CN106122968A - Preprocess method before one way of life waste incineration - Google Patents
Preprocess method before one way of life waste incineration Download PDFInfo
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- CN106122968A CN106122968A CN201610471878.2A CN201610471878A CN106122968A CN 106122968 A CN106122968 A CN 106122968A CN 201610471878 A CN201610471878 A CN 201610471878A CN 106122968 A CN106122968 A CN 106122968A
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- refuse
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- fertilizer
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- 238000000034 method Methods 0.000 title claims abstract description 60
- 238000004056 waste incineration Methods 0.000 title claims abstract description 13
- 239000010815 organic waste Substances 0.000 claims abstract description 28
- 239000003337 fertilizer Substances 0.000 claims abstract description 25
- 238000002156 mixing Methods 0.000 claims abstract description 17
- 239000003245 coal Substances 0.000 claims abstract description 16
- 230000005611 electricity Effects 0.000 claims abstract description 7
- 238000010298 pulverizing process Methods 0.000 claims abstract description 6
- 238000001914 filtration Methods 0.000 claims description 17
- HEMHJVSKTPXQMS-UHFFFAOYSA-M Sodium hydroxide Chemical compound [OH-].[Na+] HEMHJVSKTPXQMS-UHFFFAOYSA-M 0.000 claims description 15
- XLYOFNOQVPJJNP-UHFFFAOYSA-N water Substances O XLYOFNOQVPJJNP-UHFFFAOYSA-N 0.000 claims description 15
- 241000283690 Bos taurus Species 0.000 claims description 12
- 229910000365 copper sulfate Inorganic materials 0.000 claims description 12
- ARUVKPQLZAKDPS-UHFFFAOYSA-L copper(II) sulfate Chemical compound [Cu+2].[O-][S+2]([O-])([O-])[O-] ARUVKPQLZAKDPS-UHFFFAOYSA-L 0.000 claims description 12
- 239000010902 straw Substances 0.000 claims description 12
- 210000003608 fece Anatomy 0.000 claims description 11
- 229910001385 heavy metal Inorganic materials 0.000 claims description 11
- 239000010871 livestock manure Substances 0.000 claims description 11
- VSCWAEJMTAWNJL-UHFFFAOYSA-K aluminium trichloride Chemical compound Cl[Al](Cl)Cl VSCWAEJMTAWNJL-UHFFFAOYSA-K 0.000 claims description 10
- 239000002245 particle Substances 0.000 claims description 10
- 239000002516 radical scavenger Substances 0.000 claims description 10
- 238000005273 aeration Methods 0.000 claims description 9
- XEEYBQQBJWHFJM-UHFFFAOYSA-N iron Substances [Fe] XEEYBQQBJWHFJM-UHFFFAOYSA-N 0.000 claims description 9
- 238000004332 deodorization Methods 0.000 claims description 7
- 238000001556 precipitation Methods 0.000 claims description 6
- 239000013049 sediment Substances 0.000 claims description 6
- 229910021380 Manganese Chloride Inorganic materials 0.000 claims description 5
- GLFNIEUTAYBVOC-UHFFFAOYSA-L Manganese chloride Chemical compound Cl[Mn]Cl GLFNIEUTAYBVOC-UHFFFAOYSA-L 0.000 claims description 5
- WAEMQWOKJMHJLA-UHFFFAOYSA-N Manganese(2+) Chemical compound [Mn+2] WAEMQWOKJMHJLA-UHFFFAOYSA-N 0.000 claims description 5
- CKUAXEQHGKSLHN-UHFFFAOYSA-N [C].[N] Chemical compound [C].[N] CKUAXEQHGKSLHN-UHFFFAOYSA-N 0.000 claims description 5
- REDXJYDRNCIFBQ-UHFFFAOYSA-N aluminium(3+) Chemical compound [Al+3] REDXJYDRNCIFBQ-UHFFFAOYSA-N 0.000 claims description 5
- 238000005352 clarification Methods 0.000 claims description 5
- 238000000855 fermentation Methods 0.000 claims description 5
- 230000004151 fermentation Effects 0.000 claims description 5
- 239000000706 filtrate Substances 0.000 claims description 5
- 238000005189 flocculation Methods 0.000 claims description 5
- 230000016615 flocculation Effects 0.000 claims description 5
- 239000008187 granular material Substances 0.000 claims description 5
- 229910052742 iron Inorganic materials 0.000 claims description 5
- FBAFATDZDUQKNH-UHFFFAOYSA-M iron chloride Chemical compound [Cl-].[Fe] FBAFATDZDUQKNH-UHFFFAOYSA-M 0.000 claims description 5
- 239000011565 manganese chloride Substances 0.000 claims description 5
- 229940099607 manganese chloride Drugs 0.000 claims description 5
- 235000002867 manganese chloride Nutrition 0.000 claims description 5
- 229910001437 manganese ion Inorganic materials 0.000 claims description 5
- 238000002360 preparation method Methods 0.000 claims description 5
- 238000012216 screening Methods 0.000 claims description 5
- 239000006228 supernatant Substances 0.000 claims description 5
- 239000002244 precipitate Substances 0.000 claims description 3
- 239000007789 gas Substances 0.000 claims description 2
- 238000005406 washing Methods 0.000 claims description 2
- 239000007788 liquid Substances 0.000 claims 2
- 239000013039 cover film Substances 0.000 claims 1
- -1 iron ion Chemical class 0.000 claims 1
- 239000002893 slag Substances 0.000 claims 1
- 239000002699 waste material Substances 0.000 abstract description 7
- 239000003344 environmental pollutant Substances 0.000 abstract description 3
- 231100000719 pollutant Toxicity 0.000 abstract description 3
- 229910052751 metal Inorganic materials 0.000 abstract description 2
- 239000002184 metal Substances 0.000 abstract description 2
- 235000013339 cereals Nutrition 0.000 description 12
- 239000010813 municipal solid waste Substances 0.000 description 10
- 239000000243 solution Substances 0.000 description 5
- 239000011259 mixed solution Substances 0.000 description 4
- 239000002912 waste gas Substances 0.000 description 4
- 241000209094 Oryza Species 0.000 description 3
- 235000007164 Oryza sativa Nutrition 0.000 description 3
- 238000010438 heat treatment Methods 0.000 description 3
- 235000009566 rice Nutrition 0.000 description 3
- 239000000126 substance Substances 0.000 description 2
- 235000002918 Fraxinus excelsior Nutrition 0.000 description 1
- 239000002956 ash Substances 0.000 description 1
- 239000003795 chemical substances by application Substances 0.000 description 1
- 238000002485 combustion reaction Methods 0.000 description 1
- 239000002361 compost Substances 0.000 description 1
- 238000005516 engineering process Methods 0.000 description 1
- 239000000463 material Substances 0.000 description 1
- 239000004531 microgranule Substances 0.000 description 1
- 238000004064 recycling Methods 0.000 description 1
- 239000007787 solid Substances 0.000 description 1
- 238000003756 stirring Methods 0.000 description 1
Classifications
-
- F—MECHANICAL ENGINEERING; LIGHTING; HEATING; WEAPONS; BLASTING
- F23—COMBUSTION APPARATUS; COMBUSTION PROCESSES
- F23G—CREMATION FURNACES; CONSUMING WASTE PRODUCTS BY COMBUSTION
- F23G5/00—Incineration of waste; Incinerator constructions; Details, accessories or control therefor
- F23G5/02—Incineration of waste; Incinerator constructions; Details, accessories or control therefor with pretreatment
-
- B—PERFORMING OPERATIONS; TRANSPORTING
- B09—DISPOSAL OF SOLID WASTE; RECLAMATION OF CONTAMINATED SOIL
- B09B—DISPOSAL OF SOLID WASTE NOT OTHERWISE PROVIDED FOR
- B09B3/00—Destroying solid waste or transforming solid waste into something useful or harmless
- B09B3/20—Agglomeration, binding or encapsulation of solid waste
-
- C—CHEMISTRY; METALLURGY
- C05—FERTILISERS; MANUFACTURE THEREOF
- C05F—ORGANIC FERTILISERS NOT COVERED BY SUBCLASSES C05B, C05C, e.g. FERTILISERS FROM WASTE OR REFUSE
- C05F17/00—Preparation of fertilisers characterised by biological or biochemical treatment steps, e.g. composting or fermentation
-
- C—CHEMISTRY; METALLURGY
- C05—FERTILISERS; MANUFACTURE THEREOF
- C05F—ORGANIC FERTILISERS NOT COVERED BY SUBCLASSES C05B, C05C, e.g. FERTILISERS FROM WASTE OR REFUSE
- C05F3/00—Fertilisers from human or animal excrements, e.g. manure
-
- C—CHEMISTRY; METALLURGY
- C05—FERTILISERS; MANUFACTURE THEREOF
- C05G—MIXTURES OF FERTILISERS COVERED INDIVIDUALLY BY DIFFERENT SUBCLASSES OF CLASS C05; MIXTURES OF ONE OR MORE FERTILISERS WITH MATERIALS NOT HAVING A SPECIFIC FERTILISING ACTIVITY, e.g. PESTICIDES, SOIL-CONDITIONERS, WETTING AGENTS; FERTILISERS CHARACTERISED BY THEIR FORM
- C05G3/00—Mixtures of one or more fertilisers with additives not having a specially fertilising activity
-
- F—MECHANICAL ENGINEERING; LIGHTING; HEATING; WEAPONS; BLASTING
- F23—COMBUSTION APPARATUS; COMBUSTION PROCESSES
- F23G—CREMATION FURNACES; CONSUMING WASTE PRODUCTS BY COMBUSTION
- F23G5/00—Incineration of waste; Incinerator constructions; Details, accessories or control therefor
- F23G5/02—Incineration of waste; Incinerator constructions; Details, accessories or control therefor with pretreatment
- F23G5/033—Incineration of waste; Incinerator constructions; Details, accessories or control therefor with pretreatment comminuting or crushing
-
- F—MECHANICAL ENGINEERING; LIGHTING; HEATING; WEAPONS; BLASTING
- F23—COMBUSTION APPARATUS; COMBUSTION PROCESSES
- F23G—CREMATION FURNACES; CONSUMING WASTE PRODUCTS BY COMBUSTION
- F23G2201/00—Pretreatment
- F23G2201/60—Separating
-
- F—MECHANICAL ENGINEERING; LIGHTING; HEATING; WEAPONS; BLASTING
- F23—COMBUSTION APPARATUS; COMBUSTION PROCESSES
- F23G—CREMATION FURNACES; CONSUMING WASTE PRODUCTS BY COMBUSTION
- F23G2201/00—Pretreatment
- F23G2201/60—Separating
- F23G2201/603—Separating recyclable material
-
- F—MECHANICAL ENGINEERING; LIGHTING; HEATING; WEAPONS; BLASTING
- F23—COMBUSTION APPARATUS; COMBUSTION PROCESSES
- F23G—CREMATION FURNACES; CONSUMING WASTE PRODUCTS BY COMBUSTION
- F23G2201/00—Pretreatment
- F23G2201/70—Blending
-
- F—MECHANICAL ENGINEERING; LIGHTING; HEATING; WEAPONS; BLASTING
- F23—COMBUSTION APPARATUS; COMBUSTION PROCESSES
- F23G—CREMATION FURNACES; CONSUMING WASTE PRODUCTS BY COMBUSTION
- F23G2201/00—Pretreatment
- F23G2201/70—Blending
- F23G2201/701—Blending with additives
-
- F—MECHANICAL ENGINEERING; LIGHTING; HEATING; WEAPONS; BLASTING
- F23—COMBUSTION APPARATUS; COMBUSTION PROCESSES
- F23G—CREMATION FURNACES; CONSUMING WASTE PRODUCTS BY COMBUSTION
- F23G2201/00—Pretreatment
- F23G2201/80—Shredding
-
- 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
- Y02E20/00—Combustion technologies with mitigation potential
- Y02E20/12—Heat utilisation in combustion or incineration of waste
-
- 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
- Y02W30/40—Bio-organic fraction processing; Production of fertilisers from the organic fraction of waste or refuse
Landscapes
- Engineering & Computer Science (AREA)
- Chemical & Material Sciences (AREA)
- Organic Chemistry (AREA)
- Mechanical Engineering (AREA)
- Life Sciences & Earth Sciences (AREA)
- General Engineering & Computer Science (AREA)
- Health & Medical Sciences (AREA)
- Pest Control & Pesticides (AREA)
- Environmental & Geological Engineering (AREA)
- Biochemistry (AREA)
- Biotechnology (AREA)
- Chemical Kinetics & Catalysis (AREA)
- General Chemical & Material Sciences (AREA)
- Microbiology (AREA)
- Molecular Biology (AREA)
- Fertilizers (AREA)
- Processing Of Solid Wastes (AREA)
Abstract
The invention belongs to technical field of waste treatment, the specifically preprocess method before one way of life waste incineration, step is as follows: carry out house refuse tearing up, after broken bag processes, filter out metallics and reclaim sale, remaining refuse classification is organic waste and inorganic refuse, organic waste is used for making fertilizer after harmless treatment, for burning electricity generation after mixing with coal grain after inorganic refuse pulverizing.Categorized consumer waste is recoverable metal, inorganic refuse and organic waste several types by the method for the present invention by categorized consumer waste, and then use different processing modes, metallics can be recycled, the fertilizer that fertilizer efficiency is good can also be prepared, being applied individually to burn additionally due to isolated inorganic refuse, the calorific value of burning is higher, it is less to burn the pollutant produced.
Description
Technical field
The present invention relates to technical field of waste treatment, having is the preprocess method before one way of life waste incineration.
Background technology
Trash processing way can be generally divided into the several ways such as health burning, burning, compost.Waste incineration, or claim rubbish
Rubbish incinerates, and is the method for a kind of refuse process, by organic substance in incinerating waste material, to reduce Waste volume.Burn and other
High temperature refuse disposal system, is all referred to as " heat treatment ".Can convert garbage into as ashes, waste gas and heating power when incinerating rubbish.Ash
Cinder is made up of the inorganic substances in refuse mostly, generally presents with forms such as the microgranules in solid and waste gas.Waste gas is being discharged into
Before in air, needing to remove wherein dusty gas and microgranule, remaining residue is then for landfill.In some situation, incinerate rubbish
Heat energy produced by rubbish can be used for generating electricity, heating.But waste incineration also has operating cost high, and incinerating combustion value is low, takes in waste gas
Carry the shortcomings such as a large amount of pollutant.So carrying out rational pretreatment before waste incineration, it is possible to effectively reduce its harm and reduce
Burn cost.
Summary of the invention
The technical problem to be solved in the present invention is to provide the preprocess method before one way of life waste incineration, to reduce rubbish
Burn the harm produced.
For solve above-mentioned technical problem, the present invention by the following technical solutions:
Preprocess method before one way of life waste incineration, be carry out house refuse tearing up, after broken bag processes, screening
Going out metallics and reclaim sale, remaining refuse classification is organic waste and inorganic refuse, and organic waste is after harmless treatment
For making fertilizer, for burning electricity generation after mixing with coal grain after inorganic refuse pulverizing.
Further improvement as technique scheme:
The method of described screening is preferably electromagnetism screening.
The process that described harmless treatment processes is: is put into by organic waste in the water of its weight 2~3 times, regulates pH value
Regulation is to 9~11, and continuous aeration processes 12~24 hours, is stirred continuously organic waste, then filters in aeration process, and filtering residue is used
In making fertilizer, filtrate puts into the heavy metal scavenger of its weight 0.1%~1%, under conditions of being stirred continuously react 30~
60min, is subsequently adding flocculant flocculation sediment, and gained supernatant is reused for carrying out mixed processing with new organic waste.
Wherein, the preparation process of described heavy metal scavenger is: add iron chloride, aluminum chloride and manganese chloride, system in water
Iron concentration be 0.5~1mol/L, aluminium ion concentration be 0.8~1.2mol/L, manganese ion concentration be 0.1~0.5mol/L
Mixed solution, in the case of being stirred continuously, add sodium hydroxide solution regulation to pH value be 7~8, stand clarification after take heavy
Form sediment, after washing precipitate 3~5 times with water, be dried and be crushed to 80~120 mesh,.
Described make fertilizer process be: by gained filtering residue, agricultural crop straw and cattle manure mixing pile 100~150 centimetres
High stockpile, spreads last layer Testa oryzae, then overlay film at stockpile outer layer, and the temperature controlling fermentation is 60~70 DEG C, and carbon-nitrogen ratio is≤
20, after fermenting 10~20 days, after mixing homogeneously, obtain fertilizer with copper sulfate;Filtering residue after deodorization process, agricultural crop straw, cattle
The weight ratio of excrement, Testa oryzae and copper sulfate is 30~50:50~80:10~30:5~15:1~5.
Wherein, the weight ratio of filtering residue, agricultural crop straw, cattle manure, Testa oryzae and copper sulfate after described deodorization processes is preferably
40:65:20:12:3。
Described inorganic refuse mixes with the coal grain that particle diameter is 10~20mm after being ground into the granule of particle diameter 1~10mm,
Inorganic refuse is 1:0.05~0.2 with the weight ratio of coal grain.
The invention have the benefit that
The method step of the present invention is simple and easy to control, is recoverable metal, inorganic refuse and organic rubbish by categorized consumer waste
Rubbish several types, and then use different processing modes, metallics can be recycled, moreover it is possible to prepared heavy metal free pollution,
The fertilizer that fertilizer efficiency is good, is applied individually to burn additionally due to isolated inorganic refuse, and the calorific value of burning is higher, burn generation
Pollutant are less, it is possible to realize the recycling of house refuse and reduce the purpose burning harm.
Detailed description of the invention
Below in conjunction with specific embodiment for instruction and explanation of the present invention.
Embodiment 1
Preprocess method before one way of life waste incineration, carries out house refuse tearing up, after broken bag processes, filters out
Metallics reclaims to be sold, and remaining refuse classification is organic waste and inorganic refuse, and organic waste is used after harmless treatment
In making fertilizer, for burning electricity generation after mixing with coal grain after inorganic refuse pulverizing.
The process that described harmless treatment processes is: put into by organic waste in the water of its weight 2.5 times, and regulation pH value is adjusted
Joint is to 10, and continuous aeration processes 18 hours, is stirred continuously organic waste, then filters in aeration process, and filtering residue is used for making fertilizer
Material, filtrate puts into the heavy metal scavenger of its weight 0.5%, reacts 50min, be subsequently adding flocculation under conditions of being stirred continuously
Agent flocculation sediment, gained supernatant is reused for carrying out mixed processing with new organic waste.
Wherein, the preparation process of described heavy metal scavenger is: add iron chloride, aluminum chloride and manganese chloride, system in water
Iron concentration be 0.8mol/L, aluminium ion concentration be 0.9mol/L, manganese ion concentration be the mixed solution of 0.4mol/L,
In the case of being stirred continuously, adding sodium hydroxide solution regulation is 8 to pH value, takes precipitation, wash precipitation with water after standing clarification
After thing 4 times, it is dried and is crushed to 100 mesh,.
Described make fertilizer process be: by gained filtering residue, agricultural crop straw and cattle manure mixing pile 100~150 centimetres
High stockpile, spreads last layer Testa oryzae, then overlay film at stockpile outer layer, and the temperature controlling fermentation is 60~70 DEG C, and carbon-nitrogen ratio is≤
20, after fermenting 15 days, after mixing homogeneously, obtain fertilizer with copper sulfate;Filtering residue after deodorization process, agricultural crop straw, cattle manure, rice
The weight ratio of bran and copper sulfate is 40:65:20:12:3.
Described inorganic refuse mixes with the coal grain that particle diameter is 10~20mm after being ground into the granule of particle diameter 1~10mm,
Inorganic refuse is 1:0.1 with the weight ratio of coal grain.
Embodiment 2
Preprocess method before one way of life waste incineration, carries out house refuse tearing up, after broken bag processes, filters out
Metallics reclaims to be sold, and remaining refuse classification is organic waste and inorganic refuse, and organic waste is used after harmless treatment
In making fertilizer, for burning electricity generation after mixing with coal grain after inorganic refuse pulverizing.
The process that described harmless treatment processes is: put into by organic waste in the water of its weight 2 times, regulation pH value regulation
To 9, continuous aeration processes 24 hours, is stirred continuously organic waste, then filters in aeration process, and filtering residue is used for making fertilizer,
Filtrate puts into the heavy metal scavenger of its weight 1%, reacts 30min under conditions of being stirred continuously, and is subsequently adding flocculant wadding
Retrogradation is formed sediment, and gained supernatant is reused for carrying out mixed processing with new organic waste.
Wherein, the preparation process of described heavy metal scavenger is: add iron chloride, aluminum chloride and manganese chloride, system in water
Iron concentration be 0.5mol/L, aluminium ion concentration be 1.2mol/L, manganese ion concentration be the mixed solution of 0.5mol/L,
In the case of being stirred continuously, adding sodium hydroxide solution regulation is 7 to pH value, takes precipitation, wash precipitation with water after standing clarification
After thing 3 times, it is dried and is crushed to 120 mesh,.
Described make fertilizer process be: by gained filtering residue, agricultural crop straw and cattle manure mixing pile 100~150 centimetres
High stockpile, spreads last layer Testa oryzae, then overlay film at stockpile outer layer, and the temperature controlling fermentation is 60~70 DEG C, and carbon-nitrogen ratio is≤
20, after fermenting 20 days, after mixing homogeneously, obtain fertilizer with copper sulfate;Filtering residue after deodorization process, agricultural crop straw, cattle manure, rice
The weight ratio of bran and copper sulfate is 30:50:30:15:1.
Described inorganic refuse mixes with the coal grain that particle diameter is 10~20mm after being ground into the granule of particle diameter 1~10mm,
Inorganic refuse is 1:0.05 with the weight ratio of coal grain.
Embodiment 3
Preprocess method before one way of life waste incineration, carries out house refuse tearing up, after broken bag processes, filters out
Metallics reclaims to be sold, and remaining refuse classification is organic waste and inorganic refuse, and organic waste is used after harmless treatment
In making fertilizer, for burning electricity generation after mixing with coal grain after inorganic refuse pulverizing.
The process that described harmless treatment processes is: put into by organic waste in the water of its weight 3 times, regulation pH value regulation
To 11, continuous aeration processes 12 hours, is stirred continuously organic waste, then filters in aeration process, and filtering residue is used for making fertilizer,
Filtrate puts into the heavy metal scavenger of its weight 0.1%, reacts 60min, be subsequently adding flocculant under conditions of being stirred continuously
Flocculation sediment, gained supernatant is reused for carrying out mixed processing with new organic waste.
Wherein, the preparation process of described heavy metal scavenger is: add iron chloride, aluminum chloride and manganese chloride, system in water
Iron concentration be 1mol/L, aluminium ion concentration be 0.8mol/L, manganese ion concentration be the mixed solution of 0.1mol/L, not
In the case of disconnected stirring, adding sodium hydroxide solution regulation is 8 to pH value, takes precipitation, wash precipitate 5 with water after standing clarification
After secondary, it be dried and be crushed to 80 mesh,.
Described make fertilizer process be: by gained filtering residue, agricultural crop straw and cattle manure mixing pile 100~150 centimetres
High stockpile, spreads last layer Testa oryzae, then overlay film at stockpile outer layer, and the temperature controlling fermentation is 60~70 DEG C, and carbon-nitrogen ratio is≤
20, after fermenting 10 days, after mixing homogeneously, obtain fertilizer with copper sulfate;Filtering residue after deodorization process, agricultural crop straw, cattle manure, rice
The weight ratio of bran and copper sulfate is 50:80:10:5:5.
Described inorganic refuse mixes with the coal grain that particle diameter is 10~20mm after being ground into the granule of particle diameter 1~10mm,
Inorganic refuse is 1:0.2 with the weight ratio of coal grain.
Claims (6)
1. the preprocess method before one way of life waste incineration, it is characterised in that carry out house refuse tearing up, broken bag processes it
After, filtering out metallics and reclaim sale, remaining refuse classification is organic waste and inorganic refuse, and organic waste is through innoxious
It is used for making fertilizer after process, for burning electricity generation after mixing with coal grain after inorganic refuse pulverizing.
Preprocess method the most according to claim 1, it is characterised in that the method for described screening is electromagnetism screening.
Preprocess method the most according to claim 1, it is characterised in that the process that described harmless treatment processes is: will
Organic waste puts in the water of its weight 2~3 times, and regulation pH value regulates to 9~11, and continuous aeration processes 12~24 hours, exposes
Being stirred continuously organic waste during gas, then filter, filtering residue is used for making fertilizer, and filtrate puts into its weight 0.1%~1%
Heavy metal scavenger, reacts 30~60min under conditions of being stirred continuously, is subsequently adding flocculant flocculation sediment, gained supernatant
Liquid is reused for carrying out mixed processing with new organic waste;
The preparation process of described heavy metal scavenger is: adds iron chloride, aluminum chloride and manganese chloride in water, prepares iron ion dense
Degree is 0.5~1mol/L, aluminium ion concentration is 0.8~1.2mol/L, manganese ion concentration be 0.1~0.5mol/L mixing molten
Liquid, in the case of being stirred continuously, adding sodium hydroxide solution regulation is 7~8 to pH value, takes precipitation, use water after standing clarification
After washing precipitate 3~5 times, it is dried and is crushed to 80~120 mesh,.
Preprocess method the most according to claim 3, it is characterised in that described in make the process of fertilizer and be: gained is filtered
Slag, agricultural crop straw and cattle manure mixing pile 100~150 centimetres of high stockpiles, spread last layer Testa oryzae at stockpile outer layer, then cover
Film, the temperature controlling fermentation is 60~70 DEG C, and carbon-nitrogen ratio is≤20, after fermenting 10~20 days, after mixing homogeneously with copper sulfate
To fertilizer;The weight ratio of filtering residue, agricultural crop straw, cattle manure, Testa oryzae and copper sulfate after deodorization process is 30~50:50~80:
10~30:5~15:1~5.
Preprocess method the most according to claim 4, it is characterised in that: the filtering residue after described deodorization process, crops straw
The weight ratio of stalk, cattle manure, Testa oryzae and copper sulfate is 40:65:20:12:3.
Preprocess method the most according to claim 1, it is characterised in that: described inorganic refuse is ground into particle diameter 1~10mm
Granule after mix with the coal grain that particle diameter is 10~20mm, the weight ratio of inorganic refuse and coal grain is 1:0.05~0.2.
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Cited By (2)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
CN106824984A (en) * | 2017-01-12 | 2017-06-13 | 湖南万容科技股份有限公司 | A kind of life refuse processing method |
CN108114968A (en) * | 2017-12-21 | 2018-06-05 | 杨恒武 | A kind of garbage classification processing method |
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CN1177525A (en) * | 1996-09-23 | 1998-04-01 | 中国科学院成都生物研究所 | Process for treatment of organic garbage of city |
CN1442242A (en) * | 2002-09-19 | 2003-09-17 | 齐继红 | City life garbage fast and harmless comprehensive treatment method |
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CN104801528A (en) * | 2014-01-28 | 2015-07-29 | 常州大学 | Domestic waste organic treatment method |
CN105084865A (en) * | 2014-05-08 | 2015-11-25 | 闵建华 | Process for sintering common bricks by using fresh municipal domestic waste |
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CN102701711A (en) * | 2012-06-27 | 2012-10-03 | 刘梁 | Sintered brick and manufacturing method thereof |
CN104591691A (en) * | 2013-10-30 | 2015-05-06 | 徐小芹 | Technology for firing common bricks from fresh municipal domestic waste |
CN104801528A (en) * | 2014-01-28 | 2015-07-29 | 常州大学 | Domestic waste organic treatment method |
CN105084865A (en) * | 2014-05-08 | 2015-11-25 | 闵建华 | Process for sintering common bricks by using fresh municipal domestic waste |
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CN106824984A (en) * | 2017-01-12 | 2017-06-13 | 湖南万容科技股份有限公司 | A kind of life refuse processing method |
CN108114968A (en) * | 2017-12-21 | 2018-06-05 | 杨恒武 | A kind of garbage classification processing method |
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