CN106823234A - A kind of method that hydro-thermal method prepares the solid arsenic mineral of high stability - Google Patents

A kind of method that hydro-thermal method prepares the solid arsenic mineral of high stability Download PDF

Info

Publication number
CN106823234A
CN106823234A CN201611192966.5A CN201611192966A CN106823234A CN 106823234 A CN106823234 A CN 106823234A CN 201611192966 A CN201611192966 A CN 201611192966A CN 106823234 A CN106823234 A CN 106823234A
Authority
CN
China
Prior art keywords
arsenic
mineral
solid
high stability
solution
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.)
Granted
Application number
CN201611192966.5A
Other languages
Chinese (zh)
Other versions
CN106823234B (en
Inventor
刘智勇
刘志宏
李启厚
王祖林
周亚明
李玉虎
宋柯舟
Current Assignee (The listed assignees may be inaccurate. Google has not performed a legal analysis and makes no representation or warranty as to the accuracy of the list.)
Central South University
Original Assignee
Central South University
Priority date (The priority date 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 date listed.)
Filing date
Publication date
Application filed by Central South University filed Critical Central South University
Priority to CN201611192966.5A priority Critical patent/CN106823234B/en
Publication of CN106823234A publication Critical patent/CN106823234A/en
Application granted granted Critical
Publication of CN106823234B publication Critical patent/CN106823234B/en
Active legal-status Critical Current
Anticipated expiration legal-status Critical

Links

Classifications

    • AHUMAN NECESSITIES
    • A62LIFE-SAVING; FIRE-FIGHTING
    • A62DCHEMICAL MEANS FOR EXTINGUISHING FIRES OR FOR COMBATING OR PROTECTING AGAINST HARMFUL CHEMICAL AGENTS; CHEMICAL MATERIALS FOR USE IN BREATHING APPARATUS
    • A62D3/00Processes for making harmful chemical substances harmless or less harmful, by effecting a chemical change in the substances
    • A62D3/30Processes for making harmful chemical substances harmless or less harmful, by effecting a chemical change in the substances by reacting with chemical agents
    • A62D3/33Processes for making harmful chemical substances harmless or less harmful, by effecting a chemical change in the substances by reacting with chemical agents by chemical fixing the harmful substance, e.g. by chelation or complexation
    • AHUMAN NECESSITIES
    • A62LIFE-SAVING; FIRE-FIGHTING
    • A62DCHEMICAL MEANS FOR EXTINGUISHING FIRES OR FOR COMBATING OR PROTECTING AGAINST HARMFUL CHEMICAL AGENTS; CHEMICAL MATERIALS FOR USE IN BREATHING APPARATUS
    • A62D2101/00Harmful chemical substances made harmless, or less harmful, by effecting chemical change
    • A62D2101/40Inorganic substances
    • A62D2101/43Inorganic substances containing heavy metals, in the bonded or free state

Abstract

The present invention relates to a kind of method that hydro-thermal method prepares the solid arsenic mineral of high stability, arsenic solution dearsenification high will be contained and solidified, and arsenic containing solution is obtained harmless treatment.After trivalent arsenic in arsenic containing solution is pentavalent arsenic by the present invention through catalysis oxidation, oxidated solution synthesizes the solid arsenic mineral of high stable using the heavy arsenic method hydro-thermal method of lime, can directly store up.First pass through the heavy arsenic method of lime and obtain calcium arsenate, then calcium arsenate is changed into the solid arsenic mineral of high stability using hydro-thermal method, toxicity is leached and meets GB5085.3 2007 (solid waste judging standard leaching characteristic identification) regulations.Present invention process flow is short, and arsenic effect of sinking is good, and liquid can be discharged directly after heavy arsenic, and the solid arsenic mineral stability of synthesis is high, stabilization can be stored up under the conditions of wide ph range 2~11 and strong reducing property.

Description

A kind of method that hydro-thermal method prepares the solid arsenic mineral of high stability
Technical field
The invention belongs to mineral As retention field, it is related to a kind of preparation method of the solid arsenic mineral of high stability.
Background technology
Arsenic is a kind of hypertoxic element, and has high carcinogenic, and extensive association is in various non-ferrous metal metallurgy process systems.Closely Over 30 years, as China's non-ferrous metal industry is developed rapidly, arsenic pollution problem is more severe, seriously threatens the life of people Health.Therefore, it is a urgent and relevant problem to carry out arsenic pollution Controlling research.
Current As retention mainly includes encapsulating and the solid class of arsenic two of mineral.Encapsulating is exactly with materials such as cement, glass, to containing Arsenic material is coated, and can be stablized and be stored up.This method solid waste amount is big, high cost, it is difficult to extensive use.The solid arsenic of mineral Will arsenic be converted into stability arsenic-containing ores high and store up.Gu the selection of arsenic mineral, should from leach stability, mineral arsenic content, Leach product toxicity, prepare many-sided choosing comprehensively such as complexity and cost.Primary and secondary arsenic mineral, although sum is up to More than 300 plant, but it is rare to be wherein used for " choosing of satisfaction " reality category of solid arsenic.In Ca (II)-As (V)-H2In O systems, different bars A series of calcium arsenate mineral can be synthesized under part, its stability is higher;But, solubility is larger in acid condition for calcium arsenate, and Ca (II) ion therein can be with solubilised state CO2Reaction, generates calcium carbonate and discharges arsenic again.Therefore, calcium arsenate class mineral And solid arsenic mineral should not be used as.In Fe (III)-As (V)-H2In O systems, change reaction condition can prepare a series of compositions, Crystal formation and the different precipitated ferric arsenate of crystallinity.Wherein, scorodite (FeAsO4·2H2O), because its stability is high, theoretical arsenic content Up to 32%, it is easy to the aqueous low advantage of solid-liquor separation, slag in crystalline state, is the optimal arsenic mineral admittedly generally acknowledged at present.
The preparation method of current scorodite is broadly divided into three major types:Hydro-thermal method, non-pressure process and improvement non-pressure process.Wherein hydro-thermal , due to the HTHP for needing, energy consumption is larger, it is difficult to commercial Application for method;Non-pressure process prepares scorodite, but its cycle at ambient pressure It is more long;Non-pressure process is improved in normal pressure, degree of supersaturation is controlled by slow iron protoxide ion under the conditions of 75~90 DEG C, at 7 hours High-crystallinity scorodite is inside prepared for, is optimal preparation method generally acknowledged at present.Scorodite has stronger stability, conventional Research in arsenic leaching concentration it is minimum up to 0.5mg/L, but this is only limitted under faintly acid (pH value 2~6) and oxidizing condition, and Highly acid or basic region or under reductive condition, it leaches less stable.Therefore, further research is prepared to alkalescence Scorodite with strong reducing property ambient stable is extremely necessary.
In the patent announced at present, Japan same and mining industry Co., Ltd patent of invention (CN 102153145 A, CN 101952204 A) first proposition ferrous iron be source of iron, process arsenic containing solution, and prepare scorodite and iron arsenate powder, The heavy arsenic of the method is thoroughly, simple and convenient, but the scorodite and ferric arsenate that prepare are only steady in narrower pH (2~6) scope interior energy Surely store up, the toxicity of arsenic leaches the limit for exceeding well over GB5085.3-2007 national Specifications under the conditions of alkalescence or strong reducing property Value (<5mg/L).
The content of the invention
It is an object of the invention to provide a kind of preparation method of the solid arsenic mineral of high stability, one kind can be prepared and existed The solid arsenic mineral of stabilization under the conditions of pH scopes wide and strong reducing property.Process is simple of the invention, easy to operate, the solid arsenic minerals of preparation Thing arsenic content is higher, and toxicity leaching concentration is very low, and stable region field width, stabilization can be stored up under the conditions of strong reducing property.
To realize the purpose of the present invention, there is provided following technical scheme:
A kind of preparation method of the solid arsenic mineral of high stability, comprises the following steps:
(1) arsenic containing solution catalysis oxidation
By way of catalysis oxidation, to oxidizing gas and catalyst is added in arsenic containing solution, by the As in solution3+Turn Become As5+
(2) the heavy arsenic of oxidated solution
Solution ph after step (1) gained oxidation is adjusted to 1.5~3, CaO, Ca are added in the way of continuous charging (OH)2In one or two as heavy arsenical, the mol ratio for making Ca and As in the solution is 2~8:1, the sedimentation time is 5 ~10 hours, reaction temperature was 10 DEG C~90 DEG C;
(3) the solid arsenic mineral of hydro-thermal method synthesis
Step (2) products therefrom is placed in reactor carries out solid arsenic treatment, to iron salt solutions are added in reaction system, makes The mol ratio of Fe and As is controlled 1~5:1, regulation and control reaction is carried out under the conditions of pH value 1.5~3, makes Fe3+With AsO4 3-Reaction life Into the solid arsenic mineral of high stability.
In step (1), the main component of the arsenic containing solution includes:As 5~100g/L, Sb 0.5g/L~3g/L, Pb 10~120g/L of 50ppm~800ppm, Sn 2ppm~200ppm, Te 10~500ppm, NaOH.
Oxidizing gas described in step (1) are oxygen, air or oxygen-enriched air;Preferably, the oxidizing gas Gas flow is controlled in 1~20L/min.
Catalyst described in step (1) is KMnO4;Preferably, the mol ratio of As and Mn is controlled 5:1~50:1.
The temperature that catalytic oxidation system is controlled described in step (1) is 30 DEG C~120 DEG C.
Preferably, the condition that the hydro-thermal method described in step (3) is controlled is that reaction temperature is 100 DEG C~200 DEG C, during reaction Between be 2h~10h, mixing speed 50r/min~500r/min.
Iron salt solutions described in step (3) include:In ferrum sulfuricum oxydatum solutum, ferric chloride solution or iron nitrate solution at least One kind is preferably ferrum sulfuricum oxydatum solutum.
Preferably, the addition speed of the iron salt solutions described in step (3) is 5-30ml/min.
Preferably, the reaction time described in step (3) is 2~10h.
The present invention adds iron salt solutions as heavy arsenical in the way of continuous charging, and height is synthesized surely with the arsenic in solution Qualitatively consolidate arsenic mineral.
As a kind of specific embodiment of the invention:
Specifically include following steps (flow is referred to shown in Fig. 1):
1st, arsenic containing solution catalysis oxidation operation, by way of catalysis oxidation, to adding oxidizing gas in arsenic containing solution And catalyst, by the As in solution3+It is transformed into As5+
2nd, the solid arsenic operation of oxidated solution, is adjusted to 1.5~3, with continuous charging by the solution ph after step (1) gained oxidation Mode add CaO, Ca (OH)2In one or two as heavy arsenical, make the mol ratio of Ca and As in the solution for 2~ 8:1, the sedimentation time is 5~10 hours, and reaction temperature is 10 DEG C~90 DEG C;
3rd, the solid arsenic mineral operation of hydro-thermal method synthesis, step (2) products therefrom is placed in reactor carries out solid arsenic treatment, to Iron salt solutions are added in reaction system, the mol ratio of Fe and As is controlled 1~5:1, regulation and control reaction is in the condition of pH value 1.5~3 Under carry out, make Fe3+With AsO4 3-The solid arsenic mineral of high stability is synthesized;The iron salt solutions are ferrum sulfuricum oxydatum solutum, iron chloride At least one in solution or iron nitrate solution.The addition speed of described iron salt solutions is 5-30ml/min.
Advantages of the present invention:
(1) present invention process is simple, and easy to operate, agents useful for same molysite, oxygen is laboratory common experimental material, instead Mild condition is answered, it is low for equipment requirements.
(2) the solid arsenic mineral crystallinity that prepared by the present invention is high, it is easy to solid-liquor separation.
(3) the solid arsenic mineral that the present invention is prepared is because its crystallinity is high, BET specific surface area is small, stable region field width, and has Standby high stability.And the leaching concentration of its arsenic be less than 0.5mg/L, less than GB5085.3-2007 (solid waste judging standard- Leaching characteristic identification) regulation, can store up safely, solve solid arsenic mineral and be difficult to stablize under alkalescence and reductive condition and store up this One problem.
In a word, the rational operation collocation of the present invention, by strictly controlling the conditional parameter in each operation, synthesize highly crystalline The solid arsenic mineral of degree, bulky grain, high stability, Gu arsenic mineral stability is high, and can be in wide ph range (2~11) and strong reducing property bar Stabilization is stored up under part, reduces the cost of arsenic treatment, has reached the purpose of environmental protection, economy, energy-conservation, high security, realizes the nothing of arsenic Evilization.
Brief description of the drawings
Fig. 1 the inventive method process flow diagrams.
Specific embodiment
Following examples are used to illustrate the present invention, but are not limited to the scope of the present invention.
Embodiment 1
Main component includes in arsenic containing solution:As 60g/L, Sb 1.1g/L, Pb 235ppm, Sn 38.5ppm, Te 24.4ppm, NaOH 30g/L.
A kind of preparation method of the solid arsenic mineral of high stability, comprises the following steps:Arsenic containing solution uses the side of catalysis oxidation Method is by As3+It is oxidized to As5+, the condition for controlling is that oxygen flow is 5L/min, adds KMnO4For catalyst makes As/Mn mol ratios Control is 10:1, as a result catalytic oxidation system temperature control shows at 90 DEG C, As3+Conversion ratio be 98.45%.
The pH value of oxidated solution is adjusted to 1.5, CaO and Ca (OH) is added in the way of continuous charging2As heavy arsenical, Ca/As mol ratios are 5, and the sedimentation time is 6 hours, and reaction temperature is 60 DEG C, generates calcium arsenate.The solid arsenic mineral of synthesis uses hydro-thermal Method, control condition is that calcium arsenate is placed in reactor, to ferrum sulfuricum oxydatum solutum is added in kettle, is controlled to its Fe/As mol ratio 2.5, make Fe3+With AsO4 3-The solid arsenic mineral of high stability is synthesized;Other control conditions are that reaction temperature is 120 DEG C, instead It is 6h, mixing speed 400r/min between seasonable.The solid arsenic mineral of the high stability of synthesis, according to GB5085.3-2007 (solid waste Judging standard-leaching characteristic identification) toxicity leaching is carried out, the leaching concentration of arsenic is 0.41mg/L, less than the limit value of the standard, Can safety and stability store up.
Embodiment 2
Main component includes in arsenic containing solution:As 76g/L, Sb 0.8g/L, Pb 96.7ppm, Sn 27.5ppm, Te 38.7ppm, NaOH 25g/L.
A kind of preparation method of the solid arsenic mineral of high stability, comprises the following steps:Arsenic containing solution uses the side of catalysis oxidation Method is by As3+It is oxidized to As5+, the condition for controlling is that oxygen flow is 10L/min, adds KMnO4For catalyst makes As/Mn moles Than controlling 40:1, as a result catalytic oxidation system temperature control shows at 30 DEG C, As3+Conversion ratio be 92.31%;
The pH value of oxidated solution is adjusted to 2, CaO and Ca (OH) is added in the way of continuous charging2As heavy arsenical, Ca/ As mol ratios are 8, and the sedimentation time is 8 hours, and reaction temperature is 90 DEG C, generates calcium arsenate.The solid arsenic mineral of synthesis uses hydro-thermal method, Control condition is that calcium arsenate is placed in reactor, to ferrum sulfuricum oxydatum solutum is added in kettle, its Fe/As mol ratio is controlled to 5, Fe3+With AsO4 3-The solid arsenic mineral of high stability is synthesized;Other control conditions are that reaction temperature is 150 DEG C, reaction time It is 7h, mixing speed 100r/min.The solid arsenic mineral of the high stability of synthesis, according to GB5085.3-2007, (solid waste differentiates mark Standard-leaching characteristic identification) toxicity leaching is carried out, the leaching concentration of arsenic is 0.67mg/L, less than the limit value of the standard, can be safe Stabilization is stored up.
Embodiment 3
Main component includes in arsenic containing solution:As 50g/L, Sb 1.8g/L, Pb 186ppm, Sn 34.7ppm, Te 27.8ppm, NaOH 5g/L.
A kind of preparation method of the solid arsenic mineral of high stability, comprises the following steps:Arsenic containing solution uses the side of catalysis oxidation Method is by As3+It is oxidized to As5+, the condition for controlling is that oxygen flow is 1L/min, adds KMnO4For catalyst makes As/Mn mol ratios Control is 20:1, as a result catalytic oxidation system temperature control shows at 120 DEG C, As3+Conversion ratio be 89.36%
The pH value of oxidated solution is adjusted to 1.5, CaO and Ca (OH) is added in the way of continuous charging2As heavy arsenical, Ca/As mol ratios are 5, and the sedimentation time is 10 hours, and reaction temperature is 60 DEG C, generates calcium arsenate.The solid arsenic mineral of synthesis uses water Hot method, control condition is that calcium arsenate is placed in reactor, to ferrum sulfuricum oxydatum solutum is added in kettle, controls its Fe/As mol ratio It is 3, Fe3+With AsO4 3-The solid arsenic mineral of high stability is synthesized;Other control conditions are that reaction temperature is 120 DEG C, reaction Time is 4h, mixing speed 350r/min.The solid arsenic mineral of the high stability of synthesis, according to GB5085.3-2007, (solid waste reflects Other standard-leaching characteristic identification) toxicity leaching is carried out, the leaching concentration of arsenic is 0.54mg/L, less than the limit value of the standard, can Safety and stability is stored up.
Although above having used general explanation, specific embodiment and experiment, the present invention is made to retouch in detail State, but on the basis of the present invention, it can be made some modifications or improvements, this is to those skilled in the art apparent 's.Therefore, these modifications or improvements without departing from theon the basis of the spirit of the present invention, belong to claimed Scope.

Claims (7)

1. a kind of high stability consolidates the preparation method of arsenic mineral, it is characterised in that comprise the following steps:
(1) arsenic containing solution catalysis oxidation
By way of catalysis oxidation, to oxidizing gas and catalyst is added in arsenic containing solution, by the As in solution3+It is transformed into As5+
(2) the heavy arsenic of oxidated solution
Solution ph after step (1) gained oxidation is adjusted to 1.5~3, CaO, Ca (OH) are added in the way of continuous charging2In One or two as heavy arsenical, the mol ratio for making Ca and As in the solution is 2~8:1, the sedimentation time is 5~10 small When, reaction temperature is 10 DEG C~90 DEG C;
(3) the solid arsenic mineral of hydro-thermal method synthesis
Step (2) products therefrom is placed in reactor carries out solid arsenic treatment, to iron salt solutions are added in reaction system, makes reaction The mol ratio of Fe and As is controlled 1~5 in system:1, regulation and control reaction is carried out under the conditions of pH value 1.5~3, makes Fe3+With AsO4 3- The solid arsenic mineral of reaction generation high stability;The iron salt solutions are in ferrum sulfuricum oxydatum solutum, ferric chloride solution or iron nitrate solution At least one.
2. high stability according to claim 1 consolidates the preparation method of arsenic mineral, it is characterised in that:It is described in step (1) The main component of arsenic containing solution includes:As 5~100g/L, Sb 0.5g/L~3g/L, Pb 50ppm~800ppm, Sn 2ppm 10~120g/L of~200ppm, Te 10~500ppm, NaOH.
3. high stability according to claim 1 and 2 consolidates the preparation method of arsenic mineral, it is characterised in that institute in step (1) Oxidizing gas are stated for oxygen, air or oxygen-enriched air;Preferably, the gas flow control of the oxidizing gas 1~ 20L/min。
4. the preparation method of the solid arsenic mineral of high stability according to claim any one of 1-3, it is characterised in that step (1) catalyst described in is KMnO4;Preferably, the mol ratio of As and Mn is controlled 5:1~50:1.
5. the preparation method of the solid arsenic mineral of high stability according to claim any one of 1-4, it is characterised in that step (1) temperature that catalytic oxidation system described in is controlled is 30 DEG C~120 DEG C.
6. the preparation method of the solid arsenic mineral of high stability according to claim any one of 1-5, it is characterised in that step (3) condition that the hydro-thermal method described in is controlled is that reaction temperature is 100 DEG C~200 DEG C, and the reaction time is 2h~10h, mixing speed 50r/min~500r/min.
7. the preparation method of the solid arsenic mineral of high stability according to claim any one of 1-6, it is characterised in that step (3) the addition speed of the iron salt solutions described in is 5-30ml/min.
CN201611192966.5A 2016-12-21 2016-12-21 A kind of method that hydro-thermal method preparation high stability consolidates arsenic mineral Active CN106823234B (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
CN201611192966.5A CN106823234B (en) 2016-12-21 2016-12-21 A kind of method that hydro-thermal method preparation high stability consolidates arsenic mineral

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
CN201611192966.5A CN106823234B (en) 2016-12-21 2016-12-21 A kind of method that hydro-thermal method preparation high stability consolidates arsenic mineral

Publications (2)

Publication Number Publication Date
CN106823234A true CN106823234A (en) 2017-06-13
CN106823234B CN106823234B (en) 2019-08-27

Family

ID=59135987

Family Applications (1)

Application Number Title Priority Date Filing Date
CN201611192966.5A Active CN106823234B (en) 2016-12-21 2016-12-21 A kind of method that hydro-thermal method preparation high stability consolidates arsenic mineral

Country Status (1)

Country Link
CN (1) CN106823234B (en)

Cited By (1)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN114836636A (en) * 2022-05-24 2022-08-02 江西理工大学 Method for separating arsenic from arsenic-containing alkali liquor and recovering alkali

Citations (5)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN1155519A (en) * 1996-01-16 1997-07-30 三菱重工业株式会社 Process for treating arsenic-containing waste water
CN102674526A (en) * 2012-05-14 2012-09-19 中南大学 Method for precipitating and stabilizing As from As-containing solution
CN103043812A (en) * 2011-10-13 2013-04-17 中国科学院过程工程研究所 Advanced treatment method for arsenic-containing wastewater
JP2014208338A (en) * 2013-03-29 2014-11-06 三菱マテリアル株式会社 Method for separating and immobilizing arsenic
CN106868320B (en) * 2016-12-21 2019-01-08 中南大学 A kind of high stability consolidates the preparation method of arsenic mineral

Patent Citations (5)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN1155519A (en) * 1996-01-16 1997-07-30 三菱重工业株式会社 Process for treating arsenic-containing waste water
CN103043812A (en) * 2011-10-13 2013-04-17 中国科学院过程工程研究所 Advanced treatment method for arsenic-containing wastewater
CN102674526A (en) * 2012-05-14 2012-09-19 中南大学 Method for precipitating and stabilizing As from As-containing solution
JP2014208338A (en) * 2013-03-29 2014-11-06 三菱マテリアル株式会社 Method for separating and immobilizing arsenic
CN106868320B (en) * 2016-12-21 2019-01-08 中南大学 A kind of high stability consolidates the preparation method of arsenic mineral

Non-Patent Citations (6)

* Cited by examiner, † Cited by third party
Title
BARSHA DASH等: "Arsenic removal from industrial effluents through ferric arsenate precipitation", 《RESEARCHGATE》 *
COLIN SULLIVAN等: "Disposal of water treatment wastes containing arsenic — A review", 《SCIENCE OF THE TOTAL ENVIRONMENT》 *
JIE CUI等: "A new process of continuous three-stage co-precipitation of arsenic with ferrous iron and lime", 《HYDROMETALLURGY》 *
刘琦: "高砷酸性废水除砷新工艺", 《洛阳理工学院学报(自然科学版)》 *
李启厚等: "碱性体系下As(Ⅲ)的催化氧化及其机理研究", 《矿冶工程》 *
黄自力等: "氯化铁对砷酸钙渣的药剂稳定化研究", 《矿冶工程》 *

Cited By (1)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN114836636A (en) * 2022-05-24 2022-08-02 江西理工大学 Method for separating arsenic from arsenic-containing alkali liquor and recovering alkali

Also Published As

Publication number Publication date
CN106823234B (en) 2019-08-27

Similar Documents

Publication Publication Date Title
CN106830091B (en) A kind of precipitation from arsenic containing solution obtains the high method for leaching stability scorodite
CN106868320A (en) A kind of preparation method of the solid arsenic mineral of high stability
CN111170510B (en) Method for treating arsenic-containing wastewater and solidifying arsenic
CN109574319B (en) Arsenic fixing process for high-arsenic waste acid in non-ferrous metal smelting
EP2398739B1 (en) Method for removing arsenic as scorodite
US4289746A (en) Process for preparation of micaceous iron oxide
CN109607872A (en) A kind of comprehensive utilization of the waste acid containing arsenic and the Safe disposal method of arsenic
CN103551025B (en) Harmless treatment method of arsenic-containing flue dust
CN102351294A (en) Method for treating arsenic in waste water
CN107188292B (en) Method for purifying arsenic-containing waste liquid by utilizing cyaniding silver extraction waste residues
CN106044999B (en) A kind of method of Fenton group technology processing waste water
CN114561558B (en) Method for recycling antimony and fixing arsenic from arsenic-containing crystal
CN107522370A (en) A kind of chrome tanning sludge waste liqouor Application way
CN106823234B (en) A kind of method that hydro-thermal method preparation high stability consolidates arsenic mineral
CN110407250A (en) A kind of method that arsenic-containing waste residue is converted into mansfieldite stabilization processes and Recovered sulphur
CN106823235B (en) A kind of method that regulation and control growth method prepares the solid arsenic mineral of high stability
CN107129018A (en) The method for concentration of arsenic in a kind of arsenic-containing waste water
CN104609573A (en) Method for treating acid waste water containing arsenic
CN102557152A (en) Polyferric sulfate solution and method for producing the same
CN106823233B (en) A method of distribution crystallisation preparation high stability consolidates arsenic mineral
CN111039327A (en) Method for converting arsenic slag into scorodite in one step
AU2013215248A1 (en) Treatment of manganese-containing materials
KR102411350B1 (en) Preparation method of monocalcium citrate using disposal oyster shell and application thereof
EP0110848B1 (en) A method for producing water-purifying chemicals
CN109095576A (en) A kind of method that hydrothermal reduction mineralising cooperates with solid arsenic

Legal Events

Date Code Title Description
PB01 Publication
PB01 Publication
SE01 Entry into force of request for substantive examination
SE01 Entry into force of request for substantive examination
GR01 Patent grant
GR01 Patent grant