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CN113845232A - A Wetland System for Treating River Pollution - Google Patents

A Wetland System for Treating River Pollution Download PDF

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Publication number
CN113845232A
CN113845232A CN202111300784.6A CN202111300784A CN113845232A CN 113845232 A CN113845232 A CN 113845232A CN 202111300784 A CN202111300784 A CN 202111300784A CN 113845232 A CN113845232 A CN 113845232A
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water
pond
layer
river
wetland system
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孙孝平
唐伯平
张代臻
葛宝明
汪正飞
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Yancheng Teachers University
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Yancheng Teachers University
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    • CCHEMISTRY; METALLURGY
    • C02TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02FTREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02F3/00Biological treatment of water, waste water, or sewage
    • C02F3/32Biological treatment of water, waste water, or sewage characterised by the animals or plants used, e.g. algae
    • CCHEMISTRY; METALLURGY
    • C02TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02FTREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02F3/00Biological treatment of water, waste water, or sewage
    • C02F3/02Aerobic processes
    • CCHEMISTRY; METALLURGY
    • C02TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02FTREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02F2101/00Nature of the contaminant
    • C02F2101/10Inorganic compounds
    • C02F2101/16Nitrogen compounds, e.g. ammonia
    • CCHEMISTRY; METALLURGY
    • C02TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02FTREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02F2103/00Nature of the water, waste water, sewage or sludge to be treated
    • C02F2103/007Contaminated open waterways, rivers, lakes or ponds
    • YGENERAL TAGGING OF NEW TECHNOLOGICAL DEVELOPMENTS; GENERAL TAGGING OF CROSS-SECTIONAL TECHNOLOGIES SPANNING OVER SEVERAL SECTIONS OF THE IPC; TECHNICAL SUBJECTS COVERED BY FORMER USPC CROSS-REFERENCE ART COLLECTIONS [XRACs] AND DIGESTS
    • Y02TECHNOLOGIES OR APPLICATIONS FOR MITIGATION OR ADAPTATION AGAINST CLIMATE CHANGE
    • Y02WCLIMATE CHANGE MITIGATION TECHNOLOGIES RELATED TO WASTEWATER TREATMENT OR WASTE MANAGEMENT
    • Y02W10/00Technologies for wastewater treatment
    • Y02W10/10Biological treatment of water, waste water, or sewage

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  • Life Sciences & Earth Sciences (AREA)
  • Engineering & Computer Science (AREA)
  • Water Supply & Treatment (AREA)
  • Hydrology & Water Resources (AREA)
  • Microbiology (AREA)
  • Environmental & Geological Engineering (AREA)
  • Biodiversity & Conservation Biology (AREA)
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  • Organic Chemistry (AREA)
  • Biotechnology (AREA)
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  • Purification Treatments By Anaerobic Or Anaerobic And Aerobic Bacteria Or Animals (AREA)
  • Hydroponics (AREA)

Abstract

本发明公开了一种治理河道污染的湿地系统,包括河水进入口、湿地系统和进塘口,河水进入口与沉淀池连接,沉淀池与生态稳定塘连接,并且生态稳定塘位于沉淀池下游,生态稳定塘与曝气池连接,曝气池与湿地系统连接,湿地系统与滞留池连接,滞留池与水质观测塘连接,水质观测塘与沉淀塘连接,沉淀塘与进河口连接。采用了生态稳定塘和湿地区域,该湿地区域具有逐步恢复和丰富的生态链,还原水体生态和人类和谐共生的生态环境,能够减轻河水水体的污染负荷,提高水质质量,改善水生态功能和河道景观,促使区域水质以及河水水质走向良性循环,采用了浅水植物、被子植物和水生植物的多种组合,通过其水下茎、杆上的生物膜对大部分抗生素的去除。

Figure 202111300784

The invention discloses a wetland system for treating river pollution, comprising a river water inlet, a wetland system and a pond inlet. The river inlet is connected with a sedimentation tank, the sedimentation tank is connected with an ecological stabilization pond, and the ecological stabilization pond is located downstream of the sedimentation tank. The ecological stabilization pond is connected to the aeration pond, the aeration pond is connected to the wetland system, the wetland system is connected to the retention pond, the retention pond is connected to the water quality observation pond, the water quality observation pond is connected to the sedimentation pond, and the sedimentation pond is connected to the estuary. The ecological stabilization pond and wetland area are adopted. The wetland area has a gradually restored and enriched ecological chain, restoring the ecological environment of the harmonious coexistence of water ecology and human beings, which can reduce the pollution load of river water, improve water quality, and improve water ecological functions and river channels. The landscape promotes a virtuous cycle of regional water quality and river water quality. Various combinations of shallow water plants, angiosperms and aquatic plants are used to remove most antibiotics through biofilms on their underwater stems and stems.

Figure 202111300784

Description

Wet land system for treating river pollution
Technical Field
The invention relates to the technical field of wetland systems, in particular to a wetland system for treating river pollution.
Background
With the continuous and rapid development of national economy, the improvement of the scientific and technical level and the continuous acceleration of the urbanization process, river sand is used as a raw material which is widely applied in the building and manufacturing industries, and the demand is increasing day by day. River bed unevenness caused by river sand mining forms a pool. Due to long-term sand mining, the river channel is cut downwards, the low water level is reduced, and the water intake at the water intake port of a tap water plant is difficult to take water; the salt water is traced upwards, which causes a series of problems of water quality deterioration of a water intake and the like, and serious influences are caused on drinking water, water environment, water ecology and water safety, and finally, the health and safety of human beings are endangered.
The artificial wetland is also called constructed wetland, is a ground similar to swamp in artificial construction and supervision control, and is designed and constructed by combining physical, chemical and biological actions and optimization in a natural ecosystem of the wetland, and the sewage treatment is also carried out by utilizing the coordination relationship action of the three actions.
The conventional artificial wetland system cannot efficiently clean suspended matters and antibiotics in the river channel and has poor capability of restoring the river channel. Therefore, a wetland system for treating river pollution is needed.
Disclosure of Invention
The invention aims to provide a wetland system for treating river pollution, and aims to solve the problems that the conventional artificial wetland system cannot efficiently clean suspended matters and antibiotics in a river and has poor riverway restoration capability in the background art.
In order to achieve the purpose, the invention provides the following technical scheme: a wetland system for treating river pollution comprises a river water inlet, a wetland system and a pond inlet, wherein the river water inlet is connected with a sedimentation tank, the sedimentation tank is connected with an ecological stabilization pond, the ecological stabilization pond is positioned at the downstream of the sedimentation tank, the ecological stabilization pond is connected with an aeration tank, the aeration tank is connected with the wetland system, the wetland system is connected with a retention tank, the retention tank is connected with a water quality observation pond, the water quality observation pond is connected with the sedimentation pond, and the sedimentation pond is connected with the river inlet.
Preferably, the river water inlet is used for introducing polluted river water into the sedimentation tank, the sedimentation tank is a two-stage platform, the first layer of platform is a foundation soil layer, the second layer of platform is a clay layer, the sedimentation tank enters the ecological stabilization pond through a communication water pipe, the ecological stabilization pond is internally provided with two layers, one layer is a vegetable soil layer and the other layer is a clay layer, the vegetable soil layer is arranged on the upper layer, aquatic plants are planted on the vegetable soil layer, the aquatic plants are one or more of saxifraga, water lily, lotus, yellow flag and cyperus alternifolius, the ecological stabilization pond is connected with the aeration tank through a water pump, the aeration tank automatically lifts water and aerates at regular time, simultaneously enhances the dissolved oxygen of the water body, enhances the effect of aerobic microorganisms of the water body, has a certain removing effect on COD and ammonia nitrogen, and enters the wetland system after aeration is completed.
Preferably, the wetland system comprises a wetland area, the wetland area comprises a first groove, a second groove and a third groove, the top of the left side of the wetland area is provided with a water inlet pipe, the right side of the water inlet pipe is provided with the first groove, the first groove and the second groove are both provided with four layers, the bottom layer is a pebble water filtering layer, the pebble water filtering layer is provided with a water storage layer above, the water storage layer is provided with a mixed packing layer above, the mixed packing layer is provided with a soil matrix layer above, the soil matrix layer is planted with angiosperms, the right side of the first groove is provided with a shallow water layer, the shallow water layer is planted with aquatic plants, the right side of the shallow water layer is provided with the second groove, the right upper side of the second groove is provided with the third groove, the third groove is provided with soil matrix layer, and the soil matrix layer is planted with bionic grass, a water outlet is arranged on the right side of the third groove.
Preferably, the wetland system is connected with the retention pond through the water outlet, the retention pond buffers the entering water body, then the water in the retention pond flows into the downstream water quality observation pond, the water quality observation pond performs water quality detection on the entering water body, the water enters the sedimentation pond after the detection is finished, the sedimentation pond stores the water body in the water quality observation pond, and when the water body in the river channel needs water quantity to be supplemented, the water body enters the river channel through the river inlet.
Preferably, the angiosperm is one of arbor, shrub and liana, and the shallow water plant is one or any combination of hydrilla verticillata, goldfish algae, potamogeton crispus, curly pondweed.
Preferably, the detention pond is a secondary platform land, the bottom of the pond comprises a vegetable soil layer and a clay layer from bottom to top, aquatic plants are planted in the vegetable soil layer, and the aquatic plants are one or two of calamus and allium mongolicum regel.
Preferably, the shallow water plants, angiosperms and aquatic plants remove most of the antibiotics through the biofilm on the underwater stems and rods thereof.
Compared with the prior art, the invention has the beneficial effects that: the wetland system for treating the river pollution adopts an ecological stabilization pond and a wetland area, the wetland area is provided with a gradually recovered and rich ecological chain, the ecological environment of a water body and the harmonious symbiosis of human beings is reduced, the pollution load of the water body of river water can be reduced, the water quality is improved, the water ecological function and the river landscape are improved, the water quality of the area and the water quality of the river water are promoted to move to virtuous circle, and various combinations of shallow water plants, angiosperms and aquatic plants are adopted, by removing most of antibiotics through the biomembranes on the underwater stems and rods, the aeration tank automatically lifts water and aerates, simultaneously enhances the dissolved oxygen of the water body and strengthens the action of aerobic microorganisms in the water body, the ecological restoration method has a certain effect of removing COD and ammonia nitrogen, plays the advantages of the artificial wetland, restores and improves the water ecological environment on the basis of reducing human intervention as much as possible, and gradually establishes a stable ecological system.
Drawings
FIG. 1 is a flow chart of the overall structure of the system of the present invention;
fig. 2 is a structural diagram of the wetland system of the invention.
In the figure: 1. a wetland area; 2. a mixed packing layer; 3. a aquifer; 4. a pebble water filtering layer; 5. a first groove; 6. a second groove; 7. a soil matrix layer; 8. an angiosperm plant; 9. plants in shallow water; 10. a shallow water layer; 11. a third groove; 12. a water outlet; 13. a water inlet pipe; 14. bionic grass.
Detailed Description
The technical solutions in the embodiments of the present invention will be clearly and completely described below with reference to the drawings in the embodiments of the present invention, and it is obvious that the described embodiments are only a part of the embodiments of the present invention, and not all of the embodiments. All other embodiments, which can be derived by a person skilled in the art from the embodiments given herein without making any creative effort, shall fall within the protection scope of the present invention.
Referring to fig. 1-2, the present invention provides an embodiment: a wetland system for treating river pollution comprises a river water inlet, a wetland system and a pond inlet, wherein the river water inlet is connected with a sedimentation tank, the sedimentation tank is connected with an ecological stabilization pond, the ecological stabilization pond is positioned at the downstream of the sedimentation tank, the ecological stabilization pond is connected with an aeration tank, the aeration tank is connected with the wetland system, the wetland system is connected with a retention tank, the retention tank is connected with a water quality observation pond, the water quality observation pond is connected with the sedimentation pond, and the sedimentation pond is connected with the pond inlet.
Furthermore, the river water inlet is used for introducing polluted river water into the sedimentation tank, the sedimentation tank is a two-stage platform, the first layer of platform is a foundation soil layer, the second layer of platform is a clay layer, the sedimentation tank enters the ecological stabilization pond through a communication water pipe, the ecological stabilization pond is internally provided with two layers, one layer is an vegetarian soil layer, the other layer is a clay layer, the vegetarian soil layer is arranged on the upper layer, aquatic plants are planted on the vegetarian soil layer, the aquatic plants are one or more of saxifraga, water lily, lotus flower, yellow flag and cyperus alternifolius, the ecological stabilization pond is connected with the aeration tank through a water pump, the aeration tank automatically lifts water and aerates at regular time, simultaneously enhances dissolved oxygen of the water body, enhances the effect of aerobic microorganisms of the water body, has a certain removing effect on COD and ammonia nitrogen, and enters the wetland system after aeration is completed.
Further, the wetland system comprises a wetland area 1, the wetland area 1 comprises a first groove 5, a second groove 6 and a third groove 11, the leftmost top of the wetland area 1 is provided with a water inlet pipe 13, the right side of the water inlet pipe 13 is provided with the first groove 5, the first groove 5 and the second groove 6 are both provided with four layers, the bottommost layer is a pebble water filtering layer 4, the pebble water filtering layer 4 is provided with a water storage layer 3, the water storage layer 3 is provided with a mixed packing layer 2, the mixed packing layer 2 is provided with a soil matrix layer 7, the soil matrix layer 7 is planted with angiosperm 8, the right side of the first groove 5 is provided with a shallow water layer 10, the shallow water layer 10 is planted with shallow water plants 9, the right side of the shallow water layer 10 is provided with the second groove 6, the right upper side of the second groove 6 is provided with the third groove 11, the third groove 11 is internally provided with the soil matrix layer 7, bionic grass 14 is planted on the soil matrix layer 7, and a water outlet 12 is formed in the right side of the third groove 11.
Furthermore, the wetland system is connected with the retention pond through the water outlet 12, the retention pond buffers the entering water body, then the water in the retention pond flows into the downstream water quality observation pond, the water quality observation pond performs water quality detection on the entering water body, the water enters the sedimentation pond after the detection is finished, the sedimentation pond stores the water body in the water quality observation pond, and when the water body in the river channel needs water quantity to be supplemented, the water body enters the river channel through the river inlet.
Further, the angiosperm 8 is one of arbor, shrub and liana, and the shallow water plant 9 is one or any combination of hydrilla verticillata, goldfish algae, potamogeton malabaricum, bitter grass and curly pondweed.
Furthermore, the detention pond is a secondary platform land, the bottom of the pond comprises a plain soil layer and a clay layer from bottom to top, aquatic plants are planted in the plain soil layer, and the aquatic plants are one or two of calamus and allium mongolicum regel.
Further, the shallow water plants 9, angiosperm 8 and aquatic plants remove most antibiotics through the biological membranes on the underwater stems and rods.
The wetland system for treating river pollution in the embodiment of the invention adopts the ecological stabilization pond and the wetland area 1, the wetland area 1 has gradually recovered and abundant ecological chains, reduces the ecological environment of water body and harmonious symbiosis of human beings, can reduce the pollution load of river water body, improves the water quality, improves the water ecological function and river landscape, and promotes the area water quality and the river water quality to go to virtuous circle, adopts various combinations of shallow water plants 9, angiosperms 8 and aquatic plants, removes most of antibiotics through biomembranes on underwater stems and rods, automatically lifts water and aerates in an aeration tank, simultaneously enhances dissolved oxygen in the water body, strengthens the effect of aerobic microorganisms in the water body, has certain removal effect on COD and ammonia nitrogen, exerts the advantages of the artificial wetland, has purification function on the river water and intercepting sewage, and improves the river water quality, and the river landscape is improved. The current river, wetland and animal and plant resources are fully utilized, and on the basis of reducing human intervention as much as possible, the water ecological environment is restored and improved, and a stable ecological system is gradually established.
Although the present invention has been described in detail with reference to the foregoing embodiments, it will be apparent to those skilled in the art that various changes in the embodiments and/or modifications of the invention can be made, and equivalents and modifications of some features of the invention can be made without departing from the spirit and scope of the invention.

Claims (7)

1.一种治理河道污染的湿地系统,包括河水进入口、湿地系统和进塘口,其特征在于:所述的河水进入口与沉淀池连接,所述的沉淀池与生态稳定塘连接,并且生态稳定塘位于沉淀池下游,所述的生态稳定塘与曝气池连接,所述的曝气池与湿地系统连接,所述的湿地系统与滞留池连接,所述的滞留池与水质观测塘连接,所述的水质观测塘与沉淀塘连接,所述的沉淀塘与进河口连接。1. a wetland system for controlling river pollution, comprising river water inlet, wetland system and pond inlet, it is characterized in that: described river water inlet is connected with sedimentation tank, and described sedimentation tank is connected with ecological stabilization pond, and The ecological stabilization pond is located downstream of the sedimentation tank, the ecological stabilization pond is connected with the aeration tank, the aeration tank is connected with the wetland system, the wetland system is connected with the retention pond, and the retention pond is connected with the water quality observation pond The water quality observation pond is connected with the sedimentation pond, and the sedimentation pond is connected with the inlet of the river. 2.根据权利要求1所述的一种治理河道污染的湿地系统,其特征在于:所述的河水进入口用于将受污染的河水引入沉淀池,沉淀池为两级台地,第一层台地为基土层,第二层台地为黏土层,所述的沉淀池通过连通水管进入生态稳定塘,所述的生态稳定塘内设置为两层,一层为素土层,一层为黏土层,素土层在上层,素土层上种植有水生植物,所述的水生植物为梭鱼草、睡莲、荷花、黄菖蒲、纸莎草中的一种或几种,所述的生态稳定塘通过水泵与曝气池连接,所述的曝气池定时自动提水曝气,同时增强水体溶解氧,强化水体好氧微生物的作用,对COD、氨氮具有一定的去除作用,曝气完成后进入湿地系统。2. a kind of wetland system for controlling river pollution according to claim 1, is characterized in that: described river water inlet is used to introduce polluted river water into sedimentation tank, and sedimentation tank is two-level platform, the first layer platform It is a base soil layer, the second platform is a clay layer, the sedimentation tank enters the ecological stabilization pond through a connecting water pipe, and the ecological stabilization pond is set to two layers, one is a plain soil layer, and the other is a clay layer, The plain soil layer is on the upper layer, and aquatic plants are planted on the plain soil layer. The water pump is connected to the aeration tank. The aeration tank automatically lifts water and aerates at regular intervals, and at the same time enhances the dissolved oxygen in the water body, strengthens the effect of aerobic microorganisms in the water body, and has a certain removal effect on COD and ammonia nitrogen. After the aeration is completed, it enters the wetland system. 3.根据权利要求2所述的一种治理河道污染的湿地系统,其特征在于:所述的湿地系统包括湿地区域(1),湿地区域(1)内包括第一凹槽(5),第二凹槽(6)和第三凹槽(11),所述的湿地区域(1)的最左侧顶部设置有进水管(13),所述的进水管(13)的右侧下方设置有第一凹槽(5),第一凹槽(5)和第二凹槽(6)内都设置有四层,最底层为卵石滤水层(4),所述的卵石滤水层(4)上方设置有蓄水层(3),所述的蓄水层(3)上方设置有混合填料层(2),所述的混合填料层(2)上方设置有土壤基质层(7),所述的土壤基质层(7)上种植有被子植物(8),第一凹槽(5)的右侧设置有浅水层(10),所述的浅水层(10)上种植有浅水植物(9),所述的浅水层(10)的右侧设置有第二凹槽(6),所述的第二凹槽(6)的右上方设置有第三凹槽(11),第三凹槽(11)内设置有土壤基质层(7),所述的土壤基质层(7)上种植有仿生草(14),第三凹槽(11)的右侧设置有出水口(12)。3. A wetland system for controlling river pollution according to claim 2, characterized in that: the wetland system comprises a wetland area (1), and the wetland area (1) includes a first groove (5), Two grooves (6) and a third groove (11), a water inlet pipe (13) is provided on the leftmost top of the wetland area (1), and a water inlet pipe (13) is provided on the lower right side of the water inlet pipe (13). The first groove (5), the first groove (5) and the second groove (6) are all provided with four layers, and the bottom layer is a pebble water filter layer (4), the pebble water filter layer (4) ) is provided with an aquifer (3) above, a mixed filler layer (2) is provided above the aquifer (3), and a soil matrix layer (7) is provided above the mixed filler layer (2), so Angiosperms (8) are planted on the described soil matrix layer (7), the right side of the first groove (5) is provided with a shallow water layer (10), and the shallow water layer (10) is planted with shallow water plants (9). ), the right side of the shallow water layer (10) is provided with a second groove (6), the upper right of the second groove (6) is provided with a third groove (11), the third groove (11) A soil matrix layer (7) is arranged in the soil matrix layer (7), bionic grass (14) is planted on the soil matrix layer (7), and a water outlet (12) is arranged on the right side of the third groove (11). 4.根据权利要求3所述的一种治理河道污染的湿地系统,其特征在于:所述的湿地系统通过出水口(12)与滞留池连接,所述的滞留池对进入的水体进行缓冲,随后滞留池内的水流入下游的水质观测塘,所述的水质观测塘对进入的水体进行水质检测,检测完毕后进入沉淀塘,沉淀塘对水质观测塘内的水体储存,当河道内的水体需要水量进行补充时,通过进河口进入河道内。4. The wetland system for controlling river pollution according to claim 3, wherein the wetland system is connected with a retention pond through a water outlet (12), and the retention pond buffers the water body that enters, Then the water in the detention pond flows into the downstream water quality observation pond. The water quality observation pond conducts water quality testing on the entering water body. After the test is completed, it enters the sedimentation pond. The sedimentation pond stores the water body in the water quality observation pond. When replenishing, enter the river channel through the estuary. 5.根据权利要求4所述的一种治理河道污染的湿地系统,其特征在于:所述的被子植物(8)为乔木、灌木和藤本中的一种,浅水植物(9)为黑藻、金鱼藻、马来眼子菜、苦草、菹草中的一种或任意种组合。5. a kind of wetland system for controlling river pollution according to claim 4, is characterized in that: described angiosperm (8) is a kind of in tree, shrub and vine, and shallow water plant (9) is black algae, One or any combination of hornwort, malaria, bitter grass, and calamus. 6.根据权利要求5所述的一种治理河道污染的湿地系统,其特征在于:所述的滞留池为二级台地,池底自下而上包括素土层、粘土层,素土层种植水生植物,水生植物为菖蒲、水葱中的一种或两种。6 . The wetland system for controlling river pollution according to claim 5 , wherein the retention pond is a secondary platform, and the bottom of the pond comprises a plain soil layer and a clay layer from bottom to top, and the plain soil layer is planted. 7 . Aquatic plants, aquatic plants are one or two of calamus and water onion. 7.根据权利要求6所述的一种治理河道污染的湿地系统,其特征在于:所述的浅水植物(9)、被子植物(8)和水生植物通过其水下茎、杆上的生物膜对大部分抗生素的去除。7. a kind of wetland system for controlling river pollution according to claim 6, is characterized in that: described shallow water plants (9), angiosperms (8) and aquatic plants pass through the biofilm on its underwater stems, rods Removal of most antibiotics.
CN202111300784.6A 2021-11-04 2021-11-04 A Wetland System for Treating River Pollution Withdrawn CN113845232A (en)

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Citations (6)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
EP2716607A1 (en) * 2011-05-24 2014-04-09 Sung Il En-Tech Co. Ltd. Hybrid artificial wetland water purification system, sewage treatment device using same, and natural nonpoint purification device capable of simultaneously purifying river and lake water
CN206635120U (en) * 2017-04-13 2017-11-14 北京正和恒基滨水生态环境治理股份有限公司 Mixed flow constructed wetland system
CN111115974A (en) * 2020-01-17 2020-05-08 岭南水务集团有限公司 Pond wetland system
CN212770305U (en) * 2020-01-17 2021-03-23 岭南水务集团有限公司 Pond wetland system
CN212924574U (en) * 2020-07-15 2021-04-09 杨海英 Channel type enhanced ecological interception wetland
CN113087155A (en) * 2020-01-08 2021-07-09 芜湖沃泰环保科技有限公司 Artificial wetland system for removing antibiotics

Patent Citations (6)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
EP2716607A1 (en) * 2011-05-24 2014-04-09 Sung Il En-Tech Co. Ltd. Hybrid artificial wetland water purification system, sewage treatment device using same, and natural nonpoint purification device capable of simultaneously purifying river and lake water
CN206635120U (en) * 2017-04-13 2017-11-14 北京正和恒基滨水生态环境治理股份有限公司 Mixed flow constructed wetland system
CN113087155A (en) * 2020-01-08 2021-07-09 芜湖沃泰环保科技有限公司 Artificial wetland system for removing antibiotics
CN111115974A (en) * 2020-01-17 2020-05-08 岭南水务集团有限公司 Pond wetland system
CN212770305U (en) * 2020-01-17 2021-03-23 岭南水务集团有限公司 Pond wetland system
CN212924574U (en) * 2020-07-15 2021-04-09 杨海英 Channel type enhanced ecological interception wetland

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