CN116621298A - Space intensive flocculation water treatment device - Google Patents
Space intensive flocculation water treatment device Download PDFInfo
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- CN116621298A CN116621298A CN202310441856.1A CN202310441856A CN116621298A CN 116621298 A CN116621298 A CN 116621298A CN 202310441856 A CN202310441856 A CN 202310441856A CN 116621298 A CN116621298 A CN 116621298A
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- 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
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- C02F2201/00—Apparatus for treatment of water, waste water or sewage
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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
- C02F2201/00—Apparatus for treatment of water, waste water or sewage
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Abstract
本发明公开了一种空间集约式絮凝水处理装置,包括沉降分离机构以及盘绕在其外侧的螺旋盘管,所述沉降分离机构包括第一外锥体,所述沉降分离机构内设置有第一内锥体,所述第一内锥体与第一外锥体之间设置有多层沉降锥板;所述螺旋盘管的一端设置有污水进口,另一端穿设于所述第一内锥体内,所述第一外锥体与第一内锥体之间为圆锥板分离区,所述圆锥板分离区的上方为清水区。本发明可以更大程度地利用设备的空间,单位设备体积的污水处理量更高,快速形成较大且密实的絮凝体,絮凝体与水体的分离效率高,水力停留时间较传统絮凝装置降低50%以上,提高了絮凝处理速度和效率,适合于各种污水处理,节约空间,提高效率,适用于空间受限的污水处理工程。
The invention discloses a space-intensive flocculation water treatment device, which comprises a sedimentation separation mechanism and a spiral coil coiled outside the sedimentation separation mechanism. The sedimentation separation mechanism includes a first outer cone, and a first An inner cone, a multi-layer settling cone plate is arranged between the first inner cone and the first outer cone; one end of the spiral coil is provided with a sewage inlet, and the other end is pierced through the first inner cone In the body, between the first outer cone and the first inner cone is a cone-plate separation zone, and above the cone-plate separation zone is a clear water zone. The invention can utilize the space of the equipment to a greater extent, the sewage treatment capacity per unit volume of the equipment is higher, large and dense flocs are quickly formed, the separation efficiency of the flocs and the water body is high, and the hydraulic retention time is reduced by 50% compared with the traditional flocculation device More than %, it improves the speed and efficiency of flocculation treatment, is suitable for various sewage treatment, saves space, improves efficiency, and is suitable for sewage treatment projects with limited space.
Description
技术领域technical field
本发明涉及一种空间集约式絮凝水处理装置,属于水处理技术领域。The invention relates to a space-intensive flocculation water treatment device, which belongs to the technical field of water treatment.
背景技术Background technique
絮凝法可以快速去除水中的悬浮污染物和色度,是一种重要的水处理技术,被广泛应用于各种工业污水、市政生活污水、地表污染水体的治理。Flocculation can quickly remove suspended pollutants and chroma in water. It is an important water treatment technology and is widely used in the treatment of various industrial sewage, municipal domestic sewage, and surface polluted water bodies.
絮凝方法的原理是向污水中加入助凝剂、絮凝剂、混凝剂等絮凝药剂,这些药剂通过压缩悬浮污染颗粒的双电层、电中和以及吸附架桥作用使微细的污染颗粒聚结在一起,形成一定尺度的絮凝体(俗称矾花),絮凝体的密度大于水的密度,缓慢沉降从水体中分离,从而使水质得到净化。The principle of the flocculation method is to add coagulants, flocculants, coagulants and other flocculation agents to the sewage. These agents make the fine pollution particles coalesce by compressing the electric double layer of the suspended pollution particles, neutralization and adsorption bridging. Together, a certain scale of flocs (commonly known as alum flowers) is formed. The density of the flocs is greater than that of water, and they slowly settle and separate from the water body, thereby purifying the water quality.
絮凝方法处理污水的弊端是需要较长的沉降时间,因为絮凝体与水的密度差较小,使得絮凝体的沉降速度很小,只有沉降时间足够大时才能得到澄清的水相,一般的水力停留时间要达到几个小时以上才能取得较好的处理效果,使得处理设施或设备的处理速度低,体积庞大,对于体量比较大的污水,用絮凝法处理时,由于沉降分离速度低而使得设备的体积非常庞大。传统的絮凝沉降装置有沉降澄清槽、平流沉淀池、折流沉淀池等,占地面积都比较大,为了减小絮凝处理装置的占地面积,近年来人们设计出了斜板(斜管)沉淀池,斜管和斜板可以在一定程度上提高沉淀分离效率,但是设备仍然需要较大的絮凝空间,整体设备的占地面积仍然居高不下;近年来还出现了气浮絮凝,速度有所升高,但是仍然需要较大的占地面积,装备的自身重量也比较大,附属设备多,工艺控制复杂,对于空间受限的城市内河地表河道或者周围没有硬化地面的野外河道的治理受到极大的限制。The disadvantage of the flocculation method to treat sewage is that it takes a long time for settling, because the density difference between the flocs and water is small, so that the settling speed of the flocs is very small, and only when the settling time is long enough can a clear water phase be obtained. The residence time needs to be several hours or more to achieve a good treatment effect, which makes the treatment facilities or equipment have a low treatment speed and a large volume. The size of the device is very large. Traditional flocculation settling devices include settling clarifiers, advection sedimentation tanks, baffle sedimentation tanks, etc., which occupy a relatively large area. In order to reduce the floor area of the flocculation treatment device, people have designed inclined plates (inclined tubes) in recent years. Sedimentation tanks, inclined tubes and inclined plates can improve the efficiency of sedimentation and separation to a certain extent, but the equipment still needs a large flocculation space, and the overall equipment footprint is still high; in recent years, air flotation flocculation has also appeared, and the speed is slow. However, it still requires a larger floor area, the weight of the equipment itself is relatively large, there are many auxiliary equipment, and the process control is complicated. The treatment of urban inland surface rivers with limited space or wild rivers without hardened ground around them is limited. Extremely restrictive.
发明内容Contents of the invention
为了解决上述技术问题,本发明提供一种空间集约式絮凝水处理装置,该装置可以大幅度地提高设备的空间利用率,其单位设备体积的污水处理量更高,快速形成较大且密实的絮凝体,絮凝体与水体的密度差大、分离速度高,从而使分离效率提高,水力停留时间较传统絮凝装置降低50%以上,较大地提高了絮凝处理速度和效率,减少了设备体积,适合于污水处理厂、污水处理车间或者地表污染水体的污水处理,节约空间,提高效率,尤其适用于空间受限的污水处理工程。In order to solve the above technical problems, the present invention provides a space-intensive flocculation water treatment device, which can greatly improve the space utilization rate of the equipment, and has a higher sewage treatment capacity per unit volume of equipment, and quickly forms a larger and denser water treatment device. The floc, the density difference between the floc and the water body is large, and the separation speed is high, so that the separation efficiency is improved, and the hydraulic retention time is reduced by more than 50% compared with the traditional flocculation device, which greatly improves the speed and efficiency of flocculation treatment, reduces the volume of the equipment, and is suitable for Used in sewage treatment plants, sewage treatment workshops or sewage treatment of surface polluted water bodies, saving space and improving efficiency, especially suitable for sewage treatment projects with limited space.
具体而言,包括以下技术方案:Specifically, the following technical solutions are included:
本发明提供了一种空间集约式絮凝水处理装置,包括沉降分离机构以及盘绕在其外侧的螺旋盘管,所述沉降分离机构包括第一外锥体,所述沉降分离机构内设置有第一内锥体,所述第一内锥体与第一外锥体之间设置有多层沉降锥板;所述螺旋盘管的一端设置有污水进口,另一端穿设于所述第一内锥体内,所述第一外锥体与第一内锥体之间为圆锥板分离区,所述圆锥板分离区的上方为清水区。The present invention provides a space-intensive flocculation water treatment device, which includes a settling and separating mechanism and a spiral coil coiled outside it. The settling and separating mechanism includes a first outer cone, and the settling and separating mechanism is provided with a first An inner cone, a multi-layer settling cone plate is arranged between the first inner cone and the first outer cone; one end of the spiral coil is provided with a sewage inlet, and the other end is pierced through the first inner cone In the body, between the first outer cone and the first inner cone is a cone-plate separation zone, and above the cone-plate separation zone is a clear water zone.
本发明的一种实施方式中,所述沉降分离机构还包括第二外锥体,所述第一外椎体与所述第二外椎体相互连接,所述第一外锥体位于所述第二外锥体的上方。In one embodiment of the present invention, the settling separation mechanism further includes a second outer cone, the first outer cone is connected to the second outer cone, and the first outer cone is located at the above the second outer cone.
本发明的一种实施方式中,所述第一外锥体底端的横截面积大于其顶端的横截面积;所述第二外锥体底端的横截面积小于其顶端的横截面积,第一外锥体的底端与所述第二外锥体的顶端相连;所述第一内锥体底端的横截面积大于其顶端的横截面积,第一内锥体位于所述第一外锥体内。In one embodiment of the present invention, the cross-sectional area of the bottom end of the first outer cone is larger than the cross-sectional area of the top end; the cross-sectional area of the bottom end of the second outer cone is smaller than the cross-sectional area of the top end. The bottom end of an outer cone is connected to the top of the second outer cone; the cross-sectional area of the bottom end of the first inner cone is greater than the cross-sectional area of the top end, and the first inner cone is located at the first outer cone. inside the cone.
本发明的一种实施方式中,所述多层沉降锥板包括若干个圆锥板,所述圆锥板为圆锥台结构且上下两端贯通,若干个所述圆锥板同轴线,若干个所述圆锥板层叠以形成多层喇叭状的圆锥面。In one embodiment of the present invention, the multi-layer settling cone plate includes several conical plates. The conical plates are stacked to form a multi-layered trumpet-shaped conical surface.
本发明的一种实施方式中,所述第一外锥体内的多层沉降锥板的圆锥板的倾斜角度与所述第一外锥体以及第一内锥体外壳的倾斜角度相适配;所述第二外锥体内也设置有多层沉降锥板,所述第二外锥体内的多层沉降锥板的圆锥板的倾斜角度与所述第二外锥体外壳的倾斜角度相适配。In one embodiment of the present invention, the inclination angle of the conical plates of the multi-layer settling cone plates in the first outer cone is adapted to the inclination angles of the first outer cone and the shell of the first inner cone; The second outer cone is also provided with a multi-layer settling cone plate, and the inclination angle of the conical plate of the multi-layer settling cone plate in the second outer cone is adapted to the inclination angle of the second outer cone shell .
本发明的一种实施方式中,所述沉降分离机构内还设置有第二内锥体,所述第二内锥体位于所述第一内锥体的下方,第二内锥体为圆锥体,其尖端朝向所述第一内锥体底端出口的中心位置,第二内锥体的底面位于所述第一外锥体与第二外锥体最大横截面处,所述第二内锥体用于将从第一内锥体底端流出的絮凝体以及水相横向流动分布在第一外锥体与第二外锥体的最大横截面处。In one embodiment of the present invention, a second inner cone is also provided in the settling separation mechanism, the second inner cone is located below the first inner cone, and the second inner cone is a cone , its tip is towards the center of the outlet at the bottom end of the first inner cone, the bottom surface of the second inner cone is located at the maximum cross-section of the first outer cone and the second outer cone, and the second inner cone The body is used to distribute the floc flowing out from the bottom end of the first inner cone and the lateral flow of the water phase at the maximum cross-section of the first outer cone and the second outer cone.
本发明的一种实施方式中,所述螺旋盘管上设置有第一絮凝剂进口和第二絮凝剂进口;所述螺旋盘管还连接有排气管,所述排气管用于排出螺旋盘管内污水流动过程中的聚集气体,所述排气管上设置有阀门。In one embodiment of the present invention, the spiral coil is provided with a first flocculant inlet and a second flocculant inlet; the spiral coil is also connected with an exhaust pipe, and the exhaust pipe is used to discharge the spiral coil The accumulated gas during the flow of sewage in the pipe, the exhaust pipe is provided with a valve.
本发明的一种实施方式中,所述第一内锥体的顶端向上延伸有圆筒体,所述第一外锥体的顶端为锯齿状的溢流堰,溢流堰外侧连接有溢流槽,所述溢流堰与所述第一内锥体顶端的圆筒体之间形成有清水区,所述清水区位于所述多层沉降锥板的上方,所述溢流槽开设有出水管,清水相到达多层沉降锥板上方的清水区,经过锯齿状的溢流堰流入溢流槽,由出水管排出。In one embodiment of the present invention, the top end of the first inner cone extends upwards with a cylinder, the top end of the first outer cone is a saw-toothed overflow weir, and the outside of the overflow weir is connected with an overflow A clear water area is formed between the overflow weir and the cylinder at the top of the first inner cone, the clear water area is located above the multi-layer settling cone plate, and the overflow tank is provided with an outlet In the water pipe, the clear water phase reaches the clear water area above the multi-layer settlement cone plate, flows into the overflow tank through the sawtooth overflow weir, and is discharged from the outlet pipe.
本发明的一种实施方式中,还包括机架,所述沉降分离机构通过支撑架固定在机架上;所述第二外锥体的底端设置有絮泥出口,所述絮泥出口外接有絮泥接收机构。In one embodiment of the present invention, it also includes a frame, the settling and separating mechanism is fixed on the frame through a support frame; the bottom end of the second outer cone is provided with a floc outlet, and the floc outlet is circumscribed There are floc receiving agencies.
本发明的一种实施方式中,所述第一外锥体、第二外锥体和第一内锥体均为圆锥台结构。In one embodiment of the present invention, the first outer cone, the second outer cone and the first inner cone are all truncated conical structures.
有益效果Beneficial effect
(1)本发明将通常圆筒形外壳的沉降分离机构设置为上下双锥体相互对接的外壳结构,上下双锥体外壳结构将一般的斜板或斜管沉降池中浪费的空间从沉降区域隔离出来,用于絮凝。具体地,絮凝过程发生在盘绕的螺旋盘管中,在离心力作用下发生絮凝剂与污染物的混合和絮凝,在单位占地面积和单位设备体积下,上下双锥体外壳结构相比于圆筒形外壳结构,其锥形外壳的外侧能够盘绕更多的螺旋盘管。因此,上下双锥体外壳结构能够将圆筒形外壳结构内的沉降区域中浪费的空间转化成盘绕的螺旋盘管,用于絮凝,避免了需要另外设置絮凝部分的空间,极大节约了设备空间,提高了设备的空间利用率。(1) The present invention sets the sedimentation and separation mechanism of the usual cylindrical shell as a shell structure in which the upper and lower double cones are docked with each other, and the upper and lower double cone shell structures remove the wasted space in the general inclined plate or inclined tube settling tank from the settling area Isolated and used for flocculation. Specifically, the flocculation process takes place in the coiled spiral coil, and the mixing and flocculation of flocculants and pollutants occurs under the action of centrifugal force. Under the unit floor area and unit equipment volume, the upper and lower double cone shell structures are compared with circular In the cylindrical shell structure, more helical coils can be coiled on the outside of the conical shell. Therefore, the upper and lower double-cone shell structures can convert the wasted space in the settling area in the cylindrical shell structure into coiled spiral coils for flocculation, avoiding the need to set up additional space for flocculation parts, and greatly saving equipment Space, improve the space utilization of equipment.
(2)本发明在第一外锥体与第一内锥体之间的圆锥板分离区以及第二外锥体内的絮体沉降区均设置与水流方向一致的多层沉降锥板,多层沉降锥板的若干个圆锥板形成多层喇叭状的圆锥面,为上水水流和下沉絮体都提供了更大的沉降面积。根据沉降分离的浅池理论,每增加一个圆锥面,就相应增大一倍沉降面积,增加n个圆锥面,沉降面积就增大n倍,相应的,沉降分离效率也提高大约n倍。因此多层沉降锥板极大增加了沉降面积,极大提高了絮体与水沉降分离效率,在很大程度上进一步地节约了设备空间。(2) The present invention is provided with multi-layer settling cone plates consistent with the direction of water flow in the cone-plate separation zone between the first outer cone and the first inner cone and in the floc settlement zone in the second outer cone. Several conical plates of the settling cone form a multi-layer trumpet-shaped conical surface, which provides a larger settling area for both the upper water flow and the sinking floc. According to the shallow pool theory of sedimentation separation, every time one conical surface is added, the sedimentation area will be doubled correspondingly, and if n conical surfaces are added, the sedimentation area will be increased by n times, and accordingly, the sedimentation and separation efficiency will also be increased by about n times. Therefore, the multi-layer sedimentation cone greatly increases the sedimentation area, greatly improves the sedimentation and separation efficiency of flocs and water, and further saves equipment space to a large extent.
(3)本发明在上下双锥体外壳结构中设置锥体结构的第一内锥体,絮凝过的水体进入锥体结构的第一内锥体后向下流动,第一内锥体的流通通道为流通截面积逐渐扩大的通道,根据流体流动的伯努利原理,流通截面积变大时,流速会降低,所以第一内锥体的逐渐扩大的流通面积给进水的流动提供了一个流速逐渐减小、絮体和水流的速度差逐渐变大从而更好地分离的水力条件,从而提高絮体与水的沉降分离效率;另一方面,第一内锥体外壳的倾斜角度与第一外锥体外壳的倾斜角度以及多层沉降锥板的圆锥板的倾斜角度相适配,水在第一内锥体与第一外锥体之间的空间往上流动的过程中,第一内锥体与第一外锥体之间形成的上升水流的通道面积恒定,既节约空间,又有利于水流速的稳定和水流量的平均分配,减少紊流和涡流,提高分离效率。(3) The present invention arranges the first inner cone of the cone structure in the upper and lower double cone shell structures, and the water body that is flocculated flows downward after entering the first inner cone of the cone structure, and the circulation of the first inner cone The channel is a channel with a gradually enlarged flow cross-sectional area. According to the Bernoulli principle of fluid flow, when the flow cross-sectional area becomes larger, the flow velocity will decrease, so the gradually enlarged flow area of the first inner cone provides a The flow velocity gradually decreases, and the velocity difference between flocs and water flow gradually increases to better separate the hydraulic conditions, thereby improving the sedimentation and separation efficiency of flocs and water; on the other hand, the inclination angle of the shell of the first inner cone and the second The inclination angle of the shell of an outer cone and the inclination angle of the conical plate of the multi-layer settling cone are adapted, and the first water flows upward in the space between the first inner cone and the first outer cone. The channel area of the rising water flow formed between the inner cone and the first outer cone has a constant area, which not only saves space, but also facilitates the stability of water flow rate and the average distribution of water flow, reduces turbulent flow and eddy flow, and improves separation efficiency.
(4)本发明将絮凝部分设置在上下双锥体外壳结构外侧的倾斜空间中,在盘绕的螺旋盘管中絮凝,与传统的在大体积絮凝空间中的搅拌絮凝相比,大体积空间中搅拌条件下污染物颗粒和絮凝剂的运动比较杂乱,水力停留时间不易控制,所形成的絮体的均匀性较差;而在本发明的盘管中的絮凝过程中,污染物颗粒和絮凝剂做规则的圆周运动,在离心力的作用下相互碰撞和聚结,絮体形成的速度快而且均匀,絮体形成以后在离心力的作用下逐渐移向外周,在移动过程中相互聚结成更大的矾花,所以本发明的絮凝过程更易于形成大的而且密实的絮体,与搅拌絮凝的絮体相比,本发明的大而密实的絮体沉降速度快,有利于后续的沉降分离效率的提高,进一步提高了本发明的沉降分离效率,进一步节省设备空间,从而使本发明的装置成为一种高度空间集约式水处理设备,尤其适合目前许多空间受限的工业污水和地表污水的治理。(4) The present invention arranges the flocculation part in the inclined space outside the upper and lower double-cone shell structure, and flocculates in the coiled spiral coil. Compared with the traditional stirring flocculation in the large-volume flocculation space, the large-volume space The movement of pollutant particles and flocculant is relatively messy under stirring conditions, the hydraulic retention time is not easy to control, and the uniformity of the formed flocs is relatively poor; while in the flocculation process in the coil tube of the present invention, the pollutant particles and flocculant Make a regular circular motion, collide and coalesce under the action of centrifugal force, the speed of floc formation is fast and uniform, after the flocs are formed, they gradually move to the outer periphery under the action of centrifugal force, and coalesce into larger ones during the moving process. Therefore, the flocculation process of the present invention is easier to form large and dense flocs. Compared with the flocs of stirring flocculation, the settlement speed of the large and dense flocs of the present invention is fast, which is beneficial to the subsequent sedimentation and separation efficiency. The improvement of the present invention further improves the sedimentation separation efficiency of the present invention, and further saves equipment space, thereby making the device of the present invention a highly space-intensive water treatment equipment, especially suitable for the treatment of many industrial sewage and surface sewage with limited space at present. .
(5)本发明提供的空间集约式絮凝水处理装置的体积高度集约,可以做成移动式,使用便捷,方便各种水体污染的处理,适用范围广。(5) The space-intensive flocculation water treatment device provided by the present invention has a highly intensive volume, can be made into a mobile type, is convenient to use, is convenient for the treatment of various water pollution, and has a wide range of applications.
附图说明Description of drawings
图1为本发明空间集约式絮凝水处理装置的结构示意图。Fig. 1 is a schematic structural diagram of a space-intensive flocculation water treatment device of the present invention.
图中:1、沉降分离机构;2、螺旋盘管;3、第一外锥体;4、第二外锥体;5、多层沉降锥板;6、第一内锥体;7、第二内锥体;8、溢流槽;9、出水管;10、第一絮凝剂进口;11、污水进口;12、絮泥出口;13、脚轮;14、支撑架;15、机架;16、清水区;17、溢流堰;18、第二絮凝剂进口;19、圆筒体;20、排气管;21、阀门。In the figure: 1. Sedimentation separation mechanism; 2. Spiral coil; 3. The first outer cone; 4. The second outer cone; 5. Multi-layer sedimentation cone plate; 6. The first inner cone; 7. The second 2. Inner cone; 8. Overflow tank; 9. Outlet pipe; 10. The first flocculant inlet; 11. Sewage inlet; 12. Flock outlet; 13. Casters; 14. Support frame; , clear water area; 17, overflow weir; 18, second flocculant inlet; 19, cylinder body; 20, exhaust pipe; 21, valve.
具体实施方式Detailed ways
下面将结合本发明实施例中的附图,对本发明实施例中的技术方案进行清楚、完整地描述,显然,所描述的实施例是本发明一部分实施例,而不是全部的实施例。基于本发明中的实施例,本领域普通技术人员在没有做出创造性劳动前提下所获得的所有其他实施例,都属于本发明保护的范围。The following will clearly and completely describe the technical solutions in the embodiments of the present invention with reference to the accompanying drawings in the embodiments of the present invention. Obviously, the described embodiments are some of the embodiments of the present invention, but not all of them. Based on the embodiments of the present invention, all other embodiments obtained by persons of ordinary skill in the art without making creative efforts belong to the protection scope of the present invention.
在本发明中,除非另有明确的规定和限定,术语“相连”、“连接”、“固定”应做广义理解,例如,可以是固定连接,也可以是可拆卸连接,或成一体;可以是机械连接,也可以是电连接;可以是直接相连,也可以通过中间媒介间接相连,可以是两个元件内部的连通或两个元件的相互作用关系。对于本领域的普通技术人员而言,可以具体情况理解上述术语在本发明中的具体含义。In the present invention, unless otherwise clearly specified and limited, the terms "connected", "connected" and "fixed" should be understood in a broad sense, for example, it can be a fixed connection, a detachable connection, or an integral body; It can be a mechanical connection or an electrical connection; it can be a direct connection or an indirect connection through an intermediary, it can be the internal communication of two components or the interaction relationship between two components. Those of ordinary skill in the art can understand the specific meanings of the above terms in the present invention in specific situations.
在本发明中,除非另有明确的规定和限定,第一特征在第二特征之“上”或之“下”可以包括第一和第二特征直接接触,也可以包括第一和第二特征不是直接接触而是通过它们之间的另外的特征接触。而且,第一特征在第二特征“之上”、“上方”和“上面”包括第一特征在第二特征正上方和斜上方,或仅仅表示第一特征水平高度高于第二特征。第一特征在第二特征“之下”、“下方”和“下面”包括第一特征在第二特征正下方和斜下方,或仅仅表示第一特征水平高度小于第二特征。In the present invention, unless otherwise clearly specified and limited, a first feature being "on" or "under" a second feature may include direct contact between the first and second features, and may also include the first and second features Not in direct contact but through another characteristic contact between them. Moreover, "above", "above" and "above" the first feature on the second feature include that the first feature is directly above and obliquely above the second feature, or simply means that the first feature is horizontally higher than the second feature. "Below", "beneath" and "under" the first feature to the second feature include that the first feature is directly below and obliquely below the second feature, or simply means that the first feature has a lower level than the second feature.
如图1所示,本发明提供了一种空间集约式絮凝水处理装置,包括沉降分离机构1以及盘绕在其外侧的螺旋盘管2,所述沉降分离机构1包括相互连接的第一外锥体3和第二外锥体4,所述第一外锥体3位于所述第二外锥体4的上方,所述沉降分离机构1内设置有第一内锥体6以及位于所述第一内锥体6下方的第二内锥体7,所述第一内锥体6与第一外锥体3之间设置有多层沉降锥板5;所述螺旋盘管2的一端设置有污水进口11,另一端穿设于所述第一内锥体6内,所述第一外锥体3与第一内锥体6之间为圆锥板分离区,所述圆锥板分离区的上方为清水区16,所述第二外锥体4内为絮体沉降区。As shown in Figure 1, the present invention provides a space-intensive flocculation water treatment device, which includes a sedimentation separation mechanism 1 and a spiral coil 2 coiled outside it, and the sedimentation separation mechanism 1 includes first outer cones connected to each other body 3 and a second outer cone 4, the first outer cone 3 is located above the second outer cone 4, the first inner cone 6 is arranged in the settling separation mechanism 1 and is located at the second A second inner cone 7 below the inner cone 6, a multi-layer settling cone plate 5 is arranged between the first inner cone 6 and the first outer cone 3; one end of the spiral coil 2 is provided with Sewage inlet 11, the other end of which is pierced in the first inner cone 6, between the first outer cone 3 and the first inner cone 6 is a conical plate separation area, above the conical plate separation area It is the clear water area 16, and the inside of the second outer cone 4 is the floc settlement area.
进一步地,所述第一外锥体3底端的横截面积大于其顶端的横截面积;所述第二外锥体4底端的横截面积小于其顶端的横截面积,第一外锥体3的底端与所述第二外锥体4的顶端相连;所述第一内锥体6底端的横截面积大于其顶端的横截面积,第一内锥体6位于所述第一外锥体3内。Further, the cross-sectional area of the bottom of the first outer cone 3 is greater than the cross-sectional area of its top; the cross-sectional area of the bottom of the second outer cone 4 is less than the cross-sectional area of its top, and the first outer cone The bottom end of 3 links to each other with the top of described second outer cone 4; The cross-sectional area of the bottom end of described first inner cone 6 is greater than the cross-sectional area of its top, and the first inner cone 6 is positioned at the first outer cone. Inside cone 3.
本实施例将通常圆筒形外壳的沉降分离机构设置为上下双锥体相互对接的外壳结构,上下双锥体外壳结构将一般的斜板或斜管沉降池中浪费的空间从沉降区域隔离出来,用于絮凝。具体地,絮凝过程发生在盘绕的螺旋盘管2中,污染物和絮凝剂在螺旋管道中流动,在离心力作用下发生混合、碰撞和絮凝,在单位体积下,上下双锥体外壳结构相比于圆筒形外壳结构,其锥形外壳的外侧能够盘绕更多的螺旋盘管2。因此,上下双锥体外壳结构能够将圆筒形外壳结构内的沉降区域中浪费的空间转化成盘绕的螺旋盘管2,用于絮凝,无需另外设置絮凝空间,极大节约了设备空间,提高了设备的空间利用率。此外,絮凝部分设置在上下双锥体外壳结构外侧的倾斜空间中,在盘绕的螺旋盘管2中絮凝,一方面絮凝过程发生在盘绕的螺旋盘管2中,污染物颗粒和絮凝剂在圆周运动中产生碰撞,絮体形成的速度快,而且絮体在离心力的作用下逐渐移向外周,在移动过程中相互凝结成更大的矾花,易于形成大的而且密实的絮体,这样的絮体沉降速度快,有利于后续的沉降分离效率的提高,同时节省了一般絮凝单元的空间和搅拌装置;另一方面,将絮凝过程安排在上下双锥体外壳结构的空间中,不需另外设置絮凝环节的空间,减小了设备的占地面积,节约了絮凝空间,使絮凝的时间延长,絮凝效果提高,使装置在有效完成絮凝沉降功能的前提下,空间利用率大幅提高,成为一种高度空间集约式水处理设备,尤其适合目前许多空间受限的工业污水和地表污水的治理。In this embodiment, the sedimentation and separation mechanism of the usual cylindrical shell is set as a shell structure in which the upper and lower double cones are docked with each other. The upper and lower double cone shell structures isolate the wasted space in the general inclined plate or inclined tube settling tank from the settling area. , for flocculation. Specifically, the flocculation process occurs in the coiled spiral coil 2, and the pollutants and flocculants flow in the spiral pipe, and mixing, collision and flocculation occur under the action of centrifugal force. For the cylindrical shell structure, more helical coils 2 can be coiled on the outside of the conical shell. Therefore, the upper and lower double-cone shell structures can convert the wasted space in the settling area in the cylindrical shell structure into coiled spiral coils 2 for flocculation, without additional flocculation space, which greatly saves equipment space and improves equipment space utilization. In addition, the flocculation part is set in the inclined space outside the upper and lower double-cone shell structure, and flocculates in the coiled spiral coil 2. On the one hand, the flocculation process occurs in the coiled spiral coil 2, and the pollutant particles and flocculants are in the circumference Collisions occur during the movement, and the formation of flocs is fast, and the flocs gradually move to the outer periphery under the action of centrifugal force, and condense into larger alum flowers during the moving process, which is easy to form large and dense flocs. The floc settling speed is fast, which is conducive to the improvement of the subsequent settling and separation efficiency, and saves the space of the general flocculation unit and the stirring device; on the other hand, the flocculation process is arranged in the space of the upper and lower double cone shell structures, without additional The space for the flocculation link is set, which reduces the floor area of the equipment, saves the flocculation space, prolongs the flocculation time, improves the flocculation effect, and greatly improves the space utilization rate of the device under the premise of effectively completing the flocculation and settlement function, becoming a It is a highly space-intensive water treatment equipment, especially suitable for the treatment of many industrial sewage and surface sewage with limited space.
可选地,所述多层沉降锥板5包括若干个层叠的圆锥板,所述圆锥板为圆锥台结构且上下两端贯通,若干个所述圆锥板同轴线,若干个所述圆锥板层叠以形成多层喇叭状的圆锥面。Optionally, the multi-layer settling cone plate 5 includes several stacked conical plates, the conical plate is a truncated conical structure and the upper and lower ends pass through, several of the conical plates are coaxial, and several of the conical plates Stacked to form a multi-layered trumpet-shaped conical face.
可选地,所述第一外锥体3内的多层沉降锥板5的圆锥板的倾斜角度与所述第一外锥体3以及第一内锥体6外壳的倾斜角度相适配,即第一外锥体3内的多层沉降锥板5的圆锥板的倾斜角度与第一外锥体3以及第一内锥体6外壳的倾斜角度相同或相似。Optionally, the inclination angle of the conical plate of the multi-layer settling cone plate 5 in the first outer cone 3 is adapted to the inclination angle of the shell of the first outer cone 3 and the first inner cone 6, That is, the inclination angles of the conical plates of the multi-layer settling cone plates 5 in the first outer cone 3 are the same or similar to the inclination angles of the shells of the first outer cone 3 and the first inner cone 6 .
可选地,所述第二外锥体4内也设置有多层沉降锥板5,所述第二外锥体4内的多层沉降锥板5的圆锥板的倾斜角度与所述第二外锥体4外壳的倾斜角度相适配,即第二外锥体4内的多层沉降锥板5的圆锥板的倾斜角度与第二外锥体4外壳的倾斜角度相同或相似。通过第二外锥体4内部设置的多层沉降锥板5形成多层喇叭状的圆锥面,提高絮体的沉降效率。Optionally, a multi-layer settling cone plate 5 is also arranged in the second outer cone 4, and the inclination angle of the conical plate of the multi-layer settling cone plate 5 in the second outer cone 4 is the same as that of the second The angle of inclination of the shell of the outer cone 4 is adapted, that is, the angle of inclination of the conical plate of the multi-layer settling cone plate 5 in the second outer cone 4 is the same or similar to the angle of inclination of the shell of the second outer cone 4 . The multi-layer settling cone plate 5 arranged inside the second outer cone 4 forms a multi-layer trumpet-shaped conical surface to improve the settling efficiency of flocs.
本实施例在第一外锥体3与第一内锥体6之间的圆锥板分离区以及第二外锥体4内的絮体沉降区均设置与水流方向一致的多层沉降锥板5,多层沉降锥板5的若干个圆锥板形成多层喇叭状的圆锥面,为上水水流和下沉絮体都提供了更大的沉降面积。根据沉降分离的浅池理论,每增加一个圆锥面,就相应增大一倍沉降面积,增加n个圆锥面,沉降面积就增大n倍,相应的,沉降分离效率也提高大约n倍。因此多层沉降锥板5极大增加了沉降面积,极大提高了絮体与水沉降分离效率,在很大程度上进一步地节约了设备空间。In this embodiment, the conical-plate separation zone between the first outer cone 3 and the first inner cone 6 and the floc settlement zone in the second outer cone 4 are provided with multi-layer settling cones 5 consistent with the direction of water flow. , several conical plates of the multi-layer settling cone plate 5 form a multi-layer trumpet-shaped conical surface, which provides a larger settling area for the upper water flow and the sinking floc. According to the shallow pool theory of sedimentation separation, every time one conical surface is added, the sedimentation area will be doubled correspondingly, and if n conical surfaces are added, the sedimentation area will be increased by n times, and accordingly, the sedimentation and separation efficiency will also be increased by about n times. Therefore, the multi-layer settling cone plate 5 greatly increases the settling area, greatly improves the settling and separating efficiency of flocs and water, and further saves equipment space to a large extent.
可选地,所述第一内锥体6的顶端向上延伸有圆筒体19,待絮凝的污水进入后,少量轻油脂类物质上浮至第一内锥体6顶端的圆筒体19,可以定期刮除或抽出。Optionally, a cylinder 19 extends upwards from the top of the first inner cone 6. After the flocculated sewage enters, a small amount of light oily substances float up to the cylinder 19 at the top of the first inner cone 6, which can be Scrape or pump out regularly.
可选地,所述第二内锥体7为圆锥体,其尖端朝向所述第一内锥体6底端出口的中心位置,第二内锥体7的底面位于所述第一外锥体3与第二外锥体4最大横截面处,所述第二内锥体7用于将从第一内锥体6底端流出的少量小的絮凝体以及水相横向流动分布在第一外锥体3与第二外锥体4的最大横截面处。絮凝体从第一内锥体6的底端流出后,经过第二内锥体7的圆锥面,使得水相及少量小的絮凝体横向流动,分布在第一外锥体3与第二外锥体4最大横截面处以后轻柔地流动,而不会产生剧烈的冲击和扰动,降低分离效果。Optionally, the second inner cone 7 is a cone, its tip is towards the center of the outlet at the bottom end of the first inner cone 6, and the bottom surface of the second inner cone 7 is located at the first outer cone 3 and the maximum cross-section of the second outer cone 4, the second inner cone 7 is used to distribute a small amount of small flocs flowing out from the bottom of the first inner cone 6 and the lateral flow of the water phase in the first outer The largest cross section of the cone 3 and the second outer cone 4. After the flocs flow out from the bottom of the first inner cone 6, they pass through the conical surface of the second inner cone 7, causing the water phase and a small amount of small flocs to flow laterally and distribute between the first outer cone 3 and the second outer cone. The largest cross-section of the cone 4 flows softly afterwards, without violent impact and disturbance, which reduces the separation effect.
本实施例在上下双锥体外壳结构中设置锥体结构的第一内锥体6,第一内锥体6作为进水管,絮凝过的水体进入锥体结构的第一内锥体6,一方面利用了第一内锥体6内的倾斜部分,形成一个流通截面积逐渐扩大的流通通道,使水流速逐渐减小,给进水的流动提供一个流速逐渐减小、絮体和水流的速度差逐渐变大从而更好地分离的水力条件,从而提高絮体与水的沉降分离效率;另一方面,第一内锥体6外壳的倾斜角度与第一外锥体3外壳的倾斜角度相适配,水在上流的过程中,第一内锥体6与第一外锥体3之间形成的上升水流的通道面积恒定,既节约空间,又有利于水流速的稳定和水流量的平均分配,减少紊流和涡流,提高分离效率。In this embodiment, the first inner cone 6 of the cone structure is set in the upper and lower double cone shell structure, and the first inner cone 6 is used as the water inlet pipe, and the flocculated water enters the first inner cone 6 of the cone structure, and a On the one hand, the inclined part in the first inner cone 6 is used to form a flow channel with a gradually enlarged flow cross-sectional area, so that the water flow rate gradually decreases, and a flow rate is gradually reduced, and the speed of flocs and water flow is provided for the flow of influent water. The difference gradually becomes larger so as to better separate the hydraulic conditions, thereby improving the sedimentation and separation efficiency of flocs and water; Adaptation, during the process of water flowing upwards, the channel area of the rising water formed between the first inner cone 6 and the first outer cone 3 is constant, which not only saves space, but also facilitates the stability of the water flow rate and the average of the water flow Distribution, reduce turbulence and eddy current, improve separation efficiency.
可选地,所述螺旋盘管2上设置有第一絮凝剂进口10和第二絮凝剂进口18,通过第一絮凝剂进口10和第二絮凝剂进口18向螺旋盘管2内加入絮凝剂和混凝剂。Optionally, the spiral coil 2 is provided with a first flocculant inlet 10 and a second flocculant inlet 18, and the flocculant is added into the spiral coil 2 through the first flocculant inlet 10 and the second flocculant inlet 18 and coagulant.
可选地,所述螺旋盘管2还连接有排气管20,所述排气管20用于排出螺旋盘管2内污水流动过程中的聚集气体,所述排气管20上设置有阀门21。优选地,所述排气管20连接于螺旋盘管2最高处的上方。Optionally, the spiral coil 2 is also connected with an exhaust pipe 20, the exhaust pipe 20 is used to discharge the accumulated gas during the sewage flow in the spiral coil 2, and the exhaust pipe 20 is provided with a valve twenty one. Preferably, the exhaust pipe 20 is connected above the highest point of the spiral coil pipe 2 .
可选地,所述第一外锥体3的顶端为锯齿状的溢流堰17,所述溢流堰17外侧连接有溢流槽8,所述溢流堰17与所述第一内锥体6顶端的圆筒体19之间形成有清水区16,所述清水区16位于所述多层沉降锥板5的上方,所述溢流槽8开设有出水管9,清水相到达多层沉降锥板5上方的清水区16,经过锯齿状的溢流堰17流入溢流槽8,由出水管9排出。Optionally, the top end of the first outer cone 3 is a saw-toothed overflow weir 17, and an overflow groove 8 is connected to the outside of the overflow weir 17, and the overflow weir 17 and the first inner cone A clear water zone 16 is formed between the cylinders 19 at the top of the body 6, the clear water zone 16 is located above the multi-layer settling cone plate 5, the overflow tank 8 is provided with an outlet pipe 9, and the clear water phase reaches the multi-layer The clear water area 16 above the settling cone plate 5 flows into the overflow tank 8 through the sawtooth overflow weir 17 and is discharged by the outlet pipe 9 .
可选地,还包括机架15,所述沉降分离机构1通过支撑架14固定在机架15上,所述底架15的底端设置有脚轮13;所述第二外锥体4的底端设置有絮泥出口12,所述絮泥出口12外接有絮泥接收机构,絮泥接收机构用于接收从絮泥出口12出来的絮泥。本发明提供的空间集约式絮凝水处理装置的体积高度集约,可以做成移动式,使用便捷,方便各种水体污染的处理,适用范围广。Optionally, a frame 15 is also included, the settling separation mechanism 1 is fixed on the frame 15 through a support frame 14, and casters 13 are provided at the bottom end of the bottom frame 15; the bottom of the second outer cone 4 A floc outlet 12 is provided at the end, and a floc receiving mechanism is externally connected to the floc outlet 12, and the floc receiving mechanism is used to receive the floc coming out of the floc outlet 12. The space-intensive flocculation water treatment device provided by the present invention has a highly compact volume, can be made into a mobile type, is convenient to use, facilitates the treatment of various water body pollutions, and has a wide application range.
可选地,所述第一外锥体3、第二外锥体4和第一内锥体6均为圆锥台结构,圆锥台结构的锥角可以根据实际需求进行修改,本发明对此不做具体限定。Optionally, the first outer cone 3, the second outer cone 4 and the first inner cone 6 are all truncated conical structures, and the cone angle of the truncated conical structure can be modified according to actual needs, which is not covered by the present invention. Be specific.
本发明将待处理污水从螺旋盘管2的污水进口11进入,第二外锥体4外侧盘绕的螺旋盘管2的上端通过直管(图中未示出)与第一外锥体3外侧盘绕的螺旋盘管2的上端相连,污水依次经过污水进口11、第二外锥体4外侧盘绕的螺旋盘管2的上端、第一外锥体3外侧盘绕的螺旋盘管2的上端,从第一外锥体3外侧盘绕的螺旋盘管2的下端流向第一内锥体6内。在第一絮凝剂进口10、第二絮凝剂进口18处加入絮凝剂和混凝剂,在螺旋盘管2内进行螺旋混合,优选的,可以装入静态混合器,污水在螺旋盘管2中絮凝,然后进入沉降分离机构1的第一内锥体6内。絮凝的污水进入后,少量轻油脂类物质上浮至第一内锥体6上部的圆筒体19,可以定期刮除或抽出,其余絮凝体随水流往下流动。随着第一内锥体6的横截面积变大,水流速减缓,絮凝体的沉降速度与水流速的差值增大,从而使絮凝体更好地与水体沉降分离,至第一内锥体6底部的出口流出第一内锥体6后,经过第二内锥体7的圆锥面,大的絮体沿第二内锥体的圆锥面下滑并沉降,水相及少量中等及小的絮凝体横向流动,分布在第一外锥体3与第二外锥体4最大横截面处,中等的絮体往下沉降,而水相及少量小的絮体向上流动,流经多层沉降锥板5的若干个圆锥板形成的多层喇叭状的圆锥面,其中多层圆锥面起到多层锥板沉降的作用,增大细小絮凝体的沉降分离效率。清水相到达多层沉降锥板5上方的清水区16,经过锯齿状的溢流堰17流入溢流槽8,由出水管9排出;多层圆锥面汇集的絮体下滑至第一外锥体3与第二外锥体4最大横截面处,沉入第二外锥体4,与第一内锥体6出来的大的絮凝颗粒一起逐渐沉降至第二外锥体4底部的絮泥出口12,定期排出。依实际工艺要求,所述第二外锥体4内部也可以设置多层沉降锥板5以形成多层喇叭状的圆锥面,进一步提高沉降效率。The present invention enters the sewage to be treated from the sewage inlet 11 of the spiral coil 2, and the upper end of the spiral coil 2 coiled outside the second outer cone 4 passes through a straight pipe (not shown in the figure) and the outside of the first outer cone 3 The upper end of the coiled spiral coil 2 is connected, and the sewage passes through the sewage inlet 11, the upper end of the spiral coil 2 coiled outside the second outer cone 4, and the upper end of the spiral coil 2 coiled outside the first outer cone 3, from The lower end of the spiral coil pipe 2 coiled outside the first outer cone 3 flows into the first inner cone 6 . Add flocculant and coagulant at the first flocculant inlet 10 and the second flocculant inlet 18, and perform spiral mixing in the spiral coil 2, preferably, it can be loaded into a static mixer, and the sewage is in the spiral coil 2 Flocculate, and then enter the first inner cone 6 of the settling separation mechanism 1 . After the flocculated sewage enters, a small amount of light oily matter floats up to the cylinder 19 on the top of the first inner cone 6, and can be scraped off or drawn out regularly, and the rest of the flocs flow down with the water flow. As the cross-sectional area of the first inner cone 6 becomes larger, the water flow rate slows down, and the difference between the settling velocity of the flocs and the flow rate of the water increases, so that the flocs are better separated from the settlement of the water body. After the outlet at the bottom of the body 6 flows out of the first inner cone 6, it passes through the conical surface of the second inner cone 7, and the large flocs slide down and settle down along the conical surface of the second inner cone, and the water phase and a small amount of medium and small The flocs flow laterally and are distributed at the largest cross section of the first outer cone 3 and the second outer cone 4. The medium flocs settle down, while the water phase and a small amount of small flocs flow upwards and pass through multi-layer sedimentation. The multi-layer trumpet-shaped conical surface formed by several conical plates of the cone plate 5, wherein the multi-layered conical surface plays the role of multi-layered cone-plate settlement, increasing the settlement and separation efficiency of fine flocs. The clear water phase reaches the clear water area 16 above the multi-layer settling cone plate 5, flows into the overflow tank 8 through the saw-toothed overflow weir 17, and is discharged from the outlet pipe 9; the floc collected on the multi-layer conical surface slides down to the first outer cone 3 and the largest cross-section of the second outer cone 4, sink into the second outer cone 4, and gradually settle to the floc outlet at the bottom of the second outer cone 4 together with the large floc particles from the first inner cone 6 12. Discharge regularly. According to actual technological requirements, multiple layers of settling cone plates 5 can also be arranged inside the second outer cone 4 to form a multi-layered trumpet-shaped conical surface to further improve the settling efficiency.
本发明可以大幅度地提高设备的空间利用率,其单位设备体积的污水处理量更高,其可以快速形成较大且密实的絮凝体,絮凝体与水体的密度差大、分离速度高,从而使分离效率提高,水力停留时间较传统絮凝装置降低50%以上,较大地提高了絮凝处理速度和效率,减少了设备体积,适合于污水处理厂、污水处理车间或者地表污染水体的污水处理,节约空间,提高效率,尤其适用于空间受限的污水处理工程。The present invention can greatly improve the space utilization rate of the equipment, the sewage treatment capacity per unit volume of the equipment is higher, and it can quickly form larger and dense flocs, the density difference between the flocs and the water body is large, and the separation speed is high, so that The separation efficiency is improved, the hydraulic retention time is reduced by more than 50% compared with the traditional flocculation device, the flocculation treatment speed and efficiency are greatly improved, and the equipment volume is reduced. Space, improve efficiency, especially suitable for sewage treatment projects with limited space.
尽管参照前述实施例对本发明进行了详细的说明,对于本领域的技术人员来说,其依然可以对前述各实施例所记载的技术方案进行修改,或者对其中部分技术特征进行等同更换,凡在本发明的精神和原则之内,所做的任何修改,等同替换,改进等,均应包含在本发明的保护范围之内。Although the present invention has been described in detail with reference to the aforementioned embodiments, those skilled in the art can still modify the technical solutions described in the aforementioned embodiments, or perform equivalent replacements for some of the technical features. Within the spirit and principles of the present invention, any modifications, equivalent replacements, improvements, etc., shall be included within the protection scope of the present invention.
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Cited By (1)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| CN119080186A (en) * | 2024-11-04 | 2024-12-06 | 伊金霍洛旗上善蒙苏园区供水有限责任公司 | A space-intensive flocculation water treatment device |
Citations (7)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| CN201024108Y (en) * | 2006-12-25 | 2008-02-20 | 苏思 | Pretreatment device for sewage reutilization |
| CN108203148A (en) * | 2018-02-09 | 2018-06-26 | 重庆大雨水生态科技有限公司 | A kind of flocculation sedimentation system and sewage disposal system |
| CN108773933A (en) * | 2018-06-27 | 2018-11-09 | 韩先云 | A kind of integrated sewage treating apparatus |
| CN108946890A (en) * | 2018-06-11 | 2018-12-07 | 马鞍山市天工科技股份有限公司 | A kind of sewage disposal system integrating purification with concentration |
| CN208327488U (en) * | 2018-04-03 | 2019-01-04 | 重庆市环境保护工程设计研究院有限公司 | A kind of coiled coagulative precipitation device |
| CN115710043A (en) * | 2022-11-28 | 2023-02-24 | 北矿机电科技有限责任公司 | Be applied to water treatment's sediment device |
| CN219689458U (en) * | 2023-04-23 | 2023-09-15 | 宜兴市润江水处理科技有限公司 | High-efficient flocculation water treatment facilities |
-
2023
- 2023-04-23 CN CN202310441856.1A patent/CN116621298B/en active Active
Patent Citations (7)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| CN201024108Y (en) * | 2006-12-25 | 2008-02-20 | 苏思 | Pretreatment device for sewage reutilization |
| CN108203148A (en) * | 2018-02-09 | 2018-06-26 | 重庆大雨水生态科技有限公司 | A kind of flocculation sedimentation system and sewage disposal system |
| CN208327488U (en) * | 2018-04-03 | 2019-01-04 | 重庆市环境保护工程设计研究院有限公司 | A kind of coiled coagulative precipitation device |
| CN108946890A (en) * | 2018-06-11 | 2018-12-07 | 马鞍山市天工科技股份有限公司 | A kind of sewage disposal system integrating purification with concentration |
| CN108773933A (en) * | 2018-06-27 | 2018-11-09 | 韩先云 | A kind of integrated sewage treating apparatus |
| CN115710043A (en) * | 2022-11-28 | 2023-02-24 | 北矿机电科技有限责任公司 | Be applied to water treatment's sediment device |
| CN219689458U (en) * | 2023-04-23 | 2023-09-15 | 宜兴市润江水处理科技有限公司 | High-efficient flocculation water treatment facilities |
Cited By (2)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| CN119080186A (en) * | 2024-11-04 | 2024-12-06 | 伊金霍洛旗上善蒙苏园区供水有限责任公司 | A space-intensive flocculation water treatment device |
| CN119080186B (en) * | 2024-11-04 | 2025-01-14 | 伊金霍洛旗上善蒙苏园区供水有限责任公司 | Space intensive flocculation water treatment device |
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