CN105948324A - Method for removing arsenic in sewage - Google Patents
Method for removing arsenic in sewage Download PDFInfo
- Publication number
- CN105948324A CN105948324A CN201610464041.5A CN201610464041A CN105948324A CN 105948324 A CN105948324 A CN 105948324A CN 201610464041 A CN201610464041 A CN 201610464041A CN 105948324 A CN105948324 A CN 105948324A
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- CN
- China
- Prior art keywords
- sewage
- parts
- supernatant
- arsenic
- water
- 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.)
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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
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- 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
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- 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
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- 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
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- 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
- C02F1/66—Treatment of water, waste water, or sewage by neutralisation; pH adjustment
-
- C—CHEMISTRY; METALLURGY
- C02—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F2101/00—Nature of the contaminant
- C02F2101/10—Inorganic compounds
- C02F2101/103—Arsenic compounds
Abstract
The invention belongs to the technical field of sewage treatment, and particularly relates to a method for removing arsenic in sewage. The method comprises the following steps: 1) adding limestone into sewage to regulate the pH value of the sewage to 8-10; 2) adding an arsenic remover into sewage, reacting at the rotation speed of 200-500 r/min for 5-10 minutes to obtain a mixed solution, adding zeolite powder, standing for 6-12 hours, and pouring out the supernatant; 3) adding a flocculant into the supernatant, stirring uniformly, standing for 12-24 hours, pouring out the supernatant, and adding hydrochloric acid into the obtained supernatant to regulate the pH value to 6-7. The method can effectively remove arsenic and other harmful ingredients in sewage, has the advantages of stable treatment effect, short technical process, high safety, environment friendliness and the like, is simple to operate, and thus, has wide application prospects.
Description
Technical field
The present invention relates to technical field of sewage, having is a kind of to remove the method for arsenic in sewage.
Background technology
Arsenic is a kind of element with metalloid characteristic, be distributed widely in big gas and water, soil, rock and
In organism.In natural water, the arsenic of dissolving typically with Inorganic arsenates, arsenite form or with
Methylated arsenic compound form exists.The energy force rate pentavalent arsenic that trivalent arsenic enters cell is strong, and it is malicious
Property is also stronger several times than pentavalent arsenic.But the toxicity of pentavalent arsenic also can not be ignored, it can be converted into trivalent in vivo
Arsenic;And pentavalent arsenic contestable replaces phosphate, thus affect many enzymatic biochemical reactions.
At present, in arsenic-containing waste water process field, main administering method has iron sulfate precipitation method, iron filings
The sedimentation method, sulfur dioxide method, ion exchange, electrolysis.Iron sulfate precipitation method equipment is simple, place
Reason amount is big, and dearsenization is effective, but consumption is big, the quantity of slag is big.The iron filings sedimentation method energy treatment of wastes with processes of wastes against one another, is processed into
This is low, but water treatment efficiency is unstable.Sulfur dioxide method achieves the recycling of arsenic, but sulfur dioxide
Also it is the material having certain toxicity, is not suitable for large-scale promotion and uses.The recyclable arsenic of ion exchange, place
Reason effectiveness comparison is stable, but ion exchange resin treatment cost is high.Therefore, how to select a kind of rationally,
Effectively, practical remove the method for arsenic in sewage, be the difficult problem currently generally faced.
Summary of the invention
The technical problem to be solved in the present invention is to provide a kind of removes the method for arsenic in sewage, has process effect
The advantages such as the most stable, simple to operate, safety and environmental protection.
For solve above-mentioned technical problem, the present invention by the following technical solutions:
A kind of removing the method for arsenic in sewage, step is as follows: 1) put into limestone, regulation dirt in sewage
Water pH value is 8~10;2) in sewage, arsenic removing agent is put into, under rotating speed is 200~500r/min,
Reaction 5~10min, obtains mixed solution, adds zeolite powder, stands 6~12 hours, pour out supernatant;
3) put into flocculant at supernatant, after stirring, stand 12~24 hours, pour out supernatant, institute
Obtain supernatant adding hydrochloric acid regulation is 6~7 to pH value,.
Further improvement as technique scheme:
The preparation method of described arsenic removing agent is: adds iron chloride and aluminum chloride in water, prepares iron ion dense
The mixed solution that degree is 0.1~1mol/L, aluminium ion concentration is 0.1~1mol/L, adds hydroxide
Sodium solution regulation is 7~8 to pH value, removes supernatant, wash precipitate 2~5 with water after standing clarification
After secondary, vacuum filtration machine filter and washs, solid matter crushed after being dried to 80~120 mesh, i.e.
Can.
The consumption of described arsenic removing agent is preferably the 0.05%~0.1% of sewage weight.
Described flocculant is prepared by the raw material of following weight parts: sodium silicate 1~5 parts, magnesium chloride 1~5 parts,
70% ethanol 5~10 parts, polyacrylamide 1~5 parts, titanium tetrachloride 1~5 parts, Kaolin 0.1~
0.5 part, aluminum sulfate 1~5 parts, water 10~20 parts.The preparation process of described flocculant is: 1) by silicon
Acid sodium proportionally mixes with magnesium chloride, is subsequently adding 70% ethanol and stirs;2) by polyacrylamide
Amine, titanium tetrachloride, Kaolin and aluminum sulfate co-grinding are powdered, add water mix homogeneously;3) will
Step 1) and step 2) the product mix homogeneously that obtains, i.e. can get product.
The consumption of described flocculant is preferably the 0.05%~0.5% of sewage weight.
The invention have the benefit that
Method of the invention, it is possible to the harmful components such as the arsenic effectively removed in sewage, water after single treatment
Middle residual arsenic ion concentration is less than 0.45mg/L, less than the first discharge standard of national regulation, has process
The advantages such as effect stability, simple to operate, technological process is short, safety and environmental protection, application prospect is the most wide.
Detailed description of the invention
Below in conjunction with specific embodiment for instruction and explanation of the present invention.
Embodiment 1
Removing the method for arsenic in sewage, step is as follows: 1) puts into limestone in sewage, regulates sewage
PH value is 8;2) in sewage, put into arsenic removing agent, under rotating speed is 400r/min, react 10min,
Obtain mixed solution, add zeolite powder, stand 6 hours, pour out supernatant;3) flocculation is put at supernatant
Agent, after stirring, stands 20 hours, pours out supernatant, and gained supernatant adds hydrochloric acid and regulates extremely
PH value is 7,.
Wherein, the preparation method of arsenic removing agent is: adds iron chloride and aluminum chloride in water, prepares iron ion
Concentration is 0.1mol/L, aluminium ion concentration is the mixed solution of 0.5mol/L, adds sodium hydroxide solution
Regulating to pH value is 8, removes supernatant, after washing precipitate 2 times with water, in vacuum after standing clarification
Filter on sucking filtration machine and wash, solid matter crushed after being dried to 100 mesh,.The consumption of arsenic removing agent
For sewage weight 0.1%.
Flocculant is prepared by the raw material of following weight parts: sodium silicate 1 part, 3 parts of magnesium chloride, 70% ethanol
10 parts, polyacrylamide 1 part, titanium tetrachloride 3 parts, Kaolin 0.5 part, 1 part of aluminum sulfate, water 15
Part.The preparation process of flocculant is: 1) is proportionally mixed with magnesium chloride by sodium silicate, is subsequently adding
70% ethanol stirs;2) by polyacrylamide, titanium tetrachloride, Kaolin and aluminum sulfate co-grinding
Powdered, add water mix homogeneously;3) by step 1) and step 2) the product mix homogeneously that obtains,
I.e. can get product.The consumption of flocculant is the 0.5% of sewage weight.
Embodiment 2
Removing the method for arsenic in sewage, step is as follows: 1) puts into limestone in sewage, regulates sewage
PH value is 9;2) in sewage, put into arsenic removing agent, under rotating speed is 500r/min, react 5min,
Mixed solution, adds zeolite powder, stands 8 hours, pour out supernatant;3) flocculant is put at supernatant,
After stirring, standing 24 hours, pour out supernatant, gained supernatant adds hydrochloric acid and regulates to pH value
It is 6,.
Wherein, the preparation method of arsenic removing agent is: adds iron chloride and aluminum chloride in water, prepares iron ion
Concentration is 0.5mol/L, aluminium ion concentration is the mixed solution of 1mol/L, adds sodium hydroxide solution and adjusts
Saving to pH value is 7, removes supernatant, after washing precipitate 3 times with water, take out in vacuum after standing clarification
Filter on filter and wash, solid matter crushed after being dried to 120 mesh,.The consumption of arsenic removing agent is
The 0.05% of sewage weight.
Flocculant is prepared by the raw material of following weight parts: sodium silicate 3 parts, 5 parts of magnesium chloride, 70% ethanol
5 parts, polyacrylamide 3 parts, titanium tetrachloride 5 parts, Kaolin 0.1 part, 3 parts of aluminum sulfate, water 20
Part.The preparation process of flocculant is: 1) is proportionally mixed with magnesium chloride by sodium silicate, is subsequently adding
70% ethanol stirs;2) by polyacrylamide, titanium tetrachloride, Kaolin and aluminum sulfate co-grinding
Powdered, add water mix homogeneously;3) by step 1) and step 2) the product mix homogeneously that obtains,
I.e. can get product.The consumption of flocculant is the 0.05% of sewage weight.
Embodiment 3
Removing the method for arsenic in sewage, step is as follows: 1) puts into limestone in sewage, regulates sewage
PH value is 10;2) in sewage, put into arsenic removing agent, under rotating speed is 200r/min, react 8min,
Obtain mixed solution, add zeolite powder, stand 12 hours, pour out supernatant;3) wadding is put at supernatant
Solidifying agent, after stirring, stands 12 hours, pours out supernatant, and gained supernatant adds hydrochloric acid and regulates extremely
PH value is 7,.
Wherein, the preparation method of arsenic removing agent is: adds iron chloride and aluminum chloride in water, prepares iron ion
Concentration is 1mol/L, aluminium ion concentration is the mixed solution of 0.1mol/L, adds sodium hydroxide solution and adjusts
Saving to pH value is 8, removes supernatant, after washing precipitate 5 times with water, take out in vacuum after standing clarification
Filter on filter and wash, solid matter crushed after being dried to 80 mesh,.The consumption of arsenic removing agent is dirty
The 0.06% of water weight.
Flocculant is prepared by the raw material of following weight parts: sodium silicate 5 parts, 1 part of magnesium chloride, 70% ethanol
8 parts, polyacrylamide 5 parts, titanium tetrachloride 1 part, Kaolin 0.3 part, 5 parts of aluminum sulfate, water 10
Part.The preparation process of flocculant is: 1) is proportionally mixed with magnesium chloride by sodium silicate, is subsequently adding
70% ethanol stirs;2) by polyacrylamide, titanium tetrachloride, Kaolin and aluminum sulfate co-grinding
Powdered, add water mix homogeneously;3) by step 1) and step 2) the product mix homogeneously that obtains,
I.e. can get product.The consumption of flocculant is the 0.2% of sewage weight.
Claims (6)
1. remove the method for arsenic in sewage for one kind, it is characterised in that step is as follows: 1) in sewage
Putting into limestone, regulation pH value of sewage water is 8~10;2) in sewage, arsenic removing agent is put into, at rotating speed
Be under 200~500r/min, react 5~10min, obtain mixed solution, add zeolite powder, stand 6~
12 hours, pour out supernatant;3) supernatant put into flocculant, after stirring, stand 12~
24 hours, pouring out supernatant, it is 6~7 to pH value that gained supernatant adds hydrochloric acid regulation,.
Method the most according to claim 1, it is characterised in that the preparation side of described arsenic removing agent
Method is: adding iron chloride and aluminum chloride in water, prepared iron concentration is 0.1~1mol/L, aluminum
Ion concentration is the mixed solution of 0.1~1mol/L, adds sodium hydroxide solution regulation and to pH value is
7~8, remove supernatant after standing clarification, after washing precipitate 2~5 times with water, at vacuum filtration machine
Upper filtration is also washed, solid matter crushed after being dried to 80~120 mesh,.
Method the most according to claim 2, it is characterised in that: the consumption of described arsenic removing agent is
The 0.05%~0.1% of sewage weight.
Method the most according to claim 1, it is characterised in that: described flocculant is by following heavy
The raw material of amount part prepares: sodium silicate 1~5 parts, magnesium chloride 1~5 parts, 70% ethanol 5~10 parts,
Polyacrylamide 1~5 parts, titanium tetrachloride 1~5 parts, Kaolin 0.1~0.5 part, aluminum sulfate 1~
5 parts, water 10~20 parts.
Method the most according to claim 4, it is characterised in that the preparation of described flocculant
Cheng Wei: 1) sodium silicate is proportionally mixed with magnesium chloride, be subsequently adding 70% ethanol and stir;
2) by powdered to polyacrylamide, titanium tetrachloride, Kaolin and aluminum sulfate co-grinding, then add
Water mix homogeneously;3) by step 1) and step 2) the product mix homogeneously that obtains, i.e. can be produced
Product.
Method the most according to claim 5, it is characterised in that the consumption of described flocculant is
The 0.05%~0.5% of sewage weight.
Priority Applications (1)
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CN201610464041.5A CN105948324A (en) | 2016-06-23 | 2016-06-23 | Method for removing arsenic in sewage |
Applications Claiming Priority (1)
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CN201610464041.5A CN105948324A (en) | 2016-06-23 | 2016-06-23 | Method for removing arsenic in sewage |
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CN105948324A true CN105948324A (en) | 2016-09-21 |
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CN201610464041.5A Pending CN105948324A (en) | 2016-06-23 | 2016-06-23 | Method for removing arsenic in sewage |
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Cited By (2)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
CN106335986A (en) * | 2016-11-23 | 2017-01-18 | 郑州源冉生物技术有限公司 | Heavy metal-containing sewage treatment agent and preparation method thereof |
CN114262085A (en) * | 2021-11-26 | 2022-04-01 | 云南大地丰源环保有限公司 | Method for treating arsenic-containing wastewater |
Citations (4)
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CN101049972A (en) * | 2007-05-10 | 2007-10-10 | 桂林工学院 | Method for synthesizing composite hydroxide of iron and aluminum, and application |
US20140008564A1 (en) * | 2008-12-18 | 2014-01-09 | Ut-Battelle Llc | Magnetic filtration process, magnetic filtering material, and methods of forming magnetic filtering material |
CN104556461A (en) * | 2013-10-14 | 2015-04-29 | 南京科盛环保科技有限公司 | Method for treating heavy metal wastewater |
CN105236620A (en) * | 2015-10-15 | 2016-01-13 | 桂林市春晓环保科技有限公司 | Method for removing arsenic in water |
-
2016
- 2016-06-23 CN CN201610464041.5A patent/CN105948324A/en active Pending
Patent Citations (4)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
CN101049972A (en) * | 2007-05-10 | 2007-10-10 | 桂林工学院 | Method for synthesizing composite hydroxide of iron and aluminum, and application |
US20140008564A1 (en) * | 2008-12-18 | 2014-01-09 | Ut-Battelle Llc | Magnetic filtration process, magnetic filtering material, and methods of forming magnetic filtering material |
CN104556461A (en) * | 2013-10-14 | 2015-04-29 | 南京科盛环保科技有限公司 | Method for treating heavy metal wastewater |
CN105236620A (en) * | 2015-10-15 | 2016-01-13 | 桂林市春晓环保科技有限公司 | Method for removing arsenic in water |
Non-Patent Citations (2)
Title |
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Cited By (2)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
CN106335986A (en) * | 2016-11-23 | 2017-01-18 | 郑州源冉生物技术有限公司 | Heavy metal-containing sewage treatment agent and preparation method thereof |
CN114262085A (en) * | 2021-11-26 | 2022-04-01 | 云南大地丰源环保有限公司 | Method for treating arsenic-containing wastewater |
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Application publication date: 20160921 |