CN104668266B - A kind of method for innocent treatment of waste residue of endangering containing arsenic - Google Patents

A kind of method for innocent treatment of waste residue of endangering containing arsenic Download PDF

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CN104668266B
CN104668266B CN201410723866.5A CN201410723866A CN104668266B CN 104668266 B CN104668266 B CN 104668266B CN 201410723866 A CN201410723866 A CN 201410723866A CN 104668266 B CN104668266 B CN 104668266B
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waste residue
containing arsenic
arsenic
flotation
innocent treatment
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CN104668266A (en
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季常青
黄怀国
谢洪珍
张波
陈征贤
马龙
庄荣传
张卿
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Xiamen Zijin Mining and Metallurgy Technology Co Ltd
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Xiamen Zijin Mining and Metallurgy Technology Co Ltd
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Abstract

The invention discloses a kind of method for innocent treatment of waste residue of endangering containing arsenic, comprises the steps:(1) aeration and churned mechanically compound hybrid mode are adopted, the serosity that the danger waste residue containing arsenic is tuned into concentration 5~45%;(2) adding composite drug in above-mentioned serosity carries out the activation of 5~50min, and the composite drug is 1 with the above-mentioned mass ratio containing arsenic danger waste residue:3~30;(3) slag after above-mentioned process is inserted flotation cell, adds the butylamine black powder of 2~20g/t, flotation to reclaim sulfuration arsenic mineral therein, the direct heap of the tailings after flotation enters Tailings Dam or uses it for anything else.The technique that the processing method of the present invention is combined with ore-dressing technique using chemical agent activation, realizes the recovery of arsenic sulfide resource while danger waste residue is administered.

Description

A kind of method for innocent treatment of waste residue of endangering containing arsenic
Technical field
The invention belongs to mine waste residue process field, and in particular to a kind of method for innocent treatment of waste residue of endangering containing arsenic.
Background technology
With the sustainable development that mine smelts, while being refined, substantial amounts of association endangers element to valuable metal resource The compound of arsenic is also produced and banks up, and water body to arround, soil generate harm.At present, for water body in the conventional ferrum of arsenic Salt, the method for calcium precipitation are processed;For the solidification by As polluted soil and mine tailing danger waste residue and recovery technique, mainly include work Journey repairing method, elution method and bioanalysises etc..
Engineering repairing method mainly by the method for physics, is diluted to contaminated soil and changes, so as to reach dilution Reduce arsenic concentration and reduce the purpose of its toxicity;But the technology haves the shortcomings that quantities is big, costly and destroys Soil structure. Elution method is mainly washed to As polluted soil using the chemical leaching of water or other aqueous solutions, adsorbs soil surface Arsenic enter liquid phase, lower Arsenic in Soil content;The PROCESS FOR TREATMENT efficiency is higher, but equally exists that quantities is big, expense Height, the structural deterioration to soil are larger.Bioanalysises include that microbial method and phytoremediation, the principle of microbial method arsenic removal are Some special strains can produce a kind of material similar to activated sludge in incubation, and this material plays flocculation, it Can be combined with arsenic and be formed precipitation, be reached the purpose of arsenic removal.But, the bioanalysises spawn culture cycle is long, harsh to environmental requirement, And it is commonly used for waste water arsenic removal.Phytoremediation is to remove the polluter in soil using plant or make polluter Non-toxic Technology.Filter including plant extract, phytovolatilization, rhizosphere and plant is fixed.Phytoremediation is compared with traditional restorative procedure, is had Have the advantages that low cost, work well, not welding, but the phytoremediation cycle longer, adsorption efficiency is relatively low.
Content of the invention
It is an object of the invention to overcoming prior art defect, there is provided a kind of method for innocent treatment of waste residue of endangering containing arsenic.
The concrete technical scheme of the present invention is as follows:
A kind of method for innocent treatment of waste residue of endangering containing arsenic, comprises the steps:
(1) using aeration and churned mechanically compound hybrid mode, the danger waste residue containing arsenic is added water and is tuned into concentration 5~45% Serosity, aeration rate are 5~30m3/ h, mechanical agitation speed are 10~50rpm;
(2) in the state of aeration and mechanical agitation is maintained, in above-mentioned serosity adding composite drug carries out 5~50min Activation, the composite drug with above-mentioned containing arsenic endanger waste residue mass ratio be 1:3~30, the wherein composite drug includes following weight The component of part:
10~40 weight portion of mineral material
20~60 weight portion of sodium carbonate
5~40 weight portion of sodium sulfide or NaHS
The mineral material is at least one in refuse incineration slag, slag and Concha Ostreae powder;
(3) slag after above-mentioned process is inserted flotation cell, adds the butylamine black powder of 2~20g/t, flotation to reclaim therein Sulfuration arsenic mineral, flotation aeration rate are 2~10m3/ h, the direct heap of the tailings after flotation enter Tailings Dam or use it for anything else.
In a preferred embodiment of the invention, the composite drug includes the component of following percentage by weight:
Mineral material 10~40%
Sodium carbonate 20~60%
Sodium sulfide or NaHS 5~40%.
In a preferred embodiment of the invention, the concentration of slurry in step (1) is 15~25%.
In a preferred embodiment of the invention, 5 a kind of, nothing of waste residue of endangering containing arsenic as claimed in claim 1 or 2 Evilization processing method, it is characterised in that:The composite drug is 1 with the mass ratio containing arsenic danger waste residue:20~25.
In a preferred embodiment of the invention, in step (3), the addition of butylamine black powder is 10~15g/ t.
In a preferred embodiment of the invention, the fineness of the mineral material crosses 200 mesh sieves for 90%.
The invention has the beneficial effects as follows:
1st, the technique that processing method of the invention is combined with ore-dressing technique using chemical agent activation, is administering danger waste residue While realize the recovery of arsenic sulfide resource.
2nd, treatment technology of the invention is with low cost, is simple to operate and friendly to environment, it is adaptable to related mine and chemical enterprise As polluted soil and mine tailing harmless treatment.
Specific embodiment
It is further detailed below by way of specific embodiment technical scheme and describes.
Embodiment 1
Guizhou gold mine cyaniding tailings is that toxicity leaches arsenic concentration and reaches 30mg/L, belongs to danger waste residue, nothing containing arsenic danger waste residue Method is directly discharged into Tailings Dam, need to carry out innoxious solid arsenic and process:
(1) aeration and churned mechanically compound hybrid mode are adopted, and the serosity that the danger waste residue containing arsenic is tuned into concentration 25% exposes Tolerance is 5~30m3/ h, mechanical agitation speed are 10~50rpm;
(2) in the state of aeration and mechanical agitation is maintained, in above-mentioned serosity adding composite drug carries out the work of 30min Change, the composite drug is 1 with the above-mentioned mass ratio containing arsenic danger waste residue:20, the wherein composite drug includes following weight portion percentage The component of ratio:
Mineral material 15%
Sodium carbonate 50%
Sodium sulfide 35%
The mineral material is the mixing of slag and Concha Ostreae powder, and slag is 1 with the mass ratio of Concha Ostreae powder:1, the mineral material Fineness be 90% cross 200 mesh sieves;
(3) slag after above-mentioned process is inserted flotation cell, adds the butylamine black powder of 10g/t, flotation to reclaim sulfur therein Change arsenic mineral, flotation aeration rate is 2~10m3/ h, the tailings after flotation meet national general solid waste standard after measured and require, can Directly heap enters Tailings Dam or uses it for anything else.
Embodiment 2
Certain chemical enterprise, the arsenic-containing waste water process of discharge are below standard, and farmland soil near direct exhaust emission, through Environmental Protection Agency Detection, the Arsenic in Soil content reach 200mg/kg, far beyond the 40mg/kg that standard of soil environment quality three-level is required.
(1) aeration and churned mechanically compound hybrid mode are adopted, the slurry that the above-mentioned danger waste residue containing arsenic is tuned into concentration 15% Liquid, aeration rate are 5~30m3/ h, mechanical agitation speed are 10~50rpm;
(2) in the state of aeration and mechanical agitation is maintained, in above-mentioned serosity adding composite drug carries out the work of 20min Change, the composite drug is 1 with the above-mentioned mass ratio containing arsenic danger waste residue:25, the wherein composite drug includes the group of following weight portion Point:
Mineral material 20%
Sodium carbonate 45%
Sodium sulfide 35%
Mixing of the mineral material for refuse incineration slag, slag and Concha Ostreae powder, refuse incineration slag, slag and Concha Ostreae powder Mass ratio is 1:3:1, the fineness of the mineral material crosses 200 mesh sieves for 90%;
(3) slag after above-mentioned process is inserted flotation cell, adds the butylamine black powder of 15g/t, flotation to reclaim sulfur therein Change arsenic mineral, flotation aeration rate is 2~10m3/ h, total Arsenic In Soil concentration is 10mg/kg to the tailings after flotation after measured, is less than The requirement of standard of soil environment quality one-level, can direct Planting Crops.
Embodiment 3
Guizhou gold mine cyaniding tailings is that toxicity leaches arsenic concentration and reaches 30mg/L, belongs to danger waste residue, nothing containing arsenic danger waste residue Method is directly discharged into Tailings Dam, need to carry out innoxious solid arsenic and process:
(1) aeration and churned mechanically compound hybrid mode are adopted, and the serosity that the danger waste residue containing arsenic is tuned into concentration 40% exposes Tolerance is 5~30m3/ h, mechanical agitation speed are 10~50rpm;
(2) in the state of aeration and mechanical agitation is maintained, in above-mentioned serosity adding composite drug carries out the work of 50min Change, the composite drug is 1 with the above-mentioned mass ratio containing arsenic danger waste residue:30, the wherein composite drug includes following weight portion percentage The component of ratio:
Mineral material 40%
Sodium carbonate 20%
Sodium bisulfide 40%
The mineral material is the mixing of slag and Concha Ostreae powder, and slag is 1 with the mass ratio of Concha Ostreae powder:1, the mineral material Fineness be 90% cross 200 mesh sieves;
(3) slag after above-mentioned process is inserted flotation cell, adds the butylamine black powder of 20g/t, flotation to reclaim sulfur therein Change arsenic mineral, flotation aeration rate is 2~10m3/ h, the tailings after flotation meet national general solid waste standard after measured and require, can Directly heap enters Tailings Dam or uses it for anything else.
Embodiment 4
Guizhou gold mine cyaniding tailings is that toxicity leaches arsenic concentration and reaches 30mg/L, belongs to danger waste residue, nothing containing arsenic danger waste residue Method is directly discharged into Tailings Dam, need to carry out innoxious solid arsenic and process:
(1) aeration and churned mechanically compound hybrid mode are adopted, and the serosity that the danger waste residue containing arsenic is tuned into concentration 40% exposes Tolerance is 5~30m3/ h, mechanical agitation speed are 10~50rpm;
(2) in the state of aeration and mechanical agitation is maintained, in above-mentioned serosity adding composite drug carries out the work of 5min Change, the composite drug is 1 with the above-mentioned mass ratio containing arsenic danger waste residue:3, the wherein composite drug includes following weight portion percentage ratio Component:
Mineral material 35%
Sodium carbonate 60%
Sodium bisulfide 5%
The mineral material is the mixing of slag and Concha Ostreae powder, and slag is 1 with the mass ratio of Concha Ostreae powder:1, the mineral material Fineness be 90% cross 200 mesh sieves;
(3) slag after above-mentioned process is inserted flotation cell, adds the butylamine black powder of 40g/t, flotation to reclaim sulfur therein Change arsenic mineral, flotation aeration rate is 2~10m3/ h, the tailings after flotation meet national general solid waste standard after measured and require, can Directly heap enters Tailings Dam or uses it for anything else.
Embodiment 5
(1) aeration and churned mechanically compound hybrid mode are adopted, and the serosity that the danger waste residue containing arsenic is tuned into concentration 36% exposes Tolerance is 5~30m3/ h, mechanical agitation speed are 10~50rpm;
(2) in the state of aeration and mechanical agitation is maintained, in above-mentioned serosity adding composite drug carries out the work of 40min Change, the composite drug is 1 with the above-mentioned mass ratio containing arsenic danger waste residue:23, the wherein composite drug includes the group of following weight portion Point:
Mineral material 30%
Sodium carbonate 60%
NaHS 10%
Mixing of the mineral material for refuse incineration slag, slag and Concha Ostreae powder, refuse incineration slag, slag and Concha Ostreae powder Mass ratio is 1:3:1, the fineness of the mineral material crosses 200 mesh sieves for 90%;
(3) slag after above-mentioned process is inserted flotation cell, adds the butylamine black powder of 12g/t, flotation to reclaim sulfur therein Change arsenic mineral, flotation aeration rate is 2~10m3/ h, the tailings after flotation meet national general solid waste standard after measured and require, can Directly heap enters Tailings Dam or uses it for anything else.
The above, only presently preferred embodiments of the present invention, therefore the scope of present invention enforcement can not be limited according to this, i.e., The equivalence changes that is made according to the scope of the claims of the present invention and description and modification, all still should belong in the range of the present invention covers.

Claims (7)

1. a kind of containing arsenic endanger waste residue method for innocent treatment, it is characterised in that:Comprise the steps:
(1) using aeration and churned mechanically compound hybrid mode, the danger waste residue containing arsenic is added water and is tuned into the slurry of concentration 5~45% Liquid, aeration rate are 5~30m3/ h, mechanical agitation speed are 10~50rpm;
(2) in the state of aeration and mechanical agitation is maintained, in above-mentioned serosity adding composite drug carries out the work of 5~50min Change, the composite drug is 1 with the above-mentioned mass ratio containing arsenic danger waste residue:3~30, the wherein composite drug includes following weight portion Component:
10~40 weight portion of mineral material
20~60 weight portion of sodium carbonate
5~40 weight portion of sodium sulfide or NaHS
The mineral material is at least one in refuse incineration slag, slag and Concha Ostreae powder;
(3) by process after the danger waste residue containing arsenic insert flotation cell, add the butylamine black powder of 2~20g/t, flotation to reclaim sulfur therein Change arsenic mineral, flotation aeration rate is 2~10m3/ h, the direct heap of the tailings after flotation enter Tailings Dam.
2. as claimed in claim 1 a kind of containing arsenic endanger waste residue method for innocent treatment, it is characterised in that:The composite drug Component including following percentage by weight:
Mineral material 10~40%
Sodium carbonate 20~60%
Sodium sulfide or NaHS 5~40%.
3. as claimed in claim 1 or 2 a kind of containing arsenic endanger waste residue method for innocent treatment, it is characterised in that:The step (1) concentration of slurry in is 15~25%.
4. as claimed in claim 1 or 2 a kind of containing arsenic endanger waste residue method for innocent treatment, it is characterised in that:The step (2) soak time is 20~30min.
5. as claimed in claim 1 or 2 a kind of containing arsenic endanger waste residue method for innocent treatment, it is characterised in that:Described compound Medicament is 1 with the mass ratio containing arsenic danger waste residue:20~25.
6. as claimed in claim 1 or 2 a kind of containing arsenic endanger waste residue method for innocent treatment, it is characterised in that:The step (3) in, the addition of butylamine black powder is 10~15g/t.
7. as claimed in claim 1 or 2 a kind of containing arsenic endanger waste residue method for innocent treatment, it is characterised in that:The mineral The fineness of material crosses 200 mesh sieves for 90%.
CN201410723866.5A 2014-12-03 2014-12-03 A kind of method for innocent treatment of waste residue of endangering containing arsenic Active CN104668266B (en)

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Publication number Priority date Publication date Assignee Title
JP6720214B2 (en) * 2015-12-25 2020-07-08 株式会社神戸製鋼所 Arsenic insolubilizing material and insolubilizing method
CN111013080B (en) * 2019-12-30 2020-09-22 贵州昊华工程技术有限公司 Method for harmless treatment of phosphate ore dressing tailing slag

Citations (8)

* Cited by examiner, † Cited by third party
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EP0488042A1 (en) * 1990-11-29 1992-06-03 CONTENTO TRADE S.A.S. di CIOFFI ILARIA Granules with a high degree of mechanical resistance made from inorganic industrial waste
CN101954370A (en) * 2010-09-06 2011-01-26 同济大学 Method for recycling arsenic-containing waste residues
CN102107204A (en) * 2009-12-23 2011-06-29 湖南布鲁斯凯环保科技发展有限公司 Innocent treatment process for industrial heavy metal waste residue by utilizing treating waste with waste
CN102115162A (en) * 2010-12-31 2011-07-06 马艳荣 Method for preparing arsenic trioxide by using arsenic sulfide waste slags
CN102151690A (en) * 2011-01-20 2011-08-17 杭州大地环保有限公司 Method for treating arsenic sulfide residue
CN102240600A (en) * 2010-12-01 2011-11-16 厦门紫金矿冶技术有限公司 Method for separating and recovering sulfur and arsenic from sulfur and arsenic containing materials
CN102553516A (en) * 2012-01-18 2012-07-11 厦门大学 Chemical adsorbent for treating arsenic-containing wastewater and preparation method for chemical adsorbent
CN103657868A (en) * 2013-12-03 2014-03-26 安徽朝山新材料股份有限公司 Collecting agent for separating gold from high-arsenic type gold ores and preparation method for collecting agent

Patent Citations (8)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
EP0488042A1 (en) * 1990-11-29 1992-06-03 CONTENTO TRADE S.A.S. di CIOFFI ILARIA Granules with a high degree of mechanical resistance made from inorganic industrial waste
CN102107204A (en) * 2009-12-23 2011-06-29 湖南布鲁斯凯环保科技发展有限公司 Innocent treatment process for industrial heavy metal waste residue by utilizing treating waste with waste
CN101954370A (en) * 2010-09-06 2011-01-26 同济大学 Method for recycling arsenic-containing waste residues
CN102240600A (en) * 2010-12-01 2011-11-16 厦门紫金矿冶技术有限公司 Method for separating and recovering sulfur and arsenic from sulfur and arsenic containing materials
CN102115162A (en) * 2010-12-31 2011-07-06 马艳荣 Method for preparing arsenic trioxide by using arsenic sulfide waste slags
CN102151690A (en) * 2011-01-20 2011-08-17 杭州大地环保有限公司 Method for treating arsenic sulfide residue
CN102553516A (en) * 2012-01-18 2012-07-11 厦门大学 Chemical adsorbent for treating arsenic-containing wastewater and preparation method for chemical adsorbent
CN103657868A (en) * 2013-12-03 2014-03-26 安徽朝山新材料股份有限公司 Collecting agent for separating gold from high-arsenic type gold ores and preparation method for collecting agent

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