CN102059242B - Novel method for comprehensive treatment of municipal solid wastes - Google Patents
Novel method for comprehensive treatment of municipal solid wastes Download PDFInfo
- Publication number
- CN102059242B CN102059242B CN201010515799XA CN201010515799A CN102059242B CN 102059242 B CN102059242 B CN 102059242B CN 201010515799X A CN201010515799X A CN 201010515799XA CN 201010515799 A CN201010515799 A CN 201010515799A CN 102059242 B CN102059242 B CN 102059242B
- Authority
- CN
- China
- Prior art keywords
- wet concentration
- winnowing
- selection
- organic matter
- degradative reduction
- 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.)
- Expired - Fee Related
Links
- 238000000034 method Methods 0.000 title claims abstract description 22
- 239000010813 municipal solid waste Substances 0.000 title claims abstract description 13
- XLYOFNOQVPJJNP-UHFFFAOYSA-N water Substances O XLYOFNOQVPJJNP-UHFFFAOYSA-N 0.000 claims abstract description 12
- 239000004033 plastic Substances 0.000 claims abstract description 10
- 229920003023 plastic Polymers 0.000 claims abstract description 10
- 239000011449 brick Substances 0.000 claims abstract description 7
- 239000004575 stone Substances 0.000 claims abstract description 7
- 238000000926 separation method Methods 0.000 claims abstract description 6
- 239000003337 fertilizer Substances 0.000 claims abstract description 5
- 239000004566 building material Substances 0.000 claims abstract description 4
- 230000003413 degradative effect Effects 0.000 claims description 14
- 239000010791 domestic waste Substances 0.000 claims description 11
- 239000005416 organic matter Substances 0.000 claims description 11
- QAOWNCQODCNURD-UHFFFAOYSA-N Sulfuric acid Chemical compound OS(O)(=O)=O QAOWNCQODCNURD-UHFFFAOYSA-N 0.000 claims description 6
- 239000007788 liquid Substances 0.000 claims description 6
- 239000000463 material Substances 0.000 claims description 6
- 239000007921 spray Substances 0.000 claims description 6
- VEXZGXHMUGYJMC-UHFFFAOYSA-N Hydrochloric acid Chemical compound Cl VEXZGXHMUGYJMC-UHFFFAOYSA-N 0.000 claims description 4
- NBIIXXVUZAFLBC-UHFFFAOYSA-N Phosphoric acid Chemical compound OP(O)(O)=O NBIIXXVUZAFLBC-UHFFFAOYSA-N 0.000 claims description 4
- 239000003054 catalyst Substances 0.000 claims description 4
- 238000006243 chemical reaction Methods 0.000 claims description 3
- 230000018044 dehydration Effects 0.000 claims description 3
- 238000006297 dehydration reaction Methods 0.000 claims description 3
- 238000001704 evaporation Methods 0.000 claims description 3
- 230000008020 evaporation Effects 0.000 claims description 3
- 238000001125 extrusion Methods 0.000 claims description 3
- 238000013467 fragmentation Methods 0.000 claims description 3
- 238000006062 fragmentation reaction Methods 0.000 claims description 3
- 239000007787 solid Substances 0.000 claims description 3
- 239000011343 solid material Substances 0.000 claims description 3
- GRYLNZFGIOXLOG-UHFFFAOYSA-N Nitric acid Chemical compound O[N+]([O-])=O GRYLNZFGIOXLOG-UHFFFAOYSA-N 0.000 claims description 2
- 229910000147 aluminium phosphate Inorganic materials 0.000 claims description 2
- 229910017604 nitric acid Inorganic materials 0.000 claims description 2
- 230000000593 degrading effect Effects 0.000 abstract 1
- 239000010802 sludge Substances 0.000 abstract 1
- 239000002699 waste material Substances 0.000 abstract 1
- 230000007812 deficiency Effects 0.000 description 2
- 238000009264 composting Methods 0.000 description 1
- 230000000694 effects Effects 0.000 description 1
- 230000007613 environmental effect Effects 0.000 description 1
- 229920002521 macromolecule Polymers 0.000 description 1
- 150000003384 small molecules Chemical class 0.000 description 1
- 239000000126 substance Substances 0.000 description 1
Classifications
-
- 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
- Y02A—TECHNOLOGIES FOR ADAPTATION TO CLIMATE CHANGE
- Y02A40/00—Adaptation technologies in agriculture, forestry, livestock or agroalimentary production
- Y02A40/10—Adaptation technologies in agriculture, forestry, livestock or agroalimentary production in agriculture
- Y02A40/20—Fertilizers of biological origin, e.g. guano or fertilizers made from animal corpses
-
- 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
- Y02E—REDUCTION OF GREENHOUSE GAS [GHG] EMISSIONS, RELATED TO ENERGY GENERATION, TRANSMISSION OR DISTRIBUTION
- Y02E50/00—Technologies for the production of fuel of non-fossil origin
- Y02E50/10—Biofuels, e.g. bio-diesel
-
- 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
- Y02E—REDUCTION OF GREENHOUSE GAS [GHG] EMISSIONS, RELATED TO ENERGY GENERATION, TRANSMISSION OR DISTRIBUTION
- Y02E50/00—Technologies for the production of fuel of non-fossil origin
- Y02E50/30—Fuel from waste, e.g. synthetic alcohol or diesel
Landscapes
- Processing Of Solid Wastes (AREA)
- Treatment Of Sludge (AREA)
- Fertilizers (AREA)
Abstract
The invention relates to a novel method for comprehensive treatment of municipal solid wastes, comprising the following steps: separating different components in the municipal solid wastes by the procedures of preceding separation, water separation and wind separation, wherein bricks, tiles and stones are made into building materials, and plastics are granulated; and degrading and reducing organic matters and sludge, wherein the degraded organic matters are made into fertilizers or RDF. The invention fully conforms to the waste harmlessness, reduction and reclamation principle.
Description
Technical field
The invention belongs to the environmental protection field, particularly a kind of new method of Urban Domestic Waste Comprehensive Treatment.
Background technology
China's domestic waste output is huge at present, and treating capacity does not catch up with far away.The refuse landfill in present many cities overload operation, there are problems such as occupation of land is big, processing speed is slow, percolate processing difficulty in the mode disposal of refuse with landfill simultaneously.The fertilizer that composting process is processed is difficult to accepted by market because fertilizer efficiency is not good.Directly burning is the most effective decrement mode, but the domestic waste moisture content of China is higher, directly burns very difficulty, and easy generation of secondary pollution, and environment is produced very big threat.All there are many drawbacks in a certain method disposal of refuse of simple dependence.The present invention provides a kind of method of comprehensive garbage disposal, to overcome the deficiency that above technology exists.
Summary of the invention
Technical problem to be solved by this invention is: a kind of new method of Urban Domestic Waste Comprehensive Treatment is provided, to overcome the deficiency that exists on the conventional garbage treatment technology, for garbage disposal provides a kind of new way.
Technology contents of the present invention:
A kind of new method of Urban Domestic Waste Comprehensive Treatment is characterized in that: the steps include:
(1) preceding sorting
Domestic waste sorts out big part combustible through preceding sorting, makes RDF, and residue gets into the wet concentration device.
(2) wet concentration
Rubbish is after the wet concentration apparatus processes, and dregs forms mud in water, and brick and tile, stone and separating organic matters come.Mud input degraded device processes, brick and tile, stone are made building materials again through fragmentation.
(3) selection by winnowing
The organic matter that wet concentration goes out is isolated plastics and organic matter through selection by winnowing, and plastics are wherein processed plastic grain and sold, the organic degradative reduction equipment that gets into.
(4) degradative reduction
The mud input degraded equipment that organic matter that selection by winnowing is gone out and wet concentration produce; Add catalyst (sulfuric acid, hydrochloric acid, nitric acid, phosphoric acid or in controlling catalyst at least a); Feed steam, make pressure in 0.6MPa~1.5MPa, temperature in 160~200 ℃ of scopes, carry out the reaction of 1h~3h.
(5) Separation of Solid and Liquid
After degradative reduction finishes, discharge excess liquid in the degraded equipment, handle through multiple-effect evaporation.
(6) spray quick-fried discharge
Solid material sprays quick-fried discharge in the presence of certain pressure, part moisture vapors away with steam, and the material water ratio of this moment is about 40%.Through extrusion dehydration, material water ratio can be reduced to below 30% again.Through the rubbish that degradative reduction is handled, can be used for making fertilizer, also can process RDF.
Effect of the present invention: through degradative reduction, most of macromolecular substances is degraded to small-molecule substance, has destroyed the structure of original organic matter, and constitution water is wherein also separated thereupon, changes free water into, and rubbish is dewatered more easily; Behind the degradative reduction, organic matter reaches stable state, is difficult for producing foul smell, is easy to storage.
Description of drawings
Accompanying drawing 1 is the process flow chart of this technology.
The specific embodiment
The present invention relates to dewatering organic in a kind of domestic waste, combine instance that its practical implementation step is described at present.
(1) preceding sorting
Domestic waste sorts out big part combustible through preceding sorting, makes RDF, and residue gets into the wet concentration device.
(2) wet concentration
Rubbish is after the wet concentration apparatus processes, and dregs forms mud in water, and brick and tile, stone and separating organic matters come.Mud input degraded device processes, brick and tile, stone are made building materials again through fragmentation.
(3) selection by winnowing
The organic matter that wet concentration goes out is isolated plastics and organic matter through selection by winnowing, and plastics are wherein processed plastic grain and sold, the organic degradative reduction equipment that gets into.
(4) degradative reduction
The mud input degraded equipment that organic matter that selection by winnowing is gone out and wet concentration produce adds catalyst (sulfuric acid), feeds steam, make pressure in 0.6MPa, temperature at 160 ℃, carry out the reaction of 1h.
(5) Separation of Solid and Liquid
After degradative reduction finishes, discharge excess liquid in the degraded equipment, handle through multiple-effect evaporation.
(6) spray quick-fried discharge
Solid material sprays quick-fried discharge in the presence of certain pressure, part moisture vapors away with steam, and the material water ratio of this moment is about 40%.Through extrusion dehydration, material water ratio can be reduced to below 30% again.Through the rubbish that degradative reduction is handled, process RDF.
Utilize this method disposal of refuse, processing speed is fast, and the processing cycle is short, thoroughly reaches the purpose of innoxious, minimizing, resource.
Claims (1)
1. the new method of a Urban Domestic Waste Comprehensive Treatment is characterized in that:
The steps include:
(1) preceding sorting
Domestic waste sorts out big part combustible through preceding sorting, makes RDF, and residue gets into the wet concentration device;
(2) wet concentration
Rubbish is after the wet concentration apparatus processes, and dregs forms mud in water, and brick and tile, stone and separating organic matters come; Mud input degraded device processes, brick and tile, stone are made building materials again through fragmentation;
(3) selection by winnowing
The organic matter that wet concentration goes out is isolated plastics and organic matter through selection by winnowing, and plastics are wherein processed plastic grain and sold, the organic degradative reduction equipment that gets into;
(4) degradative reduction
The mud input degraded equipment that organic matter that selection by winnowing is gone out and wet concentration produce; Add catalyst: at least a in sulfuric acid, hydrochloric acid, nitric acid, the phosphoric acid; Feed steam, make pressure in 0.6MPa~1.5MPa, temperature in 160~200 ℃ of scopes, carry out the reaction of 1h~3h;
(5) Separation of Solid and Liquid
After degradative reduction finishes, discharge excess liquid in the degraded equipment, handle through multiple-effect evaporation;
(6) spray quick-fried discharge
Solid material sprays quick-fried discharge in the presence of certain pressure, part moisture vapors away with steam, and the material water ratio of this moment is about 40%; Through extrusion dehydration, material water ratio is reduced to below 30% again; Through the rubbish that degradative reduction is handled, process fertilizer or RDF.
Priority Applications (1)
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CN201010515799XA CN102059242B (en) | 2010-10-22 | 2010-10-22 | Novel method for comprehensive treatment of municipal solid wastes |
Applications Claiming Priority (1)
Application Number | Priority Date | Filing Date | Title |
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CN201010515799XA CN102059242B (en) | 2010-10-22 | 2010-10-22 | Novel method for comprehensive treatment of municipal solid wastes |
Publications (2)
Publication Number | Publication Date |
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CN102059242A CN102059242A (en) | 2011-05-18 |
CN102059242B true CN102059242B (en) | 2012-08-15 |
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CN201010515799XA Expired - Fee Related CN102059242B (en) | 2010-10-22 | 2010-10-22 | Novel method for comprehensive treatment of municipal solid wastes |
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CN (1) | CN102059242B (en) |
Cited By (1)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
CN105175033A (en) * | 2015-09-22 | 2015-12-23 | 崇州市地龙海龙生物制品开发研究所 | Green garbage disposal method |
Families Citing this family (8)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
CN102311833A (en) * | 2011-09-16 | 2012-01-11 | 天津德为环保工程设备有限公司 | Method of preparing regenerated coal from municipal solid waste |
CN102500598B (en) * | 2011-10-27 | 2013-07-31 | 中国科学院广州能源研究所 | Method and device for efficiently sorting and extracting fermentable organic matter from household garbage |
CN103480632B (en) * | 2013-09-24 | 2015-08-19 | 华南农业大学 | A kind of Kitchen waste hydrothermal three-phase separation system |
CN103934251B (en) * | 2014-01-21 | 2017-09-15 | 上海程胜环保科技有限公司 | A kind of method of the disposal of human lives' rubbish with recycling |
CN106140778A (en) * | 2015-04-08 | 2016-11-23 | 北京神州蓝天新型环保建材有限公司 | Rubbish integrated process in construction site is dissolved method |
CN105436194A (en) * | 2015-12-25 | 2016-03-30 | 安徽继宏环保科技有限公司 | Sewage purification equipment of urban domestic waste treatment system |
CN106520245A (en) * | 2016-11-24 | 2017-03-22 | 福建省圣新能源股份有限公司 | Synthesis process and application of biomass hard material |
CN107470324B (en) * | 2017-08-15 | 2019-06-07 | 刘联仓 | A kind of recycling municipal solid waste processing method |
Citations (3)
Publication number | Priority date | Publication date | Assignee | Title |
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CN1396142A (en) * | 2002-08-27 | 2003-02-12 | 王和勋 | Process for preparing composite organic fertilizer life garbage in urban area |
CN1923383A (en) * | 2006-09-21 | 2007-03-07 | 环大环保科技(上海)有限公司 | High pressure steam catalysis hydrolysis process for treating domestic refuse |
CN101804414A (en) * | 2009-02-13 | 2010-08-18 | 叶毅 | Method and processing system for comprehensively recycling municipal solid wastes |
Family Cites Families (2)
Publication number | Priority date | Publication date | Assignee | Title |
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JPH10330855A (en) * | 1997-06-02 | 1998-12-15 | Nisso Kinzoku Kagaku Kk | Method for recovering valuable material from lithium-ion secondary battery |
JP2000185269A (en) * | 1998-12-22 | 2000-07-04 | Nkk Corp | Waste plastic regenerating treatment equipment |
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- 2010-10-22 CN CN201010515799XA patent/CN102059242B/en not_active Expired - Fee Related
Patent Citations (3)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
CN1396142A (en) * | 2002-08-27 | 2003-02-12 | 王和勋 | Process for preparing composite organic fertilizer life garbage in urban area |
CN1923383A (en) * | 2006-09-21 | 2007-03-07 | 环大环保科技(上海)有限公司 | High pressure steam catalysis hydrolysis process for treating domestic refuse |
CN101804414A (en) * | 2009-02-13 | 2010-08-18 | 叶毅 | Method and processing system for comprehensively recycling municipal solid wastes |
Non-Patent Citations (2)
Title |
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JP特开2000-185269A 2000.07.04 |
JP特开平10-330855A 1998.12.15 |
Cited By (1)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
CN105175033A (en) * | 2015-09-22 | 2015-12-23 | 崇州市地龙海龙生物制品开发研究所 | Green garbage disposal method |
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CN102059242A (en) | 2011-05-18 |
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