CN114933393B - In-situ ecological restoration structure for surface water and underground water - Google Patents
In-situ ecological restoration structure for surface water and underground water Download PDFInfo
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- CN114933393B CN114933393B CN202210569084.5A CN202210569084A CN114933393B CN 114933393 B CN114933393 B CN 114933393B CN 202210569084 A CN202210569084 A CN 202210569084A CN 114933393 B CN114933393 B CN 114933393B
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- XLYOFNOQVPJJNP-UHFFFAOYSA-N water Substances O XLYOFNOQVPJJNP-UHFFFAOYSA-N 0.000 title claims abstract description 68
- 239000002352 surface water Substances 0.000 title claims abstract description 51
- 238000011065 in-situ storage Methods 0.000 title claims abstract description 21
- 239000003673 groundwater Substances 0.000 claims abstract description 33
- 229910021536 Zeolite Inorganic materials 0.000 claims abstract description 19
- HNPSIPDUKPIQMN-UHFFFAOYSA-N dioxosilane;oxo(oxoalumanyloxy)alumane Chemical compound O=[Si]=O.O=[Al]O[Al]=O HNPSIPDUKPIQMN-UHFFFAOYSA-N 0.000 claims abstract description 19
- 239000010457 zeolite Substances 0.000 claims abstract description 19
- PNEYBMLMFCGWSK-UHFFFAOYSA-N aluminium oxide Inorganic materials [O-2].[O-2].[O-2].[Al+3].[Al+3] PNEYBMLMFCGWSK-UHFFFAOYSA-N 0.000 claims abstract description 17
- 235000019738 Limestone Nutrition 0.000 claims abstract description 16
- 239000006028 limestone Substances 0.000 claims abstract description 16
- 238000000034 method Methods 0.000 claims abstract description 11
- 230000001502 supplementing effect Effects 0.000 claims abstract description 7
- IJGRMHOSHXDMSA-UHFFFAOYSA-N Atomic nitrogen Chemical compound N#N IJGRMHOSHXDMSA-UHFFFAOYSA-N 0.000 claims description 26
- 241000196324 Embryophyta Species 0.000 claims description 21
- 239000003344 environmental pollutant Substances 0.000 claims description 20
- 231100000719 pollutant Toxicity 0.000 claims description 20
- 229910052757 nitrogen Inorganic materials 0.000 claims description 13
- 239000000919 ceramic Substances 0.000 claims description 12
- OAICVXFJPJFONN-UHFFFAOYSA-N Phosphorus Chemical compound [P] OAICVXFJPJFONN-UHFFFAOYSA-N 0.000 claims description 10
- 239000002245 particle Substances 0.000 claims description 10
- 229910052698 phosphorus Inorganic materials 0.000 claims description 10
- 239000011574 phosphorus Substances 0.000 claims description 10
- 239000002689 soil Substances 0.000 claims description 10
- 239000000945 filler Substances 0.000 claims description 8
- 244000005700 microbiome Species 0.000 claims description 8
- 229910052785 arsenic Inorganic materials 0.000 claims description 7
- RQNWIZPPADIBDY-UHFFFAOYSA-N arsenic atom Chemical compound [As] RQNWIZPPADIBDY-UHFFFAOYSA-N 0.000 claims description 7
- 238000000746 purification Methods 0.000 claims description 7
- 230000000694 effects Effects 0.000 claims description 6
- 229910052731 fluorine Inorganic materials 0.000 claims description 6
- 239000011737 fluorine Substances 0.000 claims description 6
- 238000001914 filtration Methods 0.000 claims description 5
- 239000000126 substance Substances 0.000 claims description 5
- 239000007789 gas Substances 0.000 claims description 4
- 238000005259 measurement Methods 0.000 claims description 4
- 230000008635 plant growth Effects 0.000 claims description 4
- 235000008733 Citrus aurantifolia Nutrition 0.000 claims description 3
- 235000011941 Tilia x europaea Nutrition 0.000 claims description 3
- 239000004571 lime Substances 0.000 claims description 3
- 238000012545 processing Methods 0.000 claims description 3
- 229910001220 stainless steel Inorganic materials 0.000 claims description 3
- 238000010521 absorption reaction Methods 0.000 claims description 2
- 230000000903 blocking effect Effects 0.000 claims description 2
- 230000002503 metabolic effect Effects 0.000 claims description 2
- 231100000252 nontoxic Toxicity 0.000 claims description 2
- 230000003000 nontoxic effect Effects 0.000 claims description 2
- 239000002957 persistent organic pollutant Substances 0.000 claims description 2
- 230000004083 survival effect Effects 0.000 claims description 2
- YCKRFDGAMUMZLT-UHFFFAOYSA-N Fluorine atom Chemical compound [F] YCKRFDGAMUMZLT-UHFFFAOYSA-N 0.000 claims 2
- 239000010935 stainless steel Substances 0.000 claims 1
- 238000012856 packing Methods 0.000 abstract description 4
- 230000009286 beneficial effect Effects 0.000 abstract description 2
- 239000010410 layer Substances 0.000 abstract description 2
- PXGOKWXKJXAPGV-UHFFFAOYSA-N Fluorine Chemical compound FF PXGOKWXKJXAPGV-UHFFFAOYSA-N 0.000 description 4
- 235000015097 nutrients Nutrition 0.000 description 4
- 239000011148 porous material Substances 0.000 description 3
- 241000195493 Cryptophyta Species 0.000 description 2
- 238000005273 aeration Methods 0.000 description 2
- 240000001592 Amaranthus caudatus Species 0.000 description 1
- 235000009328 Amaranthus caudatus Nutrition 0.000 description 1
- 241000252229 Carassius auratus Species 0.000 description 1
- 241000195474 Sargassum Species 0.000 description 1
- 239000002131 composite material Substances 0.000 description 1
- 239000000356 contaminant Substances 0.000 description 1
- 230000008021 deposition Effects 0.000 description 1
- 238000010586 diagram Methods 0.000 description 1
- 238000009776 industrial production Methods 0.000 description 1
- 238000011835 investigation Methods 0.000 description 1
- 230000002262 irrigation Effects 0.000 description 1
- 238000003973 irrigation Methods 0.000 description 1
- 244000144972 livestock Species 0.000 description 1
- 239000000463 material Substances 0.000 description 1
- 238000012986 modification Methods 0.000 description 1
- 230000004048 modification Effects 0.000 description 1
- 230000002093 peripheral effect Effects 0.000 description 1
- 244000144977 poultry Species 0.000 description 1
- 239000010865 sewage Substances 0.000 description 1
- 238000001179 sorption measurement Methods 0.000 description 1
- AYNNSCRYTDRFCP-UHFFFAOYSA-N triazene Chemical compound NN=N AYNNSCRYTDRFCP-UHFFFAOYSA-N 0.000 description 1
- 238000003911 water pollution Methods 0.000 description 1
Classifications
-
- C—CHEMISTRY; METALLURGY
- C02—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F9/00—Multistage treatment of water, waste water or sewage
-
- C—CHEMISTRY; METALLURGY
- C02—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F1/00—Treatment of water, waste water, or sewage
- C02F1/001—Processes for the treatment of water whereby the filtration technique is of importance
-
- C—CHEMISTRY; METALLURGY
- C02—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F1/00—Treatment of water, waste water, or sewage
- C02F1/28—Treatment of water, waste water, or sewage by sorption
- C02F1/281—Treatment of water, waste water, or sewage by sorption using inorganic sorbents
-
- C—CHEMISTRY; METALLURGY
- C02—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F1/00—Treatment of water, waste water, or sewage
- C02F1/28—Treatment of water, waste water, or sewage by sorption
- C02F1/283—Treatment of water, waste water, or sewage by sorption using coal, charred products, or inorganic mixtures containing them
-
- C—CHEMISTRY; METALLURGY
- C02—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F2103/00—Nature of the water, waste water, sewage or sludge to be treated
- C02F2103/007—Contaminated open waterways, rivers, lakes or ponds
-
- C—CHEMISTRY; METALLURGY
- C02—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F2103/00—Nature of the water, waste water, sewage or sludge to be treated
- C02F2103/06—Contaminated groundwater or leachate
-
- C—CHEMISTRY; METALLURGY
- C02—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F3/00—Biological treatment of water, waste water, or sewage
- C02F3/32—Biological treatment of water, waste water, or sewage characterised by the animals or plants used, e.g. algae
-
- 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
- Life Sciences & Earth Sciences (AREA)
- Hydrology & Water Resources (AREA)
- Engineering & Computer Science (AREA)
- Environmental & Geological Engineering (AREA)
- Water Supply & Treatment (AREA)
- Chemical & Material Sciences (AREA)
- Organic Chemistry (AREA)
- Water Treatment By Sorption (AREA)
Abstract
The invention relates to an in-situ ecological restoration structure for surface water and underground water. Is suitable for the technical field of surface water and groundwater treatment. The technical scheme adopted by the invention is as follows: an in-situ ecological restoration structure for surface water and underground water, which is characterized in that: the in-situ ecological restoration structure is paved at the bottom of a river or a lake with the water level higher than the water level of the ground water in the high water period and the water level lower than the water level of the ground water in the low water period; the ecological restoration structure in situ is from bottom to top in proper order bottom filter layer, packing layer, top filter layer and planting layer, and wherein the packing layer is activated alumina layer, biochar layer, and zeolite and limestone layer from bottom to top in proper order, plant submerged plant on the planting layer. The beneficial effects of the invention are as follows: according to the invention, the in-situ ecological restoration structure is paved at the bottom of the river and the lake, so that the surface water can be purified in the process of supplementing the surface water with the surface water, and the underground water can be purified in the process of supplementing the surface water with the underground water.
Description
Technical Field
The invention relates to an in-situ ecological restoration structure for surface water and underground water. Is suitable for the technical field of surface water and groundwater treatment.
Background
The silt deposition on the downstream of the yellow river leads the surface of the river dike inner bar to be generally higher than the ground surface of two banks by 4-6 m, and the height difference of partial river segments is even more than 10m, so that an overground suspended river is formed, and a unique water circulation system is also formed, namely, the yellow river water is supplied with shallow groundwater in one way all year round, so that the groundwater level is increased. Therefore, when the groundwater level is higher than the surrounding surface water level, groundwater seeps from the high water level to the low water level, and surface water is supplied; when the peripheral surface water level is higher than the shallow groundwater level, the surface water is used for measuring and infiltrating and supplementing the groundwater.
The water quality pollution of the surface water is serious due to the influence of agricultural irrigation, livestock and poultry cultivation, sewage discharge and industrial production on the downstream yellow sheet area of the yellow river. Meanwhile, the shortage of water resources promotes people to continuously exploit and utilize groundwater, and the problems of original geological environment and groundwater environment pollution are also severe. According to investigation data, the regional surface water and groundwater have the problem of exceeding the standard throughout the year, and pollutants in the surface water and groundwater are exchanged along with the regional surface water and groundwater in the process of mutual supply, so that the water pollution condition is aggravated.
At present, studies on in situ purification of surface and ground water have been quite extensive, but less on achieving contaminant removal during the mutual replenishment of surface and ground water, especially under specific water quality conditions downstream of the yellow river along the yellow patch.
Disclosure of Invention
The invention aims to solve the technical problems that: aiming at the problems, an in-situ ecological restoration structure for surface water and underground water is provided.
The technical scheme adopted by the invention is as follows: an in-situ ecological restoration structure for surface water and underground water, which is characterized in that: the in-situ ecological restoration structure is paved at the bottom of a river or a lake with the water level higher than the water level of the ground water in the high water period and the water level lower than the water level of the ground water in the low water period;
The ecological restoration structure in situ is from bottom to top in proper order bottom filter layer, packing layer, top filter layer and planting layer, and wherein the packing layer is activated alumina layer, biochar layer, and zeolite and limestone layer from bottom to top in proper order, plant submerged plant on the planting layer.
The bottom filter layer is sequentially provided with a filter screen and a porous ceramic filter plate from bottom to top.
The top filter layer is sequentially provided with a porous ceramic filter plate and a filter screen from bottom to top.
The filter screen is formed by processing a stainless steel wire mesh, and the aperture is 30-50 mm; the density of the holes of the porous ceramic filter plate is 7-13/25.4 mm.
The thickness of the active alumina layer is 15-20 cm, and the particle size of the active alumina is 5-15 mm.
The thickness of the biochar layer is 20-30 cm, and the particle size of the biochar is 15-30 mm.
The thickness of the zeolite and the limestone layer is 15-20 cm, the particle size of the zeolite and the limestone is 30-50 mm, and the ratio of the zeolite to the limestone is 1:1.
The submerged plants adopt one or a combination of more plants with better effect of removing nitrogen and arsenic in water.
The beneficial effects of the invention are as follows: according to the invention, the in-situ ecological restoration structure is paved at the bottom of the river and the lake, so that the surface water can be purified in the process of supplementing the surface water with the surface water, and the underground water can be purified in the process of supplementing the surface water with the underground water.
The submerged plant can directly absorb nutrient substances from the water body through the stem and leaf, and can adsorb pollutants through developed root systems and microorganisms attached to the root systems, so that the pollutant removal rate is improved. In addition, their aeration structure is particularly developed, facilitating gas exchange in the absence of air in the water.
The invention adopts the three-layer composite filter material composed of zeolite, limestone, biochar and activated alumina, can promote the growth of plants while removing pollutants such as nitrogen, fluorine and the like in water, and indirectly strengthens the pollutant removing capability.
Drawings
Fig. 1 is a schematic layout of an embodiment.
Fig. 2 is a schematic structural diagram of an embodiment.
1. Submerged plants; 2. a soil layer; 3. a filter screen; 4. a porous ceramic filter bottom plate; 5. zeolite and limestone layers; 6. a biochar layer; 7. an activated alumina layer.
Detailed Description
The embodiment is an in-situ ecological restoration structure for surface water and underground water, which is paved at the bottom of a river or lake (such as a river channel, a lake, a pit pool and the like around a yellow river suspended river section) with the water level higher than the underground water level in a high-water period and the water level lower than the underground water level in a low-water period.
The in-situ ecological restoration structure in this example is composed of a bottom filter layer, a filler layer, a top filter layer and a planting layer from bottom to top, wherein the bottom filter layer is composed of a filter screen and a porous ceramic filter plate from bottom to top; the filler layer is composed of an active alumina layer, a biochar layer, and a zeolite and lime layer from bottom to top in sequence; the top filter layer is sequentially provided with a porous ceramic filter plate and a filter screen from bottom to top; submerged plants are planted on the planting layer.
The filter screen in the embodiment is formed by processing a stainless steel wire mesh, and the aperture is 30-50 mm so as to prevent soil from blocking the filter holes and filter large-particle pollutants; the porous ceramic filter plate has a pore density of 7-13 pores/25.4 mm.
In the embodiment, the thickness of the active alumina layer is 15-20 cm, the particle size of the active alumina is 5-15 mm, and the active alumina has a good adsorption effect on fluorine in a water body.
In the embodiment, the thickness of the biochar layer is 20-30 cm, the particle size of the biochar is 15-30 mm, and the biochar can not only utilize the larger porosity and specific surface area of the biochar to adsorb pollutants, but also remarkably promote the growth of plants, improve the capturing capability of the biochar on nutrient substances required by the plants such as organic matters, nitrogen, phosphorus and the like, and indirectly strengthen the removing capability of the pollutants.
In the embodiment, the thickness of the zeolite and the limestone layer is 15-20 cm, the particle size of the zeolite and the limestone is 30-50 mm, and the ratio of the zeolite to the limestone layer is 1:1, nitrogen and phosphorus in the water body can be effectively removed.
The thickness of the planting soil laid in this example is 350-500 mm. The submerged plant is prepared from black algae,
One or more plants with good effect of removing nitrogen and arsenic in water body, such as herba Sonchi Oleracei, goldfish algae and Sargassum foxtail. The submerged plants can directly absorb nutrient substances from water body through stems and leaves, and can absorb pollutants through developed root systems and microorganisms attached to the root systems, so that the pollutant removal rate is improved. In addition, their aeration structure is particularly developed, facilitating gas exchange in the absence of air in the water.
The working principle of this embodiment is as follows:
A. When the surface water level in the river and the lake is higher than the shallow groundwater level, the surface water seepage measurement firstly passes through submerged plants, and under the action of the submerged plants with good absorption effect on nitrogen and arsenic, part of pollutants are removed, and microorganisms attached to plant root systems can also degrade organic pollutants, nitrify and denitrify the surface water, adsorb phosphorus and the like, so that the water quality purification efficiency is improved.
Subsequently, the surface water is measured and oozes through the top filter layer, and the filter screen can intercept soil that comes from soil layer and carry, prevents that it from blockking up the filtration pore on the porous ceramic filtration bottom plate.
Then the surface water continues to be measured and permeated through the filler layer, and the first layer is a zeolite layer and a limestone layer, so that nitrogen and phosphorus in the water body can be effectively adsorbed; the second layer is a biochar layer, so that on one hand, pollutants can be directly adsorbed, on the other hand, the growth of plants can be obviously promoted, the capturing capacity of nutrients required by the plants such as organic matters, nitrogen and phosphorus is improved, and the removal of the pollutants is enhanced; the third layer is an active alumina layer which can effectively adsorb fluorine in the water body. Meanwhile, the existence of the filler provides a stable environment for the survival and propagation of microorganisms, and the microorganisms can convert pollutants in the water body into gas or non-toxic and harmless substances through metabolic activities so as to accelerate the purification of the water body.
Finally, the water body passes through the bottom filter layer again, and the surface water quality purification is realized in the process of supplementing the surface water with the underground water.
B. When the groundwater level is higher than the surface water level, the groundwater is used for measuring and percolating the surface water. The groundwater also passes through the bottom filter layer in the seepage measurement process, and the carried soil and large particulate matters are filtered; and then sequentially passing through the activated alumina layer, the biochar layer, the zeolite and lime layer and the top filter layer above, and finally passing through the planting layer to finish the supply of surface water and remove the pollutants such as triazene, phosphorus, arsenic, fluorine and the like in the groundwater in the process.
The foregoing description is only of the preferred embodiments of the present invention and is not intended to limit the invention. Several modifications which may be made by a person skilled in the relevant art without departing from the principles of the invention should also be considered as being within the scope of the invention.
Claims (3)
1. An in-situ ecological restoration structure for surface water and underground water, which is characterized in that: the in-situ ecological restoration structure is paved at the bottom of a river or a lake with the water level higher than the water level of the ground water in the high water period and the water level lower than the water level of the ground water in the low water period;
The in-situ ecological restoration structure sequentially comprises a bottom filter layer, a filler layer, a top filter layer and a planting layer from bottom to top, wherein the filler layer sequentially comprises an active alumina layer, a biochar layer, zeolite and a limestone layer from bottom to top, and submerged plants are planted on the planting layer;
the bottom filter layer is sequentially provided with a filter screen and a porous ceramic filter plate from bottom to top; the top filter layer is sequentially provided with a porous ceramic filter plate and a filter screen from bottom to top;
When the surface water level in the river and the lake is higher than the shallow groundwater level, the surface water seepage measurement firstly passes through submerged plants, and under the action of the submerged plants with good absorption effect on nitrogen and arsenic, part of pollutants are removed, and microorganisms attached to plant root systems can also degrade organic pollutants, nitrify and denitrify the surface water and adsorb phosphorus, so that the water quality purification efficiency is improved;
then, the surface water is measured and oozed and passes through the top filtering layer, and the filter screen can intercept soil carried by the soil layer and prevent the soil from blocking the filtering holes on the porous ceramic filtering bottom plate;
Then the surface water continues to be measured and permeated through the filler layer, and the first layer is a zeolite layer and a limestone layer, so that nitrogen and phosphorus in the water body can be effectively adsorbed; the second layer is a biochar layer, so that on one hand, pollutants can be directly adsorbed, on the other hand, the growth of plants can be obviously promoted, the capturing capacity of organic matters, nitrogen and phosphorus is improved, and the removal of the pollutants is enhanced; the third layer is an active alumina layer which can effectively adsorb fluorine in the water body; meanwhile, the existence of the filler provides a stable environment for the survival and propagation of microorganisms, and the microorganisms can convert pollutants in the water body into gas or non-toxic and harmless substances through metabolic activities so as to accelerate the purification of the water body;
Finally, the water body passes through the bottom filter layer again, and the surface water quality purification is realized in the process of supplementing the surface water with the underground water;
when the groundwater level is higher than the surface water level, the groundwater is used for measuring and percolating to supply the surface water; the groundwater also passes through the bottom filter layer in the seepage measurement process, and the carried soil and large particulate matters are filtered; then sequentially passing through an active alumina layer, a biochar layer, a zeolite and lime layer and a top filter layer above, and finally passing through a planting layer to finish the supply of surface water and remove nitrogen, phosphorus, arsenic and fluorine pollutants in the groundwater in the process;
The filter screen is formed by processing a stainless steel screen, and the aperture is 30-50 mm; the density of the holes of the porous ceramic filter plate is 7-13/25.4 mm;
The thickness of the active alumina layer is 15-20 cm, and the particle size of the active alumina is 5-15 mm;
the thickness of the biochar layer is 20-30 cm, and the particle size of the biochar is 15-30 mm.
2. The in situ ecological restoration structure for surface water and groundwater according to claim 1, wherein: the thickness of the zeolite and the limestone layer is 15-20 cm, the particle size of the zeolite and the limestone is 30-50 mm, and the ratio of the zeolite to the limestone layer is 1:1.
3. The in situ ecological restoration structure for surface water and groundwater according to claim 1, wherein: the submerged plants adopt one or a combination of more plants with better effect of removing nitrogen and arsenic in water.
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CN114933393B true CN114933393B (en) | 2024-04-30 |
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Citations (9)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
AT93349B (en) * | 1922-01-05 | 1923-06-25 | Alexander Ferguson | Apparatus for making hollow objects from glass. |
CN102267762A (en) * | 2011-07-12 | 2011-12-07 | 天津城市建设学院 | Intermittent water seepage type salt-alkali resistant plant-soil ecological filter bed |
CN202131155U (en) * | 2011-05-04 | 2012-02-01 | 中国海洋大学 | Horizontal subsurface constructed wetland for dealing with polluted river water and low-concentration sewage |
CN103894124A (en) * | 2012-12-27 | 2014-07-02 | 天津滨海长源化工有限公司 | Filler tower |
CN105251251A (en) * | 2015-10-23 | 2016-01-20 | 四川聚豪生物科技有限公司 | Filter with arsenic removal and fluoride removal functions and manufacturing method |
CN109160690A (en) * | 2018-09-30 | 2019-01-08 | 南京信息工程大学 | A kind of nitrate nitrogen in ground water and fluorine ion processing system and processing method |
CN209292074U (en) * | 2018-10-17 | 2019-08-23 | 深圳市万卉园景观工程有限公司 | A kind of artificial swamp structure |
CN111517470A (en) * | 2020-04-29 | 2020-08-11 | 水利部交通运输部国家能源局南京水利科学研究院 | Anti-clogging efficient nitrogen and phosphorus removal constructed wetland substrate, constructed wetland and method |
CN113152354A (en) * | 2021-02-08 | 2021-07-23 | 广州市市政工程设计研究总院有限公司 | Structure and method for pre-positioned in-situ water ecological restoration of tidal river reach |
-
2022
- 2022-05-24 CN CN202210569084.5A patent/CN114933393B/en active Active
Patent Citations (9)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
AT93349B (en) * | 1922-01-05 | 1923-06-25 | Alexander Ferguson | Apparatus for making hollow objects from glass. |
CN202131155U (en) * | 2011-05-04 | 2012-02-01 | 中国海洋大学 | Horizontal subsurface constructed wetland for dealing with polluted river water and low-concentration sewage |
CN102267762A (en) * | 2011-07-12 | 2011-12-07 | 天津城市建设学院 | Intermittent water seepage type salt-alkali resistant plant-soil ecological filter bed |
CN103894124A (en) * | 2012-12-27 | 2014-07-02 | 天津滨海长源化工有限公司 | Filler tower |
CN105251251A (en) * | 2015-10-23 | 2016-01-20 | 四川聚豪生物科技有限公司 | Filter with arsenic removal and fluoride removal functions and manufacturing method |
CN109160690A (en) * | 2018-09-30 | 2019-01-08 | 南京信息工程大学 | A kind of nitrate nitrogen in ground water and fluorine ion processing system and processing method |
CN209292074U (en) * | 2018-10-17 | 2019-08-23 | 深圳市万卉园景观工程有限公司 | A kind of artificial swamp structure |
CN111517470A (en) * | 2020-04-29 | 2020-08-11 | 水利部交通运输部国家能源局南京水利科学研究院 | Anti-clogging efficient nitrogen and phosphorus removal constructed wetland substrate, constructed wetland and method |
CN113152354A (en) * | 2021-02-08 | 2021-07-23 | 广州市市政工程设计研究总院有限公司 | Structure and method for pre-positioned in-situ water ecological restoration of tidal river reach |
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