CN102491362A - Method for preparing cation exchange content W type zeolite molecular sieve - Google Patents

Method for preparing cation exchange content W type zeolite molecular sieve Download PDF

Info

Publication number
CN102491362A
CN102491362A CN2011103837103A CN201110383710A CN102491362A CN 102491362 A CN102491362 A CN 102491362A CN 2011103837103 A CN2011103837103 A CN 2011103837103A CN 201110383710 A CN201110383710 A CN 201110383710A CN 102491362 A CN102491362 A CN 102491362A
Authority
CN
China
Prior art keywords
molecular sieve
type zeolite
zeolite molecular
ammonium
ion
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.)
Pending
Application number
CN2011103837103A
Other languages
Chinese (zh)
Inventor
席北斗
赵颖
夏训峰
李晓光
张列宇
牛永超
管伟雄
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.)
Chinese Research Academy of Environmental Sciences
Original Assignee
Chinese Research Academy of Environmental Sciences
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 Chinese Research Academy of Environmental Sciences filed Critical Chinese Research Academy of Environmental Sciences
Priority to CN2011103837103A priority Critical patent/CN102491362A/en
Publication of CN102491362A publication Critical patent/CN102491362A/en
Pending legal-status Critical Current

Links

Landscapes

  • Solid-Sorbent Or Filter-Aiding Compositions (AREA)
  • Silicates, Zeolites, And Molecular Sieves (AREA)

Abstract

一种制备阳离子交换容量W型沸石分子筛的方法,主要步骤为:A)将含有初始阳离子Ci形式的W型沸石分子筛与含有铵离子的水溶性铵化合物接触,得到的含铵离子的W型沸石分子筛中(NH4)2O/Al2O3≥0.8;B)将步骤A得到的含铵离子的W型沸石分子筛与含最终阳离子Cf的溶液接触,用至少一种所述阳离子取代铵离子,并从反应区除去挥发性氨,制得的产物中CfO/Al2O3≥0.7,(NH4)2O/Al2O3≤0.1;C)将步骤B得到的产物用含Cf的溶液洗涤,干燥,最终得到阳离子交换容量W型沸石分子筛。A method for preparing W-type zeolite molecular sieve with cation exchange capacity, the main steps are: A) contacting the W-type zeolite molecular sieve containing the initial cation Ci form with a water-soluble ammonium compound containing ammonium ions, and obtaining the W-type zeolite containing ammonium ions (NH 4 ) 2 O/Al 2 O 3 ≥ 0.8 in the zeolite molecular sieve; B) contacting the W-type zeolite molecular sieve containing ammonium ion obtained in step A with the solution containing the final cation Cf , and replacing it with at least one of the cations ammonium ions, and remove volatile ammonia from the reaction zone, C f O/Al 2 O 3 ≥ 0.7 in the obtained product, (NH 4 ) 2 O/Al 2 O 3 ≤ 0.1; C) the product obtained in step B Washing with a solution containing Cf and drying to finally obtain a W-type zeolite molecular sieve with cation exchange capacity.

Description

The method for preparing cation exchange capacity w-type zeolite molecular sieve
Technical field
The present invention relates to a kind of polynary cationic exchange and produce the method for high-cation exchange capacity W type molecular sieve; More particularly; Relate to through W type molecular sieve is at first formed the w-type zeolite molecular sieve that contains ammonium form with ammonium ion exchange; To contain the w-type zeolite molecular sieve and the target cationic source of ammonium form then, under the condition of evicting ammonia from the zone of action from, contact, produce the method for high-cation exchange capacity W type molecular sieve.
Background technology
W-type zeolite molecular sieve SiO 2/ Al 2O 3Ratio be 3.2-4.8, its positively charged ion is generally potassium ion, structural formula is generally 1.02K 2O:Al 2O 3: 3.65SiO 2: 5.1H 2O.The w-type zeolite molecular sieve belongs to phillipsite family, has a series of tetra-atomic rings, the long band of the bending that its limit forms, and the main channel is an octatomic ring, free aperture is 4.8A to the maximum.As stated, the positively charged ion of w-type zeolite is generally potassium ion, has useful function although contain the potassium w-type zeolite in many-sides such as industry and environmental protection fields, preferably they is carried out IX, with its absorption property of further enhancing.Conventional exchange step can be used for preparing many single cationic exchange zeolites economically; Yet; The conventional in all cases potassium w-type zeolite that contains exchanges a large amount of excess metal positively charged ion of needs; With the moderate of carrying out initial cationic or highly exchange, these salt itself are expensive, and it is much more expensive than the zeolite of the conventional sorbent material grade of production that this just causes producing these special ion exchange form.For the cost that reduces final form zeolite and prevent that these ions are discharged in the environment; Must carry out very big effort; From residual exchange solution and washings, reclaim excessive interested ion; Because high-cation exchange capacity W type molecular sieve has very big actual utility value as the high-efficiency adsorbent in environmental protection field, so this problem is the obvious interested problem in environmental protection field.
Usually, contain initial cationic C iThe w-type zeolite molecular sieve of form is difficult to and final positively charged ion C fPrimary ions exchanging form through routine makes and contains C fThe w-type zeolite molecular sieve of form.
Summary of the invention
The object of the present invention is to provide a kind of polynary cationic exchange to produce the method for high-cation exchange capacity W type molecular sieve, to overcome the defective that exists in the known technology.
Be the realization above-mentioned purpose, the method for preparing cation exchange capacity w-type zeolite molecular sieve provided by the invention, key step is:
A) will contain initial cationic C iThe w-type zeolite molecular sieve of form contacts with the water-soluble ammonium compound that contains ammonium ion, (NH in the w-type zeolite molecular sieve that contains ammonium ion that obtains 4) 2O/Al 2O 3>=0.8;
B) the w-type zeolite molecular sieve that contains ammonium ion that steps A is obtained with contain final positively charged ion C fSolution contact, with at least a said positively charged ion substituted ammonium ion, and remove volatile ammonia, C in the product that makes from reaction zone fO/Al 2O 3>=0.7, (NH 4) 2O/Al 2O 3≤0.1;
C) product that step B is obtained is with containing C fSolution washing, drying finally obtains cation exchange capacity w-type zeolite molecular sieve.
The method for preparing cation exchange capacity w-type zeolite molecular sieve provided by the invention can also be reacted with solid-state heating with final positively charged ion after preparing the w-type zeolite molecular sieve that contains ammonium ion, makes volatile ammonia from system evaporation or distillation.
The w-type zeolite molecular sieve drying that contains ammonium ion that specifically steps A is obtained with contain final positively charged ion C fPowder mixing post-heating, make volatile ammonia evaporation, C in the product that makes fO/Al 2O 3>=0.7, (NH 4) 2O/Al 2O 3≤0.1, then with containing C fSolution washing, drying finally obtains cation exchange capacity w-type zeolite molecular sieve.
Described preparation method, wherein, initial cationic C iWith final positively charged ion C fSelectivity coefficient Sf i f≤0.5.
Described preparation method, wherein, the temperature of reaction of steps A is 0-50 ℃, reaction soln pH is less than 7.
Described preparation method, wherein, the pH value of solution of step B >=7 (preferred pH is greater than 10), temperature is 0-100 ℃.
Described preparation method wherein, washes with purge gas between the reaction period of step B.
Described preparation method, wherein, the water-soluble ammonium compound in the steps A comprises: ammonium sulfate, ammonium chloride, an ammonium nitrate, ammonium acetate or mixture.
Described preparation method, wherein, the final positively charged ion of step B is calcium, sodium ion, mg ion or lithium ion (preferably by calcium ion, recommending calcium ion source to be preferably calcium hydroxide).
The method for preparing high-cation exchange capacity W type molecular sieve provided by the invention need not used a large amount of excessive cationic expensive salt, need not use expensive and the strong positively charged ion recovery scheme of motility simultaneously.
Embodiment
The present invention is a kind of method of utilizing the preparation of polynary cationic exchange to have high-cation exchange capacity W type molecular sieve; At first with the ammonium ion exchange in w-type zeolite molecular sieve and the ammonium thing; Replace the positively charged ion in the w-type zeolite molecular sieve with ammonium ion thus; The w-type zeolite that to cross with ammonium ion exchange then with contain final cationic solution and contact; The pH that keeps solution simultaneously is 9-12, and final acquisition contains final cationic w-type zeolite molecular sieve with high-cation exchange capacity, and wherein the target positively charged ion accounts for more than 70% of w-type zeolite positively charged ion total amount.
Technical scheme of the present invention is specific as follows:
1) will contain initial cationic C iThe w-type zeolite molecular sieve of form contacts with the water-soluble ammonium compound that contains ammonium ion.Contain initial cationic C iThe w-type zeolite molecular sieve of form and contain reaction between the water-soluble ammonium compound of ammonium ion and be preferably under about 0-50 ℃ and carry out.This reaction is preferably in less than carrying out under 7 the pH.Water-soluble ammonium compound comprises: the mixture of ammonium sulfate, ammonium chloride, an ammonium nitrate, ammonium acetate or these ammonium compounds.Ammonium concentration is 0.5mol/L-2.5mol/L, and the reaction times is controlled at 2-4h, makes final (NH 4) 2O/Al 2O 3>=0.8; Generally speaking, C iBe potassium ion.Reaction realizes solid-liquid separation through the centrifugal mode with mixed solution after finishing, and the solid that separation is obtained repeats above-mentioned experiment 3 times, promptly carries out ammonium ion exchange 3 times.Again solid is washed 3 times with the water-soluble ammonium compound that contains ammonium ion at last, centrifugal back decanted solution, the solid sample that obtains is the w-type zeolite molecular sieve that contains ammonium ion.
2) the w-type zeolite molecular sieve that contains ammonium ion that step 1 is obtained with contain final positively charged ion C fSolution contact, with at least a final positively charged ion substituted ammonium ion, and remove reaction product ammonia from reaction zone.C wherein iAnd C fSelectivity coefficient Sf i f≤0.5, final positively charged ion C fConcentration is 0.5mol/L-2.5mol/L; PH value of solution>=7 more preferably are higher than 10 times at pH and carry out.In 0-100 ℃ of water-bearing media, react, reaction times 10-24h makes final C fO/Al 2O 3>=0.7, (NH 4) 2O/Al 2O 3≤0.1; This reaction during reaction with the purge gas flushing, is guaranteed to remove volatile reaction product ammonia from reaction zone.Generally speaking, the positively charged ion of substituted ammonium ion is calcium, sodium ion, mg ion or lithium ion.Aspect more preferably, ammonium ion replaces with calcium ion.Aspect more preferably, calcium ion source is preferably calcium hydroxide.
By substituted w-type zeolite molecular sieve of ammonium ion and final positively charged ion C fReaction also can carry out with solid-state, for example carry out with dryness basically.Aspect this, this reaction is preferably under about 100-400 ℃ to be carried out.Wherein at least a reaction product (as by the substituted w-type zeolite molecular sieve of ammonium ion) is a gaseous state or volatile, from system evaporation or distillation.
3) the W type molecular sieve that step 2 is obtained is with containing C fConcentration is the solution washing of 0.02mol/L, and drying finally obtains high-cation exchange capacity w-type zeolite molecular sieve.
The present invention's preparation has high-cation exchange capacity W type molecular sieve, has overcome the problem of present implementation method.Compare with other method of producing high-cation exchange capacity W type molecular sieve, present method need not used a large amount of excessive expensive exchange cation salt, need not use expensive positively charged ion recovery scheme simultaneously.Ion exchange method of the present invention is carried out under the condition of removing a kind of reaction product from reaction zone.IX can be carried out in liquid phase, and wherein a kind of reaction product is a gaseous state or volatile, can blow out reaction zone; Perhaps IX can be solid state reaction, wherein also is that at least a reaction product is a gaseous state or volatile, from system evaporation or distillation.
Embodiment 1
1) 30g is contained the w-type zeolite molecular sieve k of potassium ion 2W and 2L concentration are the ammoniumsulphate soln reaction of 2mol/L.PH value of solution is 6.5, is reflected under the room temperature (25 ℃) to carry out, and the reaction times is 2h, realizes solid-liquid separation through the centrifugal mode then.The solid that separation is obtained repeats above-mentioned experiment 3 times, promptly carries out ammonium ion exchange 3 times.Use 2L concentration to be the ammoniumsulphate soln of 0.01mol/L washing 3 times solid at last, 1. centrifugal back decanted solution obtains sample, and 1. sample is carried out proximate analysis.
2) sample that 10g step 1 is obtained 1. (the w-type zeolite molecular sieve that contains ammonium ion) is the Ca (OH) of 2mol/L with 1L concentration 2Solution reaction is blown into nitrogen to prevent CO in solution in the reaction process 2Get in the solution and Ca (OH) 2React, and remove reaction product ammonia from reaction zone.60 ℃ of temperature of reaction, reaction times 18h, and pH of mixed remains at 9-12 in the 18h of reaction.After reaction is accomplished, with acid pH of mixed is transferred to about 7.0, then that mixed solution is centrifugal, decanted solution obtains solid sample again.
3) solid sample that step 2 is obtained uses the Ca (OH) of 1L concentration as 0.02mol/L 2Solution washing, centrifugal, it is dry again to obtain solid behind the decanted solution, finally obtains the w-type zeolite molecular sieve 2., and 2. sample is carried out proximate analysis.
4) the 2. also residual lower ammonium ion of w-type zeolite molecular sieve that obtains of step 3 adopts 500ml to contain 2mol/L CaCl 2/ NaCl (CaCl 2Be 1.5mol/L, NaCl is 0.5mol/L) 2. react with the w-type zeolite molecular sieve, 60 ℃ of temperature of reaction, reaction times 24h, and pH of mixed remains at 9-12 in the 24h of reaction.After reaction is accomplished, with acid pH of mixed is transferred to about 7.0, then that mixed solution is centrifugal, decanted solution obtains solid sample again.
(5) solid sample that step (4) is obtained uses the CaCl of 500ml concentration as 0.02mol/L 2Solution washing 33 times, centrifugal, it is dry again to obtain solid behind the decanted solution, finally obtains the w-type zeolite molecular sieve 3., and 3. sample is carried out proximate analysis.The chemical composition analysis result that 3. 1., 2. W type molecular sieve reach sees table 1.
Table 1:W type molecular sieve chemical composition analysis
Figure BDA0000113015350000051
Embodiment 2:
1) will contain initial cationic C iThe w-type zeolite molecular sieve of form contacts with the water-soluble ammonium compound that contains ammonium ion.Contain initial cationic C iThe w-type zeolite molecular sieve of form and contain reaction between the water-soluble ammonium compound of ammonium ion and be preferably under about 0-50 ℃ and carry out.This reaction is preferably in less than carrying out under 7 the pH.Water-soluble ammonium compound comprises: the mixture of ammonium sulfate, ammonium chloride, an ammonium nitrate, ammonium acetate or these ammonium compounds.Ammonium concentration is 0.005mol/L-0.1mol/L, and the reaction times is controlled at 2-4h, makes final (NH 4) 2O/Al 2O 3>=0.8; Generally speaking, C iBe potassium ion.
2) by substituted w-type zeolite molecular sieve of ammonium ion and final positively charged ion C fReaction also can carry out with solid-state, for example carry out with dryness basically.This reaction is preferably under about 100-400 ℃ to be carried out.Wherein at least a reaction product is a gaseous state or volatile, from system evaporation or distillation.
3) the W type molecular sieve that step 2 is obtained is with containing final positively charged ion C fConcentration is the solution washing of 0.002mol/L, and drying finally obtains high-cation exchange capacity w-type zeolite molecular sieve.

Claims (8)

1.一种制备阳离子交换容量W型沸石分子筛的方法,主要步骤为:1. A method for preparing cation exchange capacity W type zeolite molecular sieve, the main steps are: A)将含有初始阳离子Ci形式的W型沸石分子筛与含有铵离子的水溶性铵化合物接触,得到的含铵离子的W型沸石分子筛中(NH4)2O/Al2O3≥0.8;A) contacting the W-type zeolite molecular sieve containing the initial cation C i form with a water-soluble ammonium compound containing ammonium ions, and (NH 4 ) 2 O/Al 2 O 3 ≥ 0.8 in the obtained W-type zeolite molecular sieve containing ammonium ions; B)将步骤A得到的含铵离子的W型沸石分子筛与含最终阳离子Cf的溶液接触,用至少一种所述阳离子取代铵离子,并从反应区除去挥发性氨,制得的产物中CfO/Al2O3≥0.7,(NH4)2O/Al2O3≤0.1;B) The W-type zeolite molecular sieve containing the ammonium ion obtained in step A is contacted with the solution containing the final cation Cf , the ammonium ion is replaced with at least one of the cations, and the volatile ammonia is removed from the reaction zone, and the obtained product C f O/Al 2 O 3 ≥0.7, (NH 4 ) 2 O/Al 2 O 3 ≤0.1; C)将步骤B得到的产物用含Cf的溶液洗涤,干燥,最终得到阳离子交换容量W型沸石分子筛。C) The product obtained in step B is washed with a solution containing Cf , and dried to finally obtain a W-type zeolite molecular sieve with cation exchange capacity. 2.一种制备阳离子交换容量W型沸石分子筛的方法,主要步骤为:2. A method for preparing cation exchange capacity W type zeolite molecular sieve, the main steps are: A)将含有初始阳离子Ci形式的W型沸石分子筛与含有铵离子的水溶性铵化合物接触,得到的含铵离子的W型沸石分子筛中(NH4)2O/Al2O3≥0.8;A) contacting the W-type zeolite molecular sieve containing the initial cation C i form with a water-soluble ammonium compound containing ammonium ions, and (NH 4 ) 2 O/Al 2 O 3 ≥ 0.8 in the obtained W-type zeolite molecular sieve containing ammonium ions; B)将步骤A得到的含铵离子的W型沸石分子筛干燥与含最终阳离子Cf的粉末进行混合后加热,使挥发性氨蒸发,制得的产物中CfO/Al2O3≥0.7,(NH4)2O/Al2O3≤0.1;B) Dry the W-type zeolite molecular sieve containing ammonium ion obtained in step A and mix it with the powder containing the final cation Cf , then heat to evaporate the volatile ammonia, and the obtained product has CfO / Al2O3≥0.7 , (NH 4 ) 2 O/Al 2 O 3 ≤0.1; C)将步骤B得到的产物用含Cf的溶液洗涤,干燥,最终得到阳离子交换容量W型沸石分子筛。C) The product obtained in step B is washed with a solution containing Cf , and dried to finally obtain a W-type zeolite molecular sieve with cation exchange capacity. 3.根据权利要求1或2所述的制备方法,其中,初始阳离子Ci和最终阳离子Cf的选择性系数Sfi f≤0.5。3. The preparation method according to claim 1 or 2, wherein the selectivity coefficient Sf if of the initial cation C i and the final cation C f is ≤0.5. 4.根据权利要求1或2所述的制备方法,其中,步骤A的反应温度为0-50℃,反应溶液pH小于7。4. The preparation method according to claim 1 or 2, wherein the reaction temperature in step A is 0-50° C., and the pH of the reaction solution is less than 7. 5.根据权利要求1所述的制备方法,其中,步骤B的溶液pH≥7,温度为0-100℃。5. The preparation method according to claim 1, wherein the pH of the solution in step B is ≥ 7, and the temperature is 0-100°C. 6.根据权利要求1所述的制备方法,其中,步骤B的反应期间用吹洗气体冲洗。6. The preparation method according to claim 1, wherein, during the reaction of step B, flushing is performed with a purge gas. 7.根据权利要求1或2所述的制备方法,其中,步骤A中的水溶性铵化合物包括:硫酸铵、氯化铵、硝酸铵、乙酸铵或混合物。7. The preparation method according to claim 1 or 2, wherein the water-soluble ammonium compound in step A comprises: ammonium sulfate, ammonium chloride, ammonium nitrate, ammonium acetate or a mixture. 8.根据权利要求1或2所述的制备方法,其中,步骤B的最终阳离子为钙、钠离子、镁离子或锂离子。8. The preparation method according to claim 1 or 2, wherein the final cation of step B is calcium, sodium ion, magnesium ion or lithium ion.
CN2011103837103A 2011-11-28 2011-11-28 Method for preparing cation exchange content W type zeolite molecular sieve Pending CN102491362A (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
CN2011103837103A CN102491362A (en) 2011-11-28 2011-11-28 Method for preparing cation exchange content W type zeolite molecular sieve

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
CN2011103837103A CN102491362A (en) 2011-11-28 2011-11-28 Method for preparing cation exchange content W type zeolite molecular sieve

Publications (1)

Publication Number Publication Date
CN102491362A true CN102491362A (en) 2012-06-13

Family

ID=46183233

Family Applications (1)

Application Number Title Priority Date Filing Date
CN2011103837103A Pending CN102491362A (en) 2011-11-28 2011-11-28 Method for preparing cation exchange content W type zeolite molecular sieve

Country Status (1)

Country Link
CN (1) CN102491362A (en)

Citations (1)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN1196976A (en) * 1996-12-27 1998-10-28 美国Boc氧气集团有限公司 Method of manufacture of molecular sieves

Patent Citations (1)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN1196976A (en) * 1996-12-27 1998-10-28 美国Boc氧气集团有限公司 Method of manufacture of molecular sieves

Similar Documents

Publication Publication Date Title
CN1234451C (en) Preparing Method for magnetic active carbon used for water treatment
CN102935299B (en) A kind of method using manganese oxide sorbing material to extract lithium ion
WO2017215011A1 (en) Ion sieve material, preparation method therefor and using method thereof
CN104692406B (en) A kind of preparation method of the adsorbent of Selective Separation cesium ion from salt lake bittern
Sihn et al. Rapid extraction of uranium ions from seawater using novel porous polymeric adsorbents
KR102422463B1 (en) Reactive composition based on sodium bicarbonate and process for its production
CN101671259A (en) Synthesis of alcoholamines functionalized ionic liquid
Şenol et al. Preparation and characterization of a novel diatomite-based composite and investigation of its adsorption properties for uranyl ions
CN103769058A (en) Preparation method of carbonized chitosan adsorbent, adsorbent and application method of absorbent
CN101355998A (en) Method for separating and/or purifying a gas mixture
CN106588960B (en) A kind of metal-organic framework material and preparation method thereof for effective carbon-dioxide/nitrogen selective separation absorption
CN103301805A (en) Carbon dioxide adsorbent and preparation method thereof
CN105327687A (en) CO2 absorbent as well as preparation method and application thereof
TW202017650A (en) Metal organic frameworks material and method for preparing the same, and adsorption device employing the same
Bao et al. Preconcentration and separation of rubidium from salt lake brine by ammonium phosphomolybdate–polyacrylonitrile (AMP‐PAN) composite adsorbent
CN102671628A (en) Microporous molecular sieve-functionalized ionic liquid composite material and preparation method thereof
CN105129826A (en) Technological method for recycling lithium from lithium-containing waste liquid of medicine and synthetic plastics industries
CN106984137A (en) A kind of absorption CO of phase separation2Polyaminoacid ionic liquid preparation and its application method
CN106914102A (en) A kind of metal ion liquid-absorbant of efficient reversible absorption ammonia
CN104174275A (en) Compound type ionic liquid and preparation method and application of compound type ionic liquid as trapping agent
CN113351187A (en) Heavy metal ion imprinted hydrogel ball and preparation method and application thereof
CN107349754A (en) A kind of desulfurizing agent composition and sulfur method
CN102491362A (en) Method for preparing cation exchange content W type zeolite molecular sieve
CN113842892A (en) Method for treating uranium-containing wastewater by modifying natural fibers with amide/phosphoric acid groups
CN114057915B (en) A kind of biscarbonyl chelating resin and its preparation method and application

Legal Events

Date Code Title Description
C06 Publication
PB01 Publication
C10 Entry into substantive examination
SE01 Entry into force of request for substantive examination
C02 Deemed withdrawal of patent application after publication (patent law 2001)
WD01 Invention patent application deemed withdrawn after publication

Application publication date: 20120613