[go: up one dir, main page]

CN106929698B - A kind of processing method of chromium slag nitration mixture enhanced leaching-extraction and recovery siderochrome - Google Patents

A kind of processing method of chromium slag nitration mixture enhanced leaching-extraction and recovery siderochrome Download PDF

Info

Publication number
CN106929698B
CN106929698B CN201511023816.7A CN201511023816A CN106929698B CN 106929698 B CN106929698 B CN 106929698B CN 201511023816 A CN201511023816 A CN 201511023816A CN 106929698 B CN106929698 B CN 106929698B
Authority
CN
China
Prior art keywords
extraction
chromium slag
chromium
recovery
nitration mixture
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.)
Active
Application number
CN201511023816.7A
Other languages
Chinese (zh)
Other versions
CN106929698A (en
Inventor
杨志平
宋艳
康绍辉
李大炳
樊兴
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.)
Beijing Research Institute of Chemical Engineering and Metallurgy of CNNC
Original Assignee
Beijing Research Institute of Chemical Engineering and Metallurgy of CNNC
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 Beijing Research Institute of Chemical Engineering and Metallurgy of CNNC filed Critical Beijing Research Institute of Chemical Engineering and Metallurgy of CNNC
Priority to CN201511023816.7A priority Critical patent/CN106929698B/en
Publication of CN106929698A publication Critical patent/CN106929698A/en
Application granted granted Critical
Publication of CN106929698B publication Critical patent/CN106929698B/en
Active legal-status Critical Current
Anticipated expiration legal-status Critical

Links

Classifications

    • CCHEMISTRY; METALLURGY
    • C22METALLURGY; FERROUS OR NON-FERROUS ALLOYS; TREATMENT OF ALLOYS OR NON-FERROUS METALS
    • C22BPRODUCTION AND REFINING OF METALS; PRETREATMENT OF RAW MATERIALS
    • C22B34/00Obtaining refractory metals
    • C22B34/30Obtaining chromium, molybdenum or tungsten
    • C22B34/32Obtaining chromium
    • CCHEMISTRY; METALLURGY
    • C21METALLURGY OF IRON
    • C21BMANUFACTURE OF IRON OR STEEL
    • C21B15/00Other processes for the manufacture of iron from iron compounds
    • CCHEMISTRY; METALLURGY
    • C22METALLURGY; FERROUS OR NON-FERROUS ALLOYS; TREATMENT OF ALLOYS OR NON-FERROUS METALS
    • C22BPRODUCTION AND REFINING OF METALS; PRETREATMENT OF RAW MATERIALS
    • C22B7/00Working up raw materials other than ores, e.g. scrap, to produce non-ferrous metals and compounds thereof; Methods of a general interest or applied to the winning of more than two metals
    • C22B7/006Wet processes
    • C22B7/007Wet processes by acid leaching
    • CCHEMISTRY; METALLURGY
    • C21METALLURGY OF IRON
    • C21BMANUFACTURE OF IRON OR STEEL
    • C21B2200/00Recycling of non-gaseous waste material
    • YGENERAL TAGGING OF NEW TECHNOLOGICAL DEVELOPMENTS; GENERAL TAGGING OF CROSS-SECTIONAL TECHNOLOGIES SPANNING OVER SEVERAL SECTIONS OF THE IPC; TECHNICAL SUBJECTS COVERED BY FORMER USPC CROSS-REFERENCE ART COLLECTIONS [XRACs] AND DIGESTS
    • Y02TECHNOLOGIES OR APPLICATIONS FOR MITIGATION OR ADAPTATION AGAINST CLIMATE CHANGE
    • Y02PCLIMATE CHANGE MITIGATION TECHNOLOGIES IN THE PRODUCTION OR PROCESSING OF GOODS
    • Y02P10/00Technologies related to metal processing
    • Y02P10/20Recycling

Landscapes

  • Chemical & Material Sciences (AREA)
  • Engineering & Computer Science (AREA)
  • Organic Chemistry (AREA)
  • Materials Engineering (AREA)
  • Metallurgy (AREA)
  • Manufacturing & Machinery (AREA)
  • Mechanical Engineering (AREA)
  • Life Sciences & Earth Sciences (AREA)
  • Environmental & Geological Engineering (AREA)
  • General Life Sciences & Earth Sciences (AREA)
  • Geology (AREA)
  • Manufacture And Refinement Of Metals (AREA)
  • Processing Of Solid Wastes (AREA)

Abstract

The invention belongs to chromium slag nitration mixture enhanced leaching-extraction and recovery siderochrome technical fields, and in particular to a kind of processing method of chromium slag nitration mixture enhanced leaching-extraction and recovery siderochrome;The present invention uses nitration mixture enhanced leaching, leaches the Cr VI in later period addition reducing agent reducing leaching liquid and slag, and the iron and trivalent chromium in leachate carry out extraction and separation recycling, achievees the purpose that the harmless treatment of chromium slag and the synthetical recovery of iron.Using this method handle chromium slag, can by chromium slag Cr VI and trivalent chromium dissolve out as far as possible, reduce chromic wastes disposal after again occur brightness reversion risk.And synthetical recovery iron and chromium, Fe (OH)3With Cr (OH)3Purity is greater than 99.0%, obtained product iron hydroxide and chromium hydroxide purity is high.

Description

A kind of processing method of chromium slag nitration mixture enhanced leaching-extraction and recovery siderochrome
Technical field
The invention belongs to chromium slag nitration mixture enhanced leaching-extraction and recovery siderochrome technical fields, and in particular to a kind of chromium slag nitration mixture Enhanced leaching-extraction and recovery siderochrome processing method.
Background technique
The metal simple-substance and compound of chromium are in plating casting, chemical industry metallurgical, leather manufacture, bio-pharmaceuticals and aviation The conglomeraties such as space flight are widely used, rank most competitive one of 8 kinds of raw materials.Chromic salts is even more to hold the balance in China status, 15% product is all inseparable with its in national economy, China's chromic salts compound 2006 industrial annual value of production about 4,000,000,000.External chromium Salt production history is more than 200 years, and annual output is more than 1200kt, and mainly there are the countries such as the United States, Russia, English, day, moral in producing region.Chinese chromic salts Development only has 50 years, but develops rapidly, at present chromium salt production amount and the 1st, the world consumption figure Jun Ju.Chromic salts is economical to pull It increases rapidly while play a great role, the severe toxicity for also bringing the title of " city bomb " and " fearful city malignant tumor " is secondary Product-chromium slag.In general, the production quantity of slag of crome metal is 10 times of its output, chromic salts produces 3-5 times that the quantity of slag is its production. Total chrome content is 1-7% in chromium slag, and Cr (VI) content accounts for 1-3%, wherein water-soluble and acid-soluble Cr (VI) ratio is about 2: 3.Soluble Cr (VI) have strong oxidizing property, mutagenicity and carcinogenicity, be internationally recognized 3 kinds of carcinogenic metallic compounds it One.According to statistics, once there were 70 Duo Ge chromium salt production factories in the whole nation, and national production capacity is about 300kt/a, since technique is backward and chromium slag Pollution control burden is big, and stop production and change the line of production about more than 40 families, existing chromium salt factory 25 of the whole nation.Since production technology is backward and environmental protection Consciousness is weak, and China's left over by history chromium slag stores up total amount in 4500kt or so, and also increases every year with the quantity for being more than 800kt Add.Currently, chromium slag is arbitrarily stored up, not only occupy large amount of land resources, and the surface water of the leachate contamination containing Cr (VI) and Underground water, tiny flying dust can also pollute atmosphere, cause significant damage to ecological environment and people's life health.Early in 2005 10 Month, joint formulation announcement " chromium slag contaminated comprehensive improvement action scheme ", which has been formulated, was basically completed chromium slag contaminated site in 2012 The target administered and restored.To current cut-off, this target is not yet realized.Therefore, the innoxious and recycling for carrying out chromium slag is ground Studying carefully has extremely important realistic meaning.
Summary of the invention
For the above-mentioned prior art, it is an object of that present invention to provide a kind of chromium slag nitration mixture enhanced leaching-extraction and recovery siderochrome Processing method, to chromium slag carry out harmless treatment.
In order to achieve the above object, a kind of processing method of chromium slag nitration mixture enhanced leaching-extraction and recovery siderochrome of the present invention, packet Include following steps:
Step 1: by chromium slag certain liquid-solid ratio and at a temperature of, a certain amount of sulfuric acid and hydrochloric acid is added by six in chromium slag Valence chromium is dissolved out with trivalent chromium;
Step 2: the reduction that a certain amount of reducing agent carries out Cr VI is added after nitration mixture dissolution chromium slag;
Step 3: a certain amount of polyethers, which is added, after reduction stirs evenly and stand the regular hour, liquid is then carried out Gu separation;
Step 4: obtained leachate TBP is extracted ferric iron;
Step 5: the organic phase for having extracted iron is washed with hydrochloric acid, the impurity of entrainment is washed away, concentration of hydrochloric acid is 3~ 6mol/L, cleaning solution return to carry out the leaching of chromium slag;Load iron organic phase after washing is stripped with water, time of contact 1~20min, is 1:1~50:1 compared to O/A, 2~10 grades of series, obtains ferric chloride solution by 10~40 DEG C of temperature;
Step 6: it is 2~5 that the NaOH of the raffinate after extraction iron, which is adjusted pH value, trivalent chromium is extracted with P204;
Step 7: the organic phase for having extracted chromium is washed with the solution that pH value is 2~4, remaining impurity is washed away, is washed Water returns to carry out the leaching of chromium slag;
Step 8: the load chromium organic phase acid back extraction after washing.
The liquid-solid ratio that further chromium slag described in step 1 leaches is 3:1~20:1, and temperature is 60~100 DEG C, the time For 20~120min;The nitration mixture of addition is sulfuric acid and hydrochloric acid, and sulphuric acid is 0.1~1 times of chromium slag amount, and hydrochloric acid additional amount is 0.5~3 times of chromium slag amount.
The additional amount of reducing agent described in further step 2 is the 0.1%~5% of chromium slag amount, the reaction time 0.5 ~5h.
Reducing agent described further is that glucose, sodium sulfite, sodium pyrosulfite, sodium thiosulfate are any.
Polyethers additional amount described in further step 3 is the 0.3%~3% of chromium slag amount, and the reaction time is 0.5~2h, It is filtered after standing 12~48h.
Extractant concentration described in further step 4 is 10~30%, and diluent is sulfonated kerosene;Extraction stoste passes through Hydrochloric acid and sodium chloride is added, guarantees that acidity is greater than 0.5mol/L, chloride content is greater than 100g/L;TBP extract iron time of contact be 1~ 20min, extracts 3~9 grades of series by 10~40 DEG C of extraction temperature, extraction phase ratio O/A=1:5~5:1.
P204 concentration described in further step 6 is 10%~30%, and diluent is sulfonated kerosene, and P204 saponification degree is 20%~80%;Extraction time of contact is 1~20min, 10~40 DEG C of extraction temperature, extraction phase ratio O/A=1:5~5:1, is extracted 3~9 grades of series.
Back extraction time of contact described in further step 8 is 5~30min, and temperature is 20~40 DEG C, is compared to O/A 1:1~50:1, extraction series are 2~10 grades.
Technical solution provided in an embodiment of the present invention has the benefit that
A kind of processing method of chromium slag nitration mixture enhanced leaching-extraction and recovery siderochrome of the present invention uses nitration mixture enhanced leaching, leaching The Cr VI in reducing agent reducing leaching liquid and slag is added in the later period out, and the iron and trivalent chromium in leachate carry out extraction and separation and returns It receives, the method for reaching the harmless treatment of chromium slag and the synthetical recovery of iron.
A kind of processing method of chromium slag nitration mixture enhanced leaching-extraction and recovery siderochrome of the present invention compared with existing other methods, Thoroughly with Cr VI dissolution, trivalent chromium is also largely dissolved, and the risk of brightness reversion occurs after reduction chromic wastes disposal again, and comprehensive Iron and chromium are recycled, obtained product iron hydroxide and chromium hydroxide purity is high.
Specific embodiment
It elaborates With reference to embodiment to the present invention.
A kind of processing method of chromium slag nitration mixture enhanced leaching-extraction and recovery siderochrome of the present invention, comprising the following steps:
Step 1: by chromium slag certain liquid-solid ratio and at a temperature of, a certain amount of sulfuric acid and hydrochloric acid is added by six in chromium slag Valence chromium is dissolved out with trivalent chromium;
The liquid-solid ratio that chromium slag leaches is 3:1~20:1, and temperature is 60~100 DEG C, and the time is 20~120min;What is be added is mixed Acid is sulfuric acid and hydrochloric acid, and sulphuric acid is 0.1~1 times of chromium slag amount, and hydrochloric acid additional amount is 0.5~3 times of chromium slag amount;
Step 2: the reduction that a certain amount of reducing agent carries out Cr VI is added after nitration mixture dissolution chromium slag;
Reducing agent used is any, additional amounts such as glucose, sodium sulfite, sodium pyrosulfite, sodium thiosulfate It is the 0.1%~5% of chromium slag amount, the reaction time is 0.5~5h;
Step 3: a certain amount of polyethers, which is added, after reduction stirs evenly and stand the regular hour, liquid is then carried out Gu separation;
Polyethers additional amount is the 0.3%~3% of chromium slag amount, and the reaction time is 0.5~2h, is filtered after standing 12~48h;
Step 4: obtained leachate TBP is extracted ferric iron;
Extractant concentration is 10~30%, and diluent is sulfonated kerosene;Extract stoste by the way that hydrochloric acid and sodium chloride is added, guarantees Acidity is greater than 0.5mol/L, and chloride content is greater than 100g/L;TBP extraction iron time of contact is 1~20min, extraction temperature 10~40 DEG C, extraction phase ratio O/A=1:5~5:1 extracts 3~9 grades of series;
Step 5: the organic phase for having extracted iron is washed with hydrochloric acid, the impurity of entrainment is washed away, concentration of hydrochloric acid is 3~ 6mol/L, cleaning solution return to carry out the leaching of chromium slag;
Load iron organic phase after washing is stripped with water, 1~20min of time of contact, is compared by 10~40 DEG C of temperature O/A is 1:1~50:1,2~10 grades of series, obtains ferric chloride solution;
Step 6: it is 2~5 that the NaOH of the raffinate after extraction iron, which is adjusted pH value, trivalent chromium, P204 concentration are extracted with P204 It is 10~30%, diluent is sulfonated kerosene, and P204 saponification degree is 20%~80%;
Extraction time of contact is 1~20min, 10~40 DEG C of extraction temperature, extraction phase ratio O/A=1:5~5:1, extracts grade 3~9 grades of number;
Step 7: the organic phase for having extracted chromium is washed with the solution that pH value is 2~4, remaining impurity is washed away, is washed Water returns to carry out the leaching of chromium slag;
Step 8: the load chromium organic phase acid back extraction after washing, acid used is hydrochloric acid or sulfuric acid, concentration 0.5mol/L~ 3mol/L;
Back extraction time of contact is 5~30min, and temperature is 20~40 DEG C, is 1:1~50:1 compared to O/A, and extraction series is 2~10 grades.
Embodiment one
Certain chromium slag contains total chromium 3.12%, Cr VI 0.85%, and 6L water, the 200ml concentrated sulfuric acid, 1500ml salt is added in 1kg chromium slag Acid after reacting 60min at 60~80 DEG C, is added 40g glucose and restores 3h at 80~90 DEG C, adds polyethers 15g stirring 30min stops stirring, and standing filters afterwards for 24 hours, obtains containing total chromium 3.56g/L, Cr VI 0.5mg/L, iron 8.7g/L.Titanium dioxide The leachate of silicon 0.4g/L.Remaining slag dry weight 950g contains total chromium 0.23%, presses " hazardous waste judging standard-to the slag after washing Leaching characteristic identification " (GB5085.3-2007), HJ687-2014 alkali digestion procedure, is dissolved and is detected, water soluble hexavalent chromium Content meet as defined in " chromic salts industry pollutant emission standard ", water soluble hexavalent chromium is less than the second level of 8mg/kg in waste residue Discharge standard.
Extract Fe3+Condition: extractant 30%TBP, diluent are sulfonated kerosene.First adjusting raw material liquid acidity with hydrochloric acid is 0.5mol, and a certain amount of NaCl is added, so that Cl in solution-Reach 100g/L.Sodium chlorate is added to aoxidize at 80 DEG C 60min, sodium chlorate additional amount are 0.3%, by ferrous oxidising for ferric iron.Extraction phase ratio O/A=2, time of contact 5min, extraction Taking series is 6 grades, and raffinate contains Fe3+10mg/L.Iron organic phase 5mol/L salt acid elution is carried, O/A=5/1, scrubbing stage are compared Number is 4 grades, and wash water returns to carry out the leaching of chromium slag.Load iron organic phase after washing is stripped iron with pure water, and O/A=is compared in back extraction 10, time of contact 3min, back extraction series are 5 grades, obtain the strip liquor of iron content 30g/L.
Cr3+Extraction: extractant be 10%P204+10% n-octyl alcohol+sulfonated kerosene, saponification degree 50%.Use sodium hydroxide Adjusting has extracted ferric remaining phase, and adjusting pH value is 3.Extraction phase ratio O/A=2, time of contact 5min, extraction series are 10 grades, Raffinate contains Cr3+1.5mg/L.The water washing that chromium organic phase pH value is 3 is carried, O/A=3 is compared, series is 3 grades.After washing It carries chromium organic phase to be stripped with 1mol/L sulfuric acid, compares O/A=1/20, series is 4 grades, obtains the Cr of 35g/L3+Solution.

Claims (8)

1. a kind of processing method of chromium slag nitration mixture enhanced leaching-extraction and recovery siderochrome, which is characterized in that this method includes following step It is rapid:
Step 1: by chromium slag certain liquid-solid ratio and at a temperature of, a certain amount of sulfuric acid and hydrochloric acid is added by the Cr VI in chromium slag It is dissolved out with trivalent chromium;
Step 2: the reduction that a certain amount of reducing agent carries out Cr VI is added after nitration mixture dissolution chromium slag;
Step 3: a certain amount of polyethers, which is added, after reduction stirs evenly and stand the regular hour, then carries out liquid and divide admittedly From;
Step 4: obtained leachate TBP is extracted ferric iron;
Step 5: the organic phase for having extracted iron is washed with hydrochloric acid, the impurity of entrainment is washed away, concentration of hydrochloric acid is 3~6mol/ L, cleaning solution return to carry out the leaching of chromium slag;Load iron organic phase after washing is stripped with water, time of contact 1~ 20min, is 1:1~50:1 compared to O/A, 2~10 grades of series, obtains ferric chloride solution by 10~40 DEG C of temperature;
Step 6: it is 2~5 that the NaOH of the raffinate after extraction iron, which is adjusted pH value, trivalent chromium is extracted with P204;
Step 7: the organic phase for having extracted chromium is washed with the solution that pH value is 2~4, remaining impurity is washed away, wash water returns Go back to carry out the leaching of chromium slag;
Step 8: the load chromium organic phase acid back extraction after washing.
2. the processing method of chromium slag nitration mixture enhanced leaching-extraction and recovery siderochrome according to claim 1, which is characterized in that The liquid-solid ratio that chromium slag described in step 1 leaches is 3:1~20:1, and temperature is 60~100 DEG C, and the time is 20~120min;Add The nitration mixture entered is sulfuric acid and hydrochloric acid, and sulphuric acid is 0.1~1 times of chromium slag amount, and hydrochloric acid additional amount is the 0.5~3 of chromium slag amount Times.
3. the processing method of chromium slag nitration mixture enhanced leaching-extraction and recovery siderochrome according to claim 1, which is characterized in that The additional amount of reducing agent described in step 2 is the 0.1%~5% of chromium slag amount, and the reaction time is 0.5~5h.
4. the processing method of chromium slag nitration mixture enhanced leaching-extraction and recovery siderochrome according to claim 2, which is characterized in that The reducing agent be glucose, sodium sulfite, sodium pyrosulfite, sodium thiosulfate any one.
5. the processing method of chromium slag nitration mixture enhanced leaching-extraction and recovery siderochrome according to claim 1, which is characterized in that Polyethers additional amount described in step 3 is the 0.3%~3% of chromium slag amount, and the reaction time is 0.5~2h, after standing 12~48h Filtering.
6. the processing method of chromium slag nitration mixture enhanced leaching-extraction and recovery siderochrome according to claim 1, which is characterized in that Extractant concentration described in step 4 is 10~30%, and diluent is sulfonated kerosene;Extract stoste by the way that hydrochloric acid and chlorination is added Sodium guarantees that acidity is greater than 0.5mol/L, and chloride content is greater than 100g/L;TBP extraction iron time of contact is 1~20min, extraction temperature 10~40 DEG C, extraction phase ratio O/A=1:5~5:1, extract 3~9 grades of series.
7. the processing method of chromium slag nitration mixture enhanced leaching-extraction and recovery siderochrome according to claim 1, which is characterized in that P204 concentration described in step 6 is 10%~30%, and diluent is sulfonated kerosene, and P204 saponification degree is 20%~80%;Extraction Time of contact is 1~20min, 10~40 DEG C of extraction temperature, extraction phase ratio O/A=1:5~5:1, extracts 3~9 grades of series.
8. the processing method of chromium slag nitration mixture enhanced leaching-extraction and recovery siderochrome according to claim 1, which is characterized in that Back extraction time of contact described in step 8 is 5~30min, and temperature is 20~40 DEG C, is 1:1~50:1, extraction compared to O/A Series is 2~10 grades.
CN201511023816.7A 2015-12-30 2015-12-30 A kind of processing method of chromium slag nitration mixture enhanced leaching-extraction and recovery siderochrome Active CN106929698B (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
CN201511023816.7A CN106929698B (en) 2015-12-30 2015-12-30 A kind of processing method of chromium slag nitration mixture enhanced leaching-extraction and recovery siderochrome

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
CN201511023816.7A CN106929698B (en) 2015-12-30 2015-12-30 A kind of processing method of chromium slag nitration mixture enhanced leaching-extraction and recovery siderochrome

Publications (2)

Publication Number Publication Date
CN106929698A CN106929698A (en) 2017-07-07
CN106929698B true CN106929698B (en) 2019-02-26

Family

ID=59442687

Family Applications (1)

Application Number Title Priority Date Filing Date
CN201511023816.7A Active CN106929698B (en) 2015-12-30 2015-12-30 A kind of processing method of chromium slag nitration mixture enhanced leaching-extraction and recovery siderochrome

Country Status (1)

Country Link
CN (1) CN106929698B (en)

Families Citing this family (2)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN109536708B (en) * 2018-12-17 2021-08-06 江苏永葆环保科技有限公司 A kind of separation method of chromium and iron in pickling waste liquid
CN113477666A (en) * 2021-07-05 2021-10-08 东北大学 Method for removing hexavalent chromium from chromium slag

Citations (10)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN85105628A (en) * 1985-07-06 1987-01-14 莫玉裔 The nontoxic processing extraction Ca. and Mg of chromium slag reduction method
CN1063232A (en) * 1991-11-21 1992-08-05 邓绍齐 Countercurrent circulation sectional leaching separation method for comprehensive utilization of chromium slag
CN1085832A (en) * 1992-10-17 1994-04-27 曾庆琳 Chromium leaching slag treatment process
CN101380510A (en) * 2008-10-30 2009-03-11 杨恩清 Chromic slag wet method detoxifcation and resource comprehensive utilization new technique
CN102189093A (en) * 2010-03-09 2011-09-21 刘杰 Method for detoxicating chromium residues and comprehensive utilization of detoxicated chromium residues
CN102618726A (en) * 2012-03-16 2012-08-01 江西省洁益源环保科技有限公司 Treatment method for detoxifying and recycling chromium slag
CN102614620A (en) * 2012-03-15 2012-08-01 中国科学院过程工程研究所 Wet detoxification method of hexavalent chromium contained alkali waste residues
CN102634673A (en) * 2012-04-25 2012-08-15 中国科学院过程工程研究所 Method for deeply removing iron ions from chromium-containing waste residue pickle liquor
CN104609683A (en) * 2014-12-12 2015-05-13 浙江工商大学 Chrome tanning sludge heavy metal chromium regeneration method
CN104959369A (en) * 2015-05-20 2015-10-07 湖南永清环保研究院有限责任公司 Method used for recycling chromium from chromium-polluted soil

Patent Citations (10)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN85105628A (en) * 1985-07-06 1987-01-14 莫玉裔 The nontoxic processing extraction Ca. and Mg of chromium slag reduction method
CN1063232A (en) * 1991-11-21 1992-08-05 邓绍齐 Countercurrent circulation sectional leaching separation method for comprehensive utilization of chromium slag
CN1085832A (en) * 1992-10-17 1994-04-27 曾庆琳 Chromium leaching slag treatment process
CN101380510A (en) * 2008-10-30 2009-03-11 杨恩清 Chromic slag wet method detoxifcation and resource comprehensive utilization new technique
CN102189093A (en) * 2010-03-09 2011-09-21 刘杰 Method for detoxicating chromium residues and comprehensive utilization of detoxicated chromium residues
CN102614620A (en) * 2012-03-15 2012-08-01 中国科学院过程工程研究所 Wet detoxification method of hexavalent chromium contained alkali waste residues
CN102618726A (en) * 2012-03-16 2012-08-01 江西省洁益源环保科技有限公司 Treatment method for detoxifying and recycling chromium slag
CN102634673A (en) * 2012-04-25 2012-08-15 中国科学院过程工程研究所 Method for deeply removing iron ions from chromium-containing waste residue pickle liquor
CN104609683A (en) * 2014-12-12 2015-05-13 浙江工商大学 Chrome tanning sludge heavy metal chromium regeneration method
CN104959369A (en) * 2015-05-20 2015-10-07 湖南永清环保研究院有限责任公司 Method used for recycling chromium from chromium-polluted soil

Also Published As

Publication number Publication date
CN106929698A (en) 2017-07-07

Similar Documents

Publication Publication Date Title
CN102745657B (en) Method for extracting tellurium from tellurium copper slags
AU2013351773B2 (en) Monazite ballast separation and recovery method
CN101660054B (en) Method for extracting metal indium from waste residues generated from lead and zinc smelting
CN102173547B (en) Resource recycling process for nickel-containing sludge in electroplating enterprises
CN105274342B (en) A kind of technique for producing monohydrate zinc sulphate using spent acid, zinc slag
CN102277483B (en) Method for preparing rare earth chloride from Baiyun Obo rare earth concentrate
CN106048216B (en) The method of heterogenite leaching cobalt
CN103952560B (en) A kind of method of Leaching of Vanadium from Vanadium slag
CN104593598A (en) Method for resource utilization of multiple metals in electroplating sludge
CN101503761A (en) Method for separating and recycling valuable metal from pressure leached high sulphur slag
CN102925703A (en) Method for recycling valuable metals from lead anode slime
CN106929698B (en) A kind of processing method of chromium slag nitration mixture enhanced leaching-extraction and recovery siderochrome
CN103667693B (en) One extracts germanium method from high silicon raw material
CN101967555A (en) Method for dipping and decomposing bastnaesite after activation
US20120247271A1 (en) Process for recovering metals and metal compounds from mined ore and other metal-bearing raw source materials
CN109722528A (en) A comprehensive treatment method for solid waste containing both trivalent and pentavalent arsenic
CN104745821B (en) Method for recovering nickel and copper metals in acid pickling sludge
CN107245586A (en) Extraction vanadium extraction technology
CN102586608B (en) Method for preparing sponge indium with indium-rich slag produced in lead-zinc smelting process
CN104212976A (en) Method for recovering silver from wet zinc smelting waste slag
CN109055761A (en) A kind of method that bismuth-containing tellurium material synthetical recovery recycles
CN107142378A (en) The extracting method of lead in a kind of sintering flue dust
CN109913658A (en) A method for efficient separation and recovery of arsenic, copper and zinc in acid leaching solution of arsenic-containing copper smelting dust
CN109055737A (en) A kind of method of sulfuric acid leaching lepidolite ore
CN108441649A (en) A kind of method of chemical precipitation nickel sulfide material extraction nickel

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