CN110002567A - A kind of method that stainless steel annealing pickling waste waters neutralizes and sludge is applied flexibly - Google Patents

A kind of method that stainless steel annealing pickling waste waters neutralizes and sludge is applied flexibly Download PDF

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Publication number
CN110002567A
CN110002567A CN201910220048.6A CN201910220048A CN110002567A CN 110002567 A CN110002567 A CN 110002567A CN 201910220048 A CN201910220048 A CN 201910220048A CN 110002567 A CN110002567 A CN 110002567A
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China
Prior art keywords
sludge
stainless steel
pickling waste
waste waters
value
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Pending
Application number
CN201910220048.6A
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Chinese (zh)
Inventor
林鸿亮
荣青亮
孟丽萍
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Zhangjiagang Pohang Stainless Steel Co Ltd
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Zhangjiagang Pohang Stainless Steel Co Ltd
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Priority to CN201910220048.6A priority Critical patent/CN110002567A/en
Publication of CN110002567A publication Critical patent/CN110002567A/en
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    • CCHEMISTRY; METALLURGY
    • C02TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02FTREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02F1/00Treatment of water, waste water, or sewage
    • C02F1/52Treatment of water, waste water, or sewage by flocculation or precipitation of suspended impurities
    • CCHEMISTRY; METALLURGY
    • C02TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02FTREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02F1/00Treatment of water, waste water, or sewage
    • C02F1/58Treatment of water, waste water, or sewage by removing specified dissolved compounds
    • CCHEMISTRY; METALLURGY
    • C02TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02FTREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02F1/00Treatment of water, waste water, or sewage
    • C02F1/66Treatment of water, waste water, or sewage by neutralisation; pH adjustment
    • CCHEMISTRY; METALLURGY
    • C02TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02FTREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02F11/00Treatment of sludge; Devices therefor
    • CCHEMISTRY; METALLURGY
    • C02TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02FTREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02F11/00Treatment of sludge; Devices therefor
    • C02F11/12Treatment of sludge; Devices therefor by de-watering, drying or thickening
    • C02F11/121Treatment of sludge; Devices therefor by de-watering, drying or thickening by mechanical de-watering
    • CCHEMISTRY; METALLURGY
    • C02TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02FTREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02F2101/00Nature of the contaminant
    • C02F2101/10Inorganic compounds
    • C02F2101/16Nitrogen compounds, e.g. ammonia
    • CCHEMISTRY; METALLURGY
    • C02TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02FTREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02F2103/00Nature of the water, waste water, sewage or sludge to be treated
    • C02F2103/16Nature of the water, waste water, sewage or sludge to be treated from metallurgical processes, i.e. from the production, refining or treatment of metals, e.g. galvanic wastes
    • CCHEMISTRY; METALLURGY
    • C02TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02FTREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02F2305/00Use of specific compounds during water treatment
    • C02F2305/02Specific form of oxidant

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  • Engineering & Computer Science (AREA)
  • Life Sciences & Earth Sciences (AREA)
  • Hydrology & Water Resources (AREA)
  • Environmental & Geological Engineering (AREA)
  • Water Supply & Treatment (AREA)
  • Chemical & Material Sciences (AREA)
  • Organic Chemistry (AREA)
  • Mechanical Engineering (AREA)
  • Separation Of Suspended Particles By Flocculating Agents (AREA)

Abstract

The invention discloses the method that a kind of neutralization of stainless steel annealing pickling waste waters and sludge are applied flexibly, include the following steps: that middle predetermined value pH is arranged1=X, pH2=Y;Milk of lime is added to pickling waste waters, pickling waste waters pH value is made to reach middle predetermined value pH1, addition flocculant stirring standing;The waste water obtained to above-mentioned steps continues to add milk of lime, and sour pH value of waste water is made to reach middle predetermined value pH2Stop addition milk of lime, replaced with sodium hydrate aqueous solution, until neutralizing terminal pH=10.5, addition flocculant stirring is stood.The beneficial effects of the invention are as follows realize sludge classification precipitating using fractional neutralization method by control pH value, CaO is not put into excessively, reduce denitrogenation processing cost, guarantee Chinese effluent index, differential recycling is realized for the ingredient properties of fractional neutralization product, and economic maximization effect is realized under the premise of safety and environmental protection.

Description

A kind of method that stainless steel annealing pickling waste waters neutralizes and sludge is applied flexibly
Technical field
The invention belongs to solid liquid waste resource recycling fields in stainless steel production more particularly to a kind of stainless steel to move back The sludge obtained after fiery pickling waste waters neutralization method and neutralization applies flexibly method.
Background technique
Stainless steel is widely used because of its excellent corrosion resistance and good appearance.Stainless steel in process of production, Inevitably pass through the process such as annealing, normalizing, quenching, welding, surface can generate the oxide skin of black often.Oxidation Skin not only influences the presentation quality of stainless steel, can also have an adverse effect to the following process of product, therefore must before following process It must be removed using surface treatment methods such as pickling, polishings.Acid-washing stainless steel process is removed with sulfuric acid pre-sour first The iron scale on surface is removed, then carries out pickling with nitric acid and hydrofluoric acid nitration mixture.Nitric acid with strong oxidizing property can be by metal And metal oxide, generate Cr3+、 Fe3+And Ni2+Ion, these metal ions and hydrofluoric acid react, and generate Solvable or indissoluble metal fluoride.With the progress of acid cleaning process, the nitric acid and hydrofluoric acid to dissociate in pickling solution is fewer and fewer, Reaction product is more and more.When metal salt crystallizes precipitation from pickling solution in pickling solution, descaling bath must be cleaned or replaced.One Since straight, the processing of a large amount of pickling waste waters generated in producing stainless steel process is the problem of iron and steel enterprise.With steel and iron industry Gradually develop, people gradually recognize that pickling waste waters is especially the harm to mankind itself to environment, in addition environmental protection is to useless Water discharge has strict requirements, first must be by its harmless treatment.The processing for the pickling waste waters that acid-washing stainless steel generates is compared Complexity, there are mainly two types of thinkings at present: first is that exploring the dirt of generation after stainless steel acid cleaning waste water is neutralized using traditional lime The administering method of mud;Second is that exploring the method for directly administering stainless steel acid cleaning waste water.Most economical efficient mode is exactly traditional By the neutralisation in addition quick lime with residual acid in waste water, the flocculation sedimentation of metal hydroxides is realized, finally by filters pressing Form the lower neutralization sludge of water content.In the prior art in order to guarantee effluent index after neutralizing, the mode for taking a step to neutralize, It is put into pickling waste waters a large amount of calcium oxide (CaO), Ca ion concentration is high in water, and obtained sludge quantity is big.Neutralize obtained dirt There are two types of the processing scheme of mainstream, landfill and electric furnace reuses at present for mud.Because hydrofluoric acid is that stainless steel realizes that continuous acid-washing is most heavy The ingredient wanted, so fluorine content is very high in and in the sludge of generation.Fluorine-containing sludge directly fill be to soil it is harmful, easily It is absorbed by plants, and then constitutes a threat to plant growth and human health, and the heavy metal in sludge is easy polluted underground water, So fluorine-containing and metal sludge must select special landfill at present, but expensive, the long processing period of special landfill, sludge The metal of middle recoverable also directly wastes, so many enterprises start to select in electric furnace reuse and sludge.Same fluorine-containing dirt When mud investment electric furnace carries out smelting operation, it can be inhaled into flue, the hydrofluoric acid generated under hot conditions generates corrosion to water-cooling wall, Leak occurs, electric furnace maintenance cycle serious curtailment, maintenance cost is expensive, influences rhythm of production and has risk.In addition, investment A large amount of calcium oxide (CaO) neutralizing acid waste water will cause water outlet Ca ion concentration while removing metal ion and be significantly increased, directly Connecing influences subsequent denitrogenation water process, increases denitrogenation period and cost.
Summary of the invention
In order to overcome the deficiencies of the prior art, the purpose of the present invention is to provide a kind of stainless steel annealing pickling waste waters neutralize and The method that sludge is applied flexibly, solves the problems, such as in annealing and pickling waste water and medicament calcium oxide (CaO) input amount is excessive;Solve water outlet calcium from Sub- concentration height influences the problem of nitric efficiency;Solve the problems, such as that sludge precious metal recycles;Solve applying flexibly for fluorine-containing sludge Problem.
To achieve the above object, the present invention adopts the following technical scheme:
A kind of method that stainless steel annealing pickling waste waters neutralizes, its main feature is that including the following steps: stainless steel annealing pickling Waste water carries out fractional neutralization, and middle predetermined value pH is arranged1=X, pH2=Y;Mud, water separate for the first time, and stone is added into pickling waste waters Grey cream, makes pickling waste waters pH value reach middle predetermined value pH1, flocculant is added, stirring is stood, and obtains primary sludge and primary useless Water;The working principle of the step is that neutralization reaction is arranged according to nitric acid, hydrofluoric acid and concentration of metal ions in pickling waste waters Corresponding pH value (X), fluorinion in waste water is present in sludge with precipitation form, and precious metal ion exists with free state In Yu Yici waste water, and task is separated for the first time by adding appropriate flocculant and control stirring time of repose completion mud, water;Institute Primary sludge is stated for stainless steel smelting auxiliary material;
Mud, water secondary separation continue to add milk of lime into the waste water that above-mentioned steps obtain, reach sour pH value of waste water To middle predetermined value pH2Stop addition milk of lime, replaced with sodium hydroxide (NaOH) aqueous solution, until neutralizing terminal pH= 10.5, flocculant is added, stirring is stood, and obtains secondary sludge and secondary wastewater;The working principle of the step is anti-by neutralizing Should realize precious metal ion flocculation, precipitating, formed secondary sludge, while in order to reduce water outlet denitrogenation processing efficiency and at This, needs to add appropriate NaOH aqueous solution and completes neutralization reaction;The secondary sludge carries out precious metal recycling.
Further, the value range of the X is 4.5-5.0.
Further, the value range of the Y is 8.0-8.5.
Further, the primary sludge includes pressing the primary sludge for the step of stainless steel smelting auxiliary material Filter carries out pressure ball after mixing with electric stove dust ash, molasses on ball press, and the reuse of stainless steel smelting auxiliary material is used as after baking.
Further, the step of secondary sludge progress precious metal recycling includes pressing the secondary sludge Filter, mixes with electric stove dust ash, restores to obtain precious metal by mineral hot furnace.
Further, the secondary wastewater carries out denitrogenation processing.
Further, the processing step is suitable for the processing of hot-rolled stainless steel annealing and pickling waste water.
Compared with prior art, the beneficial effects of the present invention are: pickling waste waters is neutralized through control pH value using in substep Sludge classification precipitating is realized with method, CaO is not put into excessively, reduces denitrogenation processing cost, not only guarantees that water outlet meets discharge index, Differential recycling more importantly is realized for the ingredient properties of fractional neutralization product, reduces stainless steel smelting equipment Corrosion risk will not adversely affect rhythm of production and equipment, significantly reduce maintenance cost, before safety and environmental protection The economic maximization effect of realization is put, while also achieving metal in sludge effective recycling.
Specific embodiment
The present invention will be further described combined with specific embodiments below.
A kind of method that stainless steel annealing pickling waste waters neutralizes, its main feature is that including the following steps: stainless steel annealing pickling Waste water carries out fractional neutralization, and middle predetermined value pH is arranged1The value range of=X, X are 4.5-5.0; pH2The value range of=Y, Y It is 8.0-8.5;Mud, water separate for the first time, and milk of lime is added into pickling waste waters, and pickling waste waters pH value is made to reach middle predetermined value pH1, flocculant is added, stirring is stood, and obtains primary sludge and a waste water;The working principle of the step is according to pickling waste waters Middle nitric acid, hydrofluoric acid and concentration of metal ions are arranged the corresponding pH value of neutralization reaction (X), by fluorinion in waste water to precipitate Form is present in sludge, and precious metal ion is present in a waste water with free state, and by adding appropriate flocculant And control stirring time of repose completes mud, water separates task for the first time;The primary sludge is used for stainless steel smelting auxiliary material;Once Sludge includes that the primary sludge is carried out filters pressing for the step of stainless steel smelting auxiliary material, is mixed with electric stove dust ash, molasses Afterwards, pressure ball is carried out on ball press, and the reuse of stainless steel smelting auxiliary material is used as after baking;
Mud, water secondary separation continue to add milk of lime into the waste water that above-mentioned steps obtain, reach sour pH value of waste water To middle predetermined value pH2Stop addition milk of lime, replaced with sodium hydroxide (NaOH) aqueous solution, until neutralizing terminal pH= 10.5, flocculant is added, stirring is stood, and obtains secondary sludge and secondary wastewater;The working principle of the step is anti-by neutralizing Should realize precious metal ion flocculation, precipitating, formed secondary sludge, while in order to reduce water outlet denitrogenation processing efficiency and at This, needs to add appropriate NaOH aqueous solution and completes neutralization reaction;The secondary sludge carries out precious metal recycling;Secondary sludge into The step of row precious metal recycles includes that the secondary sludge is carried out filters pressing, is mixed with electric stove dust ash, also by mineral hot furnace Original obtains precious metal;The secondary wastewater that mud, water secondary separation are obtained carries out denitrogenation processing.
Above-mentioned processing step is suitable for the processing of hot-rolled stainless steel annealing and pickling waste water.
The principles and effects of the invention, and the implementation that part uses only is illustrated in the above embodiments Example, and is not intended to limit the present invention;It should be pointed out that for those of ordinary skill in the art, not departing from wound of the present invention Under the premise of making design, various modifications and improvements can be made, and these are all within the scope of protection of the present invention.

Claims (7)

1. a kind of method that stainless steel annealing pickling waste waters neutralizes and sludge is applied flexibly, characterized by the following steps: stainless Steel annealing and pickling waste water carries out fractional neutralization, and middle predetermined value pH is arranged1=X, pH2=Y;Mud, water separate for the first time, useless to pickling Milk of lime is added in water, and sour pH value of waste water is made to reach middle predetermined value pH1, flocculant is added, stirring is stood, and obtains primary sludge With a waste water;The primary sludge is used as stainless steel smelting auxiliary material;
Mud, water secondary separation continue to add milk of lime into the waste water that above-mentioned steps obtain, and make during sour pH value of waste water reaches Between preset value pH2Stop addition milk of lime, is replaced with sodium hydrate aqueous solution, until terminal pH=10.5 is neutralized, addition flocculation Agent, stirring are stood, and obtain secondary sludge and secondary wastewater;The secondary sludge is subjected to precious metal recycling.
A kind of method that 2. stainless steel annealing pickling waste waters neutralizes according to claim 1 and sludge is applied flexibly, it is characterised in that: The value range of the X is 4.5-5.0.
A kind of method that 3. stainless steel annealing pickling waste waters neutralizes according to claim 1 and sludge is applied flexibly, it is characterised in that: The value range of the Y is 8.0-8.5.
A kind of method that 4. stainless steel annealing pickling waste waters neutralizes according to claim 1 and sludge is applied flexibly, it is characterised in that: The primary sludge be used as stainless steel smelting auxiliary material the step of include by the primary sludge carry out filters pressing, with electric stove dust ash, After molasses mixing, pressure ball is carried out on ball press, and the reuse of stainless steel smelting auxiliary material is used as after baking.
A kind of method that 5. stainless steel annealing pickling waste waters neutralizes according to claim 1 and sludge is applied flexibly, it is characterised in that: The step of secondary sludge progress precious metal recycling includes that the secondary sludge is carried out filters pressing, mixed with electric stove dust ash It closes, restores to obtain precious metal by mineral hot furnace.
A kind of method that 6. stainless steel annealing pickling waste waters neutralizes according to claim 1 and sludge is applied flexibly, it is characterised in that: The secondary wastewater carries out denitrogenation processing.
7. any one of -4 method that a kind of stainless steel annealing pickling waste waters neutralizes and sludge is applied flexibly according to claim 1, Be characterized in that: the processing step is suitable for the processing of hot-rolled stainless steel annealing and pickling waste water.
CN201910220048.6A 2019-03-22 2019-03-22 A kind of method that stainless steel annealing pickling waste waters neutralizes and sludge is applied flexibly Pending CN110002567A (en)

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Cited By (4)

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Publication number Priority date Publication date Assignee Title
CN110317951A (en) * 2019-07-16 2019-10-11 嘉善助远再生资源回收有限公司 A method of nichrome is produced using dedusting ash of stainless steel and pickling sludge
CN111850233A (en) * 2020-07-31 2020-10-30 阴通明 Recovery process of stainless steel pickling residues
CN112358206A (en) * 2020-11-16 2021-02-12 山西太钢不锈钢股份有限公司 Method for improving activity of blast furnace slag micro powder
CN113429030A (en) * 2021-08-11 2021-09-24 攀钢集团攀枝花钢铁研究院有限公司 Method for cooperatively treating sintering desulfurization acid wastewater and machine head dedusting ash

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Cited By (4)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN110317951A (en) * 2019-07-16 2019-10-11 嘉善助远再生资源回收有限公司 A method of nichrome is produced using dedusting ash of stainless steel and pickling sludge
CN111850233A (en) * 2020-07-31 2020-10-30 阴通明 Recovery process of stainless steel pickling residues
CN112358206A (en) * 2020-11-16 2021-02-12 山西太钢不锈钢股份有限公司 Method for improving activity of blast furnace slag micro powder
CN113429030A (en) * 2021-08-11 2021-09-24 攀钢集团攀枝花钢铁研究院有限公司 Method for cooperatively treating sintering desulfurization acid wastewater and machine head dedusting ash

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