CN102690949A - Method of purifying ammonium tungstate solution - Google Patents

Method of purifying ammonium tungstate solution Download PDF

Info

Publication number
CN102690949A
CN102690949A CN201210164500XA CN201210164500A CN102690949A CN 102690949 A CN102690949 A CN 102690949A CN 201210164500X A CN201210164500X A CN 201210164500XA CN 201210164500 A CN201210164500 A CN 201210164500A CN 102690949 A CN102690949 A CN 102690949A
Authority
CN
China
Prior art keywords
ammonium tungstate
tungstate solution
ammonium
solution
dephosphorization
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
CN201210164500XA
Other languages
Chinese (zh)
Other versions
CN102690949B (en
Inventor
万林生
孙丽
徐国钻
李红超
赵立夫
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.)
Jiangxi University of Science and Technology
Chongyi Zhangyuan Tungsten Co Ltd
Original Assignee
Jiangxi University of Science and Technology
Chongyi Zhangyuan Tungsten Co Ltd
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 Jiangxi University of Science and Technology, Chongyi Zhangyuan Tungsten Co Ltd filed Critical Jiangxi University of Science and Technology
Priority to CN201210164500.XA priority Critical patent/CN102690949B/en
Publication of CN102690949A publication Critical patent/CN102690949A/en
Application granted granted Critical
Publication of CN102690949B publication Critical patent/CN102690949B/en
Active 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

Abstract

The invention provides a method of purifying ammonium tungstate solution. The method comprises the following steps of contacting the ammonium tungstate solution and magnesium salt so as to remove phosphorus in a form of magnesium ammonium phosphate sediments. By utilizing the method, the phosphorus in the ammonium tungstate solution can be effectively removed.

Description

The ammonium tungstate solution purifying method
Technical field
The invention belongs to the wolframite field of smelting.More specifically, the present invention relates to a kind of ammonium tungstate solution purifying method.
Background technology
Existing tungsten smelting technology mainly adopts alkali decomposition → calcium salt dephosphorization → anionresin → ammonium tungstate solution sulfuration removal of impurities → evaporative crystallization to produce APT technology, and wherein alkali decomposes back Na 2WO 4The solution phosphorus concentration is 0.5~1g/l, and the concentration of phosphorus is still about 0.2g/l in the ammonium tungstate solution that calcium salt dephosphorization-anionresin obtains.
Thereby the purification means to ammonium tungstate solution still remain to be improved at present.
Summary of the invention
The present invention is intended to one of solve the problems of the technologies described above at least.
The present invention is based on contriver's following discovery and accomplishes: Na 2WO 4Solution directly can be removed the phosphorus more than 90% through IX without the calcium salt dephosphorization, and the phosphorus concentration of resulting ammonium tungstate solution (does not comprise 0) yet about 0-3g/l.Therefore the calcium salt dephosphorization does not have substantial phosphor-removing effect, and this technology can directly be cancelled.In addition, there are many drawbacks in the calcium salt dephosphorization process, removes WO in the phosphorus slag 3Content up to 30 weight %, must it be returned the soda boiling pot in the production and recycle, this has consumed a large amount of raw and auxiliary materials, production cost obviously raises.In addition, the contriver is through discovering: containing phosphorus concentration and be the ammonium tungstate solution that (does not comprise 0) about 0-3g/l, to produce the APT phosphorus content through evaporative crystallization be 13ppm, can't satisfy country " 0 " grade standard (P≤7ppm).Therefore the desorbed solution after the IX needs further dephosphorization.The contriver finds, through adopting the alternative calcium salt of magnesium salts, can remove in the ammonium tungstate solution effectively the phosphorus that is contained.
In one aspect of the invention, the present invention proposes and a kind ofly can effectively remove institute's phosphorated method in the ammonium tungstate solution.According to embodiments of the invention, this method comprises: ammonium tungstate solution is contacted with magnesium salts, so that remove dephosphorization with the form of magnesium ammonium phosphate sediment.The contriver finds, through ammonium tungstate solution is contacted with magnesium salts, following reaction can take place:
Mg 2++NH 4 ++PO 4 3-+6H 2O→MgNH 4PO 4·6H 2O↓
Magnesium ammonium phosphate (Mg (the NH that reaction generates 4) PO 46H 2O) the resolution of precipitate degree is less, K SP (MgNH4PO4)=2.5 * 10 -13In the time of 20 ℃, its solubleness is 0.052%.Thus, can make the phosphorus that is comprised in the ammonium tungstate solution with magnesium ammonium phosphate (Mg (NH through ammonium tungstate solution is contacted with magnesium salts 4) PO 46H 2O) sedimentary form is removed.
In this article, broad understanding should be done in the term that is adopted " contact ", can be anyly can make the phosphorus in magnesium salts and the ammonium tungstate solution that the form of above-mentioned chemical reaction can take place; For example; According to one embodiment of present invention, can be that magnesium salts is joined in the ammonium tungstate solution, and under agitation condition, mix; Can improve the efficient of reaction thus, and then improve dephosphorization efficiency by using.
According to embodiments of the invention, the type that can use method of the present invention to carry out the ammonium tungstate of dephosphorization does not receive special restriction, as long as foregoing reaction can take place phosphorus wherein.According to embodiments of the invention, can adopt the ammonium tungstate solution that is produced in the industrial production ammonium paratungstate.According to embodiments of the invention, the ammonium tungstate solution that can adopt can contain the WO of 350g/l at the most 3, preferably contain the WO about 230g/l 3, randomly, ammonium tungstate solution contains the phosphorus that (does not comprise 0) about 0-3g/l, for example can contain the phosphorus of 0.2g/l.Thus, can remove the phosphorus in the ammonium tungstate solution effectively through above-mentioned reaction.
According to embodiments of the invention, the type that can be used to carry out the magnesium salts of purifying treatment does not receive special restriction, as long as can mg ion be provided for reaction system.According to instances more of the present invention, the magnesium salts that can be used for purifying treatment is be selected from magnesium basic carbonate, sal epsom, Natural manganese dioxide, magnesiumcarbonate, Marinco H at least a.It will be understood by those skilled in the art that and promptly can adopt independent a kind of magnesium salts, also can adopt the combination with arbitrary proportion of multiple magnesium salts.According to embodiments of the invention, the consumption that is used to purify the magnesium salts of ammonium tungstate solution does not receive special restriction.According to embodiments of the invention, the amount of the magnesium salts that is adopted is 1~1.4 times of theoretical value.Here employed term " theoretical amount " refers to, and calculates according to chemical reaction equation, removes all phosphorus in the solution, the amount of needed magnesium salts.For example, when adopting magnesiumcarbonate, for the phosphorous 0.2g/L of 200ml, contain WO 3The ammonium tungstate solution of 210g/L, the amount of the magnesiumcarbonate of theoretical amount are 0.1088g.The contriver finds, Mg in solution 2+And NH 4 +When superfluous, magnesium ammonium phosphate (Mg (NH 4) PO 46H 2O) the resolution of precipitate degree can significantly reduce, thus, and through adopting excessive magnesium salts, further dephosphorization effectively.
In addition, according to embodiments of the invention, the condition that ammonium tungstate solution and magnesium salts react does not receive special restriction.Based on instantiation of the present invention, under pH value 8-11, preferably, ammonium tungstate solution is contacted with magnesium salts pH value 9 times, for example sodium tungstate solution is mixed with magnesium salts.According to embodiments of the invention, ammonium tungstate solution and magnesium salts reaction 1-5 hour, preferred 120 minutes.Thus, can further improve the reaction efficiency of ammonium tungstate and magnesium salts, and then improve the dephosphorization efficiency by using that purifies ammonium tungstate solution.
In addition, according to embodiments of the invention, with ammonium tungstate solution with before magnesium salts contacts, at first ammonium tungstate mixes with ammonium sulfide solution.Through in reaction system, adding ammonium sulfide, with the MOO in the solution 4 2-Be sulfided into and be prone to by Cu 2+The MOS that catches 4 2-, can remove in the ammonium tungstate solution for example molybdenum of other impurity effectively through adding copper-bath again, react and be:
MoS 4 2-+CuSO 4(aq)→CuMoS 4(s)+SO 4 2-
Unnecessary (NH 4) 2S can with unnecessary CuSO 4Reaction generates the CuS throw out, makes the Cu in the solution 2+, S 2-Can be inexcessive, and can not influence follow-up cationic exchange technology, its technological principle is:
CuSO 4+(NH 4) 2S=CuS(s)+(NH 4) 2SO 4(aq)
And the contriver is surprised to find, and adds the reaction that ammonium sulfide and copper sulfate do not influence phosphorus in magnesium salts and the ammonium tungstate solution, thus, carries out simultaneously with dephosphorization with except that the reaction of other impurity, significantly improves the efficient that purifies ammonium tungstate solution.
According to embodiments of the invention, the amount of ammonium sulfide is the 1%-3.5% of ammonium tungstate solution volume.Thus, can further improve the efficient that purifies ammonium tungstate solution.
According to embodiments of the invention, after the ammonium tungstate solution that obtains through the dephosphorization removal of impurities, can resulting ammonium tungstate be used to prepare ammonium paratungstate.For example, according to specific examples of the present invention, can the ammonium tungstate solution that pass through the dephosphorization removal of impurities be carried out evaporative crystallization, so that obtain ammonium paratungstate.In addition, according to specific examples of the present invention, before the ammonium tungstate solution that will pass through dephosphorization carried out evaporative crystallization, the ammonium tungstate solution that will pass through dephosphorization carries out cationic exchange to be handled.Thus, the phosphorus content of resulting ammonium paratungstate (APT) significantly reduces.According to embodiments of the invention, can be reduced to below the 0.004g/l through purifying the ammonium tungstate solution phosphorus concentration that obtains, again through cationic exchange technology, the phosphorus content of the ammonium paratungstate that evaporative crystallization obtains can reach below the 5ppm.Thus, utilize method, cancelled calcium salt dephosphorization process, shortened process in the production, reduced production costs, improve the tungsten smelting recovery according to the embodiment of the invention, thus the method for deep phosphorous removal removal of impurities under a kind of ammonium tungstate vulcanization system that provides.
Positively effect according to the method for the purification ammonium tungstate of the embodiment of the invention:
Based on embodiments of the invention, cancelled calcium salt dephosphorization process in the existing technology, with dephosphorization process with the sulfuration impurity removal process merge to one the step carry out, not only shortened technological process, reduced production cost, simplified operation, and improved production efficiency.
According to embodiments of the invention, resultingly remove that tungstic oxide content is lower than 1% in the phosphorus slag, remove in the phosphorus slag 30% W content much smaller than calcium salt, improved the tungsten metal recovery rate greatly.
According to embodiments of the invention, adopt the magnesium salts deep phosphorous removal, phosphorus content can be reduced to 0.004g/L in the solution, and the APT impurity content that the present invention produces is lower than GB " 0 " level article APT.
Additional aspect of the present invention and advantage part in the following description provide, and part will become obviously from the following description, or recognize through practice of the present invention.
Embodiment
Describe embodiments of the invention below in detail, need to prove, these embodiment only are for the present invention is described, and scope of the present invention are not made any restriction.The all material that in the following example, is adopted all is commonly used in the industry, is commercially available getting.
Raw material: the ammonium tungstate solution in the industrial production, analytical pure magnesium basic carbonate, MAGNESIUM SULPHATE HEPTAHYDRATE 99.5, Natural manganese dioxide, magnesiumcarbonate, Marinco H, magnesium chloride, industrial ammonium sulfide.
Equipment: DF-1 heat collecting type constant temperature blender with magnetic force, 500ml glass Erlenmeyer flask, 200ml ceramic cup.
Analytical procedure: tungsten adopts the thiocyanate-absorbance method, and phosphorus adopts the yellow spectrophotometry of phosphorus molybdenum.The ammonium tungstate solution that the present invention adopts all comes from industrial production, P=0.22g/l wherein, WO 3=230g/l.
Embodiment 1
Under the normal temperature, get 300ml and contain WO 3Concentration is 230g/l; The ammonium tungstate solution that contains phosphorus concentration and be 0.22g/l is in the 500ml beaker; The industrial ammonium sulfide solution that adds the 1%-3.5% of ammonium tungstate solution volume stirs; The magnesium basic carbonate, MAGNESIUM SULPHATE HEPTAHYDRATE 99.5, Natural manganese dioxide, magnesiumcarbonate, the Marinco H that in said mixture, add 1~1.4 times of theoretical amount respectively carry out deep phosphorous removal (for magnesium basic carbonate, MAGNESIUM SULPHATE HEPTAHYDRATE 99.5, Natural manganese dioxide, magnesiumcarbonate, Marinco H; The magnesium salts consumption of 1 times of theoretical amount is respectively: 0.2069g, 0.5245g, 0.0858g, 0.1795g, 0.1235g), the pH value=9-10 of reaction soln, dephosphorization reaction times 120min; After above-mentioned experimental implementation and analysis, experimental result is as follows:
One, the magnesium basic carbonate of 1~1.4 times of theoretical multiple is seen shown in the table 1 influence of vulcanization system ammonium tungstate solution dephosphorization.Wherein the weight of the magnesium basic carbonate of 1 times of theoretical amount is 0.2069g.
Table 1 magnesium basic carbonate consumption is to the influence of vulcanization system ammonium tungstate solution deep phosphorous removal
The theoretical multiple of magnesium basic carbonate 1 1.1 1.2 1.3 1.4
Initial p concentration, g/L 0.22
Residue P concentration, g/L 0.012 0.004 0 0 0
Final WO 3: P ratio 2.5×10 4 7.5×10 4
Dephosphorizing rate, % 94.55 98.18 100 100 100
Research shows: under the vulcanization system, at high WO 3In the ammonium tungstate solution of concentration, low phosphorus concentration, along with the increase of magnesium basic carbonate consumption, phosphoric residue concentration reduces gradually in the solution.When the theoretical multiple of magnesium basic carbonate was 1 times, the phosphorus concentration in the solution was reduced to 0.012g/L from 0.22g/L, WO 3: P is 2.5 * 10 4, dephosphorizing rate 94.55% reaches the dephosphorization standard.
Two, the MAGNESIUM SULPHATE HEPTAHYDRATE 99.5 of 1~1.4 times of theoretical multiple is seen shown in the table 2 influence of vulcanization system ammonium tungstate solution dephosphorization.Wherein the weight of the MAGNESIUM SULPHATE HEPTAHYDRATE 99.5 of 1 times of theoretical amount is 0.5246g.
Table 2 MAGNESIUM SULPHATE HEPTAHYDRATE 99.5 consumption is to the influence of vulcanization system ammonium tungstate solution deep phosphorous removal
The theoretical multiple of MAGNESIUM SULPHATE HEPTAHYDRATE 99.5 1 1.1 1.2 1.3 1.4
Initial p concentration, g/L 0.22
Residue P concentration, g/L 0.014 0.006 0.004 0.006 0.007
Final WO 3: P ratio 2.14×10 4 5.0×10 4 7.5×10 4 5.0×10 4 4.29×10 4
Dephosphorizing rate, % 93.64 97.27 98.18 97.27 96.82
Research shows: under the vulcanization system, at high WO 3In the ammonium tungstate solution of concentration, low phosphorus concentration, along with the increase of MAGNESIUM SULPHATE HEPTAHYDRATE 99.5 consumption, phosphoric residue concentration reduces gradually in the solution.When the theoretical multiple of MAGNESIUM SULPHATE HEPTAHYDRATE 99.5 was 1 times, the phosphorus concentration in the solution was reduced to 0.014g/L from 0.22g/L, WO 3: P is 2.14 * 10 4, dephosphorizing rate 93.64% reaches the dephosphorization standard.
Three, the Natural manganese dioxide of 1~1.4 times of theoretical multiple is seen shown in the table 3 influence of vulcanization system ammonium tungstate solution dephosphorization.Wherein the magnesian weight of 1 times of theoretical amount is 0.0858g.
Table 3 Natural manganese dioxide consumption is to the influence of vulcanization system ammonium tungstate solution deep phosphorous removal
Magnesian theoretical multiple 1 1.1 1.2 1.3 1.4
Initial p concentration, g/L 0.22
Residue P concentration, g/L 0.059 0.016 0.009 0.006 0.004
Final WO 3: P ratio 5.08×10 3 1.88×10 4 3.33×10 4 5.0×10 4 7.5×10 4
Dephosphorizing rate, % 73.18 92.73 95.91 97.27 98.18
Research shows: under the vulcanization system, at high WO 3In the ammonium tungstate solution of concentration, low phosphorus concentration, along with the increase of Natural manganese dioxide consumption, phosphoric residue concentration reduces gradually in the solution.When the theoretical multiple of Natural manganese dioxide was 1.1 times, the phosphorus concentration in the solution was reduced to 0.016g/L from 0.22g/L, WO 3: P is 1.88 * 10 4, dephosphorizing rate 92.73% reaches the dephosphorization standard.
Four, the magnesiumcarbonate of 1~1.4 times of theoretical multiple is seen shown in the table 4 influence of vulcanization system ammonium tungstate solution dephosphorization.Wherein the weight of the magnesiumcarbonate of 1 times of theoretical amount is 0.1795g.
Table 4 magnesiumcarbonate consumption is to the influence of vulcanization system ammonium tungstate solution deep phosphorous removal
The theoretical multiple of magnesiumcarbonate 1 1.1 1.2 1.3 1.4
Initial p concentration, g/L 0.22
Residue P concentration, g/L 0.12 0.10 0.074 0.045 0.022
Final WO 3: P ratio 2.5×10 3 3.0×10 3 4.05×10 3 6.67×10 3 1.36×10 4
Dephosphorizing rate, % 45.45 54.55 66.36 79.55 90
Research shows: under the vulcanization system, at high WO 3In the ammonium tungstate solution of concentration, low phosphorus concentration, along with the increase of magnesiumcarbonate consumption, phosphoric residue concentration reduces gradually in the solution.When the theoretical multiple of magnesiumcarbonate was 1.4 times, the phosphorus concentration in the solution was reduced to 0.022g/L from 0.22g/L, WO 3: P is 1.36 * 10 4, dephosphorizing rate 90% reaches the dephosphorization standard.
Five, the Marinco H of 1~1.4 times of theoretical multiple is seen shown in the table 5 influence of vulcanization system ammonium tungstate solution dephosphorization.Wherein the weight of the Marinco H of 1 times of theoretical amount is 0.1235g.
Table 5 Marinco H consumption is to the influence of vulcanization system ammonium tungstate solution deep phosphorous removal
Figure BDA00001681029100081
Research shows: under the vulcanization system, at high WO 3In the ammonium tungstate solution of concentration, low phosphorus concentration, along with the increase of Marinco H consumption, phosphoric residue concentration is constant basically in the solution.When the theoretical multiple of Marinco H was 1 times, the phosphorus in the solution was removed rate 43.64%, continues to strengthen the consumption of Marinco H, and dephosphorizing rate raises little.Therefore the Marinco H phosphor-removing effect is not good.
Embodiment 2
Get the 300ml ammonium tungstate solution in the 500ml beaker; Add the industrial ammonium sulfide of 1 times of theoretical amount, the magnesiumcarbonate of 1 times of theoretical amount respectively, pH=9.0 in the solution, reaction is 2 hours under the room temperature; The ammonium tungstate solution phosphorus concentration that filtration obtains is 0.10g/L, and the clearance of phosphorus is 54.55%.
Embodiment 3
Get the 300ml ammonium tungstate solution in the 500ml beaker; Add the industrial ammonium sulfide of 1 times of theoretical amount, the light magnesium oxide of 1.1 times of theoretical amount respectively, pH=9.0 in the solution, reaction is 2 hours under the room temperature; The ammonium tungstate solution phosphorus concentration that filtration obtains is 0.016g/L, and the clearance of phosphorus is 92.73%.
Embodiment 4
Get the 300ml ammonium tungstate solution in the 500ml beaker; Add the industrial ammonium sulfide of 1 times of theoretical amount, the MAGNESIUM SULPHATE HEPTAHYDRATE 99.5 of 1.2 times of theoretical amount respectively, pH=9.5 in the solution, reaction is 2 hours under the room temperature; The ammonium tungstate solution phosphorus concentration that filtration obtains is 0.006g/L, and the clearance of phosphorus is 97.27%.
Embodiment 5
Get the 300ml ammonium tungstate solution in the 500ml beaker; Add the industrial ammonium sulfide of 1 times of theoretical amount, the magnesium basic carbonate of 1.1 times of theoretical amount respectively, pH=10 in the solution, reaction is 2 hours under the room temperature; The ammonium tungstate solution phosphorus concentration that filtration obtains is 0.004g/L, and the clearance of phosphorus is 98.18%.
Embodiment 6
Adopt resulting ammonium tungstate solution in " embodiment 5 ", the APT that obtains through cationic exchange → evaporative crystallization technique is " 0 " level GB product.Its major impurity is as shown in table 6.
Table 6APT major impurity element and the contrast of " 0 " level GB
Element K Na P Ca Cu Mg Mo
0 grade of GB 10 10 7 10 3 5 20
APT 6 3 <5 <5 <1 <3 8
Embodiment 7
Adopt resulting ammonium tungstate solution in " embodiment 5 ", not through cationic exchange, but directly carry out the APT that evaporative crystallization technique obtains, wherein the part element exceeds the regulation of " 0 " level GB product.Its major impurity is as shown in table 7.
Table 7APT major impurity element and the contrast of " 0 " level GB
Element K Na P Ca Cu Mg Mo
0 grade of GB 10 10 7 10 3 5 20
APT 6 3 18 15 5 3 10
In the description of this specification sheets, the description of reference term " embodiment ", " some embodiment ", " example ", " concrete example " or " some examples " etc. means the concrete characteristic, structure, material or the characteristics that combine this embodiment or example to describe and is contained at least one embodiment of the present invention or the example.In this manual, the schematic statement to above-mentioned term not necessarily refers to identical embodiment or example.And concrete characteristic, structure, material or the characteristics of description can combine with suitable manner in any one or more embodiment or example.
Although illustrated and described embodiments of the invention; Those having ordinary skill in the art will appreciate that: under the situation that does not break away from principle of the present invention and aim, can carry out multiple variation, modification, replacement and modification to these embodiment, scope of the present invention is limited claim and equivalent thereof.

Claims (10)

1. the method that ammonium tungstate solution purifies is characterized in that, comprising:
Ammonium tungstate solution is contacted with magnesium salts, so that remove dephosphorization with the form of magnesium ammonium phosphate sediment.
2. method according to claim 1 is characterized in that, said ammonium tungstate solution contains the WO of 350g/l at the most 3, preferably contain the WO of 230g/l 3
3. method according to claim 1 is characterized in that, said ammonium tungstate solution contains the phosphorus below the 3g/l.
4. method according to claim 1 is characterized in that, said magnesium salts is be selected from magnesium basic carbonate, sal epsom, Natural manganese dioxide, magnesiumcarbonate, Marinco H at least a.
5. method according to claim 1 is characterized in that, the amount of said magnesium salts is 1~1.4 times of theoretical value.
6. method according to claim 1 is characterized in that, under pH value 8-11, preferably pH value 9 times, said ammonium tungstate solution is contacted with said magnesium salts.
7. method according to claim 1 is characterized in that, said ammonium tungstate solution and the reaction of said magnesium salts 1-5 hour, preferred 120 minutes.
8. method according to claim 1 is characterized in that, said ammonium tungstate solution with before said magnesium salts contacts, is mixed said ammonium tungstate solution with ammonium sulfide, and the amount of preferred said ammonium sulfide is the 1%-3.5% of said ammonium tungstate solution volume.
9. method according to claim 1 is characterized in that, further comprises the ammonium tungstate solution through dephosphorization is carried out evaporative crystallization, so that obtain ammonium paratungstate.
10. method according to claim 9 is characterized in that, before said ammonium tungstate solution through dephosphorization is carried out evaporative crystallization, said ammonium tungstate solution through dephosphorization is carried out cationic exchange handle.
CN201210164500.XA 2012-05-24 2012-05-24 Method of purifying ammonium tungstate solution Active CN102690949B (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
CN201210164500.XA CN102690949B (en) 2012-05-24 2012-05-24 Method of purifying ammonium tungstate solution

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
CN201210164500.XA CN102690949B (en) 2012-05-24 2012-05-24 Method of purifying ammonium tungstate solution

Publications (2)

Publication Number Publication Date
CN102690949A true CN102690949A (en) 2012-09-26
CN102690949B CN102690949B (en) 2014-09-24

Family

ID=46856686

Family Applications (1)

Application Number Title Priority Date Filing Date
CN201210164500.XA Active CN102690949B (en) 2012-05-24 2012-05-24 Method of purifying ammonium tungstate solution

Country Status (1)

Country Link
CN (1) CN102690949B (en)

Cited By (8)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN104817115A (en) * 2015-04-15 2015-08-05 赣州海创钨业有限公司 Method for removing micro-phosphorus in ammonium tungstate solution
CN104973628A (en) * 2015-06-30 2015-10-14 崇义章源钨业股份有限公司 Method used for purifying sodium tungstate solution
CN108773856A (en) * 2018-09-10 2018-11-09 江钨世泰科钨品有限公司 A kind of purification technique of purification sodium tungstate solution
CN109368699A (en) * 2018-12-19 2019-02-22 金堆城钼业股份有限公司 The minimizing technology of magnesium in a kind of ammonium dimolybdate production technology
CN112877540A (en) * 2021-01-13 2021-06-01 厦门钨业股份有限公司 Tungsten-molybdenum analysis method for tungsten smelting
CN113603143A (en) * 2021-08-18 2021-11-05 崇义章源钨业股份有限公司 Method for preparing ammonium paratungstate by removing molybdenum through one-step ammonia solution dephosphorization of tungstic acid
CN113666419A (en) * 2021-08-12 2021-11-19 崇义章源钨业股份有限公司 Method for preparing ammonium paratungstate by one-step ammonia solution dephosphorization of tungstic acid
CN113943871A (en) * 2021-10-21 2022-01-18 崇义章源钨业股份有限公司 Method for treating magnesium ammonium phosphate slag containing tungsten

Citations (3)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN1266022A (en) * 1999-03-05 2000-09-13 中南工业大学 Process for treating ammonium para-tungstate crystal mother solution
CN102140578A (en) * 2011-03-07 2011-08-03 中南大学 Molybdenum-tungsten separating process for molybdenum-tungsten mixed ammonium salt solution in tungsten hydrometallurgy
CN102167401A (en) * 2011-03-14 2011-08-31 崇义章源钨业股份有限公司 Method for dephosphorizing aluminum tungstate ((NH4)2WO4) solution

Patent Citations (3)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN1266022A (en) * 1999-03-05 2000-09-13 中南工业大学 Process for treating ammonium para-tungstate crystal mother solution
CN102140578A (en) * 2011-03-07 2011-08-03 中南大学 Molybdenum-tungsten separating process for molybdenum-tungsten mixed ammonium salt solution in tungsten hydrometallurgy
CN102167401A (en) * 2011-03-14 2011-08-31 崇义章源钨业股份有限公司 Method for dephosphorizing aluminum tungstate ((NH4)2WO4) solution

Cited By (8)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN104817115A (en) * 2015-04-15 2015-08-05 赣州海创钨业有限公司 Method for removing micro-phosphorus in ammonium tungstate solution
CN104973628A (en) * 2015-06-30 2015-10-14 崇义章源钨业股份有限公司 Method used for purifying sodium tungstate solution
CN108773856A (en) * 2018-09-10 2018-11-09 江钨世泰科钨品有限公司 A kind of purification technique of purification sodium tungstate solution
CN109368699A (en) * 2018-12-19 2019-02-22 金堆城钼业股份有限公司 The minimizing technology of magnesium in a kind of ammonium dimolybdate production technology
CN112877540A (en) * 2021-01-13 2021-06-01 厦门钨业股份有限公司 Tungsten-molybdenum analysis method for tungsten smelting
CN113666419A (en) * 2021-08-12 2021-11-19 崇义章源钨业股份有限公司 Method for preparing ammonium paratungstate by one-step ammonia solution dephosphorization of tungstic acid
CN113603143A (en) * 2021-08-18 2021-11-05 崇义章源钨业股份有限公司 Method for preparing ammonium paratungstate by removing molybdenum through one-step ammonia solution dephosphorization of tungstic acid
CN113943871A (en) * 2021-10-21 2022-01-18 崇义章源钨业股份有限公司 Method for treating magnesium ammonium phosphate slag containing tungsten

Also Published As

Publication number Publication date
CN102690949B (en) 2014-09-24

Similar Documents

Publication Publication Date Title
CN102690949B (en) Method of purifying ammonium tungstate solution
US11498049B2 (en) Process for producing a calcium phosphate reactant, reactant obtained and use thereof in the purification of liquid effluents
CN106185853B (en) The method for producing the high whiteness semi-hydrated gypsum of feed grade Wet Phosphoric Acid Market co-producing high-purity
CN103194611A (en) Method for producing vanadium oxide
CN106517621B (en) Recycling process of ammonium chloride-containing wastewater
CN106745613B (en) A kind of processing method of organic phosphine precipitating reagent and the waste water of organic phosphine containing high concentration
CN101724756A (en) Phosphorus and silicon removing method of vanadium-contained clinker leaching liquor
CN107814370B (en) Circulating environment-friendly process method for preparing phosphate concentrate, product and application thereof
CN110240201B (en) Method for treating scheelite
CN101773817A (en) Composite absorption material for wastewater treatment and preparation method thereof
CN111187908B (en) Floating extraction-based tungsten-molybdenum selective separation method
CN103397209A (en) Method for extracting vanadium from high-calcium and high-phosphorus vanadium slag
KR20100015911A (en) Water-treating agent and method of treating water
CN105683097A (en) Agent for treating hazardous materials
CN101948211B (en) Method for treating vanadium oxide production wastewater
CN108947012A (en) A method of separating and recovering ammonia from ammonia nitrogen waste water
Xiong et al. Low-grade sepiolite with low loading of Na/La salts for simultaneous removal of ammonia and phosphate from wastewater
CN1321058C (en) Method for purification of phosphoric acid and high purity polyphosphoric acid
CN104803417A (en) Ammonium paratungstate and preparation method thereof
KR101293283B1 (en) Method for removing fluoride from waste water containing fluoroboric acid
Yousif et al. Studying the adsorption properties of modified red mud towards phosphate removal from its solutions
CN109319896A (en) The method for preparing flocculant with flyash and vanadium titano-magnetite
CN103449584A (en) Ammonia-nitrogen wastewater treatment method
CN109457107B (en) Method for removing fluorine from tungsten-containing solid
CN101956069A (en) Method for reducing and leaching manganese from pyrolusite in sulfuric acid solution by using sludge

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