CN1757770A - Treatment method of high alkali concentration sodium tungstate solution - Google Patents

Treatment method of high alkali concentration sodium tungstate solution Download PDF

Info

Publication number
CN1757770A
CN1757770A CNA200410046815XA CN200410046815A CN1757770A CN 1757770 A CN1757770 A CN 1757770A CN A200410046815X A CNA200410046815X A CN A200410046815XA CN 200410046815 A CN200410046815 A CN 200410046815A CN 1757770 A CN1757770 A CN 1757770A
Authority
CN
China
Prior art keywords
resin
pillar
exchange
solution
naoh
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
CNA200410046815XA
Other languages
Chinese (zh)
Other versions
CN100348751C (en
Inventor
赵中伟
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 CNB200410046815XA priority Critical patent/CN100348751C/en
Publication of CN1757770A publication Critical patent/CN1757770A/en
Application granted granted Critical
Publication of CN100348751C publication Critical patent/CN100348751C/en
Expired - Fee Related legal-status Critical Current
Anticipated expiration legal-status Critical

Links

Classifications

    • 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

  • Manufacture And Refinement Of Metals (AREA)
  • Inorganic Compounds Of Heavy Metals (AREA)

Abstract

A process for treating the high-alkaline solution of sodium tungstate by ion exchange method features that when the solution is treated by high=alkaline anionic exchange resin, the saturate resin is only desorbed, the multiple exchange columns are serially connected or the compact moving bed is used for adsorption, and the high-concentration NaOH solution after exchange is concentrated by evaporating for separating the NaCl from solution and returning it back to extracting step.

Description

The treatment process of high-alkalinity sodium tungstate solution
Technical field:
The present invention relates to hydrometallurgy, use the technology of ion exchange method processing with the alkali concn sodium tungstate solution.
Background technology:
Ion exchange method in the tungsten hydrometallurgy is used strongly basic anion exchange resin and alkaline coarse Na 2WO 4Solution generation permutoid reaction and adsorb tungsten is drained in the liquid of back and most of impurity such as phosphorus, arsenic, silicon etc. are stayed to hand over, and uses NH then 4Cl and NH 4The mixing solutions desorb of OH obtains pure (NH 4) 2WO 4Solution.Compare with original classical way, this method flow is short, can finish simultaneously and fall assorted and two tasks that make the transition, and equipment is simple, tungsten recovery rate is high, has obtained widespread use at the tungsten smelter.
But ion exchange method can only be handled the feed liquid of low alkaline concentration.For containing WO 3The sodium tungstate solution of 15-25g/l will influence the exchange capacity of tungsten more significantly when NaOH concentration during greater than 10g/l.Actual people find in production practice, and the NaOH in the solution just has a negative impact when being higher than about 4g/l.
Yet along with the black tungsten resource of high-quality consumes gradually, people have to then handle high calcium wolframite, sheelite and even low-grade complex tungsten mineral material.And when the mineral calcic is high, owing on the thermodynamics, must use more substantial NaOH (sheelite is generally more than 2.5 times of theoretical chemistry metering, and low grade ore is then also higher).Remaining alkali number is too high and have a strong impact on follow-up ion-exchange in the infusion solution that obtains like this, causes the operating capacity of resin to descend rapidly.
Owing to contain a large amount of free alkalis in the high alkaline solution, be diluted to lower concentration by traditional technology simultaneously, absorption back alkali can't reclaim, and can only discharge contaminate environment in vain.
Summary of the invention:
The objective of the invention is at this problem, a kind of technology of carrying out the ion-exchange absorption border under the high-alkalinity condition is provided, realize high-alkali high tungsten concentration (NaOH 10~100g/l, WO 3Ion-exchange under 10~200g/l) conditions realizes that high-alkalinity solution directly adsorbs, and then exchange back liquid is expected to concentrate economically to return the leaching operation.
The solution of the present invention is: use strongly basic anion exchange resin, when handling high-alkalinity solution, only saturated resin is carried out desorb.
1. use the series connection of many exchange column of fixed bed, go here and there the post operation: after the A exchange column leaked and wears, liquid flowed directly into B and changes post after the exchange of tungstenic, continued absorption; The B post further seals in the C post after leaking and wearing again; The C post further seals in the D post after leaking and wearing; Advance downstream successively; After treating that the A post reaches capacity, desorb tungsten and regenerating resin simultaneously, regenerated A post insert downstream; So hocket cycle operation.
During the operation of string post, if the linear velocity of solution below 0.1cm/min, should be operated with adverse current (solution from the bottom to top); If the linear velocity of solution is more than 0.1cm/min, then following current or counter-current operation all can.
Fixed-bed ion exchanger for present industrial use, because the whole post desorb together of actual needs in operation, then exchange zone " can only be pushed away " go out will desorb pillar, therefore at the several same exchange columns of downstream tandem, the upstream pillar leaks wears back continuation exchange, gradually exchange zone is moved on in the downstream column, after the upstream pillar is saturated, carry out desorb more separately.
2. use packed moving bed absorption: feed liquid enters continuously from the cylinder bottom, flows out from the resin bed top, and saturated resin from the bottom continuously or send out and batch emit; Simultaneously continuously or replenish the regenerating resin of equal amts at the top in batches; The desorption and regeneration of saturated resin carries out in a small ion exchange column, only needs saturated part taking-up desorb is got final product.
Advantage of the present invention and unusual effect demonstrate fully:
Handing over the main component of back liquid is NaOH and NaCl solution, and the characteristics of this mixing solutions are that NaCl solution degree concentration descends rapidly along with the raising of NaOH concentration.Utilize this characteristic, high density NaOH solution has further improved alkali concn on the one hand by evaporation concentration; can send out the NaCl in the exsolution liquid on the other hand; make superfluous free alkali can return tungsten ore and leach operation, reduced production cost, also help environment protection.
Embodiment:
Further specify the present invention below by specific embodiment.
Embodiment 1 decomposes white tungsten fine ore (WO 3Grade is 64.5%, and the NaOH consumption is 2.5 times of theoretical amount, 160 ℃ of decomposition temperatures, soaking time 4.5 hours, rate of decomposition 97.45%) the gained feed liquid contains NaOH 51.3g/l, WO 397.8g/l; Use two Φ 200 * 1400mm exchange column series connection adsorption operations, the absorption of following current is from top to bottom worn the back first pillar leakage and is inserted second pillar.After wearing, second leakage insert the 3rd pillar again, after wearing to the 3rd pillar leakage, with first independent desorb of pillar.The win working capacity of post of analysis is 125mg WO 3/ ml wet resin.Hand over back liquid to contain NaOH 47.7g/l, NaCl 24.0g/l.To hand over back liquid to be evaporated to NaOH concentration for about 250g/l, mend again solid NaOH to concentration be more than the 500g/l, be cooled to about 30 ℃ placement 4 hours; Treat NaCl from solution fully after the crystallization, centrifugation must contain the NaOH strong solution of small amount of N aCl (less than 45g/l); The NaOH that reclaims returns tungsten ore and leaches operation, has by the same terms to decompose white tungsten fine ore, and rate of decomposition is 97.17%.
Embodiment 2 decomposes high calcium black tungsten ore (tungstenic 12.8%, WO 3Grade is 43.4%, and the NaOH consumption is 3.5 times of theoretical amount, 160 ℃ of decomposition temperatures, soaking time 4.0 hours, rate of decomposition 98.45%) the gained feed liquid contains NaOH49.2g/l, WO 358.1g/l; Use two Φ 200 * 1400mm exchange column series connection adsorption operations, adverse current absorption is from bottom to top worn the back first pillar leakage and is inserted second pillar; Analyze to such an extent that working capacity is 117mgWO 3/ ml wet resin.Hand over back liquid to be evaporated to 1000g/l, cool off and placed centrifugation NaCl crystallization 8 hours; The gained concentrated NaOH solution returns and leaches batching.
Embodiment 3 feed liquids contain WO 325g/l, NaOH 20g/l, exchange column are Φ 16 * 36mm, 4 pillar series connection, following current conversion; After the upstream pillar was saturated, it was 128mg WO that independent desorb gets working capacity 3/ ml wet resin.
Embodiment 4 packed moving bed internal diameter 80mm, resin bed floor height 2000mm contains, NaOH 51.2g/l, WO 349.3g/l feed liquid flow through exchange column from bottom to top; When effluent liquid has the tungsten leakage to wear with the cinchonine check, take out the high resin of 300mm from the pillar lower end, the upper end replenishes the regenerating resin of same amount simultaneously, continuation exchange absorption.The saturated resin that takes out is packed the pillar of internal diameter 60mm into ammonia/ammonium chloride solution desorb, exchange capacity be 122mgWO 3/ ml wet resin.

Claims (8)

1. the treatment process of high-alkalinity sodium tungstate solution, use strongly basic anion exchange resin, when handling high-alkalinity solution, only saturated resin is carried out desorb, it is characterized in that: use many exchange column of fixed bed series connection, go here and there the post operation: after the A exchange column leaked and wears, liquid flowed directly into B and changes post after the exchange of tungstenic, continued absorption; The B post further seals in the C post after leaking and wearing again; The C post further seals in the D post after leaking and wearing; Advance downstream successively; After treating that the A post reaches capacity, desorb tungsten and regenerating resin simultaneously, regenerated A post insert downstream; So hocket cycle operation.
2. the treatment process of high-alkalinity sodium tungstate solution according to claim 1 is characterized in that: during the operation of string post, if the linear velocity of solution below 0.1cm/min, should be operated with adverse current (solution from the bottom to top); If the linear velocity of solution is more than 0.1cm/min, then following current or counter-current operation all can.
3. the treatment process of high-alkalinity sodium tungstate solution according to claim 1, it is characterized in that: at the several same exchange columns of downstream tandem, the upstream pillar leaks wears back continuation exchange, gradually exchange zone is moved on in the downstream column, after the upstream pillar is saturated, carry out desorb more separately.
4. the treatment process of high-alkalinity sodium tungstate solution, use strongly basic anion exchange resin, when handling high-alkalinity solution, only saturated resin is carried out desorb, it is characterized in that: use packed moving bed absorption, feed liquid enters continuously from the cylinder bottom, flows out from the resin bed top, and saturated resin from the bottom continuously or send out and batch emit; Simultaneously continuously or replenish the regenerating resin of equal amts at the top in batches; The desorption and regeneration of saturated resin carries out in a small ion exchange column, only needs saturated part taking-up desorb is got final product.
5. the treatment process of high-alkalinity sodium tungstate solution according to claim 1 is characterized in that: decompose white tungsten fine ore (WO 3Grade is 64.5%, and the NaOH consumption is 2.5 times of theoretical amount, 160 ℃ of decomposition temperatures, soaking time 4.5 hours, rate of decomposition 97.45%) the gained feed liquid contains NaOH 51.3g/l, WO 397.8g/l; Use two Φ 200 * 1400mm exchange column series connection adsorption operations, the absorption of following current is from top to bottom worn the back first pillar leakage and is inserted second pillar.After wearing, second leakage insert the 3rd pillar again, after wearing to the 3rd pillar leakage, with first independent desorb of pillar.The win working capacity of post of analysis is 125mgWO 3/ ml wet resin.Hand over back liquid to contain NaOH 47.7g/l, NaCl 24.0g/l.To hand over back liquid to be evaporated to NaOH concentration for about 250g/l, mend again solid NaOH to concentration be more than the 500g/l, be cooled to about 30 ℃ placement 4 hours; Treat NaCl from solution fully after the crystallization, centrifugation must contain the NaOH strong solution of small amount of N aCl (less than 45g/l); The NaOH that reclaims returns tungsten ore and leaches operation, has by the same terms to decompose white tungsten fine ore, and rate of decomposition is 97.17%.
6. the treatment process of high-alkalinity sodium tungstate solution according to claim 1 is characterized in that: decompose high calcium black tungsten ore (tungstenic 12.8%, WO 3Grade is 43.4%, and the NaOH consumption is 3.5 times of theoretical amount, 160 ℃ of decomposition temperatures, soaking time 4.0 hours, rate of decomposition 98.45%) the gained feed liquid contains NaOH49.2g/l, WO 358.1g/l; Use two Φ 200 * 1400mm exchange column series connection adsorption operations, adverse current absorption is from bottom to top worn the back first pillar leakage and is inserted second pillar; Analyze to such an extent that working capacity is 117mgWO 3/ ml wet resin.Hand over back liquid to be evaporated to 1000g/l, cool off and placed centrifugation NaCl crystallization 8 hours; The gained concentrated NaOH solution returns and leaches batching.
7. the treatment process of high-alkalinity sodium tungstate solution according to claim 1 is characterized in that: feed liquid contains WO 325g/l, NaOH 20g/l, exchange column are Φ 16 * 36mm, 4 pillar series connection, following current exchange; After the upstream pillar was saturated, it was 128mg WO that independent desorb gets working capacity 3/ ml wet resin.
8. the treatment process of high-alkalinity sodium tungstate solution according to claim 4 is characterized in that: packed moving bed internal diameter 80mm, resin bed floor height 2000mm contains, NaOH51.2g/l, WO 349.3g/l feed liquid flow through exchange column from bottom to top; When effluent liquid has the tungsten leakage to wear with the cinchonine check, take out the high resin of 300mm from the pillar lower end, the upper end replenishes the regenerating resin of same amount simultaneously, continuation exchange absorption.The saturated resin that takes out is packed the pillar of internal diameter 60mm into ammonia/ammonium chloride solution desorb, exchange capacity be 122mg WO 3/ ml wet resin.
CNB200410046815XA 2004-10-09 2004-10-09 Treatment method of high alkali concentration sodium tungstate solution Expired - Fee Related CN100348751C (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
CNB200410046815XA CN100348751C (en) 2004-10-09 2004-10-09 Treatment method of high alkali concentration sodium tungstate solution

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
CNB200410046815XA CN100348751C (en) 2004-10-09 2004-10-09 Treatment method of high alkali concentration sodium tungstate solution

Publications (2)

Publication Number Publication Date
CN1757770A true CN1757770A (en) 2006-04-12
CN100348751C CN100348751C (en) 2007-11-14

Family

ID=36703336

Family Applications (1)

Application Number Title Priority Date Filing Date
CNB200410046815XA Expired - Fee Related CN100348751C (en) 2004-10-09 2004-10-09 Treatment method of high alkali concentration sodium tungstate solution

Country Status (1)

Country Link
CN (1) CN100348751C (en)

Cited By (6)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN102329962A (en) * 2011-10-17 2012-01-25 中南大学 Method for deeply separating tungsten and molybdenum from high-tungsten and high-molybdenum mixed solution
CN104263972A (en) * 2014-10-09 2015-01-07 中南大学 Metallurgy system with multiple closed cycles for tungsten mineral raw materials
CN104263973A (en) * 2014-10-09 2015-01-07 江西稀有金属钨业控股集团有限公司 Method for preparing APT (Ammonium Paratungstate) from tungsten mineral raw material by multiple closed loops
CN104263971A (en) * 2014-10-09 2015-01-07 中南大学 System for preparing APT (Ammonium Paratungstate) from tungsten mineral raw material with zero pollution
CN104263974A (en) * 2014-10-09 2015-01-07 江西稀有金属钨业控股集团有限公司 Method for preparing APT (Ammonium Paratungstate) from tungsten mineral raw material with zero waste water discharge
CN111617810A (en) * 2020-05-11 2020-09-04 厦门钨业股份有限公司 Method for decomposing tungsten by using weak-base anion exchange resin

Family Cites Families (1)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN1003441B (en) * 1986-12-13 1989-03-01 核工业部北京第五研究所 Preparating of secondary ammonium tungstate with high purity using two-steption exchange method

Cited By (9)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN102329962A (en) * 2011-10-17 2012-01-25 中南大学 Method for deeply separating tungsten and molybdenum from high-tungsten and high-molybdenum mixed solution
CN102329962B (en) * 2011-10-17 2014-04-09 中南大学 Method for deeply separating tungsten and molybdenum from high-tungsten and high-molybdenum mixed solution
CN104263972A (en) * 2014-10-09 2015-01-07 中南大学 Metallurgy system with multiple closed cycles for tungsten mineral raw materials
CN104263973A (en) * 2014-10-09 2015-01-07 江西稀有金属钨业控股集团有限公司 Method for preparing APT (Ammonium Paratungstate) from tungsten mineral raw material by multiple closed loops
CN104263971A (en) * 2014-10-09 2015-01-07 中南大学 System for preparing APT (Ammonium Paratungstate) from tungsten mineral raw material with zero pollution
CN104263974A (en) * 2014-10-09 2015-01-07 江西稀有金属钨业控股集团有限公司 Method for preparing APT (Ammonium Paratungstate) from tungsten mineral raw material with zero waste water discharge
CN104263972B (en) * 2014-10-09 2016-03-16 中南大学 There is the tungsten mineral material metallurgical system of multiple closed loop
CN104263971B (en) * 2014-10-09 2016-08-24 中南大学 The system of APT is prepared by tungsten mineral material no pollution
CN111617810A (en) * 2020-05-11 2020-09-04 厦门钨业股份有限公司 Method for decomposing tungsten by using weak-base anion exchange resin

Also Published As

Publication number Publication date
CN100348751C (en) 2007-11-14

Similar Documents

Publication Publication Date Title
CN101715493B (en) Process for precious metal recovery from a sulphide ore or concentrate or other feed material
US10000825B2 (en) Process, method and plant for recovering scandium
CN102534214B (en) Method for recycling gallium from Bayer mother solution by using chelate resin
CN101880780A (en) Method for separating and extracting tungsten-molybdenum from mixed solution of tungstate-molybdate
CA2838901C (en) Method for recovering precious metals and copper from leach solutions
CN110117052A (en) A kind of absorption process of sulfide precipitation system hydrogen sulfide tail gas
CN106315682B (en) A kind of method of richness rhenium slag production ammonium perrhenate
CN111547892A (en) Treatment method of ammonia nitrogen wastewater in manganese chemical industry
CN105463204A (en) Purifying and regenerating method for gold bearing mineral containing cyanating solution
CN107519948B (en) Composite amino weakly-alkaline anion exchange resin and method for recovering rhenium from arsenic sulfide slag leachate
CN100348751C (en) Treatment method of high alkali concentration sodium tungstate solution
CN112174209A (en) Green molybdenum smelting ion exchange process
CN102329962B (en) Method for deeply separating tungsten and molybdenum from high-tungsten and high-molybdenum mixed solution
RU2342192C2 (en) Method and instrument for material desorption
CN109179506A (en) Method for synergistically recovering rhenium and molybdenum from molybdenum concentrate roasting leacheate
CN110846510B (en) Method for efficiently and selectively adsorbing and recovering rhenium and mercury from copper smelting multi-element mixed waste acid
CN110642414B (en) Control method for efficiently separating vanadium-chromium wastewater by using modified chelate resin
CN105565395B (en) A kind of processing method of copper mine raffinate
CN115927852A (en) Method for recovering gold, silver and copper from sulfur concentrate calcine washing waste liquid
CN105441685A (en) Method for recycling valuable metals in peracid waste fluid produced during copper anode mud treating process
CN108517402A (en) A kind of environmental protection carries the gold extracting method of resin adsorption desorption after gold
CN1037692A (en) Molybdenum in the ion exchange method separating tungsten acid salt solution
CN1331733C (en) Method of recovering iodine from palygorskite ore
CN106636632A (en) Method for conducting normal-pressure decomposition on wolframite or scheelite and wolframite mixture ores in alkali system
CN104496000B (en) The method of arsenic in water body, antimony is removed and is reclaimed in a kind of copper powder displacement

Legal Events

Date Code Title Description
C06 Publication
PB01 Publication
C10 Entry into substantive examination
SE01 Entry into force of request for substantive examination
C14 Grant of patent or utility model
GR01 Patent grant
C19 Lapse of patent right due to non-payment of the annual fee
CF01 Termination of patent right due to non-payment of annual fee