CN102115165A - A method for preparing arsenic trioxide from arsenic-containing wastewater - Google Patents
A method for preparing arsenic trioxide from arsenic-containing wastewater Download PDFInfo
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- CN102115165A CN102115165A CN 201010615442 CN201010615442A CN102115165A CN 102115165 A CN102115165 A CN 102115165A CN 201010615442 CN201010615442 CN 201010615442 CN 201010615442 A CN201010615442 A CN 201010615442A CN 102115165 A CN102115165 A CN 102115165A
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Abstract
A method for preparing arsenic trioxide by using arsenic sulfide waste residue comprises mixing arsenic sulfide waste residue with water, and leaching arsenic sulfide with sodium hydroxide solution; mixing the obtained arsenic sulfide and water with the mass of 2-5 times to form slurry, and reacting the slurry with a copper sulfate solution to obtain a precipitate containing arsenous acid and copper sulfide and a sulfuric acid solution; mixing the precipitate containing arsenous acid and copper sulfide with water, introducing oxygen to oxidize arsenous acid to generate water-soluble arsenic acid, and filtering to obtain arsenic acid solution and copper sulfide precipitate; reducing the obtained arsenic acid into arsenous acid by using sulfur dioxide to obtain arsenous acid; distilling arsenous acid, concentrating, filtering and drying to obtain the arsenic trioxide product. The method has the advantages of short process flow, high arsenic recovery rate, no secondary pollutant generation, simple equipment and capability of greatly reducing the arsenic recovery cost, and is a method worthy of popularization and application.
Description
Technical field
The present invention relates to the comprehensive utilization and the processing technology field of arsenic-containing waste water, particularly, relates to a kind of method for preparing white arsenic with arsenic-containing waste water.
Background technology
For a long time, arsenic-containing waste residue adopts the method for hoarding storage to handle mostly, and along with the accumulation of high density arsenic-containing waste is more and more, arsenic-containing waste residue has caused soil, stream pollution, and the phenomenon of harm people life health is more and more serious.For preventing secondary pollution, must handle the red arsenic waste residue.
Especially, experience exploitation for many years, the arsenic minerals resource is extremely limited.Since arsenic in the special purpose in fields such as agricultural, electronics, medicine, metallurgy, chemical industry, can be used for producing weedicide, wood preservative, glass clarifying discoloring agent, non-ferrous metal alloy, pottery etc.; especially photoelectron and microelectronic are to the demand of arsenic; therefore; reclaiming the demand that arsenic is not only environment protection from arsenic-containing waste residue, also is the needs of national sustained economic development.
Summary of the invention
For this reason, the applicant provides a kind of and has prepared the method for white arsenic with the red arsenic waste residue, and this method is simple to operate, and facility investment is few, and arsenic recovery utilization rate height is worthy of popularization.
In the red arsenic waste residue, contained arsenic mainly is arsenic trisulfide, and it is insoluble in water water, also is insoluble to mineral acid, in alkaline soluble metal hydroxides, carbonate and the sulfide.
Technical scheme of the present invention is as follows: a kind ofly prepare the method for white arsenic with the red arsenic waste residue, comprise following concrete steps:
Steps A: getting red arsenic content is the red arsenic waste residue of 5-20%, mix with water, water consumption is by 100-150ml/100g red arsenic waste residue, after mixing, add sodium hydroxide solution lixiviate red arsenic, wherein the consumption of sodium hydroxide is by the 2.0-3.5g/g red arsenic, after lixiviate 0.5-2 hour, filter, get filtrate one and filter residue one; With filtrate one usefulness vitriol oil neutralization alkali wherein, making the pH value of solution value is 9-11, refilters, and obtains filtrate two and filter residue two; Filtrate two is continued neutralization value PH1-3.5 with the vitriol oil again, and it is 2-4 that adding sodium sulphite makes pH, filters then, obtains filter residue three and filtrate three; Filter residue after washing drying, the red arsenic that obtain purifying;
Step B: the red arsenic of the purification of steps A gained and the water of 2-5 times of quality are mixed into slurry, under the stirring at room, mix, and to make the arsenic contained in the mixing solutions and the ratio of the molar weight of copper be 1:2 with copper-bath; Mixed solution is heated to 65-80 ℃ and carries out chemical reaction, reaction times 0.5-2 hour, be cooled to 4 ℃ after filter at low temperature, obtain containing the precipitation of arsenus acid and cupric sulfide and sulphuric acid soln;
Step C: the precipitation that contains arsenus acid and cupric sulfide of step B gained and the water of 2-5 times of quality are mixed into slurry, and aerating oxygen makes arsenus acid generate arsenic acid soluble in water through oxidation, filters, and obtains arsenic acid solution and copper sulfide precipitation;
Step D: feed sulfur dioxide gas in step C gained arsenic acid solution, gas flow is 16L/h, makes arsenic acid be reduced to arsenus acid, obtains arsenic chloride solution, reaction times 1-3 hour;
Step e:, concentrate, filtration, drying through distillation to step D gained arsenic chloride solution, obtain the white arsenic product.
Of the present inventionly prepare the method for white arsenic with the red arsenic waste residue, its chemical principle is:
As
2S
3+3CuSO
4 +4H
2O = 2HAsO
2+3CuS+3H
2SO
4
2HAsO
2+ O
2 +2H
2O =2H
3AsO
4
H
3AsO
4+S O
2 = HAsO
2+H
2SO
4
4HAsO
2=2 As
2O
3 +2H
2O
Of the present inventionly prepare the method for white arsenic with the red arsenic waste residue, technical process is short, arsenic rate of recovery height, non-secondary pollution deposits yields, and equipment is simple, greatly reduce the cost that arsenic reclaims, and is a method that is worthy of popularization.
Embodiment
Embodiment 1:
A kind ofly prepare the method for white arsenic, comprise following concrete steps with the red arsenic waste residue:
Steps A: get red arsenic content and be 10% red arsenic waste residue, mix with water, water consumption is by 120ml/100g red arsenic waste residue, after mixing, add sodium hydroxide solution lixiviate red arsenic, wherein the consumption of sodium hydroxide is by 3,0g/g red arsenic meter, after the lixiviate 1 hour, filter, get filtrate one and filter residue one; With filtrate one usefulness vitriol oil neutralization alkali wherein, making the pH value of solution value is 10, refilters, and obtains filtrate two and filter residue two; Filtrate two is continued neutralization value pH2.5 with the vitriol oil again, and it is 3 that adding sodium sulphite makes pH, filters then, obtains filter residue three and filtrate three; Filter residue after washing drying, the red arsenic that obtain purifying;
Step B: the red arsenic of the purification of steps A gained and the water of 4 times of quality are mixed into slurry, under the stirring at room, mix, and to make the arsenic contained in the mixing solutions and the ratio of the molar weight of copper be 1:2 with copper-bath; Mixed solution is heated to 70 ℃ and carries out chemical reaction, 1 hour reaction times, be cooled to 4 ℃ after filter at low temperature, obtain containing the precipitation of arsenus acid and cupric sulfide and sulphuric acid soln;
Step C: the precipitation that contains arsenus acid and cupric sulfide of step B gained and the water of 4 times of quality are mixed into slurry, and aerating oxygen makes arsenus acid generate arsenic acid soluble in water through oxidation, filters, and obtains arsenic acid solution and copper sulfide precipitation;
Step D: feed sulfur dioxide gas in step C gained arsenic acid solution, gas flow is 16L/h, makes arsenic acid be reduced to arsenus acid, obtains arsenic chloride solution, 2 hours reaction times;
Step e:, concentrate, filtration, drying through distillation to step D gained arsenic chloride solution, obtain the white arsenic product.
Embodiment 2:
A kind ofly prepare the method for white arsenic, comprise following concrete steps with the red arsenic waste residue:
Steps A: get red arsenic content and be 20% red arsenic waste residue, mix with water, water consumption is by 150ml/100g red arsenic waste residue, after mixing, add sodium hydroxide solution lixiviate red arsenic, wherein the consumption of sodium hydroxide is by the 3.5g/g red arsenic, and lixiviate is after 2 hours, filter, get filtrate one and filter residue one; With filtrate one usefulness vitriol oil neutralization alkali wherein, making the pH value of solution value is 11, refilters, and obtains filtrate two and filter residue two; Filtrate two is continued neutralization value pH3.5 with the vitriol oil again, and it is 4 that adding sodium sulphite makes pH, filters then, obtains filter residue three and filtrate three; Filter residue after washing drying, the red arsenic that obtain purifying;
Step B: the red arsenic of the purification of steps A gained and the water of 5 times of quality are mixed into slurry, under the stirring at room, mix, and to make the arsenic contained in the mixing solutions and the ratio of the molar weight of copper be 1:2 with copper-bath; Mixed solution is heated to 80 ℃ and carries out chemical reaction, 2 hours reaction times, be cooled to 4 ℃ after filter at low temperature, obtain containing the precipitation of arsenus acid and cupric sulfide and sulphuric acid soln;
Step C: the precipitation that contains arsenus acid and cupric sulfide of step B gained and the water of 5 times of quality are mixed into slurry, and aerating oxygen makes arsenus acid generate arsenic acid soluble in water through oxidation, filters, and obtains arsenic acid solution and copper sulfide precipitation;
Step D: feed sulfur dioxide gas in step C gained arsenic acid solution, gas flow is 16L/h, makes arsenic acid be reduced to arsenus acid, obtains arsenic chloride solution, 3 hours reaction times;
Step e:, concentrate, filtration, drying through distillation to step D gained arsenic chloride solution, obtain the white arsenic product.
Embodiment 3:
A kind ofly prepare the method for white arsenic, comprise following concrete steps with the red arsenic waste residue:
Steps A: get red arsenic content and be 5% red arsenic waste residue, mix with water, water consumption is by 100ml/100g red arsenic waste residue, after mixing, add sodium hydroxide solution lixiviate red arsenic, wherein the consumption of sodium hydroxide is by the 2.0g/g red arsenic, and lixiviate is after 0.5 hour, filter, get filtrate one and filter residue one; With filtrate one usefulness vitriol oil neutralization alkali wherein, making the pH value of solution value is 9, refilters, and obtains filtrate two and filter residue two; Filtrate two is continued neutralization value pH1 with the vitriol oil again, and it is 2 that adding sodium sulphite makes pH, filters then, obtains filter residue three and filtrate three; Filter residue after washing drying, the red arsenic that obtain purifying;
Step B: the red arsenic of the purification of steps A gained and the water of 2 times of quality are mixed into slurry, under the stirring at room, mix, and to make the arsenic contained in the mixing solutions and the ratio of the molar weight of copper be 1:2 with copper-bath; Mixed solution is heated to 65 ℃ and carries out chemical reaction, 0.5 hour reaction times, be cooled to 4 ℃ after filter at low temperature, obtain containing the precipitation of arsenus acid and cupric sulfide and sulphuric acid soln;
Step C: the precipitation that contains arsenus acid and cupric sulfide of step B gained and the water of 2 times of quality are mixed into slurry, and aerating oxygen makes arsenus acid generate arsenic acid soluble in water through oxidation, filters, and obtains arsenic acid solution and copper sulfide precipitation;
Step D: feed sulfur dioxide gas in step C gained arsenic acid solution, gas flow is 16L/h, makes arsenic acid be reduced to arsenus acid, obtains arsenic chloride solution, 1 hour reaction times;
Step e:, concentrate, filtration, drying through distillation to step D gained arsenic chloride solution, obtain the white arsenic product.
Above content be in conjunction with concrete preferred implementation to further describing that the present invention did, can not assert that concrete enforcement of the present invention is confined to these explanations.For the general technical staff of the technical field of the invention, without departing from the inventive concept of the premise, its framework form can be flexible and changeable, can the subseries product.Just make some simple deduction or replace, all should be considered as belonging to the scope of patent protection that the present invention is determined by claims of being submitted to.
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Cited By (6)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| CN105177316A (en) * | 2015-08-28 | 2015-12-23 | 湖南雷恩蒙特冶化环境与资源科技有限公司 | Treatment method for arsenical waste liquid |
| CN105603217A (en) * | 2015-12-28 | 2016-05-25 | 中南大学 | Method for enriching and recovering antimony in contaminated acid vulcanization residue |
| CN105950874A (en) * | 2016-06-30 | 2016-09-21 | 中南大学 | Combined treatment method for copper smelting soot and polluted acid |
| CN106834736A (en) * | 2016-12-29 | 2017-06-13 | 东营方圆有色金属有限公司 | The separating technology of copper and arsenic in arsenic sulfide slag |
| CN114317962A (en) * | 2021-11-22 | 2022-04-12 | 长沙有色冶金设计研究院有限公司 | Method for separating copper from sulfuric acid leaching solution containing copper ions |
| CN119614878A (en) * | 2024-11-14 | 2025-03-14 | 湘南学院 | Process for comprehensively recovering valuable metals from tin-containing ash |
Citations (3)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| US4438079A (en) * | 1981-03-30 | 1984-03-20 | Sumitomo Metal Mining Company Limited | Method for manufacture of arsenious anhydride |
| CN101125682A (en) * | 2007-09-07 | 2008-02-20 | 中南大学 | Method for preparing arsenic trioxide from arsenic-containing wastewater |
| CN101786659A (en) * | 2009-11-16 | 2010-07-28 | 瓮福(集团)有限责任公司 | Method for recovering arsenic sulfide from arsenic-containing waste residue |
-
2010
- 2010-12-31 CN CN 201010615442 patent/CN102115165A/en active Pending
Patent Citations (3)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| US4438079A (en) * | 1981-03-30 | 1984-03-20 | Sumitomo Metal Mining Company Limited | Method for manufacture of arsenious anhydride |
| CN101125682A (en) * | 2007-09-07 | 2008-02-20 | 中南大学 | Method for preparing arsenic trioxide from arsenic-containing wastewater |
| CN101786659A (en) * | 2009-11-16 | 2010-07-28 | 瓮福(集团)有限责任公司 | Method for recovering arsenic sulfide from arsenic-containing waste residue |
Non-Patent Citations (2)
| Title |
|---|
| 《环境保护》 19961231 罗华良 从硫化砷渣中回收砷、铜、硫 , 第9期 2 * |
| 《矿产综合利用》 20020228 寇建军等 As2O3湿法提取工艺进展 , 第1期 2 * |
Cited By (8)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| CN105177316A (en) * | 2015-08-28 | 2015-12-23 | 湖南雷恩蒙特冶化环境与资源科技有限公司 | Treatment method for arsenical waste liquid |
| CN105177316B (en) * | 2015-08-28 | 2018-01-19 | 湖南欧泰稀有金属有限公司 | A kind of processing method containing arsenic waste solution |
| CN105603217A (en) * | 2015-12-28 | 2016-05-25 | 中南大学 | Method for enriching and recovering antimony in contaminated acid vulcanization residue |
| CN105950874A (en) * | 2016-06-30 | 2016-09-21 | 中南大学 | Combined treatment method for copper smelting soot and polluted acid |
| CN105950874B (en) * | 2016-06-30 | 2017-08-22 | 中南大学 | A kind of Copper making cigarette ash and the method for waste acid Combined Treatment |
| CN106834736A (en) * | 2016-12-29 | 2017-06-13 | 东营方圆有色金属有限公司 | The separating technology of copper and arsenic in arsenic sulfide slag |
| CN114317962A (en) * | 2021-11-22 | 2022-04-12 | 长沙有色冶金设计研究院有限公司 | Method for separating copper from sulfuric acid leaching solution containing copper ions |
| CN119614878A (en) * | 2024-11-14 | 2025-03-14 | 湘南学院 | Process for comprehensively recovering valuable metals from tin-containing ash |
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Application publication date: 20110706 |