CN219567711U - A Vertical Flow Constructed Wetland Simulation Device - Google Patents
A Vertical Flow Constructed Wetland Simulation Device Download PDFInfo
- Publication number
- CN219567711U CN219567711U CN202320013295.0U CN202320013295U CN219567711U CN 219567711 U CN219567711 U CN 219567711U CN 202320013295 U CN202320013295 U CN 202320013295U CN 219567711 U CN219567711 U CN 219567711U
- Authority
- CN
- China
- Prior art keywords
- pipe
- simulation device
- vertical flow
- shaped pipe
- barrel body
- Prior art date
- Legal status (The legal status is an assumption and is not a legal conclusion. Google has not performed a legal analysis and makes no representation as to the accuracy of the status listed.)
- Expired - Fee Related
Links
- 238000004088 simulation Methods 0.000 title claims abstract description 22
- XLYOFNOQVPJJNP-UHFFFAOYSA-N water Substances O XLYOFNOQVPJJNP-UHFFFAOYSA-N 0.000 claims abstract description 50
- 239000002245 particle Substances 0.000 claims abstract description 28
- 239000011159 matrix material Substances 0.000 claims abstract description 17
- 239000000945 filler Substances 0.000 claims abstract description 12
- 239000007787 solid Substances 0.000 claims abstract description 12
- 230000000813 microbial effect Effects 0.000 claims abstract description 10
- 230000002572 peristaltic effect Effects 0.000 claims description 7
- 229910001220 stainless steel Inorganic materials 0.000 claims description 4
- 239000010935 stainless steel Substances 0.000 claims description 4
- 238000005485 electric heating Methods 0.000 claims description 2
- 239000004575 stone Substances 0.000 claims 1
- 238000000034 method Methods 0.000 abstract description 6
- 230000000694 effects Effects 0.000 abstract description 4
- 229920000426 Microplastic Polymers 0.000 description 14
- 239000007788 liquid Substances 0.000 description 5
- IJGRMHOSHXDMSA-UHFFFAOYSA-N Atomic nitrogen Chemical compound N#N IJGRMHOSHXDMSA-UHFFFAOYSA-N 0.000 description 4
- 238000001514 detection method Methods 0.000 description 4
- 238000010586 diagram Methods 0.000 description 3
- 239000010865 sewage Substances 0.000 description 3
- 239000010802 sludge Substances 0.000 description 3
- 239000008399 tap water Substances 0.000 description 3
- 235000020679 tap water Nutrition 0.000 description 3
- 239000002351 wastewater Substances 0.000 description 3
- OAICVXFJPJFONN-UHFFFAOYSA-N Phosphorus Chemical compound [P] OAICVXFJPJFONN-UHFFFAOYSA-N 0.000 description 2
- 239000004744 fabric Substances 0.000 description 2
- 238000010438 heat treatment Methods 0.000 description 2
- 244000005700 microbiome Species 0.000 description 2
- 229910052757 nitrogen Inorganic materials 0.000 description 2
- 229910052698 phosphorus Inorganic materials 0.000 description 2
- 239000011574 phosphorus Substances 0.000 description 2
- 241001465754 Metazoa Species 0.000 description 1
- 230000009286 beneficial effect Effects 0.000 description 1
- 230000007812 deficiency Effects 0.000 description 1
- 238000005516 engineering process Methods 0.000 description 1
- 238000001914 filtration Methods 0.000 description 1
- 239000011521 glass Substances 0.000 description 1
- 229910001385 heavy metal Inorganic materials 0.000 description 1
- 238000005457 optimization Methods 0.000 description 1
- 239000002244 precipitate Substances 0.000 description 1
- 239000002689 soil Substances 0.000 description 1
- 238000001179 sorption measurement Methods 0.000 description 1
Classifications
-
- Y—GENERAL 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
- Y02—TECHNOLOGIES OR APPLICATIONS FOR MITIGATION OR ADAPTATION AGAINST CLIMATE CHANGE
- Y02W—CLIMATE CHANGE MITIGATION TECHNOLOGIES RELATED TO WASTEWATER TREATMENT OR WASTE MANAGEMENT
- Y02W10/00—Technologies for wastewater treatment
- Y02W10/10—Biological treatment of water, waste water, or sewage
Landscapes
- Hydroponics (AREA)
Abstract
本实用新型公开了一种垂直流人工湿地模拟装置,包括:桶体,作为人工湿地模拟载体,在所述桶体内放置有具有微生物膜的基质填料,在基质填料上方设置有预留空间放置植物;进水管,通向桶体上方,且在进水管上设置有进水阀门;出水管,设置在桶体底部,且在出水管上设置有出水阀门;J形管,J形管的短部端与出水管可拆卸连接,且在J形管的短部端口处设置有筛网;所述J形管的长部端延伸至与桶体顶端方向,且所述J形管长部管体与桶体相互并列。本实用新型能够实现人工湿地模拟过程中微塑料固体颗粒的有效收集且保证进出水流速一致提高了试验效果。
The utility model discloses a vertical flow constructed wetland simulation device, which comprises: a barrel body, as a simulated carrier of a constructed wetland, a matrix filler with a microbial film is placed in the barrel body, and a reserved space is arranged above the matrix filler to place plants ; The water inlet pipe leads to the top of the bucket body, and a water inlet valve is arranged on the water inlet pipe; the water outlet pipe is arranged at the bottom of the bucket body, and a water outlet valve is arranged on the water outlet pipe; J-shaped pipe, the short part of the J-shaped pipe The end is detachably connected to the outlet pipe, and a screen is provided at the short end of the J-shaped pipe; the long end of the J-shaped pipe extends to the direction of the top of the barrel, and the long part of the J-shaped pipe Side by side with the barrel body. The utility model can realize the effective collection of micro-plastic solid particles in the artificial wetland simulation process, and ensures the consistent flow rate of the water in and out, thereby improving the test effect.
Description
技术领域technical field
本实用新型属于人工湿地技术领域,尤其涉及一种垂直流人工湿地模拟装置。The utility model belongs to the technical field of artificial wetlands, in particular to a vertical flow artificial wetland simulation device.
背景技术Background technique
人工湿地是由人工建造和控制运行的与沼泽地类似的地面,将污水、污泥有控制的投配到经人工建造的湿地上,污水与污泥在沿一定方向流动的过程中,主要利用土壤、人工介质、植物、微生物的物理、化学、生物三重协同作用,对污水、污泥进行处理的一种技术。在试验过程中需要利用人工湿地模拟装置获取试验数据。Constructed wetland is a ground similar to swampland that is artificially constructed and operated under control. Sewage and sludge are distributed to the artificially constructed wetland in a controlled manner. When sewage and sludge flow in a certain direction, they are mainly used It is a technology for treating sewage and sludge through the triple synergy of physics, chemistry and biology of soil, artificial medium, plants and microorganisms. During the test, it is necessary to use the artificial wetland simulation device to obtain test data.
现在的大部分模拟装置都是将流出液通过漏斗引入一个容器后再去对容器内的流出液进行化验。但那只适用于检测流出液的总磷、总氮、重金属元素的去除效果。现在微塑料去除是一个新兴领域,以往的人工湿地桶体的流出液收集方式已经不适用,因为微塑料检测是把微塑料固体颗粒拿去检测,而氮磷等元素检测是把流出液体拿去检测,所以如果先接流出液,再把流出液过滤后挑出微塑料固体颗粒就放大了人为因素的影响,因为人工挑选是远不能照顾到滤出的所有固体颗粒的,肯定会遗漏很多肉眼看不见的固体颗粒。并且现有的装置出水和进水端流速不同,在水流冲击下会对内部人工湿地环境产生影响,影响实验过程的数据准确性。Most of the present simulation devices introduce the effluent into a container through a funnel and then test the effluent in the container. But that is only suitable for detecting the removal effect of total phosphorus, total nitrogen and heavy metal elements in the effluent. Now microplastic removal is an emerging field, and the previous method of collecting effluent from constructed wetland barrels is no longer applicable, because the detection of microplastics is to detect the solid particles of microplastics, while the detection of elements such as nitrogen and phosphorus is to take the effluent Detection, so if the effluent is connected first, and then the microplastic solid particles are picked out after filtering the effluent, the influence of human factors will be magnified, because manual selection is far from taking care of all the solid particles filtered out, and many naked eyes will definitely be missed Invisible solid particles. Moreover, the flow velocity of the outlet and inlet of the existing device is different, which will affect the internal constructed wetland environment under the impact of the water flow, and affect the accuracy of the data in the experimental process.
实用新型内容Utility model content
为了克服现有技术方法的不足,本实用新型的目的在于提出一种垂直流人工湿地模拟装置,能够实现人工湿地模拟过程中微塑料固体颗粒的有效收集且保证进出水流速一致提高了试验效果。In order to overcome the deficiencies of the prior art methods, the purpose of this utility model is to propose a vertical flow artificial wetland simulation device, which can realize the effective collection of microplastic solid particles in the artificial wetland simulation process and ensure the consistent flow rate of water in and out to improve the test effect.
为实现以上目的,本实用新型采用技术方案是:一种垂直流人工湿地模拟装置,包括:In order to achieve the above purpose, the technical solution adopted by the utility model is: a vertical flow artificial wetland simulation device, including:
桶体,作为人工湿地模拟载体,在所述桶体内放置有具有微生物膜的基质填料,在基质填料上方设置有预留空间放置植物;The barrel body is used as a simulated carrier of the artificial wetland, and a matrix filler with a microbial film is placed in the barrel body, and a reserved space is provided above the matrix filler to place plants;
进水管,通向桶体上方,且在进水管上设置有进水阀门;The water inlet pipe leads to the top of the bucket body, and a water inlet valve is arranged on the water inlet pipe;
出水管,设置在桶体底部,且在出水管上设置有出水阀门;The water outlet pipe is arranged at the bottom of the bucket body, and a water outlet valve is arranged on the water outlet pipe;
J形管,J形管的短部端与出水管可拆卸连接,且在J形管的短部端口处设置有筛网;所述J形管的长部端延伸至与桶体顶端方向,且所述J形管长部管体与桶体相互并列。J-shaped pipe, the short end of the J-shaped pipe is detachably connected to the outlet pipe, and a screen is provided at the short end of the J-shaped pipe; the long end of the J-shaped pipe extends to the direction of the top of the barrel, And the long part of the J-shaped tube and the barrel are juxtaposed with each other.
进一步的是,所述人工湿地基质填料包括从下到上依次叠加的鹅卵石垫层、大粒砾石层和小粒砾石层,且在石子表面包裹有微生物膜。Further, the constructed wetland matrix filler includes a cobblestone cushion layer, a large-grain gravel layer and a small-grain gravel layer stacked sequentially from bottom to top, and a microbial film is wrapped on the surface of the pebbles.
进一步的是,所述小粒砾石层采用18cm厚的3~6mm粒径的砾石;所述大粒砾石层采用42cm厚的6~9mm粒径的砾石;所述鹅卵石垫层采用5cm厚的20~40mm粒径的鹅卵石。Further, the small gravel layer adopts gravels with a particle size of 3 to 6 mm with a thickness of 18 cm; the large gravel layer adopts gravels with a particle size of 6 to 9 mm with a thickness of 42 cm; particle size pebbles.
进一步的是,所述小粒砾石层采用18cm厚的9~12mm粒径的砾石;所述大粒砾石层采用42cm厚的12~15mm粒径的砾石;所述鹅卵石垫层采用5cm厚的20~40mm粒径的鹅卵石垫层。Further, the small gravel layer adopts gravels with a particle size of 9 to 12 mm in thickness of 18 cm; the large gravel layer adopts gravels with a particle size of 12 to 15 mm in thickness of 42 cm; Grain-sized cobblestone underlayment.
进一步的是,所述J形管的短部端与出水管通过螺纹拧和连接。Further, the short end of the J-shaped pipe is screwed and connected to the outlet pipe through threads.
进一步的是,所述筛网采用300目的不锈钢网筛收集固体颗粒。Further, the sieve adopts a 300-mesh stainless steel mesh sieve to collect solid particles.
进一步的是,所述筛网半径大于J形管内壁半径且小于J形管外壁半径,架设在管壁顶端。Further, the radius of the screen is greater than the radius of the inner wall of the J-shaped tube and smaller than the radius of the outer wall of the J-shaped tube, and is erected on the top of the tube wall.
进一步的是,在所述进水管处连接有蠕动泵。Further, a peristaltic pump is connected to the water inlet pipe.
进一步的是,在所述桶体外缠绕有电热丝。Further, a heating wire is wound outside the barrel.
采用本技术方案的有益效果:The beneficial effect of adopting this technical solution:
本实用新型通过采用J形管可拆卸连接在桶体底部的出水端处,使得出水端引到和桶体里的水面齐平,从而使进水端进多少水,出水端就能出多少水,从而保证进出水的流量一致,避免桶体内部环境受水流影响。但考虑到微塑料密度大,J形管又太长,固体颗粒会在J形管内积累,因此在短端处设置筛网把微塑料过滤出来,然后过滤后的水就走U形管出口溢出。The utility model is detachably connected to the water outlet at the bottom of the bucket body by adopting a J-shaped tube, so that the water outlet end is led to be flush with the water surface in the bucket body, so that as much water enters the water inlet end, as much water can be discharged from the water outlet end , so as to ensure the consistent flow of water in and out, and avoid the internal environment of the barrel from being affected by the water flow. However, considering the high density of microplastics and the J-shaped tube is too long, solid particles will accumulate in the J-shaped tube, so a screen is set at the short end to filter out the microplastics, and then the filtered water will overflow from the outlet of the U-shaped tube .
本实用新型进水端和出水端都装了阀门从而方便控制是否进出水和控制出水流量。The water inlet and outlet of the utility model are equipped with valves so as to facilitate the control of water in and out and the flow of water out.
附图说明Description of drawings
图1为本实用新型的一种垂直流人工湿地模拟装置的结构示意图;Fig. 1 is a structural schematic diagram of a vertical flow constructed wetland simulation device of the present invention;
图2为本实用新型实施例中J形管与出水管的连接结构示意图;Fig. 2 is a schematic diagram of the connection structure between the J-shaped pipe and the water outlet pipe in the embodiment of the utility model;
图3为本实用新型实施例中J形管与筛网的配合示意图;Fig. 3 is the cooperative schematic diagram of J-shaped pipe and screen cloth in the utility model embodiment;
其中,1是桶体,2是基质填料,3是进水管,4是进水阀门,5是出水管,6是出水阀门,7是J形管,8是筛网,9是螺纹。Wherein, 1 is barrel body, 2 is matrix filler, 3 is water inlet pipe, 4 is water inlet valve, 5 is water outlet pipe, 6 is water outlet valve, 7 is J-shaped pipe, 8 is screen, and 9 is screw thread.
具体实施方式Detailed ways
为了使实用新型的目的、技术方案和优点更加清楚,下面结合附图对本实用新型作进一步阐述。In order to make the purpose, technical solution and advantages of the utility model clearer, the utility model will be further elaborated below in conjunction with the accompanying drawings.
在本实施例中,参见图1-图2所示,一种垂直流人工湿地模拟装置,包括:In this embodiment, as shown in Fig. 1-Fig. 2, a vertical flow artificial wetland simulation device includes:
桶体1,作为人工湿地模拟载体,在所述桶体1内放置有具有微生物膜的基质填料2,在基质填料2上方设置有预留空间放置植物;The barrel body 1 is used as a constructed wetland simulation carrier, and a matrix filler 2 with a microbial film is placed in the barrel body 1, and a reserved space is provided above the matrix filler 2 to place plants;
进水管3,通向桶体1上方,且在进水管3上设置有进水阀门4;The water inlet pipe 3 leads to the top of the barrel body 1, and the water inlet pipe 3 is provided with a water inlet valve 4;
出水管5,设置在桶体1底部,且在出水管5上设置有出水阀门6;The water outlet pipe 5 is arranged at the bottom of the bucket body 1, and the water outlet pipe 5 is provided with a water outlet valve 6;
J形管7,J形管7的短部端与出水管5可拆卸连接,且在J形管7的短部端口处设置有筛网8;所述J形管7的长部端延伸至与桶体1顶端方向,且所述J形管7长部管体与桶体1相互并列。J-shaped pipe 7, the short end of J-shaped pipe 7 is detachably connected with outlet pipe 5, and screen cloth 8 is provided at the short portion port of J-shaped pipe 7; the long portion end of described J-shaped pipe 7 extends to It is in the direction of the top end of the barrel body 1, and the long part of the J-shaped pipe 7 is parallel to the barrel body 1.
具体的,桶体1采用半径18cm且高度为100cm的有机玻璃构成。每个桶体1内部预先根据实验需求装填了不同粒径、不同深度的基质层,并在基质层中养护好了微生物膜,以模拟人工湿地基质。Specifically, the barrel body 1 is made of organic glass with a radius of 18 cm and a height of 100 cm. Each barrel 1 is pre-filled with matrix layers of different particle sizes and depths according to the experimental requirements, and the microbial film is maintained in the matrix layer to simulate the constructed wetland matrix.
作为上述实施例的优化方案,所述人工湿地基质填料2包括从下到上依次叠加的鹅卵石垫层、大粒砾石层和小粒砾石层,且在石子表面包裹有微生物膜。As an optimization scheme of the above-mentioned embodiment, the constructed wetland matrix filler 2 includes a cobblestone cushion layer, a large-grained gravel layer and a small-grained gravel layer stacked sequentially from bottom to top, and a microbial film is wrapped on the surface of the pebbles.
方案一,所述小粒砾石层采用18cm厚的3~6mm粒径的砾石;所述大粒砾石层采用42cm厚的6~9mm粒径的砾石;所述鹅卵石垫层采用5cm厚的20~40mm粒径的鹅卵石。Option 1, the small-grained gravel layer adopts gravels with a particle size of 18 cm thick and 3-6 mm; the large-grained gravel layer adopts gravels with a particle size of 42 cm thick and 6-9 mm; trail of pebbles.
方案二,所述小粒砾石层采用18cm厚的9~12mm粒径的砾石;所述大粒砾石层采用42cm厚的12~15mm粒径的砾石;所述鹅卵石垫层采用5cm厚的20~40mm粒径的鹅卵石垫层。Option two, the small-grained gravel layer adopts gravels with a particle size of 9 to 12 mm with a thickness of 18 cm; the large-grained gravel layer adopts gravels with a particle size of 12 to 15 mm with a thickness of 42 cm; Path of cobblestone cushion.
作为上述实施例的优化方案,所述J形管7的短部端与出水管5通过螺纹9拧和连接。As an optimized solution of the above-mentioned embodiment, the short end of the J-shaped pipe 7 is screwed and connected to the outlet pipe 5 through a screw thread 9 .
所述筛网8采用300目的不锈钢网筛收集固体颗粒。The sieve 8 adopts a 300-mesh stainless steel mesh sieve to collect solid particles.
所述筛网8半径大于J形管7内壁半径且小于J形管7外壁半径,架设在管壁顶端如,图3所示,RD<RW<RDe。The radius of the screen 8 is greater than the radius of the inner wall of the J-shaped tube 7 and smaller than the radius of the outer wall of the J-shaped tube 7, and is erected on the top of the tube wall. As shown in FIG. 3 , R D < R W < R De .
作为上述实施例的优化方案,在所述进水管3处连接有蠕动泵。由蠕动泵供水并控制入流量,将软管一端接入加了微塑料的自来水或合成废水,软管另一端从桶体1顶端的阀门伸入桶体1。As an optimized solution of the above embodiment, a peristaltic pump is connected to the water inlet pipe 3 . Water is supplied by a peristaltic pump and the inflow is controlled. One end of the hose is connected to tap water or synthetic wastewater added with microplastics, and the other end of the hose extends into the barrel 1 from the valve at the top of the barrel 1.
作为上述实施例的优化方案,在所述桶体1外缠绕有电热丝。它可以为桶体1加热,而且电热丝带有温控器(温控范围在-55~110℃),这样就可以确保常年湿冷的气候下成功培育微生物膜,否则太冷了就养不活微生物。As an optimized solution of the above embodiment, a heating wire is wound outside the barrel body 1 . It can heat the barrel body 1, and the electric heating ribbon has a temperature controller (the temperature control range is -55 ~ 110 ℃), so that it can ensure the successful cultivation of microbial film in the humid and cold climate all the year round, otherwise it will not be able to support microorganisms if it is too cold .
为了更好的理解本实用新型,下面对本实用新型的工作原理作一次完整的描述:In order to better understand the utility model, a complete description is made to the working principle of the utility model below:
①每个桶体1由蠕动泵供水并控制入流量,将软管一端接入加了微塑料的自来水或合成废水(根据雨水中微塑料含量,将自来水或合成废水的微塑料浓度设为30particlas/L),软管另一端从桶体1顶端的阀门伸入桶体1。①Each bucket body 1 is supplied with water by a peristaltic pump and controls the inflow flow. Connect one end of the hose to tap water or synthetic wastewater with added microplastics (according to the content of microplastics in rainwater, set the concentration of microplastics in tap water or synthetic wastewater to 30particlas /L), the other end of the hose extends into the barrel 1 from the valve at the top of the barrel 1.
②关闭桶体1下端阀门。根据垂直流人工湿地需求将水力负荷设计为0.8m/d,启动蠕动泵,将液体输送进桶体1,以喂养人工湿地。待液面高出基质顶层5cm时缓慢开启桶体1下端阀门,将下端流量尽量控制得和顶端蠕动泵入流量相同,以保证液体自上而下通过桶体1的同时维持液面稳定。②Close the valve at the lower end of barrel body 1. According to the demand of the vertical flow constructed wetland, the hydraulic load is designed to be 0.8m/d, and the peristaltic pump is started to transport the liquid into the barrel 1 to feed the constructed wetland. When the liquid level is 5cm higher than the top layer of the matrix, slowly open the valve at the lower end of barrel 1, and control the flow at the lower end to be the same as the flow rate of the peristaltic pump at the top, so as to ensure that the liquid passes through barrel 1 from top to bottom while maintaining a stable liquid level.
③每个桶体1下面都放设置J型管,J型管短端放一个300目48μm的不锈钢网筛收集固体颗粒(微塑料),每五天收集一次网筛上的固体颗粒物进行检测。③A J-shaped tube is placed under each bucket body 1, and a 300-mesh 48 μm stainless steel mesh screen is placed at the short end of the J-shaped tube to collect solid particles (microplastics). The solid particles on the mesh screen are collected for detection every five days.
人工湿地去除微塑料的具体机理是通过基质的拦截作用、微生物膜的吸附作用、动植物影响,使液体中的微塑料颗粒絮凝、沉淀,从而达到去除效果。The specific mechanism of removing microplastics in constructed wetlands is to flocculate and precipitate microplastic particles in the liquid through the interception of the matrix, the adsorption of microbial films, and the influence of animals and plants, so as to achieve the removal effect.
以上显示和描述了本实用新型的基本原理、主要特征和本实用新型的优点。本行业的技术人员应该了解,本实用新型不受上述实施例的限制,上述实施例和说明书中描述的只是说明本实用新型的原理,在不脱离本实用新型精神和范围的前提下,本实用新型还会有各种变化和改进,这些变化和改进都落入要求保护的本实用新型范围内。本实用新型要求保护范围由所附的权利要求书及其等效物界定。The basic principles, main features and advantages of the present utility model have been shown and described above. Those skilled in the industry should understand that the utility model is not limited by the above-mentioned embodiments. The above-mentioned embodiments and descriptions only illustrate the principles of the utility model. Without departing from the spirit and scope of the utility model, the utility model The new model also has various changes and improvements, and these changes and improvements all fall within the scope of the claimed utility model. The scope of protection required by the utility model is defined by the appended claims and their equivalents.
Claims (9)
Priority Applications (1)
Application Number | Priority Date | Filing Date | Title |
---|---|---|---|
CN202320013295.0U CN219567711U (en) | 2023-01-04 | 2023-01-04 | A Vertical Flow Constructed Wetland Simulation Device |
Applications Claiming Priority (1)
Application Number | Priority Date | Filing Date | Title |
---|---|---|---|
CN202320013295.0U CN219567711U (en) | 2023-01-04 | 2023-01-04 | A Vertical Flow Constructed Wetland Simulation Device |
Publications (1)
Publication Number | Publication Date |
---|---|
CN219567711U true CN219567711U (en) | 2023-08-22 |
Family
ID=87665009
Family Applications (1)
Application Number | Title | Priority Date | Filing Date |
---|---|---|---|
CN202320013295.0U Expired - Fee Related CN219567711U (en) | 2023-01-04 | 2023-01-04 | A Vertical Flow Constructed Wetland Simulation Device |
Country Status (1)
Country | Link |
---|---|
CN (1) | CN219567711U (en) |
-
2023
- 2023-01-04 CN CN202320013295.0U patent/CN219567711U/en not_active Expired - Fee Related
Similar Documents
Publication | Publication Date | Title |
---|---|---|
CN207108742U (en) | A kind of livestock/poultry wastewater treatment system | |
CN204208345U (en) | A kind of buried rainwater treatment device | |
CN204079602U (en) | A kind of artificial swamp of assisting aeration and solving blocking with back flushing measure | |
CN104829064A (en) | Artificial wetland system | |
CN106242070A (en) | A kind of automated sewage processing system based on artificial swamp and control method thereof | |
CN219567711U (en) | A Vertical Flow Constructed Wetland Simulation Device | |
CN101759298B (en) | Rapid manual land infiltration treatment system and method for purifying river water by applying the same | |
CN211367142U (en) | A constructed wetland system using dredging pipes to prevent blockage | |
CN101875513A (en) | A method and device for removing Cr6+ in domestic sewage | |
CN208594165U (en) | A kind of domestic sewage processing system | |
CN105836891A (en) | Bidirectional flow distribution artificial wetland and treatment method thereof | |
CN202777962U (en) | Pretreatment device for applying horizontal subsurface flow constructed wetland to landscape water body purification | |
CN207537311U (en) | A kind of automatic control type ecological shore protection system for riverway water quality purification | |
CN104986863A (en) | Rural domestic sewage manual wetland system and purification method | |
CN203048673U (en) | Artificial wetland system for treating lead-contained wastewater | |
CN2828027Y (en) | Underflow artificial wet land simulator | |
CN215712075U (en) | Ecological treatment system for denitrification of aquaculture wastewater | |
CN105060609A (en) | Deep treatment method and device for coalbed methane produced water | |
CN201567278U (en) | A Remediation System for Groundwater Contaminated by Organic Matter | |
CN108609736A (en) | A kind of horizontal flow artificial wetland anti-clogging purifier | |
CN209602206U (en) | A sewage treatment system | |
CN104176882B (en) | A kind of inlet method and device improving artificial filtration system nitric efficiency | |
CN204625444U (en) | A kind of device for circular utilizing underground water | |
CN210085012U (en) | A filter device for treating roof rainwater | |
CN203700040U (en) | Carrier for biological treatment of dyeing and finishing industrial wastewater |
Legal Events
Date | Code | Title | Description |
---|---|---|---|
GR01 | Patent grant | ||
GR01 | Patent grant | ||
CF01 | Termination of patent right due to non-payment of annual fee |
Granted publication date: 20230822 |
|
CF01 | Termination of patent right due to non-payment of annual fee |