CN102247967B - Harmless treatment process for arsenic-containing waste dangerous chemicals - Google Patents

Harmless treatment process for arsenic-containing waste dangerous chemicals Download PDF

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CN102247967B
CN102247967B CN201010177806.XA CN201010177806A CN102247967B CN 102247967 B CN102247967 B CN 102247967B CN 201010177806 A CN201010177806 A CN 201010177806A CN 102247967 B CN102247967 B CN 102247967B
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arsenic
cement
treatment process
harmless treatment
waste
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CN102247967A (en
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孙斌
陈燕
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Zhejiang Guizero Environmental Protection Technology Co ltd
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SHANGHAI FUTUO ENVIRONMENT TECHNOLOGY CO LTD
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Abstract

The invention provides a harmless treatment process of arsenic-containing waste chemicals, which comprises the following steps: 1) mixing the arsenic-containing waste with water, adding ferric salt or ferrous salt, and adjusting the pH value of the solution to be less than 2 by using nitric acid; then adding hydrogen peroxide to convert all the organic arsenic and trivalent As in the reaction system into AsO4 2-While making Fe2+All conversion to Fe3+(ii) a 2) Adjusting the pH value of the solution obtained in the step 1) to 9-10 by using calcium hydroxide to form arsenic-iron complex precipitate; 3) adding cement into the sediment and the waste liquid generated in the step 2) for solidification treatment to obtain a cement solidified body. The process provided by the invention organically integrates a chemical treatment technology and a cement curing technology, and the leaching toxicity concentration of arsenic of the obtained cement cured body is less than 5mg/L, thereby reaching the relevant national harmless standard.

Description

A kind of harmless treatment process containing arsenic waste dangerous chemical
Technical field
The invention belongs to waste treatment processes technical field, relate in particular to a kind of harmless treatment process containing arsenic waste dangerous chemical.
Background technology
Cement solidification technology is to process the important means of heavy metal refuse and other nonmetal hazardous waste.By solidifying, harmful waste is fixed in a kind of fluid-tight matrix of inertia, refuse can change hazardous contaminant into low-solubility, low migration and the more stable material of hypotoxic physics and chemistry characteristic after overcuring is processed.
The mechanism that curing technology is stablized waste component is that Chemical bonding between refuse and coagulating agent, coagulating agent are to the physical inclusion of refuse, the acting in conjunction of coagulating agent hydrated product to absorption of refuse etc., make refuse change not charge of flowable solids into or form tight solid, change permeability, compressibility and the intensity of refuse.Hazardous waste can reach and alleviates or eliminate himself harmfulness after overcuring is processed, and can transport safely, and can carry out easily final disposal.
Cement is the most frequently used hazardous waste stabilizing agent.Because cement is a kind of cement inorganic material, after hydration reaction, can generate hard solidified cement body, thereby reach, reduce the object that in refuse, hazard component leaches.Cement adding rate is different and different according to processing type of waste, and its excursion can reach 5%~60%.
The curing technology that the cement of take is base material is for the treatment of the electroplating sludge containing different heavy metals (as cadmium, chromium, copper, lead, zinc etc.), also for the treatment of containing organic complex waste, as PCBs, grease, resin, asbestos etc.
At home, cement solidification technology is never successfully applied to containing arsenic waste dangerous chemical and processes, main cause is that pending material is containing arsenic rate high (conventionally more than 15%), + 3 valencys and+5 valency arsenic react the calcium arsenite or calcium arsenate (calcium arsenate belongs to toxic articles) the total arsenic in sulfuric acid-nitric acid digestion agent (< < solid waste Leaching leaching method sulfuric acid nitrate method > > (HJ/T299-2007)) of pH=3.20 ± 0.05 that generate and significantly leach with cement, innoxious standard far above 5mg/L, its subsequent treatment cannot reach the requirement of safety-health-environmental protection.
Meaning containing arsenic waste dangerous chemical harmlessness disposing:
Waste dangerous chemical, refer to the hazardous chemical of being abandoned or abandoning by everyone without use, superseded, of poor quality, expired, to lose efficacy hazardous chemical, the hazardous chemical that the hazardous chemical of in accordance with the law being taken in administrative management activity by authorities such as public security, customs, quality inspection, industry and commerce, agricultural, security control, environmental protection and the public of reception submit.The < < Hazardous Waste List > > of country (2008) lists 498 kinds of preferential administrative class waste dangerous chemicals, containing arsenic class, (comprise 2-atoxylate, 3-atoxylate, Ponazuril, Ponazuril hydrogen sodium, phenyl dichloro arsenic, phenylarsonic acid, propyl group arsenic acid, anthraquinone-1-arsenic acid, hexichol (base) chloroarine, diphenylamine-arsine chloride, diiodo-phenylarsine, 4-dimethyl amino-azo-benzene-4 '-arsenic acid, methanearsonic acid, pyroarsenic acid, 2-chlorovinyldichloroarsine, arsenic acid, sodium metaarsenate, (4-hydroxyl-3-nitrobenzophenone) arsenic acid, arsenic triiodide, arsenic trifluoride, arsenic trichloride, arsenic tribromide, three oxidation (two) arsenic, arsenic, arsenic mercury, arsenic hydride, arsenic acid, barium arsenate, potassium dihydrogen arsenate, monosodium arsenate, calcium arsenate, mercuric arsenate, Macquer's salt, magnesium arsenate, natrium arsenicum, lead arsenate, diammonium hydrogen arsenate, disodium hydrogen arsenate, arsenic acid antimony, ferric arsenate, copper arsenate, zinc arsenate, ferrous arsenate, silver arsenate, (2-nitrobenzophenone) arsenic acid, (3-nitrobenzophenone) arsenic acid, (4-nitrobenzophenone) arsenic acid, barium arsenite, calcium arsenite, potassium arsenite, sodium arsenite, lead arsenite, strontium arsenite, arsenious acid antimony, iron arsenite, copper arsenite, zinc arsenite, silver arsenite, ethyl dichloroarsine, copper acetoarsenite etc.) 60 kinds, account for 12% of kind sum.
Severe poisonous chemicals refers to the chemicals with very violent toxic hazard, comprises artificial synthetic chemicals and composition thereof (containing agricultural chemicals) and natural toxin.< < severe poisonous chemicals register > > (2002 editions) includes 335 kinds altogether, wherein, containing 16 kinds of arsenic classes, comprises phenyl dichloro arsenic, diphenylamine-arsine chloride, 2-chlorovinyldichloroarsine, arsenic trichloride, three oxidation (two) arsenic, arsenic hydride, arsenic acid, calcium arsenate, copper arsenate, potassium arsenite, sodium arsenite, copper acetoarsenite etc.
The frequency that participates in International Operations along with China improves day by day, the importance of anti-terrorism work becomes increasingly conspicuous, in time, Safety destroy is discarded containing arsenic hazardous chemical toxic articles guarantee to eliminate respective environment hidden danger particularly, becomes the vital task of the departments of government such as various places public security, environmental protection.Yet compared with developed countries, China lacks really can realize the discarded technology containing arsenic hazardous chemical harmlessness disposing, up to now, the domestic destruction unit that not yet occurs possessing corresponding disposal qualification and actual disposing capacity.Most areas are deposited and are failed for many years to obtain Safety destroy and have great potential safety hazard containing arsenic toxic articles.
Summary of the invention
The object of the present invention is to provide a kind of harmless treatment process containing arsenic waste dangerous chemical, to realize containing arsenic toxic articles, destroy nearby, fill up the blank of correlation technique.
Of the present inventionly solve by the following technical solutions above-mentioned technical problem:
A harmless treatment process containing arsenic waste chemicals, comprises the following steps:
1) will mix with water containing arsenic discarded object, add molysite or ferrous salt, then be less than 2 with the pH value of nitric acid regulator solution; Then add hydrogen peroxide, make organo-arsenic and trivalent As in reaction system all be converted into AsO 4 3-, make Fe simultaneously 2+all be converted into Fe 3+;
2) take calcium hydroxide regulating step 1) the pH value of gained solution is 9~10, forms arsenic iron complex precipitation;
3) to step 2) in add cement to be cured processing in the precipitation that produces and waste liquid, obtain solidified cement body.
Described step 1), in, the addition of water should be controlled at and can make to form the aqueous solution or suspension containing arsenic discarded object.
Preferably, step 1) in, the Fe element in described molysite or ferrous salt is more than or equal to 2.5:1 with the mol ratio that contains the As element in arsenic discarded object.Described ferrous salt can be ferrous sulfate, frerrous chloride or ferrous nitrate.
Preferably, step 1) in, the mass percent concentration of described hydrogen peroxide is 20%~30%; For guaranteeing that organo-arsenic and trivalent As in reaction system are all converted into AsO 4 3-, make Fe simultaneously 2+all be converted into Fe 3+, the H in hydrogen peroxide 2o 2be greater than 3:1 with the mol ratio that contains the As element in arsenic discarded object.
Preferably, step 3) in, the addition of described cement and the described mass ratio that contains arsenic discarded object are (3~5): 1.Curing processing described in the present invention adopts cement solidification treatment technology conventional in this area.
Technique provided by the present invention is organically integrated chemical disposal technology and cement solidification technology, by selecting specific pH condition, makes AsO 4 3-be converted into specific arsenic iron complex precipitation, then be cured processing formation solidified cement body.Finally make the Leaching concentration of the arsenic of obtained solidified cement body be less than 5mg/L, reached national relevant innoxious standard.
Compared with prior art, the present invention also has the following advantages:
1, whole industrial flow is safe and reliable, and except having when disposing organo-arsenic carbon dioxide discharge, without waste gas, discharge of wastewater, waste residue toxicity can be ignored, and amount send professional landfill yard direct landfill at least, and amount can be concentrated greatly and send arsenic refinement unit to recycle.
2, practical, can realize site disposal or destroy nearby in conjunction with portable chemical laboratory, avoid toxic articles uncertain security risk and a large amount of manpower and materials of saving in sending disposal transportation outside, eliminated the social safety hidden danger containing arsenic toxic articles completely.
Accompanying drawing explanation
Fig. 1 is the harmless treatment process schematic flow sheet containing arsenic waste dangerous chemical of the present invention.
The specific embodiment
The present invention selects the multiple mixture containing arsenic toxic articles as processing object, adopts chemical disposal-cement solidification technique to pass through respectively pilot scale and through engineering approaches application, and its implementation process is:
Embodiment 1 pilot process:
(1) process object
Suzhou Shang Mei international cosmetic Co., Ltd contains arsenic toxic articles: natrium arsenicum 300g, and arsenic trioxide 493g, sodium arsenite 250g, the total arsenic of original mixture leachate is higher than 50000mg/L.
(2) treatment process process
Process flow diagram is as shown in Figure 1:
In movable type reaction still, by above-mentioned, containing arsenic toxic articles mixture, be added to the water, add ferrous sulfate, form solution, make the mol ratio of Fe and As in solution be more than or equal to 2.5:1, again by nitric acid regulator solution pH value to being less than 2, then add hydrogen peroxide (mass percent concentration of hydrogen peroxide is 20%~30%) to carry out oxidation reaction; Wherein control the H in hydrogen peroxide 2o 2with the mol ratio 3:1 that contains the arsenic element in arsenic discarded object.Reaction was carried out after 1-2 hour, then to add calcium hydroxide regulator solution pH value be 9~10, now formed arsenic iron complex and precipitated.Gained precipitation is together added in 200L carbon steel tank with waste liquid, then add 4000g cement, be cured and process the stable solidified cement body of formation.
(3) experimental rig specification and size
Portable reaction still: 50L, material is double-deck Pyrex (GG17 material), configuration frequency control agitator 1 cover (250W), temperature-controlling system etc.
Solidification equipment: 200L carbon steel tank.
(4) test effect
By < < household refuse landfill sites, polluting control criterion > > GB16889-2008 detects, it is 0.07mg/L that solidified cement body leaches total arsenic concentration, meets the direct landfill requirement of household refuse landfill sites.
Embodiment 2 through engineering approaches application:
(1) process object
Wujiang green happy solid waste recycling disposal Co., Ltd is containing arsenic hazardous chemical, 15 tons, arsenic content (on average) 37.18%, leaching arsenic 29702mg/L.
(2) each processing unit technological parameter
Reaction tank: reaction tank is PP structure, is of a size of Φ 3.0m * 2.2m, dischargeable capacity 14m 3, configuring 1 agitating device, power is 7.5kW, above establishes exhaust system (air-introduced machine power is 5.5kW), divides into plate and frame filter press 1 cover (80m 2).
Solidify machine: two shaft pugmill mixer, productivity ratio 25m 3/ h.
Process flow diagram is as shown in Figure 1:
By above-mentioned, containing arsenic hazardous chemical 200kg, drop in reaction tank, add ferrous chloride aqueous solution, making the mol ratio of Fe and As in solution is 2.5:1, then by nitric acid regulator solution pH value to being less than 2, then add hydrogen peroxide (mass percent concentration of hydrogen peroxide is 30%) to carry out oxidation reaction; Wherein control the H in hydrogen peroxide 2o 2with the mol ratio of arsenic element containing in arsenic discarded object be 3:1.Reaction was carried out after 2 hours, then to add calcium hydroxide regulator solution pH value be 9~10, now formed arsenic iron complex and precipitated.Finally add again 900kg cement, in solidifying machine, be cured and process the stable solidified cement body of formation.
(3) through engineering approaches application treatment effect
By < < hazard waste landfill, polluting control criterion > > GB18598-2001 detects, it is 1.7mg/L that solidified cement body leaches total arsenic concentration, meets the direct landfill requirement of hazardous waste landfill.
(4) technical economic analysis
By engineering operation cost analysis (mainly taking five parts by labour cost, the electricity charge, medicament expense, laboratory fee, landfill forms), per ton is 71453 yuan (by 200kg/ days scales) containing the disposal cost of arsenic hazardous chemical.

Claims (4)

1. containing a harmless treatment process for arsenic waste chemicals, comprise the following steps:
1) will mix with water containing arsenic discarded object, add molysite or ferrous salt, then be less than 2 with the pH value of nitric acid regulator solution; Then add hydrogen peroxide, make organo-arsenic and trivalent As in reaction system all be converted into AsO 4 3-, make Fe simultaneously 2+all be converted into Fe 3+;
2) take calcium hydroxide regulating step 1) the pH value of gained solution is 9~10, forms arsenic iron complex precipitation;
3) to step 2) in add cement to be cured processing in the precipitation that produces and waste liquid, obtain solidified cement body.
2. the harmless treatment process containing arsenic waste chemicals as claimed in claim 1, is characterized in that step 1) in, the Fe element in described molysite or ferrous salt is more than or equal to 2.5:1 with the mol ratio that contains the As element in arsenic discarded object.
3. the harmless treatment process containing arsenic waste chemicals as claimed in claim 1, is characterized in that step 1) in, the H in described hydrogen peroxide 2o 2be greater than 3:1 with the mol ratio that contains the As element in arsenic discarded object.
4. the harmless treatment process containing arsenic waste chemicals as described in arbitrary claim in claim 1-4, is characterized in that step 3) in, the addition of described cement and the described mass ratio that contains arsenic discarded object are (3~5): 1.
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* Cited by examiner, † Cited by third party
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CN107188292A (en) * 2017-05-19 2017-09-22 山东国大黄金股份有限公司 A kind of utilization silver extraction by cyanidation waste residue purifies the method containing arsenic waste solution

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CN103551378B (en) * 2013-11-20 2015-06-24 华北电力大学 Combined microwave oxidation compound repair system and method aiming at organic arsenic pollution in soil
CN104043645B (en) * 2014-06-13 2016-02-10 中国科学院武汉岩土力学研究所 A kind of arsenic Polluted Soil restorative procedure
CN104174634B (en) * 2014-08-15 2015-12-30 江苏理工学院 The stable curing method of highly acid arsenones waste residue
CN104438288B (en) * 2014-11-19 2016-03-23 中南大学 A kind of containing the stable of arsenic in arsenic waste material and separation method
CN104475431B (en) * 2015-01-01 2017-09-29 扬州杰嘉工业固废处置有限公司 A kind of stabilisation curing of high poison waste residue
CN106180138B (en) * 2016-07-15 2018-12-11 深圳市深投环保科技有限公司 A kind of processing method of arsenic-containing waste
CN111151550A (en) * 2018-11-07 2020-05-15 祥云县黄金工业有限责任公司 Harmless treatment process for arsenic-containing waste residues
CN111035882A (en) * 2019-11-21 2020-04-21 扬州杰嘉工业固废处置有限公司 Method for the synergistic treatment of arsenic-containing waste and barium-containing waste for stabilization and solidification
CN112717319B (en) * 2020-12-16 2022-04-08 陕西新天地固体废物综合处置有限公司 Harmless treatment method for arsenic-containing waste reagent
CN114681856A (en) * 2020-12-28 2022-07-01 有研资源环境技术研究院(北京)有限公司 Immobilized combined agent and method for immobilizing waste residue containing As (III) and heavy metals
CN112919801B (en) * 2021-02-23 2022-03-15 浙江本尊新材料科技有限公司 Method for preparing arsenic-containing borosilicate glass by arsenic solid waste treatment
CN115554647B (en) * 2022-10-26 2023-09-01 中节能(攀枝花)清洁技术发展有限公司 Method for cooperatively treating dangerous chemicals

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CN101041498A (en) * 2007-04-29 2007-09-26 东北大学 Method for reclaiming valuable element from acidic arsenic-containing biological oxidation gold extraction waste liquor
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CN101502840A (en) * 2009-03-10 2009-08-12 浙江大学 Harmless treatment technique of solid dangerous waste

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CN1095648A (en) * 1992-09-22 1994-11-30 詹姆斯·汉密尔顿·凯尔 The composition and the method that are used for waste disposal
CN1569289A (en) * 2004-05-12 2005-01-26 上海洁申实业有限公司 Harmless treatment method for arsenic contained rejectamenta
US7338429B2 (en) * 2006-03-20 2008-03-04 Council Of Scientific & Industrial Research Method for direct solidification and stabilization of liquid hazardous wastes containing up to 100,000 mg/L of arsenic
CN101041498A (en) * 2007-04-29 2007-09-26 东北大学 Method for reclaiming valuable element from acidic arsenic-containing biological oxidation gold extraction waste liquor
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Publication number Priority date Publication date Assignee Title
CN107188292A (en) * 2017-05-19 2017-09-22 山东国大黄金股份有限公司 A kind of utilization silver extraction by cyanidation waste residue purifies the method containing arsenic waste solution

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