CN108911298A - A kind of sewage water treatment method - Google Patents
A kind of sewage water treatment method Download PDFInfo
- Publication number
- CN108911298A CN108911298A CN201811123728.8A CN201811123728A CN108911298A CN 108911298 A CN108911298 A CN 108911298A CN 201811123728 A CN201811123728 A CN 201811123728A CN 108911298 A CN108911298 A CN 108911298A
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- China
- Prior art keywords
- water
- parts
- sewage
- added
- fence
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- 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.)
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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
- C02F1/46—Treatment of water, waste water, or sewage by electrochemical methods
- C02F1/4608—Treatment of water, waste water, or sewage by electrochemical methods using electrical discharges
-
- 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
- C02F1/50—Treatment of water, waste water, or sewage by addition or application of a germicide or by oligodynamic treatment
-
- 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
- C02F1/52—Treatment of water, waste water, or sewage by flocculation or precipitation of suspended impurities
-
- 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
- C02F1/52—Treatment of water, waste water, or sewage by flocculation or precipitation of suspended impurities
- C02F1/5236—Treatment of water, waste water, or sewage by flocculation or precipitation of suspended impurities using inorganic agents
-
- 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
- C02F1/52—Treatment of water, waste water, or sewage by flocculation or precipitation of suspended impurities
- C02F1/5236—Treatment of water, waste water, or sewage by flocculation or precipitation of suspended impurities using inorganic agents
- C02F1/5245—Treatment of water, waste water, or sewage by flocculation or precipitation of suspended impurities using inorganic agents using basic salts, e.g. of aluminium and iron
-
- 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
- C02F1/52—Treatment of water, waste water, or sewage by flocculation or precipitation of suspended impurities
- C02F1/54—Treatment of water, waste water, or sewage by flocculation or precipitation of suspended impurities using organic material
- C02F1/56—Macromolecular compounds
-
- 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
- C02F1/72—Treatment of water, waste water, or sewage by oxidation
- C02F1/722—Oxidation by peroxides
-
- 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
- C02F1/72—Treatment of water, waste water, or sewage by oxidation
- C02F1/78—Treatment of water, waste water, or sewage by oxidation with ozone
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)
- Separation Of Suspended Particles By Flocculating Agents (AREA)
Abstract
The present invention relates to a kind of environment-protective process more particularly to a kind of sewage water treatment methods.A kind of sewage water treatment method, includes the following steps：1. sewage is filtered by fence, then passes to settling pit desilting, sedimentation basin is entered back into；2. precipitate in water is fallen, upper layer clear water enters next step after flocculant is added in sedimentation basin；3. by oxidant is added in the water after precipitating；4. disinfectant is added in water；5. clear water can be used by obtaining after being filtered by ceramic filter plate；6. being fabricated to building ceramsite after directly adding the additives such as coal ash powder after the generation filtrate in the above process, sediment are mixed.The present invention can deal with the water condition of the various complexity in municipal sewage, the industrial water that can be used, and the waste that sewage treatment generates can be turned waste into wealth, and have good economic value and the value of environmental protection.
Description
Technical field
The present invention relates to a kind of environment-protective process more particularly to a kind of sewage water treatment methods.
Background technique
For municipal sewage due to complicated component, processing difficulty is larger, and the waste of treated solid or semisolid is still
It so is difficult to handle, present method is landfill, but landfill is at high cost, then how to invent a kind of sewage water treatment method, both may be used
Relatively perfectly to handle sewage, while the waste that sewage treatment generates can be turned waste into wealth, exactly inventor will solve
The problem of.
Summary of the invention
The present invention solves above-mentioned problem, and sewage can preferably be handled by providing one kind, and can be by sewage treatment
The sewage treatment process that the waste of generation is turned waste into wealth, specific technical solution are as follows：
A kind of sewage water treatment method, includes the following steps：
1. sewage is filtered by fence, then passes to settling pit desilting, sedimentation basin is entered back into；
2. precipitate in water is fallen, upper layer clear water enters next step after flocculant is added in sedimentation basin；
3. by oxidant is added in the water after precipitating；
4. disinfectant is added in water；
5. clear water can be used by obtaining after being filtered by ceramic filter plate；
6. being fabricated to after directly adding the additives such as coal ash powder after the generation filtrate in the above process, sediment are mixed
Building ceramsite.
The clear water of above step production can be used directly as industrial water, and pottery for building is made in filtrate, sediment
Do not have to the problems such as worrying landfill place after grain, cement consumption can be saved instead, turned waste into wealth.
Preferably, the step 1. in fence be followed successively by thick fence, thin fence, metal mesh, lead on the metal mesh
Precipitation by metallic ion and partial organic substances can be electrolysed by electricity with killing small-sized biological such as small fish etc..
The step 2. in flocculant and its application method be：It is by weight percentage by raw material：Polystyrene amide 4
Part, 1 part of polycarbonate, 1 part of aluminium polychloride, 4~8 parts of ferric sulfate, 4~6 parts of iron chloride, 8~10 parts of inorganic salts, active carbon 3
~5 parts, 50~70 parts of bentonite, 3 parts of zinc oxide, 8~10 parts of ethyl alcohol, be heated up to after the mixing of the raw material that 18~22 part of water 50 °~
55 ° of interval ranges, and stirring always one hour, then put into catalyst reaction one hour, by the dry materials, broken after reaction
After broken, sieving, flocculant particle is obtained, then flocculant particle is sprinkled into water.This flocculant is easy to use, and can
To adapt to complicated water condition.
Preferably, the step 3. in oxidant be hydrogen peroxide and ozone.
Preferably, the step 4. in disinfectant be chlorine.
Preferably, the step 5. in ceramic filter plate be ceramic filter plate that capillary aperture is 10~20 microns.
Preferably, the step 6. the specific steps are：By weight percentage, by 30%~60% filtrate, sediment
Product mix mixes aluminium slag powder 3~7%, and industrial flyash 30~50%, desulfurized gypsum 5~10%, white lime is 1~3%, three
The sum of weight percent of 1~3% the above components of ethanol amine is 100%, and various raw material mix in proportion, are then fed into
Ball machine balling-up, then shell adding, at normal temperature, the maintenance of relative humidity 90% or so 5 days or more are finished product to resulting haydite.
The present invention can deal with the water condition of the various complexity in municipal sewage, the industrial water that can be used,
And the waste that sewage treatment generates can be turned waste into wealth, there is good economic value and the value of environmental protection.
Specific embodiment
Embodiment 1
The embodiment of the present invention 1 is described in further detail below：
A kind of sewage water treatment method, includes the following steps：
1. sewage is filtered by fence, then passes to settling pit desilting, sedimentation basin is entered back into；
2. precipitate in water is fallen, upper layer clear water enters next step after flocculant is added in sedimentation basin；
3. by oxidant is added in the water after precipitating；
4. disinfectant is added in water；
5. clear water can be used by obtaining after being filtered by ceramic filter plate；
6. being fabricated to after directly adding the additives such as coal ash powder after the generation filtrate in the above process, sediment are mixed
Building ceramsite.
The step 1. in fence be followed successively by thick fence, thin fence, metal mesh, be powered on the metal mesh small to kill
Type biology such as small fish etc., and can be electrolysed by precipitation by metallic ion and by partial organic substances.
The step 2. in flocculant and its application method be：It is by weight percentage by raw material：Polystyrene amide 4
Part, 1 part of polycarbonate, 1 part of aluminium polychloride, 4~8 parts of ferric sulfate, 4~6 parts of iron chloride, 8~10 parts of inorganic salts, active carbon 3
~5 parts, 50~70 parts of bentonite, 3 parts of zinc oxide, 8~10 parts of ethyl alcohol, be heated up to after the mixing of the raw material that 18~22 part of water 50 °~
55 ° of interval ranges, and stirring always one hour, then put into catalyst reaction one hour, by the dry materials, broken after reaction
After broken, sieving, flocculant particle is obtained, then flocculant particle is sprinkled into water.
The step 3. in oxidant be hydrogen peroxide and ozone.
The step 4. in disinfectant be chlorine.
The step 5. in ceramic filter plate be ceramic filter plate that capillary aperture is 10~20 microns.
The step 6. the specific steps are：By weight percentage, 30%~60% filtrate, sediment product mix are mixed
Entering aluminium slag powder 3~7%, industrial flyash 30~50%, desulfurized gypsum 5~10%, white lime is 1~3%, triethanolamine 1~
The sum of weight percent of 3% the above components is 100%, and various raw material mix in proportion, is then fed into formed by balling machine,
Shell adding again, at normal temperature, the maintenance of relative humidity 90% or so 5 days or more are finished product to resulting haydite.
It is emphasized that:The above is only presently preferred embodiments of the present invention, not do in any form to the present invention
Limitation, any simple modification, equivalent change and modification that above embodiments are done according to the technical essence of the invention,
It still falls within protection category of the present invention.
Claims (3)
1. a kind of sewage water treatment method, which is characterized in that include the following steps：
1. sewage is filtered by fence, then passes to settling pit desilting, sedimentation basin is entered back into；
2. precipitate in water is fallen, upper layer clear water enters next step after flocculant is added in sedimentation basin；
3. by oxidant is added in the water after precipitating；
4. disinfectant is added in water；
5. clear water can be used by obtaining after being filtered by ceramic filter plate；
6. being fabricated to building after directly adding the additives such as coal ash powder after the generation filtrate in the above process, sediment are mixed
Use haydite.
2. a kind of sewage water treatment method according to claim 1, which is characterized in that the step 1. in fence be followed successively by
Thick fence, thin fence, metal mesh are powered to kill small-sized biological such as small fish etc. on the metal mesh, and metal ion can sink
It forms sediment and is electrolysed partial organic substances.
3. a kind of sewage water treatment method according to claim 1, which is characterized in that the step 2. in flocculant and its
Application method is：It is by weight percentage by raw material：4 parts of polystyrene amide, 1 part of polycarbonate, 1 part of aluminium polychloride, sulphur
4~8 parts of sour iron, 4~6 parts of iron chloride, 8~10 parts of inorganic salts, 3~5 parts of active carbon, 50~70 parts of bentonite, 3 parts of zinc oxide,
8~10 parts of ethyl alcohol, 50 °~55 ° interval ranges are heated up to after the raw material mixing that 18~22 parts of water, and stir one hour always,
Then put into catalyst reaction one hour, by after reaction dry materials, after broken, sieving, obtain flocculant particle, then will
Flocculant particle is sprinkled into water.
Priority Applications (1)
| Application Number | Priority Date | Filing Date | Title |
|---|---|---|---|
| CN201811123728.8A CN108911298A (en) | 2018-09-26 | 2018-09-26 | A kind of sewage water treatment method |
Applications Claiming Priority (1)
| Application Number | Priority Date | Filing Date | Title |
|---|---|---|---|
| CN201811123728.8A CN108911298A (en) | 2018-09-26 | 2018-09-26 | A kind of sewage water treatment method |
Publications (1)
| Publication Number | Publication Date |
|---|---|
| CN108911298A true CN108911298A (en) | 2018-11-30 |
Family
ID=64409161
Family Applications (1)
| Application Number | Title | Priority Date | Filing Date |
|---|---|---|---|
| CN201811123728.8A Withdrawn CN108911298A (en) | 2018-09-26 | 2018-09-26 | A kind of sewage water treatment method |
Country Status (1)
| Country | Link |
|---|---|
| CN (1) | CN108911298A (en) |
Cited By (1)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| CN110937741A (en) * | 2019-11-13 | 2020-03-31 | 西安重光明宸检测技术有限公司 | Sewage treatment method |
-
2018
- 2018-09-26 CN CN201811123728.8A patent/CN108911298A/en not_active Withdrawn
Cited By (1)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| CN110937741A (en) * | 2019-11-13 | 2020-03-31 | 西安重光明宸检测技术有限公司 | Sewage treatment method |
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| PB01 | Publication | ||
| PB01 | Publication | ||
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| WW01 | Invention patent application withdrawn after publication | ||
| WW01 | Invention patent application withdrawn after publication |
Application publication date: 20181130 |