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 PDF

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Publication number
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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layer
water
surface water
ecological restoration
groundwater
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CN114933393A (en
Inventor
周国旺
关永发
潘乘浪
康雅茹
钱爱国
宋思远
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PowerChina Huadong Engineering Corp Ltd
PowerChina East China Engineering Zhengzhou Corp Ltd
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PowerChina Huadong Engineering Corp Ltd
PowerChina East China Engineering Zhengzhou Corp Ltd
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    • CCHEMISTRY; METALLURGY
    • C02TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02FTREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02F9/00Multistage treatment of water, waste water or sewage
    • CCHEMISTRY; METALLURGY
    • C02TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02FTREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02F1/00Treatment of water, waste water, or sewage
    • C02F1/001Processes for the treatment of water whereby the filtration technique is of importance
    • CCHEMISTRY; METALLURGY
    • C02TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02FTREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02F1/00Treatment of water, waste water, or sewage
    • C02F1/28Treatment of water, waste water, or sewage by sorption
    • C02F1/281Treatment of water, waste water, or sewage by sorption using inorganic sorbents
    • CCHEMISTRY; METALLURGY
    • C02TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02FTREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02F1/00Treatment of water, waste water, or sewage
    • C02F1/28Treatment of water, waste water, or sewage by sorption
    • C02F1/283Treatment of water, waste water, or sewage by sorption using coal, charred products, or inorganic mixtures containing them
    • 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
    • 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
    • C02F2103/06Contaminated groundwater or leachate
    • 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
    • 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)
  • 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

In-situ ecological restoration structure for surface water and underground water
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.
CN202210569084.5A 2022-05-24 2022-05-24 In-situ ecological restoration structure for surface water and underground water Active CN114933393B (en)

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Citations (9)

* Cited by examiner, † Cited by third party
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

Patent Citations (9)

* Cited by examiner, † Cited by third party
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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