CN101514033A - Environment friendly processing method of waste acid containing ferrous sulphate - Google Patents

Environment friendly processing method of waste acid containing ferrous sulphate Download PDF

Info

Publication number
CN101514033A
CN101514033A CNA2009100198810A CN200910019881A CN101514033A CN 101514033 A CN101514033 A CN 101514033A CN A2009100198810 A CNA2009100198810 A CN A2009100198810A CN 200910019881 A CN200910019881 A CN 200910019881A CN 101514033 A CN101514033 A CN 101514033A
Authority
CN
China
Prior art keywords
spent acid
water
filter
reaction
waste acid
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
CNA2009100198810A
Other languages
Chinese (zh)
Inventor
庞仁杰
李军英
寇洪庆
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.)
Shandong Junhui Construction & Installation Engineering Co Ltd
Original Assignee
Shandong Junhui Construction & Installation Engineering 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 Shandong Junhui Construction & Installation Engineering Co Ltd filed Critical Shandong Junhui Construction & Installation Engineering Co Ltd
Priority to CNA2009100198810A priority Critical patent/CN101514033A/en
Publication of CN101514033A publication Critical patent/CN101514033A/en
Pending legal-status Critical Current

Links

Images

Landscapes

  • Separation Using Semi-Permeable Membranes (AREA)

Abstract

The invention discloses an environment friendly processing method of waste acid containing ferrous sulphate, mainly comprising the following steps: the waste acid containing ferrous sulphate is oxidized by hydrogen peroxide and neutralized and displaced by magnesium oxide to generate ferric hydroxide deposit and magnesium sulphate by reaction, and fine powder of ferric oxide is obtained after the generated ferric hydroxide deposit is filtered, washed by water and dried while hot. In the whole processing course, no three wastes are discharged; the fine powder products of ferric oxide and magnesium sulphate products obtained through processing can be sold and the obtained magnesium sulphate products can also be reused; the treated water discharged during production can be recycled as primary water, thus radically solving nuisanceless disposal of the waste acid containing ferrous sulphate, greatly saving the processing cost of waste acid and obtaining by-products to be sold, therefore, the comprehensive benefits are high.

Description

The environment-friendly treatment method that contains the ferrous sulfate spent acid
Technical field
The present invention relates to the spent acid treatment process.
Background technology
At present, in the production process of special steel and titanium white, need to consume a large amount of sulfuric acid, produce one ton of titanium dioxide and need discharge about 8 tons and contain H 2SO 420% dilute sulphuric acid contains a large amount of ferrous sulfate in the acid.This useless vitriolic treatment process is at present: adopt unslaked lime to neutralize, the neutralization back generates contains lot of F e 2O 3Gypsum owing to contain Fe 2O 3The gypsum usability of discharge is limited to, generally it is stored up as industrial residue, so fundamentally do not solve problem of environmental pollution, just be exchanged into another kind of pollution mode.Become current special steel, titanium powder industry problem demanding prompt solution so invent a kind of environment-friendly treatment method of spent acid.
Summary of the invention
The purpose of this invention is to provide a kind of environment-friendly treatment method that contains the ferrous sulfate spent acid, this treatment process has not only solved existing treatment process and has caused secondary pollution problem easily, and the chemical substance recycle again that obtains after handling.
For achieving the above object, spent acid treatment process of the present invention is as follows:
The first step: the spent acid that will contain ferrous sulfate is delivered in the oxidation tank, constantly adds hydrogen peroxide oxidant when stirring, and makes the ferrous sulfate complete oxidation in the spent acid generate ferric sulfate, and chemical equation is
Figure A20091001988100031
Figure A20091001988100032
Second step: the spent acid behind the complete oxidation is sent in the neutralization tank, adding magnesium oxide in neutralization tank stirs, during spent acid carried out and replacement(metathesis)reaction, magnesium oxide elder generation and sulfuric acid reaction, then with spent acid in the ferric sulfate reaction generate sorrel ferric hydroxide precipitate and sal epsom; Question response stops to add magnesium oxide during to PH=4-5, and neutralization finishes, and the ferro element in this moment spent acid all generates the ferric hydroxide precipitate of indissoluble, and this moment, the spent acid temperature of reaction reached more than 80 ℃.Chemical equation is:
H 2SO 4+MgO=MgSO 4+H 2O
MgO+H 2O=Mg(OH) 2
3Mg(OH) 2+Fe 2(SO 4) 3=3MgSO 4+2Fe(OH) 3
The 3rd step: the solution that contains a large amount of ferric hydroxide precipitate of above-mentioned second step neutralization reaction generation is sent into filter while hot filter, obtain Fe (OH) 3Filter cake is used the clear water washing leaching cake again, with the sal epsom washes clean in the filter cake, and send in the dryer and does, and obtains the iron oxide fine powder after the oven dry.
The 4th step: filtrate and washing water that the 3rd step filter was discharged filter through activated charcoal filter, remove the organic impurity in the solution, and the solution after will filtering then enters membrane separation unit and carries densely, and the fresh water of membrane sepn is discharged the back and continued use as a water; The dope of membrane sepn is the saturated solution of magnesium sulfate of concentration more than 40%.
The 5th step: saturated solution of magnesium sulfate is pumped in the vaporizer, and heating concentrates, the dope crystallization, and the solution of advantages of good crystallization enters whizzer and separates the sal epsom (MgSO that obtains containing n hydrate 4.nH 2O), regulate the sal epsom that Tc obtains containing different hydrates, the centrifugate that whizzer is discharged enters vaporizer again and carries out the circulating and evaporating crystallization; The water of condensation that vaporizer produces turns back in the system and continues to use as a water.
It is low to utilize the present invention to handle the sal epsom impurity that spent acid obtains, and can be used as feed grade sal epsom and sells.Or send and calcine production sulfuric acid in the calcining furnace.The magnesium oxide reuse again that calcining obtains.The flue gas that calcining furnace produces is removed dust in flue gas through purification system, but the magnesia powder reuse again that cyclonic separation is discharged.
Positively effect of the present invention is, in the entire treatment process, no waste discharge, treatedly obtain iron oxide fine powder product and the sal epsom product can be sold, the sal epsom product that obtains can carry out reuse again, and the treating water of discharging in the production process can be used as a water cycle and uses, so fundamentally solved the nuisanceless handling problem of the ferrous spent acid of sulfur acid, and saved the spent acid processing cost greatly, and can obtain by-product sale again, comprehensive benefit is higher.
Description of drawings
The present invention is further described below in conjunction with drawings and Examples.
Fig. 1 is a process flow diagram of the present invention.
Embodiment
From Fig. 1 process flow diagram as can be seen, technological process of the present invention is as follows:
The chemical industry sulfur waste acid of discharging from the production process of special steel and titanium white is delivered in the oxidation tank, adds continuous stirring of hydrogen peroxide oxidant simultaneously and carries out oxidizing reaction, and the complete reaction under the oxygenant effect of hydrogen peroxide of the ferrous sulfate in the sulfur waste acid generates ferric sulfate; Spent acid behind the complete oxidation is sent in the neutralization tank, add simultaneously magnesium oxide sulfur waste acid is carried out in and replacement(metathesis)reaction, in reaction process, magnesium oxide elder generation and sulfuric acid generation neutralization reaction, then with spent acid in ferric sulfate reaction generate sorrel ferric hydroxide precipitate and sal epsom, question response stops to add magnesium oxide during to PH=4-5, and neutralization finishes; The solution that will contain ferric hydroxide precipitate is sent into filter while hot and is filtered, and obtains Fe (OH) 3Filter cake and filtrate are sent after with the sal epsom washes clean in the filter cake in the dryer with clear water and to be done, and obtain the iron oxide fine powder; Filtrate and washing water enter membrane separation unit and carry densely after activated charcoal filter filters, the fresh water of membrane sepn is discharged the back and continued to use as a water; The dope of membrane sepn is that the saturated solution of magnesium sulfate of concentration more than 40% is pumped in the vaporizer, and heating concentrates, crystallization, and the solution of advantages of good crystallization enters whizzer and separates the sal epsom (MgSO that obtains containing n hydrate 4.nH 2O), regulate the sal epsom that Tc obtains containing different hydrates, the centrifugate that whizzer is discharged enters vaporizer again and carries out the circulating and evaporating crystallization; The water of condensation that vaporizer produces turns back in the system and continues to use as a water.

Claims (1)

1, a kind of environment-friendly treatment method that contains the ferrous sulfate spent acid is characterized in that it may further comprise the steps:
The first step: the spent acid that will contain ferrous sulfate is delivered in the oxidation tank, constantly adds hydrogen peroxide oxidant when stirring, and makes the ferrous sulfate complete oxidation in the spent acid generate ferric sulfate;
Second step: the spent acid behind the complete oxidation is sent in the neutralization tank, adding magnesium oxide in neutralization tank stirs, during spent acid carried out and replacement(metathesis)reaction, magnesium oxide elder generation and sulfuric acid reaction, then with spent acid in the ferric sulfate reaction generate sorrel ferric hydroxide precipitate and sal epsom; Question response stops to add magnesium oxide during to PH=4-5, and neutralization finishes, and the ferro element in this moment spent acid all generates the ferric hydroxide precipitate of indissoluble, and this moment, the spent acid temperature of reaction reached more than 80 ℃;
The 3rd step: the solution that contains a large amount of ferric hydroxide precipitate of above-mentioned second step neutralization reaction generation is sent into filter while hot filter, obtain Fe (OH) 3Filter cake is used the clear water washing leaching cake again, will obtain the iron oxide fine powder after the sal epsom washes clean in the filter cake, the oven dry;
The 4th step: filtrate and washing water that the 3rd step filter was discharged filter through activated charcoal filter, remove the organic impurity in the solution, and the solution after will filtering then enters membrane separation unit and carries densely, and the fresh water of membrane sepn is discharged the back and continued use as a water; The dope of membrane sepn is the saturated solution of magnesium sulfate of concentration more than 40%;
The 5th step: saturated solution of magnesium sulfate is pumped in the vaporizer, and heating concentrates, crystallization, and the solution of advantages of good crystallization enters whizzer and separates the sal epsom MgSO that obtains containing n hydrate 4.nH 2O regulates the sal epsom that Tc obtains containing different hydrates, and the centrifugate that whizzer is discharged enters vaporizer again and carries out the circulating and evaporating crystallization; The water of condensation that vaporizer produces turns back in the system and continues to use as a water.
CNA2009100198810A 2009-03-21 2009-03-21 Environment friendly processing method of waste acid containing ferrous sulphate Pending CN101514033A (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
CNA2009100198810A CN101514033A (en) 2009-03-21 2009-03-21 Environment friendly processing method of waste acid containing ferrous sulphate

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
CNA2009100198810A CN101514033A (en) 2009-03-21 2009-03-21 Environment friendly processing method of waste acid containing ferrous sulphate

Publications (1)

Publication Number Publication Date
CN101514033A true CN101514033A (en) 2009-08-26

Family

ID=41038668

Family Applications (1)

Application Number Title Priority Date Filing Date
CNA2009100198810A Pending CN101514033A (en) 2009-03-21 2009-03-21 Environment friendly processing method of waste acid containing ferrous sulphate

Country Status (1)

Country Link
CN (1) CN101514033A (en)

Cited By (2)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN102107911A (en) * 2011-03-04 2011-06-29 大连海事大学 Method for preparing ferrous sulfate by reducing iron mud under induction action of solution discharge plasma
CN109836002A (en) * 2017-11-24 2019-06-04 常州第六元素材料科技股份有限公司 The hierarchical processing method of the spent acid containing manganese

Cited By (4)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN102107911A (en) * 2011-03-04 2011-06-29 大连海事大学 Method for preparing ferrous sulfate by reducing iron mud under induction action of solution discharge plasma
CN102107911B (en) * 2011-03-04 2012-07-04 大连海事大学 Method for preparing ferrous sulfate by reducing iron mud under induction action of solution discharge plasma
CN109836002A (en) * 2017-11-24 2019-06-04 常州第六元素材料科技股份有限公司 The hierarchical processing method of the spent acid containing manganese
CN109836002B (en) * 2017-11-24 2021-12-03 常州第六元素材料科技股份有限公司 Grading treatment method for manganese-containing waste acid

Similar Documents

Publication Publication Date Title
CN101538652B (en) Method for separating and recovering vanadium and chrome from vanadium and chrome-containing waste
CN104030328B (en) The method of active porous shape earth silicon material is prepared with serpentine extraction magnesium oxide
CN102634673B (en) Method for deeply removing iron ions from chromium-containing waste residue pickle liquor
CN101491771A (en) Fenton and Fenton-like reaction catalyst regeneration and reclamation method
CN101168450B (en) Method for separating and reclaiming arsenic and iron from acidic waste liquid containing arsenic acid and ferric sulfate
CN101709390B (en) On-line circulation method for process for extracting vanadium from stone coal
CN104086027B (en) Method for treating titanium dioxide wastewater through sulfuric acid process
CN101760641B (en) Technology for recovering magnesium from magnesium sulfate solution
CN101824554A (en) Liquid alkali roasting decomposition extraction process of mixed rare earth concentrates
CN107162276B (en) Chromium removal method for ferric trichloride etching waste liquid
CN113401938B (en) Titanium dioxide manufacturing method and system based on sulfur-iron-titanium co-production method
CN102351231A (en) Resource utilization method for titanium white by-product ferrous sulphate
US8603420B2 (en) Galvanic waste sludge treatment and manufacturing of nano-sized iron oxides
CN101509073A (en) Solvent extraction of ferronickel powder and waste liquor processing method
CN102745791A (en) Method for treating industrial wastewater
CN101760646A (en) Leaching method of magnesium-containing ore
CN102923674B (en) The recoverying and utilizing method of the by product of sulfur acid ferrous iron in production process of titanium pigment
CN103964512B (en) Titanium white by product product spent acid and ferrous sulfate is utilized to prepare iron oxide black
CN101760637B (en) Leaching technology of magnesium-containing ore
CN104192971A (en) Method for treating industrial wastewater containing sulfuric acid
CN101760638B (en) Method for recovering magnesium from magnesium sulfate solution
CN1749173A (en) Comprehensively utilizing new process for ferrous sulfate
CN101514033A (en) Environment friendly processing method of waste acid containing ferrous sulphate
Zhou et al. A near-zero-waste approach using simple physical-chemical methods recovery high concentrations of ammonia nitrogen, heavy metal, and sodium salts from hazardous vanadium-extracted solution
CN108373249B (en) Resource utilization method and treatment system for high-chlorine iron-containing waste 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
C02 Deemed withdrawal of patent application after publication (patent law 2001)
WD01 Invention patent application deemed withdrawn after publication

Open date: 20090826