CN109607978A - A kind of processing method for river water pollution - Google Patents

A kind of processing method for river water pollution Download PDF

Info

Publication number
CN109607978A
CN109607978A CN201910065185.7A CN201910065185A CN109607978A CN 109607978 A CN109607978 A CN 109607978A CN 201910065185 A CN201910065185 A CN 201910065185A CN 109607978 A CN109607978 A CN 109607978A
Authority
CN
China
Prior art keywords
river
water
heavy metal
processing method
pick
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.)
Pending
Application number
CN201910065185.7A
Other languages
Chinese (zh)
Inventor
侯萍
Current Assignee (The listed assignees may be inaccurate. Google has not performed a legal analysis and makes no representation or warranty as to the accuracy of the list.)
Individual
Original Assignee
Individual
Priority date (The priority date 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 date listed.)
Filing date
Publication date
Application filed by Individual filed Critical Individual
Priority to CN201910065185.7A priority Critical patent/CN109607978A/en
Publication of CN109607978A publication Critical patent/CN109607978A/en
Pending legal-status Critical Current

Links

Classifications

    • 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
    • EFIXED CONSTRUCTIONS
    • E02HYDRAULIC ENGINEERING; FOUNDATIONS; SOIL SHIFTING
    • E02BHYDRAULIC ENGINEERING
    • E02B15/00Cleaning or keeping clear the surface of open water; Apparatus therefor
    • E02B15/04Devices for cleaning or keeping clear the surface of open water from oil or like floating materials by separating or removing these materials
    • E02B15/10Devices for removing the material from the surface
    • 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
    • C02F1/52Treatment of water, waste water, or sewage by flocculation or precipitation of suspended impurities
    • 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
    • C02F1/58Treatment of water, waste water, or sewage by removing specified dissolved compounds
    • C02F1/62Heavy metal compounds
    • 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
    • C02F2101/105Phosphorus compounds
    • 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
    • C02F2101/00Nature of the contaminant
    • C02F2101/10Inorganic compounds
    • C02F2101/20Heavy metals or heavy metal compounds
    • 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
    • C02F2209/00Controlling or monitoring parameters in water treatment
    • C02F2209/06Controlling or monitoring parameters in water treatment pH
    • CCHEMISTRY; METALLURGY
    • C02TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02FTREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02F2209/00Controlling or monitoring parameters in water treatment
    • C02F2209/22O2
    • CCHEMISTRY; METALLURGY
    • C02TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02FTREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02F2303/00Specific treatment goals
    • C02F2303/02Odour removal or prevention of malodour
    • 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
    • C02F3/327Biological treatment of water, waste water, or sewage characterised by the animals or plants used, e.g. algae characterised by animals and plants
    • CCHEMISTRY; METALLURGY
    • C02TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02FTREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02F7/00Aeration of stretches of water
    • 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
    • Y02ATECHNOLOGIES FOR ADAPTATION TO CLIMATE CHANGE
    • Y02A20/00Water conservation; Efficient water supply; Efficient water use
    • Y02A20/40Protecting water resources
    • Y02A20/402River restoration

Abstract

The invention discloses a kind of processing methods for river water pollution, the specific steps are as follows: mechanical algae removement: the pollutants such as algae generated using pick-up boat to river surface eutrophication are crushed, are salvaged, and provide route for pick-up boat traveling.A kind of processing method for river water pollution of the present invention, alkaline matter is added when overturning to mud, heavy metal will form silicate under higher pH environment, carbonate, hydroxide slightly solubility sediment, heavy metal can be inhibited to enter water body with solubilised state, it is capable of increasing the precipitation process to heavy metal in river, efficiently mix with the mud after overturning and increases deposition efficiency, flocculation sedimentation is carried out after the completion of heavy metal precipitation, it can effectively be flocculated to the muddiness generated is salvaged, and the alkaline matter that precipitated metal is added neutralizes, flocculation sedimentation is for controlling the endogenous phosphorus load of polluted river, the especially phosphorus release of bed mud in river, there is certain effect, bring better prospect of the application.

Description

A kind of processing method for river water pollution
Technical field
The present invention relates to the invention of water pollution processing method, improve water pollution process field traditionally, in particular to one Kind is used for the processing method of river water pollution.
Background technique
The range and transmission capacity of water resource pollution in river due to river, it is easy to regional water environment be caused to dislike Change, in turn result in the Arrested Development of social economy, brings long-term negative effect to local investment environment, water pollution can be to me Living environment cause directly to endanger, insulting health, a kind of water medium extremely wide as spread scope, water pollution is also The relay that can cause a variety of communicable diseases, it is also very big for the harm at water source, water quality, therefore, the water pollution in river for The economic development in China and Social Ecology improvement suffer from very crucial effect, have properly renovated river water pollution problems not It is only capable of promoting the urbanization process in China, moreover it is possible to play huge facilitation to the improvement of China's mode of economic development;
The processing method of existing river water pollution there are limitation, is unable to reach effectively the processing of heavy metal in river Processing, rubbish are easy to cause mud intrinsic heavy metal to enter water body with solubilised state when salvaging, aggravate water pollution, for this purpose, we It is proposed a kind of processing method for river water pollution.
Summary of the invention
The main purpose of the present invention is to provide a kind of processing methods for river water pollution, can effectively solve background The problems in technology.
To achieve the above object, the technical scheme adopted by the invention is as follows:
A kind of processing method for river water pollution, the specific steps are as follows:
(1) mechanical algae removement: the pollutants such as algae generated using pick-up boat to river surface eutrophication are crushed, are salvaged, Route is provided for pick-up boat traveling;
(2) river pollutants salvaging and heavy metal precipitation: after the completion of removing algae in step (1), using pick-up boat to river bed The pollutants such as rubbish are salvaged, and are overturn to mud, add alkaline matter into river water in switching process, by mud PH control in 7-8, heavy metal can be inhibited to enter water body with solubilised state;
(3) it flocculation sedimentation: adds in the river water in step (2) after heavy metal precipitation and is polluted in coagulant removal water body Object, to reach improvement water quality;
(4) river surface is cleared up: in step (3) after the completion of flocculation sedimentation, using pick-up boat to river surface because salvaging the rubbish generated The pollutants such as rubbish are cleared up, and river water light transmission 1-1.5m is kept;
(5) watercourse aeration: it is passed through aerator in the river in step (4) after river surface cleaning, from atmosphere into water body Diffusion dissolution oxygen, water body watercourse aeration make river channel ecology system be restored to normal condition;
(6) animals and plants are introduced into: planting plants, introduction aquatic animal in the river in step (5) after the completion of watercourse aeration, A variety of water plants have good removal effect to phosphorus and nitrogen, introduce the indigenous type to have disappeared again, make biological species Group's diversification.
Preferably, strainer is installed on pick-up boat when mechanical algae removement in the step (1), to the bulky grain rubbish of river surface It is collected, strainer mesh number is 2-4 mesh.
Preferably, step (2) the neutral and alkali substance includes one of lime, calcium silicate slag or steel slag or a variety of, Heavy metal will form silicate, carbonate, hydroxide slightly solubility sediment under higher pH environment, but control alkalinity The dosage of substance.
Preferably, in the step (3) coagulant include ferrous sulfate, it is frerrous chloride, aluminum sulfate, aluminium chloride, bright One of alum, polyacrylamide and Sodium Polyacrylate are a variety of, flocculation sedimentation 3-4h.
Preferably, the dosage of each component is respectively ferrous sulfate 80-100mg/L, chlorination in coagulant in the step (3) Ferrous 50-70mg/L, aluminum sulfate 50-100mg/L, aluminium chloride 30-60mg/L, alum 100-150mg/L, polyacrylamide 100-120mg/L and Sodium Polyacrylate 120-140mg/L, the above are dosages when general turbidity, and water is more muddy, coagulant Dosage should be bigger, but to control dosage of PAC.
Preferably, filter cloth is installed on pick-up boat when river surface is cleared up in the step (4), to the little particle rubbish of river surface It is collected, the mesh number of filter cloth is 30-35 mesh.
Preferably, watercourse aeration working principle in the step (5) are as follows: between the dissolved oxygen and black sordes matter of water body Redox reaction has occurred, black sordes matter is H2S, FeS has the substance of reproducibility.
Preferably, water plant includes: duckweed, Eichhornia crassipes, Azolla imbricata, Chinese scholartree Ye Ping, hornwort, fringe in the step (6) Flower watermifoil, potamogeton malaianus, water caltrop, eel grass and water quality grass, can effectively absorb nitrogen, the phosphorus in water body, reduce the richness of water body Nutrient laden is horizontal.
Compared with prior art, the invention has the following beneficial effects:
1, alkaline matter is added when overturning to mud, heavy metal will form silicate, carbon under higher pH environment Hydrochlorate, hydroxide slightly solubility sediment, can inhibit heavy metal to enter water body with solubilised state, be capable of increasing to a huge sum of money in river The precipitation process of category carries out efficiently mixing increase deposition efficiency with the mud after overturning, while controlling alkaline matter dosage and keeping away Exempt to cause secondary pollution;
2, flocculation sedimentation is carried out after the completion of heavy metal precipitation, can effectively be flocculated to the muddiness generated is salvaged, and The alkaline matter that precipitated metal is added neutralizes, and flocculation sedimentation is for controlling the endogenous phosphorus load of polluted river, especially river The phosphorus release for flowing bed mud, there is certain effect.
Detailed description of the invention
Fig. 1 is a kind of method flow diagram of the processing method for river water pollution of the present invention.
Specific embodiment
To be easy to understand the technical means, the creative features, the aims and the efficiencies achieved by the present invention, below with reference to Specific embodiment, the present invention is further explained.
Embodiment 1
(1) mechanical algae removement: the pollutants such as algae generated using pick-up boat to river surface eutrophication are crushed, are salvaged, Route is provided for pick-up boat traveling, and when mechanical algae removement is equipped with strainer on pick-up boat, receives to the bulky grain rubbish of river surface Collection, strainer mesh number are 2 mesh;
(2) river pollutants salvaging and heavy metal precipitation: after the completion of removing algae in step (1), using pick-up boat to river bed The pollutants such as rubbish are salvaged, and are overturn to mud, add alkaline matter into river water in switching process, by mud PH control 7, heavy metal can be inhibited to enter water body with solubilised state, alkaline matter includes lime, calcium silicate slag or steel slag One of or it is a variety of, heavy metal will form silicate, carbonate, hydroxide slightly solubility sediment under higher pH environment, But to control the dosage of alkaline matter;
(3) it flocculation sedimentation: adds in the river water in step (2) after heavy metal precipitation and is polluted in coagulant removal water body Object, to reach improvement water quality, coagulant includes ferrous sulfate, frerrous chloride, aluminum sulfate, aluminium chloride, alum, polyacrylamide One of amine and Sodium Polyacrylate are a variety of, flocculation sedimentation 3h, and the dosage of each component is respectively ferrous sulfate in coagulant 80mg/L, frerrous chloride 50mg/L, aluminum sulfate 50mg/L, aluminium chloride 30mg/L, alum 100mg/L, polyacrylamide 100mg/L and Sodium Polyacrylate 120mg/L, the above are dosages when general turbidity, and water is more muddy, and the dosage of coagulant should be cured Greatly, but dosage of PAC is controlled;
(4) river surface is cleared up: in step (3) after the completion of flocculation sedimentation, using pick-up boat to river surface because salvaging the rubbish generated The pollutants such as rubbish are cleared up, and keep river water light transmission 1m, river surface is equipped with filter cloth when clearing up on pick-up boat, to small of river surface Grain rubbish is collected, and the mesh number of filter cloth is 30 mesh;
(5) watercourse aeration: it is passed through aerator in the river in step (4) after river surface cleaning, from atmosphere into water body Diffusion dissolution oxygen, water body watercourse aeration make river channel ecology system be restored to normal condition, watercourse aeration working principle are as follows: enter water Redox reaction has occurred between the dissolved oxygen of body and black sordes matter, black sordes matter is H2S, FeS has the substance of reproducibility;
(6) animals and plants are introduced into: planting plants, introduction aquatic animal in the river in step (5) after the completion of watercourse aeration, A variety of water plants have good removal effect to phosphorus and nitrogen, introduce the indigenous type to have disappeared again, make biological species Group diversification, water plant include: duckweed, Eichhornia crassipes, Azolla imbricata, Chinese scholartree Ye Ping, hornwort, Haloragidaceae Myriophyllum spicatum, potamogeton malaianus, Water caltrop, eel grass and water quality grass, can effectively absorb nitrogen, the phosphorus in water body, reduce the eutrophication of water body.
Embodiment 2
(1) mechanical algae removement: the pollutants such as algae generated using pick-up boat to river surface eutrophication are crushed, are salvaged, Route is provided for pick-up boat traveling, and when mechanical algae removement is equipped with strainer on pick-up boat, receives to the bulky grain rubbish of river surface Collection, strainer mesh number are 3 mesh;
(2) river pollutants salvaging and heavy metal precipitation: after the completion of removing algae in step (1), using pick-up boat to river bed The pollutants such as rubbish are salvaged, and are overturn to mud, add alkaline matter into river water in switching process, by mud PH control 7, heavy metal can be inhibited to enter water body with solubilised state, alkaline matter includes lime, calcium silicate slag or steel slag One of or it is a variety of, heavy metal will form silicate, carbonate, hydroxide slightly solubility sediment under higher pH environment, But to control the dosage of alkaline matter;
(3) it flocculation sedimentation: adds in the river water in step (2) after heavy metal precipitation and is polluted in coagulant removal water body Object, to reach improvement water quality, coagulant includes ferrous sulfate, frerrous chloride, aluminum sulfate, aluminium chloride, alum, polyacrylamide One of amine and Sodium Polyacrylate are a variety of, flocculation sedimentation 3.5h, and the dosage of each component is respectively ferrous sulfate in coagulant 90mg/L, frerrous chloride 60mg/L, aluminum sulfate 75mg/L, aluminium chloride 45mg/L, alum 125mg/L, polyacrylamide 110mg/L and Sodium Polyacrylate 130mg/L, the above are dosages when general turbidity, and water is more muddy, and the dosage of coagulant should be cured Greatly, but dosage of PAC is controlled;
(4) river surface is cleared up: in step (3) after the completion of flocculation sedimentation, using pick-up boat to river surface because salvaging the rubbish generated The pollutants such as rubbish are cleared up, and keep river water light transmission 1.3m, river surface is equipped with filter cloth when clearing up on pick-up boat, to the small of river surface Particle rubbish is collected, and the mesh number of filter cloth is 32 mesh;
(5) watercourse aeration: it is passed through aerator in the river in step (4) after river surface cleaning, from atmosphere into water body Diffusion dissolution oxygen, water body watercourse aeration make river channel ecology system be restored to normal condition, watercourse aeration working principle are as follows: enter water Redox reaction has occurred between the dissolved oxygen of body and black sordes matter, black sordes matter is H2S, FeS has the substance of reproducibility;
(6) animals and plants are introduced into: planting plants, introduction aquatic animal in the river in step (5) after the completion of watercourse aeration, A variety of water plants have good removal effect to phosphorus and nitrogen, introduce the indigenous type to have disappeared again, make biological species Group diversification, water plant include: duckweed, Eichhornia crassipes, Azolla imbricata, Chinese scholartree Ye Ping, hornwort, Haloragidaceae Myriophyllum spicatum, potamogeton malaianus, Water caltrop, eel grass and water quality grass, can effectively absorb nitrogen, the phosphorus in water body, reduce the eutrophication of water body.
Embodiment 3
(1) mechanical algae removement: the pollutants such as algae generated using pick-up boat to river surface eutrophication are crushed, are salvaged, Route is provided for pick-up boat traveling, and when mechanical algae removement is equipped with strainer on pick-up boat, receives to the bulky grain rubbish of river surface Collection, strainer mesh number are 4 mesh;
(2) river pollutants salvaging and heavy metal precipitation: after the completion of removing algae in step (1), using pick-up boat to river bed The pollutants such as rubbish are salvaged, and are overturn to mud, add alkaline matter into river water in switching process, by mud PH control 8, heavy metal can be inhibited to enter water body with solubilised state, alkaline matter includes lime, calcium silicate slag or steel slag One of or it is a variety of, heavy metal will form silicate, carbonate, hydroxide slightly solubility sediment under higher pH environment, But to control the dosage of alkaline matter;
(3) it flocculation sedimentation: adds in the river water in step (2) after heavy metal precipitation and is polluted in coagulant removal water body Object, to reach improvement water quality, coagulant includes ferrous sulfate, frerrous chloride, aluminum sulfate, aluminium chloride, alum, polyacrylamide One of amine and Sodium Polyacrylate are a variety of, flocculation sedimentation 4h, and the dosage of each component is respectively ferrous sulfate in coagulant 100mg/L, frerrous chloride 70mg/L, aluminum sulfate 100mg/L, aluminium chloride 60mg/L, alum 150mg/L, polyacrylamide 120mg/L and Sodium Polyacrylate 140mg/L, the above are dosages when general turbidity, and water is more muddy, and the dosage of coagulant should be cured Greatly, but dosage of PAC is controlled;
(4) river surface is cleared up: in step (3) after the completion of flocculation sedimentation, using pick-up boat to river surface because salvaging the rubbish generated The pollutants such as rubbish are cleared up, and keep river water light transmission 1.5m, river surface is equipped with filter cloth when clearing up on pick-up boat, to the small of river surface Particle rubbish is collected, and the mesh number of filter cloth is 35 mesh;
(5) watercourse aeration: it is passed through aerator in the river in step (4) after river surface cleaning, from atmosphere into water body Diffusion dissolution oxygen, water body watercourse aeration make river channel ecology system be restored to normal condition, watercourse aeration working principle are as follows: enter water Redox reaction has occurred between the dissolved oxygen of body and black sordes matter, black sordes matter is H2S, FeS has the substance of reproducibility;
(6) animals and plants are introduced into: planting plants, introduction aquatic animal in the river in step (5) after the completion of watercourse aeration, A variety of water plants have good removal effect to phosphorus and nitrogen, introduce the indigenous type to have disappeared again, make biological species Group diversification, water plant include: duckweed, Eichhornia crassipes, Azolla imbricata, Chinese scholartree Ye Ping, hornwort, Haloragidaceae Myriophyllum spicatum, potamogeton malaianus, Water caltrop, eel grass and water quality grass, can effectively absorb nitrogen, the phosphorus in water body, reduce the eutrophication of water body.
Table 1 be in the processing method of the river embodiment 1-3 water pollution each data to when being examined to river course environment The data measured, comparing result such as following table (are tested three sections with river):
Three groups of embodiments known to 1 experimental data of table are handled river water pollution, and wherein embodiment 3 is optimal Selection, the processing method of river water pollution provided by the invention adds alkaline matter when overturning to mud, higher Heavy metal will form silicate, carbonate, hydroxide slightly solubility sediment under pH environment, heavy metal can be inhibited with solubilised state Into water body, it is capable of increasing the precipitation process to heavy metal in river, carries out efficiently mixing increase precipitating with the mud after overturning Efficiency, while controlling alkaline matter dosage and avoiding secondary pollution, flocculation sedimentation, energy are carried out after the completion of heavy metal precipitation It is enough effectively to be flocculated to the muddiness for salvaging generation, and the alkaline matter that precipitated metal is added neutralizes, flocculation sedimentation pair In the phosphorus release of the control endogenous phosphorus load of polluted river, especially bed mud in river, there is certain effect.
The above shows and describes the basic principles and main features of the present invention and the advantages of the present invention.The technology of the industry Personnel are it should be appreciated that the present invention is not limited to the above embodiments, and the above embodiments and description only describe this The principle of invention, without departing from the spirit and scope of the present invention, various changes and improvements may be made to the invention, these changes Change and improvement all fall within the protetion scope of the claimed invention.The claimed scope of the invention by appended claims and its Equivalent thereof.

Claims (8)

1. a kind of processing method for river water pollution, which is characterized in that specific step is as follows:
(1) mechanical algae removement: the pollutants such as algae generated using pick-up boat to river surface eutrophication are crushed, are salvaged, to beat Shipping agency is fished out into offer route;
(2) river pollutants salvaging and heavy metal precipitation: after the completion of removing algae in step (1), using pick-up boat to river bed rubbish Equal pollutants are salvaged, and are overturn to mud, alkaline matter are added into river water in switching process, by the pH of mud Control can inhibit heavy metal to enter water body with solubilised state in 7-8;
(3) flocculation sedimentation: adding pollutant in coagulant removal water body in the river water in step (2) after heavy metal precipitation, with Reach improvement water quality;
(4) river surface is cleared up: in step (3) after the completion of flocculation sedimentation, using pick-up boat to river surface because salvaging the rubbish etc. generated Pollutant is cleared up, and river water light transmission 1-1.5m is kept;
(5) watercourse aeration: it is passed through aerator in the river in step (4) after river surface cleaning, is spread from atmosphere into water body Dissolved oxygen, water body watercourse aeration make river channel ecology system be restored to normal condition;
(6) animals and plants are introduced into: planting plants, introduction aquatic animal in the river in step (5) after the completion of watercourse aeration, it is a variety of Water plant has good removal effect to phosphorus and nitrogen, introduces the indigenous type to have disappeared again, keeps biological group more Sample.
2. a kind of processing method for river water pollution according to claim 1, which is characterized in that the step (1) Strainer is installed on pick-up boat when middle mechanical algae removement, the bulky grain rubbish of river surface is collected, strainer mesh number is 2-4 mesh.
3. a kind of processing method for river water pollution according to claim 1, which is characterized in that the step (2) Neutral and alkali substance includes one of lime, calcium silicate slag or steel slag or a variety of, and heavy metal will form under higher pH environment Silicate, carbonate, hydroxide slightly solubility sediment, but to control the dosage of alkaline matter.
4. a kind of processing method for river water pollution according to claim 1, which is characterized in that the step (3) Middle coagulant includes in ferrous sulfate, frerrous chloride, aluminum sulfate, aluminium chloride, alum, polyacrylamide and Sodium Polyacrylate One or more, flocculation sedimentation 3-4h.
5. a kind of processing method for river water pollution according to claim 1, which is characterized in that the step (3) The dosage of each component is respectively ferrous sulfate 80-100mg/L, frerrous chloride 50-70mg/L, aluminum sulfate 50- in middle coagulant 100mg/L, aluminium chloride 30-60mg/L, alum 100-150mg/L, polyacrylamide 100-120mg/L and Sodium Polyacrylate 120-140mg/L, the above are dosages when general turbidity, and water is more muddy, and the dosage of coagulant should be bigger, but to control Dosage of PAC.
6. a kind of processing method for river water pollution according to claim 1, which is characterized in that the step (4) Middle river surface is equipped with filter cloth when clearing up on pick-up boat, is collected to the little particle rubbish of river surface, and the mesh number of filter cloth is 30-35 Mesh.
7. a kind of processing method for river water pollution according to claim 1, which is characterized in that the step (5) Middle watercourse aeration working principle are as follows: redox reaction, black sordes has occurred between the dissolved oxygen and black sordes matter of water body Matter is H2S, FeS has the substance of reproducibility.
8. a kind of processing method for river water pollution according to claim 1, which is characterized in that the step (6) Middle water plant includes: duckweed, Eichhornia crassipes, Azolla imbricata, Chinese scholartree Ye Ping, hornwort, Haloragidaceae Myriophyllum spicatum, potamogeton malaianus, water caltrop, hardship Grass and water quality grass, can effectively absorb nitrogen, the phosphorus in water body, reduce the eutrophication of water body.
CN201910065185.7A 2019-01-23 2019-01-23 A kind of processing method for river water pollution Pending CN109607978A (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
CN201910065185.7A CN109607978A (en) 2019-01-23 2019-01-23 A kind of processing method for river water pollution

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
CN201910065185.7A CN109607978A (en) 2019-01-23 2019-01-23 A kind of processing method for river water pollution

Publications (1)

Publication Number Publication Date
CN109607978A true CN109607978A (en) 2019-04-12

Family

ID=66017225

Family Applications (1)

Application Number Title Priority Date Filing Date
CN201910065185.7A Pending CN109607978A (en) 2019-01-23 2019-01-23 A kind of processing method for river water pollution

Country Status (1)

Country Link
CN (1) CN109607978A (en)

Cited By (2)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN110092546A (en) * 2019-05-24 2019-08-06 济南市莱芜雪野水库管理处 A kind of river regulation purification method
WO2022207006A3 (en) * 2022-04-07 2023-01-26 China Urban Construction Design & Research Institute Co., Ltd. Waterscape device capable of removing nitrogen, phosphorus and algae simultaneously and the application thereof

Citations (4)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
WO2008113840A1 (en) * 2007-03-21 2008-09-25 Omya Development Ag Surface treated calcium carbonate and its use in waste water treatment
CN104386888A (en) * 2014-06-08 2015-03-04 何晋勇 Immobilization processing method for composite heavy-metal-polluted bottom sediment
CN106277622A (en) * 2016-08-31 2017-01-04 云南能投生态环境科技有限公司 A kind of restorative procedure of body eutrophication
CN109111065A (en) * 2018-08-07 2019-01-01 上海久树环境科技有限公司 A kind of riverbed ecology synthesis restorative procedure

Patent Citations (4)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
WO2008113840A1 (en) * 2007-03-21 2008-09-25 Omya Development Ag Surface treated calcium carbonate and its use in waste water treatment
CN104386888A (en) * 2014-06-08 2015-03-04 何晋勇 Immobilization processing method for composite heavy-metal-polluted bottom sediment
CN106277622A (en) * 2016-08-31 2017-01-04 云南能投生态环境科技有限公司 A kind of restorative procedure of body eutrophication
CN109111065A (en) * 2018-08-07 2019-01-01 上海久树环境科技有限公司 A kind of riverbed ecology synthesis restorative procedure

Non-Patent Citations (2)

* Cited by examiner, † Cited by third party
Title
段云霞等: "《城市黑臭水体治理实用技术及案例分析》", 31 March 2018, 天津大学出版社 *
马兴冠等: "《辽河流域水环境突发污染事故应急处置技术与管理体系》", 30 September 2018, 辽宁科学技术出版社 *

Cited By (3)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN110092546A (en) * 2019-05-24 2019-08-06 济南市莱芜雪野水库管理处 A kind of river regulation purification method
CN110092546B (en) * 2019-05-24 2020-03-03 济南市莱芜雪野水库管理处 River channel treatment and purification method
WO2022207006A3 (en) * 2022-04-07 2023-01-26 China Urban Construction Design & Research Institute Co., Ltd. Waterscape device capable of removing nitrogen, phosphorus and algae simultaneously and the application thereof

Similar Documents

Publication Publication Date Title
CN106542701A (en) For the method for purifying water in river course
CN108325498A (en) A method of synchronizing nitrogen phosphorus in recycling waste water using magnesium hydroxide modified meerschaum
CN109607978A (en) A kind of processing method for river water pollution
CN111517562A (en) Biological flocculation technology coupled aeration algae pond sewage treatment system
CN107758763A (en) A kind of domestic sewage treating compound
CN208471811U (en) A kind of sewage disposal system
CN101444719B (en) Biosorption agent and application method thereof
CN103043868A (en) Sewage treating system and sewage treating method for river course
CN109824213A (en) A kind of urban catchments water purification system and method
CN110194532A (en) A kind of comprehensive wet land system of purification of water quality
KR101061982B1 (en) Retrofitted wastewater and sewage treatment plant for phosphorus removal
CN105668792A (en) Bio-contact oxidation filter sedimentation tank
CN108751598A (en) A kind of city domestic sewage treatment process
CN107651717A (en) A kind of sewage-treating agent
CN108059297A (en) A kind of carbon nano tube compound material sewage treatment drug and processing method
CN209113686U (en) A kind of combination unit handling hc effluent with high salt
CN209098305U (en) A kind of aeration and sedimentation integrated reacting device for spoil disposal aquatic organism oxidation demanganization
CN112125356B (en) Preparation method of light composite algaecide with dephosphorization effect and floating type algae removal method on light composite algaecide
CN105936519A (en) Water treatment agent
CN208843882U (en) Thermal power plant's water resource optimization based on water balance utilizes system
CN208413999U (en) A kind of device suitable for high rigidity wastewater hardness removing
CN207552128U (en) A kind of device of integrated membrane process hydridization removal low concentration selenium-containing wastewater
CN206089376U (en) Black and odorous water body treatment system
KR100292975B1 (en) Coagulant composition manufactured with fly ash from power plant using coal
CN212954612U (en) Algae-based water treatment device

Legal Events

Date Code Title Description
PB01 Publication
PB01 Publication
SE01 Entry into force of request for substantive examination
SE01 Entry into force of request for substantive examination
RJ01 Rejection of invention patent application after publication
RJ01 Rejection of invention patent application after publication

Application publication date: 20190412