Integrated water supply treatment device

By constructing a coagulation sedimentation tank, a filter tank, an ozone contact tank, and an activated carbon adsorption tank, combined with inclined tube sedimentation and mechanical flocculation, the problems of large land area and high operating costs of rural surface water treatment devices have been solved, achieving efficient and low-cost water quality improvement.

CN224578149UActive Publication Date: 2026-07-31CHINA POWER CONSTR GRP ARCHITECTURAL PLANNING & DESIGN INST CO LTD +1
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Patent Information

Authority / Receiving Office
CN · China
Patent Type
Utility models(China)
Current Assignee / Owner
CHINA POWER CONSTR GRP ARCHITECTURAL PLANNING & DESIGN INST CO LTD
Filing Date
2025-07-31
Publication Date
2026-07-31

AI Technical Summary

Technical Problem

In rural areas, surface water quality is unstable. Conventional integrated treatment devices occupy a large area, have high operating costs, and are difficult to cope with changes in water volume. Existing devices are prone to clogging and have complex operation and management.

Method used

The system combines coagulation sedimentation tanks, filters, ozone contact tanks, activated carbon adsorption tanks, and supporting facilities, all sharing common tank walls. It integrates inclined tube sedimentation, mechanical flocculation, ozone contact, and activated carbon adsorption technologies, reduces head loss through channel connections, and incorporates overpass gates for flexible process flow adjustment.

Benefits of technology

It reduces the footprint, lowers operating costs, improves effluent quality, simplifies management, adapts to changes in water volume, and ensures that the effluent meets drinking water standards.

✦ Generated by Eureka AI based on patent content.

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Abstract

This utility model provides an integrated water treatment device, comprising a coagulation sedimentation tank, a filter, an ozone contact tank, an activated carbon adsorption tank, a combined pump room, and a backwash fan room. The coagulation sedimentation tank, filter, activated carbon adsorption tank, ozone contact tank, combined pump room, and backwash fan room are constructed together, sharing common tank walls. The filter and activated carbon adsorption tank share a common integrated pipe gallery, reducing the footprint. An bypass gate is installed between the filter effluent and the activated carbon adsorption tank effluent channel, bypassing the ozone contact tank and activated carbon adsorption tank, reducing operating costs. This utility model employs mechanical mixing and mechanical flocculation, increasing the depth of treatment processes, and the combined construction of structures saves land, reduces operating costs, and improves effluent quality.
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Description

Technical Field

[0001] This utility model belongs to the field of water supply treatment technology, specifically relating to an integrated water supply treatment device. Background Technology

[0002] In most rural areas, self-supplied wells are used as drinking water sources, which are then consumed directly without treatment. However, with societal progress, users have increasingly higher demands for water quality. Furthermore, excessive groundwater extraction has led to problems such as land subsidence and reduced groundwater resources. Currently, many areas are replacing groundwater sources with surface water. Because the original self-supplied wells were scattered and difficult to operate and manage, after replacing groundwater with surface water, an integrated water treatment system needs to be installed to centrally supply water to each village.

[0003] Surface water sources are characterized by high turbidity, high levels of organic pollutants, and occasional high algae content during the rainy season. Treatment processes must address the influent issue to ensure effluent meets drinking water standards. Considering the limited land and technical management capabilities in rural areas, a small-footprint, easily managed treatment device is required. Conventional small-scale integrated treatment devices used in rural areas employ conventional coagulation, sedimentation, and filtration processes, using tubular static mixers for mixing. However, tubular static mixers suffer from significant head losses and are unsuitable for water plants with large water volume fluctuations. Grid flocculation tanks are used, but during summer algae blooms, these tanks are prone to algae growth and mesh clogging, leading to cumbersome operation and increased operating costs. Given the significant seasonal variations in surface water quality and the large fluctuations in water consumption in rural areas, there is an urgent need to develop a small-scale integrated treatment device for surface water sources that requires minimal space and produces high-quality effluent. Utility Model Content

[0004] Based on the above-mentioned problems, this utility model provides an integrated water treatment device that can effectively solve problems such as poor operation, poor water output, and high operating costs.

[0005] The technical solution adopted by this utility model is as follows: An integrated water treatment device includes a coagulation sedimentation tank, a filter tank, an ozone contact tank, an activated carbon adsorption tank, a comprehensive pump room, and a backwash fan room. The coagulation sedimentation tank, filter tank, activated carbon adsorption tank, ozone contact tank, comprehensive pump room, and backwash fan room are built together and share the same tank wall.

[0006] Furthermore, the coagulation sedimentation tank connected to the inlet pipe is an inclined tube sedimentation tank. The effluent channel of the coagulation sedimentation tank is embedded in the coagulation sedimentation tank. The width of the coagulation sedimentation tank is consistent with the total width of the filter, activated carbon adsorption tank and supporting integrated pipe gallery. The filter, activated carbon adsorption tank and integrated pipe gallery are located outside the effluent channel of the coagulation sedimentation tank and share the tank wall with the effluent channel of the coagulation sedimentation tank. The effluent channel of the coagulation sedimentation tank is connected to the inlet channel of the filter through holes.

[0007] Furthermore, the filter tank and the activated carbon adsorption tank have the same bottom plate elevation and width, and share the same central integrated pipe gallery.

[0008] Furthermore, the integrated pump house shares pool walls with the filter, activated carbon adsorption tank, and integrated pipe gallery. The filter effluent channel and the activated carbon adsorption tank effluent channel are vertically arranged side by side in the integrated pump house, with a filter effluent overflow gate in the middle. An effluent pipe connected to the clear water tank is installed on the activated carbon adsorption tank effluent channel. The integrated pump house is equipped with an intermediate lift pump connecting the filter effluent channel and the ozone contact tank, a filter backwash pump connecting the filter effluent channel and the filter, and an activated carbon adsorption tank backwash pump connecting the activated carbon adsorption tank effluent channel and the activated carbon adsorption tank.

[0009] Furthermore, the outlet pipe of the ozone contact tank is connected to the activated carbon adsorption tank.

[0010] Furthermore, the backwashing blower room is jointly constructed with the integrated pump room and the ozone contact tank, sharing the same tank wall; the backwashing blower room is equipped with a filter backwashing blower and an activated carbon adsorption tank backwashing blower; the filter backwashing blower is connected to the filter through a filter backwashing air pipe, and the activated carbon adsorption tank backwashing blower is connected to the activated carbon adsorption tank through an activated carbon adsorption tank backwashing air pipe. The bottom elevation of the filter backwashing air pipe is more than 50cm higher than the highest water level of the filter, and the bottom elevation of the activated carbon adsorption tank backwashing air pipe is more than 50cm higher than the highest water level of the activated carbon adsorption tank.

[0011] Furthermore, the filter backwash water pump is connected to the filter via a filter backwash water pipe, and the activated carbon adsorption tank backwash water pump is connected to the activated carbon adsorption tank via an activated carbon adsorption tank backwash water pipe.

[0012] Furthermore, the filter backwashing air pipe, the activated carbon adsorption tank backwashing air pipe, the filter backwashing water pipe, and the activated carbon adsorption tank backwashing water pipe are installed in the integrated pipe gallery.

[0013] Furthermore, the filter beds are arranged in four groups, and the filter media is uniformly sized quartz sand with a particle size range of 0.9-1.2 mm and a non-uniformity coefficient K. 60 ≤1.6; Four sets of activated carbon adsorption tanks are arranged, and the filter media is briquette crushed carbon with a particle size range of 1.2-1.3mm and a filter media layer height of 2m.

[0014] This utility model has the following advantages:

[0015] 1. The water treatment structures, including coagulation sedimentation tanks, filter tanks, ozone contact tanks, activated carbon adsorption tanks, and supporting integrated pump rooms and backwash fan rooms, are constructed in a combined manner, sharing tank walls to reduce the footprint. Integrated equipment can be used, which reduces the difficulty of construction.

[0016] 2. The water treatment structure includes an ozone contact tank and an activated carbon adsorption tank for advanced treatment. The activated carbon adsorption tank removes low-molecular-weight organic matter generated by ozone oxidation. Activated carbon can also adsorb dissolved organic matter, effectively removing organic pollutants from surface water sources, reducing the total amount of organic matter, and ensuring the quality of effluent.

[0017] 3. An overpass gate is installed between the effluent channel of the filter bed and the effluent channel of the activated carbon adsorption tank. When the surface water quality is good, the overpass gate can be opened to stop the operation of the ozone contact tank and the activated carbon adsorption tank, thereby reducing operating costs. Attached Figure Description

[0018] Figure 1 This utility model provides an integrated water treatment device.

[0019] Figure 2 for Figure 1 Cross-sectional view of the integrated water treatment unit AA.

[0020] In the diagram, 1-coagulation sedimentation tank, 2-filter, 3-ozone oxidation tank, 4-activated carbon adsorption tank, 5-coagulation sedimentation tank effluent channel, 6-filter effluent channel, 7-intermediate lift pump, 8-ozone contact tank effluent pipe, 9-activated carbon adsorption tank effluent channel, 10-integrated pump room, 11-filter effluent bypass gate, 12-backwash blower room, 13-integrated pipe gallery, 14-filter backwash water pump, 15-activated carbon adsorption tank backwash water pump, 16-filter backwash water pipe, 17-activated carbon adsorption tank backwash water pipe, 18-filter backwash blower, 19-activated carbon adsorption tank backwash blower, 20-filter backwash water pipe, 21-activated carbon adsorption tank backwash water pipe. Detailed Implementation

[0021] To make the objectives, technical solutions, and advantages of this utility model clearer, the following detailed description is provided in conjunction with embodiments. It should be understood that the specific embodiments described herein are merely illustrative and not intended to limit the scope of this utility model.

[0022] In the description of this utility model, it should be understood that the terms "center", "longitudinal", "lateral", "upper", "lower", "front", "rear", "left", "right", "vertical", "horizontal", "top", "bottom", "inner", and "outer" indicate the orientation or positional relationship based on the orientation or positional relationship shown in the accompanying drawings. They are only for the convenience of describing this utility model and simplifying the description, and do not indicate or imply that the device or element referred to must have a specific orientation, or be constructed and operated in a specific orientation. Therefore, they should not be construed as limitations on this utility model.

[0023] In the description of this utility model, it should be noted that, unless otherwise explicitly specified and limited, the terms "installation," "connection," and "joining" should be interpreted broadly. For example, they can refer to a fixed connection, a detachable connection, or an integral connection; they can refer to a mechanical connection or an electrical connection; they can refer to a direct connection or an indirect connection through an intermediate medium; and they can refer to the internal connection of two components. Those skilled in the art can understand the specific meaning of the above terms in this utility model based on the specific circumstances.

[0024] like Figure 1 , 2 As shown, the integrated water treatment device of this utility model includes a coagulation sedimentation tank 1, a filter tank 2, an ozone contact tank 3, an activated carbon adsorption tank 4, a comprehensive pump room 10, and a backwash fan room 12. The coagulation sedimentation tank 1, the filter tank 2, the activated carbon adsorption tank 4, the ozone contact tank 3, the comprehensive pump room 10, and the backwash fan room 12 are built together and share the same tank wall.

[0025] Specifically, the coagulation sedimentation tank connected to the inlet pipe is an inclined tube sedimentation tank. The coagulation sedimentation tank outlet channel 5 is embedded in the coagulation sedimentation tank 1. The width of the coagulation sedimentation tank is consistent with the total width of the filter tank 2, the activated carbon adsorption tank 4 and the supporting integrated pipe gallery 13. The filter tank 2, the activated carbon adsorption tank 4 and the integrated pipe gallery 13 are located outside the coagulation sedimentation tank outlet channel 5 and share the tank wall with the coagulation sedimentation tank outlet channel 5. The coagulation sedimentation tank outlet channel 5 is connected to the filter tank 2 inlet channel through holes.

[0026] Preferably, the bottom plate of the filter tank 2 and the activated carbon adsorption tank 4 have the same elevation and width, and they share the same central integrated pipe gallery 13.

[0027] The integrated pump house 10 shares a pool wall with the filter pool 2, the activated carbon adsorption pool 4, and the integrated pipe gallery 13. The filter pool outlet channel 6 and the activated carbon adsorption pool outlet channel 9 are vertically arranged side by side in the integrated pump house 10, with a filter pool outlet overflow gate 11 in the middle. The activated carbon adsorption pool outlet channel 9 is equipped with an outlet pipe connected to the clear water pool. The integrated pump house 10 is equipped with an intermediate lift pump 7 connecting the filter pool outlet channel 6 and the ozone contact pool 3, a filter pool backwash water pump 14 connecting the filter pool outlet channel 6 and the filter pool 2, and an activated carbon adsorption pool backwash water pump 15 connecting the activated carbon adsorption pool outlet channel 9 and the activated carbon adsorption pool 4.

[0028] The outlet pipe 8 of the ozone contact tank is connected to the activated carbon adsorption tank 4.

[0029] The backwash blower room 12 is jointly constructed with the integrated pump room 10 and the ozone contact tank 3, sharing the same tank wall. The backwash blower room 12 is equipped with a filter backwash blower 18 and an activated carbon adsorption tank backwash blower 19. The filter backwash blower 18 is connected to the filter 2 through the filter backwash air pipe 20, and the activated carbon adsorption tank backwash blower 19 is connected to the activated carbon adsorption tank 4 through the activated carbon adsorption tank backwash air pipe 21. The bottom elevation of the filter backwash air pipe 20 is more than 50cm higher than the highest water level of the filter 2, and the bottom elevation of the activated carbon adsorption tank backwash air pipe 21 is more than 50cm higher than the highest water level of the activated carbon adsorption tank 4.

[0030] The filter backwash water pump 14 is connected to the filter 2 via the filter backwash water pipe 16, and the activated carbon adsorption tank backwash water pump 15 is connected to the activated carbon adsorption tank 4 via the activated carbon adsorption tank backwash water pipe 17.

[0031] Preferably, the filter backwashing air pipe 20, the activated carbon adsorption tank backwashing air pipe 21, the filter backwashing water pipe 16, and the activated carbon adsorption tank backwashing water pipe 17 are installed in the integrated pipe gallery 13.

[0032] Preferably, the filter tanks 2 are arranged in 4 groups, and the filter media is uniformly sized quartz sand with a particle size range of 0.9-1.2 mm and a non-uniformity coefficient K. 60 ≤1.6; 4 sets of activated carbon adsorption tanks are arranged, and the filter media is briquette crushed carbon with a particle size range of 1.2-1.3mm and a filter media layer height of 2m.

[0033] Specifically, the coagulation sedimentation tank mainly removes suspended solids and colloidal substances, reduces turbidity, removes some organic matter and phosphorus, and creates favorable conditions for subsequent treatment units. Considering the changes in water consumption by residential users and the rationality of the layout, the coagulation sedimentation tank is designed in four groups, with the total width of the coagulation sedimentation tank being close to the width of the filter and activated carbon adsorption tank. Mechanical mixing is used, with a mixing agitator and a mixing time of 60 seconds; mechanical flocculation is used, with a flocculation agitator and a flocculation time of 20 minutes. The mixing tank, flocculation tank, and inclined tube sedimentation tank are combined to form the coagulation sedimentation tank. Raw water enters the mixing tank of coagulation sedimentation tank 1 through the inlet pipe. Coagulation sedimentation tank 1 and filter 2 enter filter 2 through the sedimentation tank outlet channel 5, which is embedded inside the coagulation sedimentation tank. The outer partition wall serves as the side wall for the filter and activated carbon adsorption tank.

[0034] The filter tank 2 is configured with 4 groups, and the filter media is uniformly sized quartz sand with a particle size range of 0.9-1.2 mm and a non-uniformity coefficient K. 60≤1.6. Filter tank 2 and activated carbon adsorption tank 4 are arranged symmetrically, with the bottom plate at the same elevation as activated carbon adsorption tank 4. Between filter tank 2 and activated carbon adsorption tank 4 is a comprehensive pipe gallery 13, which houses filter tank backwash water pipe 16, activated carbon adsorption tank backwash water pipe 17, filter tank backwash air pipe 20, activated carbon adsorption tank backwasher pipe 21, and maintenance platform. Filter tank backwash water pipe 16 and activated carbon adsorption tank backwash water pipe 17 are located below the maintenance platform.

[0035] The activated carbon adsorption tank 4 is configured with 4 sets of filter media, using briquetted crushed carbon with a particle size range of 1.2-1.3 mm and a filter media layer height of 2 m. The bottom plate is at the same elevation as filter tank 2, and the total width is consistent with filter tank 2. The ozone contact tank effluent pipe 8 is connected to the activated carbon adsorption tank 4.

[0036] The integrated pump station serves as an auxiliary facility for filter tank 2 and activated carbon adsorption tank 4, and includes filter tank outlet channel 6, activated carbon adsorption tank outlet channel 9, backwash water pump 7, and pipelines. Filter tank outlet channel 6 is used as a backwash water tank, and the filter tank outlet channel 6 and activated carbon adsorption tank outlet channel 9 share the same tank wall, with a filter tank outlet bypass gate 11 installed in between.

[0037] The ozone contact tank 3 includes an aeration disc, a tail gas destruction device, a demister, and other devices. The ozone contact time is 20 minutes, and the ozone dosage is 2 mg / L. The ozone contact tank outlet pipe 8 is connected to the activated carbon adsorption tank via a stainless steel pipe.

[0038] The integrated water treatment device includes backwashing facilities for the filter tank 2 and the activated carbon adsorption tank 4. These backwashing facilities are located within a comprehensive pump house 13, which shares a wall with the filter tank 2 and the activated carbon adsorption tank 4, reducing pipeline length. The comprehensive pump house includes a filter effluent tank 6, an activated carbon adsorption tank effluent tank 9, a filter backwashing pump 14, an activated carbon adsorption tank backwashing pump 15, and an intermediate lift pump 7. An bypass gate 11 is installed between the filter effluent channel and the activated carbon adsorption tank effluent channel. Based on the influent and effluent water quality requirements, it is determined whether to operate the deep treatment structures. If the influent water quality is excellent and the concentration of organic pollutants is low, the intermediate lift pump 7, the ozone contact tank 3, and the activated carbon adsorption tank 4 are stopped, and the bypass gate 11 is opened, allowing the water to be discharged into the clear water tank through the effluent channel 9.

[0039] The integrated water treatment device includes a backwash blower for the filter tank and activated carbon adsorption tank. The backwash blower is installed in the backwash blower room 12. According to the layout height and size requirements of the integrated device, it is built together with the integrated pump room and the ozone contact tank, sharing the tank wall.

[0040] This utility model integrates a coagulation sedimentation tank, a filter, an ozone contact tank, and an activated carbon filter into a single treatment unit. The connection between these structures, previously via pipes, has been replaced with a channel connection, minimizing head loss and saving energy. The coagulation sedimentation tank in this integrated unit effectively removes suspended solids such as algae, employing mechanical flocculation to reduce operational complexity. The integrated water treatment unit includes advanced treatment structures such as an ozone contact tank and an activated carbon adsorption tank, reducing organic matter and ensuring effluent quality. Furthermore, the use of bypass gates allows for flexible adjustment of the process flow based on influent and effluent quality requirements, saving on operating costs.

[0041] The above description is only a preferred embodiment of the present utility model and is not intended to limit the present utility model. Any modifications, equivalent substitutions and improvements made within the spirit and principles of the present utility model should be included within the protection scope of the present utility model.

Claims

1. An integrated water treatment device, comprising a coagulation sedimentation tank (1), a filter tank (2), an ozone contact tank (3), an activated carbon adsorption tank (4), a comprehensive pump station (10), and a backwash fan room (12), characterized in that, The coagulation sedimentation tank (1), filter tank (2), activated carbon adsorption tank (4), ozone contact tank (3), integrated pump room (10), and backwash blower room (12) are built together and share the tank walls; The coagulation sedimentation tank connected to the inlet pipe is an inclined tube sedimentation tank. The coagulation sedimentation tank outlet channel (5) is embedded in the coagulation sedimentation tank (1). The width of the coagulation sedimentation tank is consistent with the total width of the filter (2), the activated carbon adsorption tank (4) and the supporting integrated pipe gallery (13). The filter (2), the activated carbon adsorption tank (4) and the integrated pipe gallery (13) are located outside the coagulation sedimentation tank outlet channel (5) and share the tank wall with the coagulation sedimentation tank outlet channel (5). The coagulation sedimentation tank outlet channel (5) is connected to the filter (2) inlet channel through holes. The bottom plate of the filter (2) and the activated carbon adsorption tank (4) have the same elevation and width, and share the middle part of the integrated pipe gallery (13). The integrated pump house (10) shares the pool wall with the filter (2), activated carbon adsorption pool (4) and integrated pipe gallery (13). The filter effluent channel (6) and the activated carbon adsorption pool effluent channel (9) are vertically arranged side by side in the integrated pump house (10). The filter effluent overflow gate (11) is set in the middle. The activated carbon adsorption pool effluent channel (9) is equipped with an effluent pipe connected to the clear water pool. The integrated pump house (10) is equipped with an intermediate lift pump (7) connecting the filter effluent channel (6) and the ozone contact pool (3), a filter backwash pump (14) connecting the filter effluent channel (6) and the filter (2), and an activated carbon adsorption pool backwash pump (15) connecting the activated carbon adsorption pool effluent channel (9) and the activated carbon adsorption pool (4).

2. The integrated water treatment device according to claim 1, wherein The outlet pipe (8) of the ozone contact tank is connected to the activated carbon adsorption tank (4).

3. The integrated water treatment device of claim 1, wherein The backwash blower room (12) is built together with the integrated pump room (10) and the ozone contact pool (3), sharing the pool wall. The backwash blower room (12) is equipped with a filter backwash blower (18) and an activated carbon adsorption pool backwash blower (19). The filter backwash blower (18) is connected to the filter (2) through the filter backwash air pipe (20), and the activated carbon adsorption pool backwash blower (19) is connected to the activated carbon adsorption pool (4) through the activated carbon adsorption pool backwash air pipe (21). The bottom elevation of the filter backwash air pipe (20) is more than 50cm higher than the highest water level of the filter (2), and the bottom elevation of the activated carbon adsorption pool backwash air pipe (21) is more than 50cm higher than the highest water level of the activated carbon adsorption pool (4).

4. The integrated water treatment device of claim 1, wherein The filter backwash water pump (14) is connected to the filter (2) through the filter backwash water pipe (16), and the activated carbon adsorption tank backwash water pump (15) is connected to the activated carbon adsorption tank (4) through the activated carbon adsorption tank backwash water pipe (17).

5. The integrated water treatment device of claim 3, wherein The filter backwash air pipe (20), activated carbon adsorption tank backwash air pipe (21), filter backwash water pipe (16) and activated carbon adsorption tank backwash water pipe (17) are installed in the integrated pipe gallery (13).

6. The integrated water treatment device of claim 1, wherein The filter tanks (2) are arranged in 4 groups, and the filter media is uniform quartz sand with a particle size range of 0.9-1.2 mm and a non-uniformity coefficient K. 60 ≤1.6; 4 groups of activated carbon adsorption tanks (4) are arranged. The filter material is briquette crushed carbon with a particle size range of 1.2-1.3mm and a filter material layer height of 2m.