CN101086035A - Discarded metal sludge recovery and utilization method - Google Patents
Discarded metal sludge recovery and utilization method Download PDFInfo
- Publication number
- CN101086035A CN101086035A CNA2007100248702A CN200710024870A CN101086035A CN 101086035 A CN101086035 A CN 101086035A CN A2007100248702 A CNA2007100248702 A CN A2007100248702A CN 200710024870 A CN200710024870 A CN 200710024870A CN 101086035 A CN101086035 A CN 101086035A
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- China
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- metal sludge
- counterweight
- utilizing method
- mud
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- Y—GENERAL TAGGING OF NEW TECHNOLOGICAL DEVELOPMENTS; GENERAL TAGGING OF CROSS-SECTIONAL TECHNOLOGIES SPANNING OVER SEVERAL SECTIONS OF THE IPC; TECHNICAL SUBJECTS COVERED BY FORMER USPC CROSS-REFERENCE ART COLLECTIONS [XRACs] AND DIGESTS
- Y02—TECHNOLOGIES OR APPLICATIONS FOR MITIGATION OR ADAPTATION AGAINST CLIMATE CHANGE
- Y02P—CLIMATE CHANGE MITIGATION TECHNOLOGIES IN THE PRODUCTION OR PROCESSING OF GOODS
- Y02P10/00—Technologies related to metal processing
- Y02P10/20—Recycling
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- Y—GENERAL TAGGING OF NEW TECHNOLOGICAL DEVELOPMENTS; GENERAL TAGGING OF CROSS-SECTIONAL TECHNOLOGIES SPANNING OVER SEVERAL SECTIONS OF THE IPC; TECHNICAL SUBJECTS COVERED BY FORMER USPC CROSS-REFERENCE ART COLLECTIONS [XRACs] AND DIGESTS
- Y02—TECHNOLOGIES OR APPLICATIONS FOR MITIGATION OR ADAPTATION AGAINST CLIMATE CHANGE
- Y02W—CLIMATE CHANGE MITIGATION TECHNOLOGIES RELATED TO WASTEWATER TREATMENT OR WASTE MANAGEMENT
- Y02W30/00—Technologies for solid waste management
- Y02W30/50—Reuse, recycling or recovery technologies
- Y02W30/91—Use of waste materials as fillers for mortars or concrete
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- Treatment Of Sludge (AREA)
Abstract
The invention relates to a method for recovering and utilizing waste metal sludge. It is characterized in that the waste metal sludge can be recycled as renewable resources, which causes no pollution and avoids the harm for water resource and human environment brought from industrial solid waste deep bury. The method comprises adding hydrogen peroxide and potassium permanganate into waste metal sludge for oxidation, which combines with autoxidation to form metal powder that is suitable for extraction.
Description
Technical field
The present invention relates to industrial solid castoff metal sludge treatment technology, be specially the discarded metal sludge recoverying and utilizing method.
Background technology
Development along with China's industrial economy construction, the continuous expansion of commercial production scale, caused the sharp increase of solid waste, conventional way adopts the underground landfill of deep layer exactly, this not only takies a large amount of soils, and serious environment pollution and groundwater resource, bring very big harm to existent environment of people.
Summary of the invention
At the problems referred to above, the present invention aims to provide the discarded metal sludge recoverying and utilizing method, it can make the metal solid waste sludge become the renewable resource recycle, and is environment friendly and pollution-free, the harm of having avoided the water resources brought after the buried processing of industrial solid castoff and human environment to pollute.
Technical scheme of the present invention, the discarded metal sludge recoverying and utilizing method:
It is characterized in that: hydrogen peroxide and potassium permanganate carry out strong oxidation and the air natural oxidation forms the metal powder material that is fit to refinement with adding in the discarded metal sludge.
It is further characterized in that: metal powder material ironmaking that iron level is high or production counterweight or production raw material cement, the metal powder material that iron level is low is produced raw material cement or is carried out roasting, maturing temperature is at 1200 ℃~1300 ℃, and the powder after the roasting can be used for ironmaking or produce counterweight;
Produce counterweight, with the metal powder material after the roasting and cement, water mixing mold pressing typing, concrete blending ratio is as long as cement can solidify;
Produce counterweight, material mixing with following umber, 60 parts~80 parts of metal powder materials, 10 parts~20 parts of Resins, epoxy, 10 parts~20 parts of thinners, 0.3 part~0.4 part in solidifying agent, 0.3 part~0.5 part of toughner, stir fast, at 5 minutes~15 minutes internal mold compression set types, described thinner is a dimethylbenzene, and described solidifying agent is the second diamino, and described toughner is dibutylester;
Produce counterweight: 40 parts~60 parts of the powders of plastic waste are mixed for 40 parts~60 parts with metal powder material, go up pressure die-casting machine then and be cast into the plastics counterweight;
Described discarded metal sludge is any or any several mixture in the mud that forms of metal pickling mud, pharmaceutical chemical industry iron mud, pesticide chemical iron mud, pyrometallurgy mud, metallurgical spent acid and dyeing waste water neutralizing treatment.
The present invention can make the metal solid waste sludge realize pollution-free recycle and resource recovery, make the waste of discharging become the environmental type iron ore of China's output maximum, solved the water resources and the human environment pollution hazard that bring after the buried processing of industrial solid castoff of the annual up to ten million tons of present China.
Embodiment
Hydrogen peroxide and potassium permanganate carry out strong oxidation and the air natural oxidation forms the metal powder material that is fit to refinement with adding in the discarded metal sludge.The metal powder material that iron level is high is smelted iron or is produced counterweight or send the cement mill to produce raw material cement, the metal powder material that iron level is low send the cement mill to produce raw material cement or carries out roasting, maturing temperature is at 1200 ℃~1300 ℃, and the powder after the roasting can be used for ironmaking or produce counterweight.
With the metal powder material after the roasting and cement, water mixing mold pressing typing, concrete blending ratio is as long as cement can solidify when producing counterweight, and this is for producing the embodiment 1 of counterweight;
Material mixing with following umber, 60 parts~80 parts of metal powder materials, 10 parts~20 parts of Resins, epoxy, 10 parts~20 parts of thinners, 0.3 part~0.4 part in solidifying agent, 0.3 part~0.5 part of toughner, optimum proportion is 70 parts of metal powder materials, 15 parts of Resins, epoxy, 15 parts of thinners, 0.35 part in solidifying agent, 0.4 part of toughner, stir fast, at 5 minutes~15 minutes internal mold compression set types, Best Times was 10 minutes; Described thinner is a dimethylbenzene, and described solidifying agent is the second diamino, and described toughner is dibutylester, and this is for producing the embodiment 2 of counterweight;
40 parts~60 parts of the powders of plastic waste are mixed for 40 parts~60 parts with metal powder material, go up pressure die-casting machine then and be cast into the plastics counterweight, this is for producing the embodiment 3 of counterweight.
Described discarded metal sludge is any or any several mixture in the mud that forms of metal pickling mud, pharmaceutical chemical industry iron mud, pesticide chemical iron mud, pyrometallurgy mud, metallurgical spent acid and dyeing waste water neutralizing treatment.
Claims (7)
1, discarded metal sludge recoverying and utilizing method is characterized in that: hydrogen peroxide and potassium permanganate carry out strong oxidation and the air natural oxidation forms the metal powder material that is fit to refinement with adding in the discarded metal sludge.
2, according to the described discarded metal sludge recoverying and utilizing method of claim 1, it is characterized in that: the metal powder material that iron level is high is smelted iron or is produced counterweight or produces raw material cement, the metal powder material that iron level is low is produced raw material cement or is carried out roasting, maturing temperature is at 1200 ℃~1300 ℃, and the powder after the roasting can be used for ironmaking or produce counterweight.
3, according to the described discarded metal sludge recoverying and utilizing method of claim 2, it is characterized in that: produce counterweight, with the metal powder material after the roasting and cement, water mixing mold pressing typing, concrete blending ratio is as long as cement can solidify.
4, according to the described discarded metal sludge recoverying and utilizing method of claim 2, it is characterized in that: produce counterweight, material mixing with following umber, 60 parts~80 parts of metal powder materials, 10 parts~20 parts of Resins, epoxy, 10 parts~20 parts of thinners, 0.3 part~0.4 part in solidifying agent, 0.3 part~0.5 part of toughner, stir fast, at 5 minutes~15 minutes internal mold compression set types.
5, according to the described discarded metal sludge recoverying and utilizing method of claim 4, it is characterized in that: described thinner is a dimethylbenzene, and described solidifying agent is the second diamino, and described toughner is dibutylester.
6, according to the described discarded metal sludge recoverying and utilizing method of claim 2, it is characterized in that: produce counterweight: 40 parts~60 parts of the powders of plastic waste are mixed for 40 parts~60 parts with metal powder material, go up pressure die-casting machine then and be cast into the plastics counterweight.
7, according to the described discarded metal sludge recoverying and utilizing method of claim 1, it is characterized in that: described discarded metal sludge is any or any several mixture in the mud that forms of metal pickling mud, pharmaceutical chemical industry iron mud, pesticide chemical iron mud, pyrometallurgy mud, metallurgical spent acid and dyeing waste water neutralizing treatment.
Priority Applications (1)
Application Number | Priority Date | Filing Date | Title |
---|---|---|---|
CNB2007100248702A CN100535140C (en) | 2007-06-28 | 2007-06-28 | Discarded metal sludge recovery and utilization method |
Applications Claiming Priority (1)
Application Number | Priority Date | Filing Date | Title |
---|---|---|---|
CNB2007100248702A CN100535140C (en) | 2007-06-28 | 2007-06-28 | Discarded metal sludge recovery and utilization method |
Publications (2)
Publication Number | Publication Date |
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CN101086035A true CN101086035A (en) | 2007-12-12 |
CN100535140C CN100535140C (en) | 2009-09-02 |
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Family Applications (1)
Application Number | Title | Priority Date | Filing Date |
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CNB2007100248702A Expired - Fee Related CN100535140C (en) | 2007-06-28 | 2007-06-28 | Discarded metal sludge recovery and utilization method |
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CN (1) | CN100535140C (en) |
Cited By (6)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
CN103589863A (en) * | 2013-11-08 | 2014-02-19 | 乔安平 | Technology for blocking steelmaking metal powder |
CN108687935A (en) * | 2017-04-12 | 2018-10-23 | 吴靖松 | A kind of production technology of environmental protection clump weight |
WO2020089650A1 (en) * | 2018-11-02 | 2020-05-07 | Darlow Lloyd & Sons Limited | Method and apparatus for treating waste material comprising iron |
CN111663044A (en) * | 2020-05-14 | 2020-09-15 | 中冶南方工程技术有限公司 | Acid sludge and waste acid resource recovery device and process |
CN111732085A (en) * | 2020-05-14 | 2020-10-02 | 中冶南方工程技术有限公司 | Acid sludge and waste acid integrated recovery device and process |
CN115608740A (en) * | 2022-10-17 | 2023-01-17 | 北京中岩大地环境科技有限公司 | Gravity energy storage block after contaminated soil solidification and stabilization and preparation method thereof |
-
2007
- 2007-06-28 CN CNB2007100248702A patent/CN100535140C/en not_active Expired - Fee Related
Cited By (10)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
CN103589863A (en) * | 2013-11-08 | 2014-02-19 | 乔安平 | Technology for blocking steelmaking metal powder |
CN108687935A (en) * | 2017-04-12 | 2018-10-23 | 吴靖松 | A kind of production technology of environmental protection clump weight |
WO2020089650A1 (en) * | 2018-11-02 | 2020-05-07 | Darlow Lloyd & Sons Limited | Method and apparatus for treating waste material comprising iron |
GB2578645A (en) * | 2018-11-02 | 2020-05-20 | Darlow Lloyd & Sons Ltd | Method and apparatus for treating waste material |
GB2578645B (en) * | 2018-11-02 | 2021-11-24 | Darlow Lloyd & Sons Ltd | Method and apparatus for treating waste material |
CN111663044A (en) * | 2020-05-14 | 2020-09-15 | 中冶南方工程技术有限公司 | Acid sludge and waste acid resource recovery device and process |
CN111732085A (en) * | 2020-05-14 | 2020-10-02 | 中冶南方工程技术有限公司 | Acid sludge and waste acid integrated recovery device and process |
CN111663044B (en) * | 2020-05-14 | 2023-12-29 | 中冶南方工程技术有限公司 | Acidic sludge and waste acid recycling device and process |
CN111732085B (en) * | 2020-05-14 | 2023-12-29 | 中冶南方工程技术有限公司 | Integrated recovery device and process for acid sludge and waste acid |
CN115608740A (en) * | 2022-10-17 | 2023-01-17 | 北京中岩大地环境科技有限公司 | Gravity energy storage block after contaminated soil solidification and stabilization and preparation method thereof |
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Publication number | Publication date |
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CN100535140C (en) | 2009-09-02 |
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Granted publication date: 20090902 Termination date: 20160628 |
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