CN104250018A - High iron slag treatment process - Google Patents

High iron slag treatment process Download PDF

Info

Publication number
CN104250018A
CN104250018A CN201310260486.8A CN201310260486A CN104250018A CN 104250018 A CN104250018 A CN 104250018A CN 201310260486 A CN201310260486 A CN 201310260486A CN 104250018 A CN104250018 A CN 104250018A
Authority
CN
China
Prior art keywords
deironing
solution
value
processing technique
high ferro
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
CN201310260486.8A
Other languages
Chinese (zh)
Other versions
CN104250018B (en
Inventor
王鹏
李来时
刘涛涛
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.)
Shenyang Aluminum and Magnesium Engineering and Research Institute Co Ltd
Original Assignee
Shenyang Aluminum and Magnesium Engineering and Research Institute 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 Shenyang Aluminum and Magnesium Engineering and Research Institute Co Ltd filed Critical Shenyang Aluminum and Magnesium Engineering and Research Institute Co Ltd
Priority to CN201310260486.8A priority Critical patent/CN104250018B/en
Publication of CN104250018A publication Critical patent/CN104250018A/en
Application granted granted Critical
Publication of CN104250018B publication Critical patent/CN104250018B/en
Active legal-status Critical Current
Anticipated expiration legal-status Critical

Links

Landscapes

  • Processing Of Solid Wastes (AREA)

Abstract

The invention discloses a high iron slag treatment process which comprises step-by-step iron removal, mixed sediment treatment and solution treatment and other steps. According to the process, the aluminum ions loss in the process of iron removal by application of ammonium sulfate sintering process for fly ash treatment can be reduced, and no other impurity is introduced. The iron ion content in an aluminum sulfate solution with iron removed is less than 20mg / L, meets the requirements of alumina production; and in the process, the produced precipitate is easy to filter.

Description

A kind of high ferro residues processing technique
Technical field
The present invention relates to a kind of high ferro residues processing technique, particularly relate to flyash and produce the iron dross removing treatment process produced in alumina process.
Background technology
At present, the utilization of China's flyash mainly concentrate on building, building materials, agricultural [etc. aspect, belonging to low value added utilizes, especially for aluminous fly-ash (alumina content is greater than 30%) kind of waste beyond doubt.The main method of process aluminous fly-ash has: limestone sintering process, pre-desiliconizing-soda-lime sintering process, sulfuric acid process, hydrochloric acid method and ammonium sulfate sintering process etc.But the equal Shortcomings of various method.Only have ammonium sulfate sintering process preparation process to be decrement process, the quantity of slag is little; Reaction system is weak acid system, and equipment is easier to solve, and is beneficial to industrialization.
Ammonium sulfate obtains Tai-Ace S 150, ferric sulfate and ferrous sulfate mixing grog with flyash is baking mixed, Tai-Ace S 150, ferric sulfate and ferrous sulfate mixing solutions is obtained after Clinker digestion, in order to obtain the lower ferrum sulfuricum oxydatum solutum of iron-holder, therefore deironing process must be carried out to dissolution fluid.Due to Fe 3+the pH value of hydrolysis and Al 3+the pH value of hydrolysis is comparatively close, therefore must have the loss of some aluminum ions in iron removal, in order to reduce aluminum ions loss, necessarily process this part iron dross removing.
Summary of the invention
In order to solve the problem, the invention provides a kind of high ferro residues processing technique, object makes to reduce aluminum ions loss in using sulfated ammonium sintering process treated coal ash iron removal.
For achieving the above object, the invention provides a kind of high ferro residues processing technique, after stepwise deironing, mixed sediment process and solution-treated, obtain alum liquor.
Stepwise deironing is the pH value by adding ammoniacal liquor adjusted stepwise leach liquor, makes iron ion content in final solution be less than 20mg/L; A deironing is ferriammonium sulfate for obtaining product, and the product that secondary deironing obtains is aluminium ammonium alum and ferriammonium sulfate mixture; One time deironing regulator solution pH value is 1.4-1.7; Secondary deironing regulator solution pH value is 2.5-3.0.
Mixed sediment process is that the monoammonium sulfate being 20%-50% by aluminium ammonium alum and ferriammonium sulfate mixture and concentration reacts, and temperature of reaction is 60-90 DEG C, and the reaction times is 0.5-1 hour.
Solution-treated is that reaction product is turned back to leaching operation.
The alum liquor iron level obtained is less than 20mg/L.
Advantageous effect of the present invention: make to reduce aluminum ions loss in using sulfated ammonium sintering process treated coal ash iron removal, and do not introduce other impurity.Iron from aluminium sulfate solution ion content after deironing is less than 20mg/L, meets the requirement of alumina producing; The throw out generated in the process is easy to filter.
Accompanying drawing explanation
Fig. 1 is process flow sheet of the present invention.
1, leach; 2, a deironing; 3, ferriammonium sulfate; 4, secondary deironing; 5, aluminium ammonium alum and ferriammonium sulfate; 6, ammonium bisulfate solution; 7, alum liquor.
Embodiment
below in conjunction with accompanying drawing, the invention will be further described.
Embodiment 1
The pH value of leach liquor is regulated by adding ammoniacal liquor, the pH value of a deironing is 1.4, the pH value of secondary deironing is 2.5, secondary iron dross removing and concentration are that 20% ammonium bisulfate solution reacts, temperature of reaction is 60 DEG C, reaction times is 0.5 hour, and after dissolving, solution turns back to leaching operation, and its result is as shown in table 1:
Table 1
Embodiment 2
The pH value of leach liquor is regulated by adding ammoniacal liquor, the pH value of a deironing is 1.5, the pH value of secondary deironing is 2.6, secondary iron dross removing and concentration are that 30% ammonium bisulfate solution reacts, temperature of reaction is 80 DEG C, reaction times is 1 hour, and after dissolving, solution turns back to leaching operation, and its result is as shown in table 2:
Table 2
Embodiment 3
The pH value of leach liquor is regulated by adding ammoniacal liquor, the pH value of a deironing is 1.6, the pH value of secondary deironing is 2.7, secondary iron dross removing and concentration are that 30% ammonium bisulfate solution reacts, temperature of reaction is 70 DEG C, reaction times is 1 hour, and after dissolving, solution turns back to leaching operation, and its result is as shown in table 3:
Table 3
Embodiment 4
The pH value of leach liquor is regulated by adding ammoniacal liquor, the pH value of a deironing is 1.7, the pH value of secondary deironing is 3.0, secondary iron dross removing and concentration are that 50% ammonium bisulfate solution reacts, temperature of reaction is 90 DEG C, reaction times is 1 hour, and after dissolving, solution turns back to leaching operation, and its result is as shown in table 4:
Table 4

Claims (5)

1. a high ferro residues processing technique, is characterized in that obtaining alum liquor after stepwise deironing, mixed sediment process and solution-treated.
2. a kind of high ferro residues processing technique according to claim 1, its feature is the pH value by adding ammoniacal liquor adjusted stepwise leach liquor at stepwise deironing, makes iron ion content in final solution be less than 20mg/L; A deironing is ferriammonium sulfate for obtaining product, and the product that secondary deironing obtains is aluminium ammonium alum and ferriammonium sulfate mixture; One time deironing regulator solution pH value is 1.4-1.7; Secondary deironing regulator solution pH value is 2.5-3.0.
3. a kind of high ferro residues processing technique according to claim 1, it is characterized in that mixed sediment process is that the monoammonium sulfate being 20%-50% by aluminium ammonium alum and ferriammonium sulfate mixture and concentration reacts, temperature of reaction is 60-90 DEG C, and the reaction times is 0.5-1 hour.
4. a kind of high ferro residues processing technique according to claim 1, is characterized in that solution-treated is that reaction product is turned back to leaching operation.
5. a kind of high ferro residues processing technique according to claim 1, is characterized in that obtained alum liquor iron level is less than 20mg/L.
CN201310260486.8A 2013-06-27 2013-06-27 A kind of high ferro residues processing technique Active CN104250018B (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
CN201310260486.8A CN104250018B (en) 2013-06-27 2013-06-27 A kind of high ferro residues processing technique

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
CN201310260486.8A CN104250018B (en) 2013-06-27 2013-06-27 A kind of high ferro residues processing technique

Publications (2)

Publication Number Publication Date
CN104250018A true CN104250018A (en) 2014-12-31
CN104250018B CN104250018B (en) 2016-02-10

Family

ID=52185308

Family Applications (1)

Application Number Title Priority Date Filing Date
CN201310260486.8A Active CN104250018B (en) 2013-06-27 2013-06-27 A kind of high ferro residues processing technique

Country Status (1)

Country Link
CN (1) CN104250018B (en)

Cited By (1)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN112939572A (en) * 2019-12-11 2021-06-11 桂阳县皓钰新材料有限公司 Process for treating iron slag of steel plant by tunnel kiln

Citations (3)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN101497455A (en) * 2009-03-13 2009-08-05 李睿德 Method for producing limestone powder and aluminium ammonium sulfate using heat-engine plant desulfurized gypsum and fly ash
CN102424391A (en) * 2011-09-01 2012-04-25 东北大学 Method for comprehensive utilization of aluminum-containing material
CN103086408A (en) * 2013-01-24 2013-05-08 沈阳铝镁设计研究院有限公司 Method for producing alumina by mixing and roasting flyash and ammonium sulfate

Patent Citations (3)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN101497455A (en) * 2009-03-13 2009-08-05 李睿德 Method for producing limestone powder and aluminium ammonium sulfate using heat-engine plant desulfurized gypsum and fly ash
CN102424391A (en) * 2011-09-01 2012-04-25 东北大学 Method for comprehensive utilization of aluminum-containing material
CN103086408A (en) * 2013-01-24 2013-05-08 沈阳铝镁设计研究院有限公司 Method for producing alumina by mixing and roasting flyash and ammonium sulfate

Cited By (1)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN112939572A (en) * 2019-12-11 2021-06-11 桂阳县皓钰新材料有限公司 Process for treating iron slag of steel plant by tunnel kiln

Also Published As

Publication number Publication date
CN104250018B (en) 2016-02-10

Similar Documents

Publication Publication Date Title
CN104498714B (en) Ferrum, aluminum, calcium, the method for titana matter is removed from containing scandium solution separates
CN103602819B (en) Comprehensive recovery method of vanadate-chromate-containing solution
CN108658131B (en) Iron oxide red and gypsum cementing material based on titanium gypsum and preparation method thereof
CN103146930A (en) Method for preparing vanadium oxide
CN103266231B (en) A kind of Tungsten smelting method of high-efficiency cleaning
CN106830244B (en) Method for separating and recovering fluorine and acid from fluorine-containing acidic wastewater
CN104261433A (en) Method for producing potassium sulfate from potassium/chlorine-ion-containing solid waste
CN104743585A (en) Method for preparing flame retardant grade magnesium hydroxide
CN111549239B (en) Resourceful treatment method of magnesium-containing raw material
CN105668888A (en) Low-grade mixed rare earth ore concentrate chemical dressing and chemical dressing waste water resource comprehensively recycling method
CN105036413A (en) Treatment process for wastewater containing thallium
CN104250018B (en) A kind of high ferro residues processing technique
CN104086032A (en) Method for recycling vanadium precipitating wastewater
CN104016357B (en) A kind of manganese slag for comprehensive utilizes the method for producing industrial chemicals
CN103833061B (en) A kind of flyash dissolution fluid combination method deferrization process
CN108374085A (en) A kind of method for removing iron of shale vanadium extraction pickle liquor
CN105217825A (en) A kind of staging treating method of fluorine-containing heavy metal wastewater thereby
CN105884065A (en) Treatment method for transformation MgSO4 wastewater produced during baotite smelting
CN104630465A (en) Method for extracting nickel and cobalt from leaching solution obtained by normal-pressure acid leaching of laterite-nickel ore
CN104250015A (en) Fly ash wet method iron removal process
CN103496723B (en) Method for improving leaching rate of magnesium oxide in serpentine ammonium salt roasting product
CN105692833A (en) Process for treating wastewater in copper industry by using polymeric ferric sulfate
CN104250019A (en) Process for production of aluminum sulfate from fly ash
CN109592818A (en) A kind of stainless steel acid-washing waste liquid commercialization method and system
CN104045189A (en) Comprehensive treatment method of phosphorous production wastewater

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