CN101306827A - Method for preparing polyaluminium chloride by firing waste residues with sludge - Google Patents
Method for preparing polyaluminium chloride by firing waste residues with sludge Download PDFInfo
- Publication number
- CN101306827A CN101306827A CNA2008101147436A CN200810114743A CN101306827A CN 101306827 A CN101306827 A CN 101306827A CN A2008101147436 A CNA2008101147436 A CN A2008101147436A CN 200810114743 A CN200810114743 A CN 200810114743A CN 101306827 A CN101306827 A CN 101306827A
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- CN
- China
- Prior art keywords
- sludge
- aluminum
- waste slag
- burnt waste
- hydrochloric acid
- Prior art date
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- 239000002699 waste material Substances 0.000 title claims abstract description 42
- 239000010802 sludge Substances 0.000 title claims abstract description 33
- 238000000034 method Methods 0.000 title claims abstract description 26
- VEXZGXHMUGYJMC-UHFFFAOYSA-M Chloride anion Chemical compound [Cl-] VEXZGXHMUGYJMC-UHFFFAOYSA-M 0.000 title abstract 3
- 238000010304 firing Methods 0.000 title abstract 3
- XAGFODPZIPBFFR-UHFFFAOYSA-N aluminium Chemical compound [Al] XAGFODPZIPBFFR-UHFFFAOYSA-N 0.000 claims abstract description 48
- 229910052782 aluminium Inorganic materials 0.000 claims abstract description 48
- VEXZGXHMUGYJMC-UHFFFAOYSA-N Hydrochloric acid Chemical compound Cl VEXZGXHMUGYJMC-UHFFFAOYSA-N 0.000 claims abstract description 36
- VSCWAEJMTAWNJL-UHFFFAOYSA-K aluminium trichloride Chemical compound Cl[Al](Cl)Cl VSCWAEJMTAWNJL-UHFFFAOYSA-K 0.000 claims abstract description 22
- 238000003756 stirring Methods 0.000 claims abstract description 10
- BRPQOXSCLDDYGP-UHFFFAOYSA-N calcium oxide Chemical compound [O-2].[Ca+2] BRPQOXSCLDDYGP-UHFFFAOYSA-N 0.000 claims abstract description 8
- 239000000292 calcium oxide Substances 0.000 claims abstract description 8
- ODINCKMPIJJUCX-UHFFFAOYSA-N calcium oxide Inorganic materials [Ca]=O ODINCKMPIJJUCX-UHFFFAOYSA-N 0.000 claims abstract description 8
- 238000000926 separation method Methods 0.000 claims abstract description 8
- 239000002253 acid Substances 0.000 claims abstract description 7
- 238000006243 chemical reaction Methods 0.000 claims abstract description 7
- 239000007788 liquid Substances 0.000 claims abstract description 7
- 239000000843 powder Substances 0.000 claims abstract description 6
- 239000000203 mixture Substances 0.000 claims abstract description 3
- PNEYBMLMFCGWSK-UHFFFAOYSA-N aluminium oxide Inorganic materials [O-2].[O-2].[O-2].[Al+3].[Al+3] PNEYBMLMFCGWSK-UHFFFAOYSA-N 0.000 claims abstract 3
- 239000002893 slag Substances 0.000 claims description 34
- 238000012545 processing Methods 0.000 claims description 10
- 238000005660 chlorination reaction Methods 0.000 claims description 9
- TWNQGVIAIRXVLR-UHFFFAOYSA-N oxo(oxoalumanyloxy)alumane Chemical compound O=[Al]O[Al]=O TWNQGVIAIRXVLR-UHFFFAOYSA-N 0.000 claims description 8
- 235000008733 Citrus aurantifolia Nutrition 0.000 claims description 5
- 235000011941 Tilia x europaea Nutrition 0.000 claims description 5
- 239000004571 lime Substances 0.000 claims description 5
- 230000035484 reaction time Effects 0.000 claims description 4
- 238000005119 centrifugation Methods 0.000 claims description 3
- 238000006116 polymerization reaction Methods 0.000 claims description 2
- 239000010865 sewage Substances 0.000 abstract description 11
- 238000000197 pyrolysis Methods 0.000 abstract description 6
- 238000004519 manufacturing process Methods 0.000 abstract description 4
- 230000009286 beneficial effect Effects 0.000 abstract description 2
- 239000003344 environmental pollutant Substances 0.000 abstract description 2
- 231100000719 pollutant Toxicity 0.000 abstract description 2
- AZDRQVAHHNSJOQ-UHFFFAOYSA-N alumane Chemical class [AlH3] AZDRQVAHHNSJOQ-UHFFFAOYSA-N 0.000 abstract 2
- 239000008394 flocculating agent Substances 0.000 abstract 2
- 125000004122 cyclic group Chemical group 0.000 abstract 1
- 238000004090 dissolution Methods 0.000 abstract 1
- 238000011084 recovery Methods 0.000 abstract 1
- 239000004411 aluminium Substances 0.000 description 12
- 229910000329 aluminium sulfate Inorganic materials 0.000 description 7
- 239000003814 drug Substances 0.000 description 7
- 159000000013 aluminium salts Chemical class 0.000 description 6
- 238000005189 flocculation Methods 0.000 description 6
- 230000016615 flocculation Effects 0.000 description 6
- XLYOFNOQVPJJNP-UHFFFAOYSA-N water Substances O XLYOFNOQVPJJNP-UHFFFAOYSA-N 0.000 description 5
- 229910001570 bauxite Inorganic materials 0.000 description 4
- -1 aluminium chlorohydroxide Chemical compound 0.000 description 3
- 238000001354 calcination Methods 0.000 description 3
- 239000012141 concentrate Substances 0.000 description 3
- 238000005261 decarburization Methods 0.000 description 3
- 238000000746 purification Methods 0.000 description 3
- 238000004064 recycling Methods 0.000 description 3
- 238000013019 agitation Methods 0.000 description 2
- DIZPMCHEQGEION-UHFFFAOYSA-H aluminium sulfate (anhydrous) Chemical compound [Al+3].[Al+3].[O-]S([O-])(=O)=O.[O-]S([O-])(=O)=O.[O-]S([O-])(=O)=O DIZPMCHEQGEION-UHFFFAOYSA-H 0.000 description 2
- 239000002956 ash Substances 0.000 description 2
- 230000008901 benefit Effects 0.000 description 2
- 230000015572 biosynthetic process Effects 0.000 description 2
- 239000010840 domestic wastewater Substances 0.000 description 2
- FAHBNUUHRFUEAI-UHFFFAOYSA-M hydroxidooxidoaluminium Chemical compound O[Al]=O FAHBNUUHRFUEAI-UHFFFAOYSA-M 0.000 description 2
- 239000012263 liquid product Substances 0.000 description 2
- 238000005303 weighing Methods 0.000 description 2
- 239000005995 Aluminium silicate Substances 0.000 description 1
- 241000628997 Flos Species 0.000 description 1
- 230000003044 adaptive effect Effects 0.000 description 1
- 235000012211 aluminium silicate Nutrition 0.000 description 1
- 229910052934 alunite Inorganic materials 0.000 description 1
- 239000010424 alunite Substances 0.000 description 1
- 238000013459 approach Methods 0.000 description 1
- 239000004927 clay Substances 0.000 description 1
- 239000003245 coal Substances 0.000 description 1
- 238000011161 development Methods 0.000 description 1
- 238000004043 dyeing Methods 0.000 description 1
- 238000005516 engineering process Methods 0.000 description 1
- 238000003912 environmental pollution Methods 0.000 description 1
- 239000012467 final product Substances 0.000 description 1
- 239000010881 fly ash Substances 0.000 description 1
- 229910052500 inorganic mineral Inorganic materials 0.000 description 1
- 229920000592 inorganic polymer Polymers 0.000 description 1
- NLYAJNPCOHFWQQ-UHFFFAOYSA-N kaolin Chemical compound O.O.O=[Al]O[Si](=O)O[Si](=O)O[Al]=O NLYAJNPCOHFWQQ-UHFFFAOYSA-N 0.000 description 1
- 239000011707 mineral Substances 0.000 description 1
- 239000002245 particle Substances 0.000 description 1
- 238000007639 printing Methods 0.000 description 1
- 239000000047 product Substances 0.000 description 1
- 239000002994 raw material Substances 0.000 description 1
- 238000007670 refining Methods 0.000 description 1
- 238000011160 research Methods 0.000 description 1
- 238000004062 sedimentation Methods 0.000 description 1
- 239000002910 solid waste Substances 0.000 description 1
- 238000005979 thermal decomposition reaction Methods 0.000 description 1
- KPZTWMNLAFDTGF-UHFFFAOYSA-D trialuminum;potassium;hexahydroxide;disulfate Chemical compound [OH-].[OH-].[OH-].[OH-].[OH-].[OH-].[Al+3].[Al+3].[Al+3].[K+].[O-]S([O-])(=O)=O.[O-]S([O-])(=O)=O KPZTWMNLAFDTGF-UHFFFAOYSA-D 0.000 description 1
- 239000002351 wastewater Substances 0.000 description 1
- 238000004065 wastewater treatment Methods 0.000 description 1
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Landscapes
- Separation Of Suspended Particles By Flocculating Agents (AREA)
Abstract
The invention relates to a method for preparing polyaluminium chloride by using sludge firing waste residue, wherein the sludge firing waste residue is added with hydrochloric acid with the concentration of 10-30% according to the equivalent ratio of alumina to hydrochloric acid of 1.0: 1.0-1.5, and the mixture is stirred for acid dissolution reaction at normal temperature for 2-10 hours for solid-liquid separation; adding calcium oxide powder into the separated acid liquor containing aluminum chloride according to the weight ratio of the aluminum chloride to the calcium oxide of 1.0: 0.3-0.6, and stirring and reacting at normal temperature for 2-24 hours to obtain the polyaluminium chloride solution. The aluminum salt flocculating agent for sewage treatment provided by the invention is used for sludge pyrolysis and incineration waste residue resource treatment, can realize recovery and cyclic utilization of the aluminum salt flocculating agent added in the sewage treatment process, reduces pollutant discharge and aluminum resource consumption, and is beneficial to clean production and resource saving of a sewage treatment system.
Description
Technical field
The present invention relates to a kind of method for preparing polymeric aluminum with burnt waste slag of sludge, this method is applicable to process water, sewage-farms such as industrial sewage such as oil field, refinery and urban domestic wastewater carry out purifying treatment with aluminium salt flocculation medicament and mud concentrates the mud that forms, its waste slag of aluminum that contains through burn forming, or reclaim and utilize again through the aluminium salt that contains waste slag of aluminum of calcination decarburization again through the residue of pyrolysis processing.
Background technology
Polymeric aluminum has another name called aluminium chlorohydroxide or aluminium chlorohydroxide.It has that coagulability is strong, consumption is few, water purification usefulness height, characteristics that adaptive faculty is strong, is widely used in printing and dyeing, the process water and the wastewater treatment of industry such as process hides, medicine, oil, papermaking, makeup.Its water purification is can force rate Tai-Ace S 150 high 8~10 times, and it is fast and particle is big to form the speed of floss during cohesion.Polymeric aluminum is a kind of efficient flocculant that the scientist of states such as moral, Japan and the United States found in the thirties, and the later stage sixties forms scale production in developed country, and the output surge seventies is called as epoch-making inorganic polymer flocculation seventies medicament.China develops this product since the seventies, is subjected to the influence of aluminium deep processing, and the aluminium ash is collected difficulty and limited development, and the eighties, the poly-aluminium of the explained hereafter that has nothing in common with each other is adopted according to its cheap bauxite resource advantage in various places.
At present, domestic production polymeric aluminum is mainly based in acid-soluble one-step, the acidleach and two-step approach, gel method, thermal decomposition method etc.Raw material commonly used mainly contains pure aluminum (various aluminium processing fents such as aluminium ingot, aluminium ash, aluminium bits), aluminum-containing mineral (as bauxite, clay, kaolin, alunite, coal gangue etc.), aluminium salt compound (as aluminum chloride, Tai-Ace S 150 etc.), flyash etc.
Polymeric aluminum is at process water, is extensive use of during industrial sewage such as oil field, refinery and urban domestic wastewater purifying treatment and mud concentrate, and belongs to disposable running stores, finally enters environment with the mud that forms or the waste residue of its burning or pyrolysis processing.Through the aluminium of the general sewage disposal pyrolyzing sludge of research and appraisal residue (with Al
2O
3Meter) content can reach more than 20%, and Gao Zheke reaches 50% to 60%, and higher aluminium content is arranged, if not to its recycling, it had both wasted bauxite resource, also has environmental pollution simultaneously.Adopt burnt waste slag of sludge to prepare polymeric aluminum, all be of great practical significance from the aspects such as useless improvement, resources conservation and economic benefit admittedly in sewage-farm so that it obtains certain utilization.
Summary of the invention
The purpose of this invention is to provide a kind of method for preparing polymeric aluminum with burnt waste slag of sludge, solution contains that aluminium solid waste is innoxious, minimizing and resource utilization problem, and emphasis is to solve a large amount of aluminium salt flocculation medicaments to be used for a large amount of mud that form after the sewage disposal and the innoxious and resource recycling of burning or pyrolysis processing waste residue thereof.
The inventive method is achieved in that burnt waste slag of sludge is placed closed reactor, presses aluminum oxide (Al contained in the burnt waste slag of sludge
2O
3) with the equivalence ratio of hydrochloric acid be that 1.0: 1.0~1.5 to add concentration be 10~30% aqueous hydrochloric acid, stir at normal temperatures and carry out sour molten reaction, sour molten reaction 2~10 hours; The solidliquid mixture that forms is carried out solid-liquid separation, must contain the chlorination aluminum solutions; Contain aluminum chloride (AlCl in the acid solution that separation is obtained then
3) weight ratio of weight and calcium oxide is 1.0: 0.3~0.6 to add lime powder, stirs at normal temperatures and carries out polyreaction, polymerization reaction time is 2-24 hour, get final product polymeric aluminum solution.
Concrete processing parameter and condition are done following description:
1, burnt waste slag of sludge is to carry out the sewage purification processing with aluminium salt flocculation medicament to concentrate the mud that forms with mud, through burning the waste residue of formation, or through the residue of pyrolysis processing again through the waste residue of calcination decarburization, the aluminum oxide (Al of burnt waste slag
2O
3) content is 10~60%, the best is 30~60%.
2, the used acid of sour molten reaction is hydrochloric acid, and the hydrochloric acid consumption is 1.0: 1.0~1.2 by equivalence ratio the best of the salic and hydrochloric acid of burnt waste slag of sludge; Concentration of hydrochloric acid the best is 20~30%; The molten reaction times the best of acid is 2~5 hours.
What 3, described solid-liquid separation adopted is separating centrifuge, is the best with the horizontal helical type separating centrifuge wherein.Also can adopt sedimentation method to isolate and contain the chlorination aluminum solutions.
4, the weight ratio that contains aluminum chloride weight contained in the chlorination aluminum solutions and calcium oxide that obtains by separation is 1.0: 0.4~0.5; The polyreaction churning time is 5-10 hour the best.Get polymeric aluminum solution.
The invention has the beneficial effects as follows: the method for preparing polymeric aluminum with burnt waste slag of sludge is used for the mud that purifying treatment and the concentrated formation of mud are carried out with aluminium salt flocculation medicament in sewage-farms such as oil field, refinery, urban industry and sanitary wastewater, it is through burning the waste slag of aluminum that contains that forms, or through the residue of pyrolysis processing again through the recycling treatment that contains waste slag of aluminum of calcination decarburization, can realize the recycle and reuse of the aluminium salt flocculation medicament that sewage treatment process adds, reduce pollutant emission and bauxite resource consumption, help Sewage treatment systems cleaner production and resources conservation.
Description of drawings
Fig. 1 is the present invention prepares the method for polymeric aluminum with burnt waste slag of sludge a process flow sheet.
Embodiment
Embodiment 1: consult Fig. 1.
1. take by weighing 228g oilfield sewage burnt waste slag of sludge, the aluminum oxide (Al in the burnt waste slag of sludge
2O
3) content is 30%.
2. press the equivalence ratio 1: 1.17 of aluminum oxide contained in the burnt waste slag of sludge and hydrochloric acid, adding concentration is 30% aqueous hydrochloric acid 508ml in the 2L Erlenmeyer flask, under magnetic agitation, slowly add above-mentioned burnt waste slag, add the airtight stirring in back after 2 hours 30 minutes, adopt the horizontal helical type separating centrifuge to isolate and contain aluminum chloride (AlCl
3) solution;
3. under powerful stirring condition, by containing aluminum chloride (AlCl contained in the chlorination aluminum solutions
3) with the weight ratio of calcium oxide be 1: 0.52, containing of going out slowly add lime powder 60g in the aluminic acid liquid to centrifugation, stirred 3 hours, obtain the liquid product polymeric aluminum, its aluminium (is pressed Al
2O
3Meter) content is 10.52%, and basicity is 61.24%.
Embodiment 2: consult Fig. 1.
1. take by weighing 450g oil refining sewerage burnt waste slag of sludge, the aluminum oxide (Al that contains in the burnt waste slag of sludge
2O
3) be 45%.
2. press the equivalence ratio 1: 1.08 of aluminum oxide contained in the burnt waste slag of sludge and hydrochloric acid, add the aqueous hydrochloric acid 1383ml of concentration at the 2L Erlenmeyer flask for adding 30%, under magnetic agitation, slowly add above-mentioned roasting residue, add the airtight stirring in back after 3 hours, adopt the centrifugal settling method to isolate and contain aluminum chloride (AlCl
3) solution;
3. under powerful stirring condition, the weight ratio of contained aluminum chloride and calcium oxide is 1: 0.43 in the chlorination aluminum solutions by containing, and containing of going out slowly adds lime powder 140g in the chlorination aluminic acid liquid to centrifugation, stirs 3 hours, obtain the liquid product polymeric aluminum, its aluminium (is pressed Al
2O
3Meter) content is 10.34%, and basicity is 69.82%.
Claims (6)
1, a kind ofly prepare the method for polymeric aluminum, it is characterized in that with burnt waste slag of sludge:
Burnt waste slag of sludge is done following processing:
A, burnt waste slag of sludge is placed closed reactor, equivalence ratio by aluminum oxide contained in the burnt waste slag of sludge and hydrochloric acid is 1.0: 1.0~1.5, adding concentration is 10~30% aqueous hydrochloric acid, stirs at normal temperatures and carries out sour molten reaction, sour molten reaction 2~10 hours;
B, the solidliquid mixture that forms is carried out solid-liquid separation, must contain the chlorination aluminum solutions;
C, the weight ratio that contains aluminum chloride weight contained in the chlorination aluminum solutions and calcium oxide that obtains by separation are 1.0: 0.3~0.6 adding lime powder, stir at normal temperatures and carry out polyreaction, and polymerization reaction time is 2-24 hour, gets polymeric aluminum solution.
2, a kind ofly prepare the method for polymeric aluminum with burnt waste slag of sludge according to claim 1 is described, it is characterized in that: the alumina content of burnt waste slag of sludge is 10-60%.
3, a kind ofly prepare the method for polymeric aluminum with burnt waste slag of sludge according to claim 1 is described, it is characterized in that: the alumina content of burnt waste slag of sludge is 30-60%.
4, describedly a kind ofly prepare the method for polymeric aluminum with burnt waste slag of sludge according to claim 1 or 2 or 3, it is characterized in that: the used acid of sour molten reaction is hydrochloric acid, and the aluminum oxide that the hydrochloric acid consumption contains by burnt waste slag of sludge and the equivalence ratio of hydrochloric acid are 1.0: 1.0~1.2; Concentration of hydrochloric acid is 20-30%; The molten reaction times of acid is 2-5 hour.
5, a kind ofly prepare the method for polymeric aluminum with burnt waste slag of sludge according to claim 1 is described, it is characterized in that: described solid-liquid separation is centrifugation, and the separating device of use is the horizontal helical type separating centrifuge.
6, a kind ofly prepare the method for polymeric aluminum with burnt waste slag of sludge according to claim 1 is described, it is characterized in that: the lime powder amount that polyreaction adds is 1.0: 0.4~0.5 by the weight ratio that contains aluminum chloride weight contained in the chlorination aluminum solutions and calcium oxide; The polyreaction churning time is 5-10 hour.
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CN2008101147436A CN101306827B (en) | 2008-06-11 | 2008-06-11 | Method for preparing polyaluminium chloride by firing waste residues with sludge |
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CN2008101147436A CN101306827B (en) | 2008-06-11 | 2008-06-11 | Method for preparing polyaluminium chloride by firing waste residues with sludge |
Publications (2)
Publication Number | Publication Date |
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CN101306827A true CN101306827A (en) | 2008-11-19 |
CN101306827B CN101306827B (en) | 2010-07-28 |
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Cited By (4)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
CN103121779A (en) * | 2013-02-04 | 2013-05-29 | 刘进龙 | Cyclic regeneration method and application of town sewage treatment medicament |
CN107285355A (en) * | 2017-08-01 | 2017-10-24 | 广西新晶科技有限公司 | A kind of method for preparing aluminium polychloride using discarded anthraquinone regenerative agent |
CN110963662A (en) * | 2019-12-09 | 2020-04-07 | 上海净屹环保科技有限公司 | Method for recovering aluminum salt coagulant from aluminum-containing sludge |
CN114804315A (en) * | 2022-06-06 | 2022-07-29 | 中国铁工投资建设集团有限公司 | Polyaluminum ferric chloride and composite flocculant prepared from municipal sludge drying pyrolysis residues |
Family Cites Families (4)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
FR2626567B1 (en) * | 1988-01-29 | 1991-09-27 | Atochem | BASIC ALUMINUM CHLOROSULFATE, MANUFACTURING METHOD THEREOF, USE THEREOF AS FLOCCULATING AGENT |
CN1106766A (en) * | 1994-02-08 | 1995-08-16 | 董正康 | Process for production of aluminium polychloride |
CN100355656C (en) * | 2004-07-09 | 2007-12-19 | 中国石油天然气股份有限公司 | Preparation method of polyaluminum chloride with high aluminum content |
CN100513337C (en) * | 2006-07-28 | 2009-07-15 | 中国石油天然气股份有限公司 | Resourceful treatment method for oily sludge |
-
2008
- 2008-06-11 CN CN2008101147436A patent/CN101306827B/en active Active
Cited By (5)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
CN103121779A (en) * | 2013-02-04 | 2013-05-29 | 刘进龙 | Cyclic regeneration method and application of town sewage treatment medicament |
CN107285355A (en) * | 2017-08-01 | 2017-10-24 | 广西新晶科技有限公司 | A kind of method for preparing aluminium polychloride using discarded anthraquinone regenerative agent |
CN107285355B (en) * | 2017-08-01 | 2019-01-04 | 广西新晶科技有限公司 | A method of aluminium polychloride is prepared using discarded anthraquinone regenerative agent |
CN110963662A (en) * | 2019-12-09 | 2020-04-07 | 上海净屹环保科技有限公司 | Method for recovering aluminum salt coagulant from aluminum-containing sludge |
CN114804315A (en) * | 2022-06-06 | 2022-07-29 | 中国铁工投资建设集团有限公司 | Polyaluminum ferric chloride and composite flocculant prepared from municipal sludge drying pyrolysis residues |
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CN101306827B (en) | 2010-07-28 |
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