CN103420430B - Polyaluminum ferrous chloride purifier and production method thereof - Google Patents

Polyaluminum ferrous chloride purifier and production method thereof Download PDF

Info

Publication number
CN103420430B
CN103420430B CN201310359619.7A CN201310359619A CN103420430B CN 103420430 B CN103420430 B CN 103420430B CN 201310359619 A CN201310359619 A CN 201310359619A CN 103420430 B CN103420430 B CN 103420430B
Authority
CN
China
Prior art keywords
gained solution
stirring
added
normal temperature
reaction
Prior art date
Legal status (The legal status is an assumption and is not a legal conclusion. Google has not performed a legal analysis and makes no representation as to the accuracy of the status listed.)
Active
Application number
CN201310359619.7A
Other languages
Chinese (zh)
Other versions
CN103420430A (en
Inventor
董申伟
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.)
Guangdong Zhongtai Environmental Protection Technology Co ltd
Original Assignee
Jiangmen City Zhongda Environmental Protection Technology 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 Jiangmen City Zhongda Environmental Protection Technology Co ltd filed Critical Jiangmen City Zhongda Environmental Protection Technology Co ltd
Priority to CN201310359619.7A priority Critical patent/CN103420430B/en
Publication of CN103420430A publication Critical patent/CN103420430A/en
Application granted granted Critical
Publication of CN103420430B publication Critical patent/CN103420430B/en
Active legal-status Critical Current
Anticipated expiration legal-status Critical

Links

Landscapes

  • Compounds Of Alkaline-Earth Elements, Aluminum Or Rare-Earth Metals (AREA)
  • Removal Of Specific Substances (AREA)
  • Separation Of Suspended Particles By Flocculating Agents (AREA)

Abstract

The invention provides a polyaluminum ferrous chloride purifier and a production method thereof. The production method using the following raw materials includes the steps of firstly, feeding technical hydrochloric acid and aluminum sludge into a sealed reaction vessel, and stirring at normal temperature and pressure; secondly, adding CaCl2 to the solution obtained by the first step, stirring at normal temperature and pressure until complete reaction, and filtering to remove sedimentation; thirdly, adding steel acid pickling waste liquor into the solution obtained after filtering of the second step, and well mixing by stirring; fourthly, adding oxidant to the solution obtained by the third step; fifthly, adding calcium aluminate powder to the solution obtained by the fourth step, allowing for reaction, and filtering and aging to obtain the polyaluminum ferrous chloride purifier. The production method has the advantages that CaCl2 is added to control contents of SO42- in the product so as to prevent SO42- from reacting with the subsequently added calcium aluminate powder, and product stability is increased.

Description

Poly aluminium chloride silicic acid and manufacture method thereof
Technical field
The invention belongs to water purification agent field, be specifically related to a kind of poly aluminium chloride silicic acid and manufacture method thereof.
Background technology
In the surface treatment process of Iron And Steel Industry and aluminium section bar processing industry, in order to improve the performance of steel, aluminium shape surface, usually need to utilize mineral acid to carry out corrosion treatment, to remove the oxide compound on surface.Surface acid-washing process can produce a large amount of iron ion bearing scrap acid solution and Aluminiferous waste slag, these trade wastes cannot recycle for steel and aluminium section bar enterprise itself, if can not get effectively disposing to become secondary pollution source, being discharged into physical environment can havoc ecotope.How effectively to dispose and to utilize spent pickle liquor and aluminium body refuse, be steel and aluminium section bar enterprise problem in the urgent need to address always.To employ new technology means, trade waste is carried out a kind of new direction, new trend that resource utilization is just becoming environmental improvement.
Can produce a large amount of containing FeCl at steel surface treating processes hydrochloric acid soln corrosion steel surface 2spent pickle liquor, this spent pickle liquor contains the FeCl of 8 ~ 10wt% 2and a small amount of hydrochloric acid.In aluminium shape surface process, use sulfuric acid washing, because in solution, aluminium composition is lower, adopt in alkali and after processed finally produces white aluminium body refuse, the activated alumina containing 10 ~ 20wt% in aluminium body refuse more.If iron and steel pickling waste liquid and aluminium body refuse can be applied to the manufacture of the polychloride ferro-aluminum of water treatment agent, will significantly reduce the production cost of water purification agent, solve the problem of iron and steel and aluminium section bar enterprise waste liquid and refuse environmental pollution simultaneously.
Utilize spent pickle liquor at present, patent that aluminium body refuse prepares liquid aluminium polychloride silicic acid and bibliographical information more, as patent CN103043759A utilizes spent pickle liquor and aluminum feedstock, adopt oxidation acid-soluble, add the polymerization of NaOH alkali tune again and prepare water purification agent, but NaOH alkalescence is too strong, the process of adding is easy to be formed with ferro-aluminum ion precipitate, and product basicity is low, affects flocculating effect.Patent CN102774889A adopts alkaline residue, hydrochloric acid, molysite, oxygenant, calcium aluminate powder to be that aluminium iron polychloride prepared by raw material, does not consider in alkaline residue containing a large amount of SO 4 2-with Ca in calcium aluminate powder 2+form the drawback of a large amount of precipitation, cause product instability to be easy to layering, finally affect the flocculating property of product, simultaneous reactions process produces a large amount of precipitation even may cause reaction tank material gel, cannot complete water purification agent polymerization processes for preparing.Patent CN1948156A utilizes aluminium mud, hydrochloric acid, manufacturing polyaluminium chloride with calcium aluminate powder, does not consider SO in aluminium mud equally 4 2-on the impact of production technique and product performance.
Summary of the invention
In order to overcome the deficiencies in the prior art, the invention provides a kind of poly aluminium chloride silicic acid and manufacture method thereof, by adding CaCl in the fabrication process 2control SO in product 4 2-content, avoids SO 4 2-react with the follow-up calcium aluminate powder added, improve product stability.
The technical solution adopted for the present invention to solve the technical problems is:
A kind of poly aluminium chloride silicic acid, adopts following raw material and step preparation:
(1) technical hydrochloric acid and aluminium body refuse are dropped into closed reaction vessel, normal temperature and pressure stirring reaction;
(2) CaCl is added to step (1) gained solution 2, after normal temperature and pressure stirring reaction, cross and filter precipitation;
(3) iron and steel pickling waste liquid is added, stirring and evenly mixing in gained solution after filtering to step (2);
(4) in step (3) gained solution, oxygenant is added, stirring and evenly mixing;
(5) add calcium aluminate powder to step (4) gained solution, after reaction, after filtration, ageing, obtain poly aluminium chloride silicic acid of the present invention
Preferably, this poly aluminium chloride silicic acid adopts following raw material and step preparation:
(1) by weight, 65-135 part technical hydrochloric acid and 100 parts of aluminium body refuses are dropped into closed reaction vessel, normal temperature and pressure stirring reaction 0.5-1h;
(2) 32-64 part CaCl is added to step (1) gained solution 2, after normal temperature and pressure stirring reaction, cross and filter precipitation;
(3) 10-109 part iron and steel pickling waste liquid is added, stirring and evenly mixing in gained solution after filtering to step (2);
(4) in step (3) gained solution, add oxygenant, stir;
(5) add 212-400 part calcium aluminate powder to step (4) gained solution, reaction 3-4h, obtains poly aluminium chloride silicic acid of the present invention after filtering ageing.
Described oxygenant is sodium chlorate or hydrogen peroxide.
Wherein, above-mentioned aluminium body refuse for use sulfuric acid washing in aluminium shape surface process, then adopts in alkali and the final white mass produced after processed, the activated alumina containing 10 ~ 20wt% in aluminium body refuse.
Above-mentioned iron and steel pickling waste liquid for corrode steel surface with hydrochloric acid soln in steel surface treating processes, generation containing a large amount of FeCl 2spent pickle liquor, this spent pickle liquor contains the FeCl of 8 ~ 10wt% 2and a small amount of hydrochloric acid.
In actual production process, in aluminium body refuse, aluminum oxide is first by enough dissolving with hydrochloric acid, and colloidal state aluminium hydroxide is dissolved as AlCl 3solution, aluminium enters solution with ionic state, then adopts " technical grade polymerize aluminum chloride standard GB/T/T22627-2008 " method to detect aluminium content; SO 4 2-content detection then measures, according to SO with reference to GB11899-89 weighting method 4 2-content adds enough CaCl 2, allow SO 4 2-react with calcium ion and form CaSO 4precipitation is separated from solution; In iron and steel pickling waste liquid, iron ion content then measures with reference to " GBT1621-1993 industrial chlorinations is ferrous " oxidation reduction process.
Optimum ferro-aluminum ratio can be determined, to reach best water treatment efficiency according to different sewage water quality characteristics in poly aluminium chloride silicic acid preparation process.In product of the present invention, iron aluminium quality is 1:(1-10 than span of control).
Calcium aluminate powder is alkaline matter, can H in neutralization solution with ferro-aluminum acidic mixed solution reaction +ion, and impel ferro-aluminum ion that hydrolysis occurs further to produce more Polycarboxy-heterocyclic compound, improve poly aluminium chloride silicic acid product basicity to 50-90% scope, ensure water purification agent water treatment coagulation effect.
The invention has the beneficial effects as follows:
The poly aluminium chloride silicic acid that the present invention produces, by adding CaCl in the fabrication process 2control SO in product 4 2-content, avoids SO 4 2-react with the follow-up calcium aluminate powder added, improve product stability; Industrial waste resource utilization, recycle is turned waste into wealth, and reduces water purification agent production process to the exploitation of Mineral resources, reduces water purification agent manufacturing cost; Simplify water purification agent product manufacture flow process, reduce water purification agent and manufacture energy consumption, a kind of new preparation process technology is provided; Compare improve water treatment coagulating sedimentation effect with traditional Tai-Ace S 150, polyaluminium chloride water purification agent.
Embodiment
Below in conjunction with specific embodiment, set forth the present invention further.
Embodiment 1
(1) by weight, get 65 parts of technical hydrochloric acids and drop into airtight acid tolerance response container, under whipped state, evenly add 100 parts of aluminium body refuses, normal temperature and pressure stirring reaction 0.5-1h, obtain containing Na after reactants dissolved is complete 2sO 4alCl 3acidic solution;
(2) 32 parts of CaCl are added to step (1) gained solution 2, stir under normal temperature and pressure and make to react completely, cross and filter CaSO 4precipitation, obtains AlCl 3acidic solution;
(3) in step (2) gained solution, add 10 parts of iron and steel pickling waste liquids, stir, mix rear formation AlCl 3and FeCl 2mixed acid solution;
(4) in step (3) gained solution, add oxygenant sodium chlorate, its add-on is with by Fe all in solution 2+be oxidized to Fe 3+be as the criterion, obtain AlCl 3and FeCl 3mixed acid solution;
(5) add 212 parts of calcium aluminate powder for water treatment agents to step (4) gained solution, acid-soluble polyreaction 3-4h, after filtering ageing, obtain poly aluminium chloride silicic acid of the present invention.
Embodiment 2
(1) by weight, get 100 parts of technical hydrochloric acids and drop into airtight acid tolerance response container, under whipped state, evenly add 100 parts of aluminium body refuses, normal temperature and pressure stirring reaction 0.5-1h, obtain containing Na after reactants dissolved is complete 2sO 4alCl 3acidic solution;
(2) 48 parts of CaCl are added to step (1) gained solution 2, stir under normal temperature and pressure and make to react completely, cross and filter CaSO 4precipitation, obtains AlCl 3acidic solution;
(3) in step (2) gained solution, add 60 parts of iron and steel pickling waste liquids, stir, mix rear formation AlCl 3and FeCl 2mixed acid solution;
(4) in step (3) gained solution, add oxidants hydrogen peroxide, its add-on is with by Fe all in solution 2+be oxidized to Fe 3+be as the criterion, obtain AlCl 3and FeCl 3mixed acid solution;
(5) add 305 parts of calcium aluminate powder for water treatment agents to step (4) gained solution, acid-soluble polyreaction 3-4h, after filtering ageing, obtain poly aluminium chloride silicic acid of the present invention.
Embodiment 3
(1) by weight, get 135 parts of technical hydrochloric acids and drop into airtight acid tolerance response container, under whipped state, evenly add 100 parts of aluminium body refuses, normal temperature and pressure stirring reaction 0.5-1h, obtain containing Na after reactants dissolved is complete 2sO 4alCl 3acidic solution;
(2) 64 parts of CaCl are added to step (1) gained solution 2, stir under normal temperature and pressure and make to react completely, cross and filter CaSO 4precipitation, obtains AlCl 3acidic solution;
(3) in step (2) gained solution, add 109 parts of iron and steel pickling waste liquids, stir, mix rear formation AlCl 3and FeCl 2mixed acid solution;
(4) in step (3) gained solution, add oxidants hydrogen peroxide, its add-on is with by Fe all in solution 2+be oxidized to Fe 3+be as the criterion, obtain AlCl 3and FeCl 3mixed acid solution;
(5) add 400 parts of calcium aluminate powder for water treatment agents to step (4) gained solution, acid-soluble polyreaction 3-4h, after filtering ageing, obtain poly aluminium chloride silicic acid of the present invention.
Should be understood that these embodiments are only not used in for illustration of the present invention to limit the scope of the invention.After the content of having read the present invention's instruction, those skilled in the art can do various conversion or amendment with any same or similar means to the present invention, and these equivalent form of values fall within protection scope of the present invention equally.

Claims (5)

1. prepare a method for poly aluminium chloride silicic acid, it is characterized in that being made up of following steps:
(1) technical hydrochloric acid and aluminium body refuse are dropped into closed reaction vessel, normal temperature and pressure stirring reaction;
(2) CaCl is added to step (1) gained solution 2, after normal temperature and pressure stirring reaction, cross and filter precipitation;
(3) iron and steel pickling waste liquid is added, stirring and evenly mixing in gained solution after filtering to step (2);
(4) in step (3) gained solution, oxygenant is added, stirring and evenly mixing;
(5) add calcium aluminate powder to step (4) gained solution, after reaction, after filtration, ageing, obtain poly aluminium chloride silicic acid.
2. method according to claim 1, is characterized in that being made up of following steps:
(1) by weight, 65-135 part technical hydrochloric acid and 100 parts of aluminium body refuses are dropped into closed reaction vessel, normal temperature and pressure stirring reaction 0.5-1h;
(2) 32-64 part CaCl is added to step (1) gained solution 2, after normal temperature and pressure stirring reaction, cross and filter precipitation;
(3) 10-109 part iron and steel pickling waste liquid is added, stirring and evenly mixing in gained solution after filtering to step (2);
(4) in step (3) gained solution, oxygenant is added, stirring and evenly mixing;
(5) add 212-400 part calcium aluminate powder to step (4) gained solution, reaction 3-4h, obtains poly aluminium chloride silicic acid after filtering ageing.
3. method according to claim 1 and 2, is characterized in that: the oxygenant in described step (4) is sodium chlorate or hydrogen peroxide.
4. method according to claim 1 and 2, is characterized in that: described aluminium body refuse is containing the aluminum oxide of 10-20wt%.
5. method according to claim 1 and 2, is characterized in that: described iron and steel pickling waste liquid contains the FeCl of 8-10wt% 2.
CN201310359619.7A 2013-08-16 2013-08-16 Polyaluminum ferrous chloride purifier and production method thereof Active CN103420430B (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
CN201310359619.7A CN103420430B (en) 2013-08-16 2013-08-16 Polyaluminum ferrous chloride purifier and production method thereof

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
CN201310359619.7A CN103420430B (en) 2013-08-16 2013-08-16 Polyaluminum ferrous chloride purifier and production method thereof

Publications (2)

Publication Number Publication Date
CN103420430A CN103420430A (en) 2013-12-04
CN103420430B true CN103420430B (en) 2015-03-25

Family

ID=49645874

Family Applications (1)

Application Number Title Priority Date Filing Date
CN201310359619.7A Active CN103420430B (en) 2013-08-16 2013-08-16 Polyaluminum ferrous chloride purifier and production method thereof

Country Status (1)

Country Link
CN (1) CN103420430B (en)

Families Citing this family (12)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN104150576B (en) * 2014-07-20 2016-08-31 榆林学院 A kind of coal ash for manufacturing is for the method for PAFC
CN104495994A (en) * 2014-12-04 2015-04-08 常州大学 Method for improving filter-pressing performance of particles in poly-aluminum ferric chloride
CN105217752A (en) * 2015-09-10 2016-01-06 吴建华 The preparation method of aluminium iron sulfate solution
CN105152295A (en) * 2015-09-10 2015-12-16 吴建华 Preparation method of aluminum ferric chloride solution
CN105236531A (en) * 2015-09-10 2016-01-13 吴建华 Poly aluminum chloride preparation method
CN105217754A (en) * 2015-09-28 2016-01-06 江苏永葆环保科技股份有限公司 A kind of method fully utilizing ferro-aluminum surface acid-washing spent acid waste residue and prepare compound coagulant
CN105776465B (en) * 2016-03-04 2018-04-10 江苏永葆环保科技股份有限公司 A kind of compound coagulant for treatment of dyeing wastewater and preparation method thereof
CN106430321B (en) * 2016-08-31 2018-03-23 海南宜净环保股份有限公司 Method for synthesizing polyaluminum ferric chloride
CN106395917B (en) * 2016-12-06 2017-11-10 长江大学 A kind of PAFC fluid product and preparation method thereof
CN108557831B (en) * 2018-05-29 2021-06-08 西南科技大学 Method for preparing silicon micropowder and coproducing polyaluminium chloride by leaching quartz processing sludge with hydrochloric acid
CN109292849A (en) * 2018-11-07 2019-02-01 张家界贵友环保材料科技有限公司 A kind of polyaluminium chloride water purification agent and preparation method thereof containing rare earth element
CN111872027B (en) * 2020-07-16 2021-09-07 常熟理工学院 Method for co-processing waste incineration fly ash and printing and dyeing waste liquid

Citations (3)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN102372308A (en) * 2010-08-12 2012-03-14 北京万水净水剂有限公司 Process for producing polymeric aluminum ferric chloride coagulating agent by using pickling waste water containing iron
CN102910716A (en) * 2012-08-27 2013-02-06 浙江大学 Method for preparing polymeric ferric aluminum by utilizing metal chlorohydric acid pickling waste liquor
CN103043759A (en) * 2012-12-14 2013-04-17 广东工业大学 Method for preparing polyaluminium ferric chloride flocculating agent by pickling waste liquid and waste aluminium material

Patent Citations (3)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN102372308A (en) * 2010-08-12 2012-03-14 北京万水净水剂有限公司 Process for producing polymeric aluminum ferric chloride coagulating agent by using pickling waste water containing iron
CN102910716A (en) * 2012-08-27 2013-02-06 浙江大学 Method for preparing polymeric ferric aluminum by utilizing metal chlorohydric acid pickling waste liquor
CN103043759A (en) * 2012-12-14 2013-04-17 广东工业大学 Method for preparing polyaluminium ferric chloride flocculating agent by pickling waste liquid and waste aluminium material

Non-Patent Citations (2)

* Cited by examiner, † Cited by third party
Title
"利用盐酸酸洗废液制备聚合氯化铁铝混凝剂的研究";邱慧琴等;《中国给水排水》;20090131;第25卷(第1期);第64-67页 *
"工业废酸与高铁赤泥制取聚合氯化铝铁的实验研究";王海峰等;《贵州大学学报(自然科学版)》;20060831;第23卷(第3期);第323-325页 *

Also Published As

Publication number Publication date
CN103420430A (en) 2013-12-04

Similar Documents

Publication Publication Date Title
CN103420430B (en) Polyaluminum ferrous chloride purifier and production method thereof
CN101816829B (en) Chromium residue detoxifying process
CN103043759B (en) Method for preparing polyaluminium ferric chloride flocculating agent by pickling waste liquid and waste aluminium material
CN107473353B (en) Preparation method of flocculant polyaluminum ferric chloride
CN101003390A (en) Method for preparing flocculant of ferric chloride of polysilicon acid
CN101973586A (en) Method for preparing polymeric aluminum ferric sulfate by using aluminium ore washing gangue
CN109502655B (en) Production process of polymeric ferric sulfate
CN102689906B (en) Method for preparing polysilicate aluminum ferric chloride by using aluminum foil acid and ferrous acid
CN101928031A (en) Production method of polyaluminium chloride
CN102040238A (en) Recycling method for treating sludge containing heavy metals
CN109336236B (en) Method for preparing aluminum-iron flocculating agent from red mud
CN105502609A (en) Method for treating wastewater containing hypochlorite
CN104003492A (en) Preparation method of polyaluminum ferric sulfate silicate coagulant
CN104512951A (en) Method for co-production of ploysilicate aluminium ferric sulphate and waste water treatment powder by PAC (poly aluminum chloride) residues
CN104108814A (en) Method for treating rutile titanium dioxide waste water
CN102910716A (en) Method for preparing polymeric ferric aluminum by utilizing metal chlorohydric acid pickling waste liquor
CN106745582B (en) A kind of method that sial slag prepares polyaluminum silicate chloride coagulant
CN104773748B (en) A kind of method for preparing low iron polyaluminium sulfate using the acid mother liquor of sulfur waste containing aluminium
CN104649385A (en) Method for preparing poly-aluminum ferric chloride composite water purifying agent with waste hydrochloric acid
CN109988902B (en) Method for dealkalizing iron-reinforced red mud and separating and recovering iron
CN102701549A (en) Novel reclamation method of electroplating sludge
CN101070202A (en) Method for producing ferro-aluminium composite water purifying agent using aluminium hydroxide mud
CN112062343A (en) MAP method-based harmless recycling treatment method for phosphogypsum yard leachate
CN208632118U (en) A kind of aluminium wastewater recycles the device of aluminium hydroxide using ammonia as precipitating reagent
CN101417870B (en) Method for producing architectural materials by using white slime

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
TR01 Transfer of patent right
TR01 Transfer of patent right

Effective date of registration: 20180604

Address after: 529000 room 106, Dan well Li 27, Pengjiang District, Jiangmen, Guangdong.

Patentee after: Jiangmen green water environmental water treatment Co.,Ltd.

Address before: 529000 Guangdong province Jiangmen city Du Ruan Zhen Zi Cotton Industrial Zone

Patentee before: JIANGMEN CITY ZHONGDA ENVIRONMENTAL PROTECTION TECHNOLOGY Co.,Ltd.

TR01 Transfer of patent right
TR01 Transfer of patent right

Effective date of registration: 20231218

Address after: 529000, 2nd Floor, Runan Road, Duanfen Town, Taishan City, Jiangmen City, Guangdong Province

Patentee after: Guangdong Zhongtai Environmental Protection Technology Co.,Ltd.

Address before: 529000 room 106, Dan well Li 27, Pengjiang District, Jiangmen, Guangdong.

Patentee before: Jiangmen green water environmental water treatment Co.,Ltd.