specifically, under the suction of the mud pump, the sludge drainage water from the water plant is fully mixed with the dissolution agent from the coagulant dissolution agent dosing system in the tubular static mixer; the mixed liquid enters the hydraulic power in the tangential direction. After the cyclone system, the coagulant dissolution process from the solid phase to the liquid phase is first realized in the coagulant dissolution reaction zone, with the aid of the coagulant dissolution agent and ultrasonic, and then the hydrocyclone solid-liquid separation is continued; The overflow clear liquid is rich in coagulant, and sent to the raw water well of the water plant to be directly mixed with the raw water to realize the recycling of sludge water and coagulant.
本发明方法中,在所述的超声作用下,利用超声效应促进混凝剂从固相向液相的迁移过程,明显提高了混凝剂的溶出率。In the method of the present invention, under the action of the ultrasonic, the migration process of the coagulant from the solid phase to the liquid phase is promoted by the ultrasonic effect, and the dissolution rate of the coagulant is obviously improved.
作为优选,所述的混凝剂溶出药剂为HCl或H2SO4。Preferably, the coagulant dissolution agent is HCl or H 2 SO 4 .
作为优选,控制混合器中的溶液的pH为3.0~4.0。Preferably, the pH of the solution in the mixer is controlled to be 3.0 to 4.0.
超声波的频率没有特别要求,例如为950~1050kHz。The frequency of the ultrasonic wave is not particularly required, but is, for example, 950 to 1050 kHz.
采用上述技术方案的自来水厂排泥水同步浓缩与混凝剂回收的方法及其装置,其机理简述于下:The method and device for synchronous concentration and coagulant recovery of sludge drainage in a waterworks using the above-mentioned technical scheme, its mechanism is briefly described as follows:
由泥泵抽吸的排泥水,首先与混凝剂溶出药剂在管式静态混合器中快速完成均匀混合。混合液由切向入口进入直管段混凝剂溶出反应区,在反应区内的混合液高速旋转并呈螺旋形向下运动;反应区内混合液固相中的混凝剂,在混凝剂溶出药剂作用下,自固相向液相进行迁移。混合液螺旋向下运动过程中,在离心力作用下,固相污泥颗粒将克服阻力作用与液体逐渐分离开,污泥颗粒之间彼此剧烈碰撞,同时在超声波的振动作用下,污泥颗粒发生破碎,相互之间摩擦、挤压,上述碰撞、破碎、摩擦、挤压作用,促进了混凝剂由固相向液相的迁移。混合液向下运行至直筒段固液分离区后,由于液体的螺旋运动,水力旋流器轴线附近成为低压区,器壁附近处压力最高,同时混凝剂继续由固相向液相溶出,污泥颗粒和液体也进一步分离。混合液继续下行至圆锥段固液分离区,大部分污泥颗粒将克服阻力作用向水力旋流器边壁移动,与液体分离开,最终由底流管排出,形成底流浓缩污泥,送至离心脱水机脱水;富含混凝剂的水和细微颗粒向低压区移动,边旋转边向上做螺旋运动,形成内旋流,最终以溢流清液形式从溢流管排出。离心脱水机脱水滤液与溢流清液合并后,送至自来水厂原水井进行回用。The muddy water sucked by the mud pump is firstly mixed with the coagulant dissolution agent quickly and uniformly in the tubular static mixer. The mixed liquid enters the coagulant dissolution reaction zone of the straight pipe section from the tangential inlet, and the mixed liquid in the reaction zone rotates at a high speed and moves downward in a spiral shape; the coagulant in the solid phase of the mixed liquid in the reaction zone is Under the action of the dissolution agent, it migrates from the solid phase to the liquid phase. During the spiral downward movement of the mixed liquid, under the action of centrifugal force, the solid phase sludge particles will overcome the resistance and gradually separate from the liquid, and the sludge particles collide violently with each other. Fragmentation, friction and extrusion between each other, and the above-mentioned collision, crushing, friction and extrusion effects promote the migration of the coagulant from the solid phase to the liquid phase. After the mixed liquid runs down to the solid-liquid separation zone of the straight cylinder section, due to the spiral motion of the liquid, the vicinity of the axis of the hydrocyclone becomes a low-pressure zone, and the pressure near the wall is the highest, and the coagulant continues to dissolve from the solid phase to the liquid phase. Sludge particles and liquid are also further separated. The mixed liquid continues to descend to the solid-liquid separation area of the conical section. Most of the sludge particles will overcome the resistance and move to the side wall of the hydrocyclone, separated from the liquid, and finally discharged from the underflow pipe to form underflow concentrated sludge, which is sent to the centrifugal The dehydrator is dehydrated; the water and fine particles rich in coagulant move to the low pressure area, and make a spiral motion upward while rotating, forming an internal swirling flow, which is finally discharged from the overflow pipe in the form of overflow clear liquid. After the dehydration filtrate of the centrifugal dehydrator is combined with the overflow clear liquid, it is sent to the raw water well of the waterworks for reuse.
发明具有的优点和有益效果Advantages and beneficial effects of the invention
本发明具有的优点及有益效果:The advantages and beneficial effects that the present invention has:
1、同步实现排泥水的固液分离与混凝剂回收。本发明在传统水力旋流器基础上,通过适当延长直筒段长度,形成直筒段混凝剂溶出区和直筒段固液分离区,排泥水的固液分离和混凝剂回收得以在水力旋流器中同步实现。1. Simultaneously realize the solid-liquid separation and coagulant recovery of the muddy water. On the basis of the traditional hydrocyclone, the present invention forms a coagulant dissolution zone and a solid-liquid separation zone in the straight cylinder section by appropriately extending the length of the straight cylinder section. Synchronization in the device.
2、固液分离效果好,无需投加混凝剂。排泥水的浓缩分离,主要依靠水力旋流器内排泥水高速旋转产生的离心力来实现,固液分离效果好,无需投加混凝剂来提高排泥水的浓缩性能。2. Good solid-liquid separation effect, no need to add coagulant. The concentration and separation of the muddy water is mainly realized by the centrifugal force generated by the high-speed rotation of the muddy water in the hydrocyclone, and the solid-liquid separation effect is good.
3、混凝剂的溶出效率高。在直筒段混凝剂溶出区,排泥水固体颗粒由于高速旋转和超声波振动,将发生破碎、相互碰撞、摩擦、挤压等作用,促进了混凝剂由固相向液相的迁移过程,混凝剂的溶出效率高。3. The dissolution efficiency of the coagulant is high. In the coagulant dissolution zone of the straight cylinder section, due to high-speed rotation and ultrasonic vibration, the solid particles of the muddy water will be broken, collided, rubbed, and squeezed, which promotes the migration process of the coagulant from the solid phase to the liquid phase. The dissolution efficiency of the coagulant is high.
4、混凝剂溶出药剂的消耗量小。水力旋流分离系统中排泥水的高速旋转和超声波振动,提升了混凝剂的溶出效率,相应的混凝剂溶出药剂所需投加量得以大幅降低。4. The consumption of coagulant dissolution agent is small. The high-speed rotation and ultrasonic vibration of the muddy water in the hydrocyclone separation system improve the dissolution efficiency of the coagulant, and the dosage of the corresponding coagulant dissolution agent can be greatly reduced.
5、占地面积小,易于实现自动化控制。本发明提出的排泥水处理装置,由于固液分离效果好、混凝剂溶出效率高,单位面积条件下处理负荷高,具备占地面积小的显著优势;排泥水浓缩与混凝剂回收过程在水力旋流器内同步完成,设备工艺紧凑、集成化程度高,易于实现自动化控制。5. Small footprint, easy to realize automatic control. Due to the good solid-liquid separation effect, high coagulant dissolution efficiency, and high processing load per unit area, the sludge drainage water treatment device proposed by the present invention has a significant advantage of small footprint; the sludge drainage water concentration and coagulant recovery process are The hydrocyclone is synchronously completed, the equipment process is compact, the degree of integration is high, and it is easy to realize automatic control.
综上所述,本发明是一种占地面积小、集成化程度高、固液分离效果好、混凝剂溶出效率高,且能同步实现排泥水浓缩与混凝剂回收的自来水厂排泥水处理的方法及其装置。To sum up, the present invention is a tap water plant drained water with small footprint, high integration degree, good solid-liquid separation effect, high coagulant dissolution efficiency, and simultaneous realization of sludge drainage concentration and coagulant recovery. A method of treatment and an apparatus therefor.
附图说明Description of drawings
图1为本发明的自来水厂排泥水同步固液分离与混凝剂回收的方法流程示意图。FIG. 1 is a schematic flow chart of the method for synchronous solid-liquid separation and coagulant recovery of sludge drainage from a water plant according to the present invention.
图2为本发明中水力旋流器结构示意图。Figure 2 is a schematic structural diagram of a hydrocyclone in the present invention.
图3为本发明中超声波发生器安装示意图Fig. 3 is the installation schematic diagram of the ultrasonic generator in the present invention
以下结合附图对本发明的具体实施方式作进一步详细地说明。The specific embodiments of the present invention will be described in further detail below with reference to the accompanying drawings.
具体实施方式Detailed ways
参见图1、图2和图3,本发明提供的实现自来水厂排泥水同步固液分离与混凝剂回收的系统,包括泥泵(3)、混凝剂溶出药剂混合投加系统(I)、水力旋流分离系统(II)和离心脱水机(8)。混凝剂溶出药剂混合投加系统(I)由混凝剂溶出药剂配制桶(1)和混凝剂溶出药剂投加泵(2)组成;其中,混凝剂溶出药剂配制桶(1)的出口与混凝剂溶出药剂投加泵(2)的输入端连接。Referring to Fig. 1, Fig. 2 and Fig. 3, the system for realizing synchronous solid-liquid separation and coagulant recovery of sludge and water discharge from a waterworks provided by the present invention includes a mud pump (3), a coagulant dissolution agent mixing and dosing system (1) , Hydrocyclone separation system (II) and centrifugal dehydrator (8). The coagulant dissolution agent mixing and dosing system (1) is composed of a coagulant dissolution agent preparation barrel (1) and a coagulant dissolution agent addition pump (2); wherein, the coagulant dissolution agent preparation barrel (1) is composed of The outlet is connected with the input end of the coagulant dissolution agent dosing pump (2).
水力旋流分离系统(II)包括管式静态混合器(4)、水力旋流分离器(5)、溢流清液排放阀门(6)和底流浓缩污泥排放阀门(7)。泥泵(3)的出口与管式静态混合器(4)的进口由管道连接;混凝剂溶出药剂投加泵(2)的输出端和投加点位于管式静态混合器(4)的进口之前(混凝剂溶出药剂投加泵(2)的输出端通过连接管路与泥泵(3)与管式静态混合器(4)的管路连接)。The hydrocyclone separation system (II) includes a tubular static mixer (4), a hydrocyclone separator (5), an overflow clear liquid discharge valve (6) and an underflow thickened sludge discharge valve (7). The outlet of the mud pump (3) is connected with the inlet of the tubular static mixer (4) by a pipeline; the output end and the injection point of the coagulant dissolution agent dosing pump (2) are located at the inlet of the tubular static mixer (4) Before (the output end of the coagulant dissolution agent dosing pump (2) is connected with the pipeline of the mud pump (3) and the tubular static mixer (4) through the connecting pipeline).
所述的水力旋流器(5)的主体自上向下依次为带溢流管(9)的顶盖板(10)、上直筒段(11)、下直筒段(12)、圆锥段(13)和带底流管(15)的底板(14)组成,各部分采用法兰连接;上直筒段(11)围成的区域为直筒段混凝剂溶出反应区(A),下直筒段(12)围成的区域为直筒段固液分离区(B)、圆锥段围成的区域为圆锥段固液分离区(C)。水力旋流器(5)的进水管(17)与上直筒段(11)沿切线方向连接。溢流管(9)、顶盖板(10)、上直筒段(11)、下直筒段(12)、圆锥段(13)、底流管(15)、底板(14)和进水管(17)的规格根据处理规模和自来水厂排泥水的性质选择不同规格。The main body of the hydrocyclone (5) is, from top to bottom, a top cover plate (10) with an overflow pipe (9), an upper straight cylinder section (11), a lower straight cylinder section (12), and a conical section (10). 13) and a bottom plate (14) with an underflow pipe (15), and each part is connected by flanges; the area enclosed by the upper straight section (11) is the straight section coagulant dissolution reaction zone (A), and the lower straight section ( 12) The enclosed area is the solid-liquid separation area of the straight cylinder section (B), and the area enclosed by the conical section is the solid-liquid separation area of the conical section (C). The water inlet pipe (17) of the hydrocyclone (5) is connected with the upper straight cylinder section (11) along the tangential direction. Overflow pipe (9), top cover plate (10), upper straight cylinder section (11), lower straight cylinder section (12), conical section (13), bottom flow pipe (15), bottom plate (14) and water inlet pipe (17) The specifications of different specifications are selected according to the processing scale and the nature of the muddy water discharged from the water plant.
上直筒段(11)的外壁设有超声波发生器(16),超声波发生器(16)由2块对称的轴瓦状超声波发生器通过栓接方式相连而成,固定于上直筒段(11)的外壁。The outer wall of the upper straight cylinder section (11) is provided with an ultrasonic generator (16), and the ultrasonic generator (16) is formed by two symmetrical bearing-shaped ultrasonic generators connected by bolting, and is fixed on the upper straight cylinder section (11). outer wall.
管式静态混合器(4)的出口与水力旋流器(5)的进口相连。水力旋流器(5)的溢流管(9)上设置有溢流清液排放阀门(6),水力旋流器(5)底部的底流管(15)上设置有底流浓缩污泥排放阀门(7);水力旋流器(5)的分流比由溢流清液排放阀门(6)和底流浓缩污泥排放阀门(7)实现控制。底流浓缩污泥排放阀门(7)的出口与离心脱水机(8)连接,底流浓缩污泥进入离心脱水机(8)进行脱水,脱水泥饼外运处置,脱水滤液与来自溢流清液排放阀门(6)排放的富含混凝剂的溢流清液混合后,送至自来水厂原水井进行回用。The outlet of the tubular static mixer (4) is connected to the inlet of the hydrocyclone (5). The overflow pipe (9) of the hydrocyclone (5) is provided with an overflow clear liquid discharge valve (6), and the underflow pipe (15) at the bottom of the hydrocyclone (5) is provided with an underflow concentrated sludge discharge valve (7); The diversion ratio of the hydrocyclone (5) is controlled by the overflow clear liquid discharge valve (6) and the underflow thickened sludge discharge valve (7). The outlet of the underflow thickened sludge discharge valve (7) is connected to the centrifugal dewatering machine (8), and the underflow thickened sludge enters the centrifugal dewatering machine (8) for dehydration, the de-cemented cake is transported for disposal, and the dewatered filtrate and the clear liquid from the overflow are discharged. The coagulant-rich overflow clear liquid discharged from the valve (6) is mixed and sent to the raw water well of the waterworks for reuse.
本发明提供的自来水厂排泥水同步固液分离与混凝剂回收的方法,以水力旋流分离系统为核心,离心脱水机与水力旋流分离系统直接相连,泥泵抽吸的自来水厂排泥水与来自混凝剂溶药剂混合投加系统的混凝剂溶出药剂混合后,进入水力旋流分离系统同步进行排泥水浓缩和混凝剂溶出,得到的富含混凝剂的溢流清液直接送至自来水厂原水井进行回用,底流浓缩污泥排入离心脱水机脱水。The method for synchronizing solid-liquid separation and coagulant recovery of muddy water from a tap water plant provided by the present invention takes a hydrocyclone separation system as the core, the centrifugal dehydrator is directly connected with the hydrocyclone separation system, and the muddy water from the tap water plant is pumped by a mud pump. After mixing with the coagulant dissolution agent from the coagulant solvent agent mixing and dosing system, it enters the hydrocyclone separation system for simultaneous sludge drainage and coagulant dissolution, and the obtained overflow clear liquid rich in coagulant is directly It is sent to the raw water well of the waterworks for reuse, and the underflow thickened sludge is discharged into the centrifugal dehydrator for dehydration.
具体地,利用泥泵(3)抽吸自来水厂排泥水,排泥水与来自混凝剂溶出药剂混合投加系统(I)的混凝剂溶出药剂混合后,进入水力旋流分离系统(II)同步进行固液分离和混凝剂溶出,得到的富含混凝剂的溢流清液回用至自来水厂原水井;底流浓缩污泥进入离心脱水机(8)进行脱水,脱水滤液与溢流清液合并后进行回用,脱水泥饼则外运处置。Specifically, the mud pump (3) is used to pump the muddy water from the waterworks, and after the muddy water is mixed with the coagulant dissolution agent from the coagulant dissolution agent mixing and dosing system (I), it enters the hydrocyclone separation system (II) Simultaneous solid-liquid separation and coagulant dissolution are carried out, and the obtained overflow clear liquid rich in coagulant is reused to the raw water well of the water plant; the underflow thickened sludge enters the centrifugal dehydrator (8) for dehydration, and the dewatered filtrate and overflow The supernatant liquid is combined and reused, and the de-cemented cake is shipped out for disposal.
混凝剂溶出药剂采用HCl或者H2SO4。The coagulant dissolution agent adopts HCl or H 2 SO 4 .
本发明以水力旋流分离系统为核心,通过适当延长直筒段长度,形成直筒段混凝剂溶出区和直筒段固液分离区,排泥水的固液分离和混凝剂回收得以在水力旋流器中同步实现。本发明中固液分离通过水力旋流器内排泥水高速旋转产生的离心力来实现,固液分离效果好,无需投加混凝剂;在混凝剂溶出区,借助排泥水固体颗粒高速旋转和超声波振动产生的破碎、相互碰撞、摩擦、挤压等作用,大幅提升了混凝剂的溶出效率,混凝剂溶出药剂的消耗量小;设备处理负荷高、占地面积小,工艺紧凑、集成化程度高。总之,本发明具有占地面积小、固液分离效果好、混凝剂回收效率高、药耗低、同步实现排泥水浓缩和混凝剂回收的优势。The invention takes the hydraulic cyclone separation system as the core, and by appropriately extending the length of the straight cylinder section, the straight cylinder section coagulant dissolution zone and the straight cylinder section solid-liquid separation zone are formed. Synchronization in the device. In the present invention, the solid-liquid separation is realized by the centrifugal force generated by the high-speed rotation of the muddy water in the hydrocyclone, the solid-liquid separation effect is good, and no coagulant needs to be added; The crushing, mutual collision, friction, extrusion and other effects caused by ultrasonic vibration greatly improve the dissolution efficiency of coagulant, and the consumption of coagulant dissolution agent is small; the equipment has high processing load, small footprint, compact and integrated process high degree of chemistry. In a word, the invention has the advantages of small footprint, good solid-liquid separation effect, high coagulant recovery efficiency, low chemical consumption, and simultaneous realization of sludge drainage concentration and coagulant recovery.
采用上述的系统对排泥水进行处理。The sludge water is treated by the above system.
实施例1Example 1
本实施方式以我国南方某城市自来水厂排泥水作为处理对象,在排泥水处理预留场地搭建排泥水同步固液分离与混凝剂回收的小型装置,处理规模1m3/h。泥泵扬程为30m。排泥水的含水率在99.0%~99.7%之间。This embodiment takes the sludge drainage of a water plant in a city in southern China as the treatment object, and builds a small device for simultaneous solid-liquid separation and coagulant recovery of sludge drainage in a reserved site for sludge drainage, with a treatment scale of 1 m 3 /h. The lift of the mud pump is 30m. The moisture content of the muddy water is between 99.0% and 99.7%.
参阅图1和图2,排泥水由泥泵(3)抽吸,与来自混凝剂溶出药剂混合投加系统(I)的混凝剂溶出药剂,一同送至管式静态混合器(4)进行混合,之后送至水力旋流分离器(5)进行同步固液分离和混凝剂溶出。水力旋流器的直筒段混凝剂溶出反应区(A)直径200mm,高度200mm;直筒段固液分离区(B)直径200mm,高度100mm;圆锥段固液分离区(C)顶部直径200mm,底部直径50mm,锥角8°。混凝剂溶出药剂采用H2SO4,投加量为控制排泥水混合液pH值在3.5左右。排泥水混合液沿水力旋流器(5)切线方向进入直筒段混凝剂溶出反应区(A),在H2SO4的溶出作用,以及排泥水固体颗粒高速旋转和超声波振动(功率为1000W)产生的破碎、相互碰撞、摩擦、挤压等作用,排泥水固相中的混凝剂向液相发生迁移;排泥水继续螺旋向下运动,依次进入直筒段固液分离区(B)和圆锥段固液分离区(C),在离心力作用下,完成固液分离过程。排泥水中混凝剂的回收率为40~50%,富含混凝剂的清液向水力旋流器中心的低压区移动,以内旋流形式向上做螺旋运动,最终以溢流清液形式从溢流管(9)排出;底流浓缩泥渣含水率90~94%左右,经底流管(15)送至离心脱水机(8)脱水,脱水泥饼含水率60%左右,运至厂外处置,产生的脱水滤液与溢流清液混合后送至自来水厂原水井回用。Referring to Figure 1 and Figure 2, the muddy water is sucked by the mud pump (3), and sent to the tubular static mixer (4) together with the coagulant dissolution agent from the coagulant dissolution agent mixing and dosing system (1). After mixing, it is sent to a hydrocyclone (5) for simultaneous solid-liquid separation and coagulant dissolution. The diameter of the coagulant dissolution reaction zone (A) of the straight section of the hydrocyclone is 200mm and the height is 200mm; the diameter of the solid-liquid separation section of the straight section (B) is 200mm and the height of 100mm; the diameter of the top of the solid-liquid separation section of the conical section (C) is 200mm, Bottom diameter 50mm,
当然,以上实施例仅用以说明本发明的技术方案而非对其限制,尽管参照上述实施例对本发明进行了详细的说明,所属领域的普通技术人员应当理解,依然可以对本发明的具体实施方式进行修改或者等同替换,而未脱离本发明精神和范围的任何修改或者等同替换,其均应涵盖在本发明的权利要求范围中。Of course, the above embodiments are only used to illustrate the technical solutions of the present invention and not to limit them. Although the present invention has been described in detail with reference to the above embodiments, those of ordinary skill in the art should understand that the specific embodiments of the present invention can still be explained. Any modification or equivalent replacement without departing from the spirit and scope of the present invention should be included in the scope of the claims of the present invention.
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