CN106116640A - The method of comprehensive utilization of one way of life rubbish - Google Patents
The method of comprehensive utilization of one way of life rubbish Download PDFInfo
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- CN106116640A CN106116640A CN201610481671.3A CN201610481671A CN106116640A CN 106116640 A CN106116640 A CN 106116640A CN 201610481671 A CN201610481671 A CN 201610481671A CN 106116640 A CN106116640 A CN 106116640A
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- C—CHEMISTRY; METALLURGY
- C04—CEMENTS; CONCRETE; ARTIFICIAL STONE; CERAMICS; REFRACTORIES
- C04B—LIME, MAGNESIA; SLAG; CEMENTS; COMPOSITIONS THEREOF, e.g. MORTARS, CONCRETE OR LIKE BUILDING MATERIALS; ARTIFICIAL STONE; CERAMICS; REFRACTORIES; TREATMENT OF NATURAL STONE
- C04B38/00—Porous mortars, concrete, artificial stone or ceramic ware; Preparation thereof
- C04B38/06—Porous mortars, concrete, artificial stone or ceramic ware; Preparation thereof by burning-out added substances by burning natural expanding materials or by sublimating or melting out added substances
- C04B38/063—Preparing or treating the raw materials individually or as batches
- C04B38/0635—Compounding ingredients
- C04B38/0645—Burnable, meltable, sublimable materials
- C04B38/068—Carbonaceous materials, e.g. coal, carbon, graphite, hydrocarbons
-
- C—CHEMISTRY; METALLURGY
- C02—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F9/00—Multistage treatment of water, waste water or sewage
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- C—CHEMISTRY; METALLURGY
- C04—CEMENTS; CONCRETE; ARTIFICIAL STONE; CERAMICS; REFRACTORIES
- C04B—LIME, MAGNESIA; SLAG; CEMENTS; COMPOSITIONS THEREOF, e.g. MORTARS, CONCRETE OR LIKE BUILDING MATERIALS; ARTIFICIAL STONE; CERAMICS; REFRACTORIES; TREATMENT OF NATURAL STONE
- C04B33/00—Clay-wares
- C04B33/02—Preparing or treating the raw materials individually or as batches
- C04B33/13—Compounding ingredients
- C04B33/132—Waste materials; Refuse; Residues
- C04B33/1324—Recycled material, e.g. tile dust, stone waste, spent refractory material
-
- C—CHEMISTRY; METALLURGY
- C05—FERTILISERS; MANUFACTURE THEREOF
- C05D—INORGANIC FERTILISERS NOT COVERED BY SUBCLASSES C05B, C05C; FERTILISERS PRODUCING CARBON DIOXIDE
- C05D9/00—Other inorganic fertilisers
- C05D9/02—Other inorganic fertilisers containing trace elements
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- 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
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- C—CHEMISTRY; METALLURGY
- C10—PETROLEUM, GAS OR COKE INDUSTRIES; TECHNICAL GASES CONTAINING CARBON MONOXIDE; FUELS; LUBRICANTS; PEAT
- C10L—FUELS NOT OTHERWISE PROVIDED FOR; NATURAL GAS; SYNTHETIC NATURAL GAS OBTAINED BY PROCESSES NOT COVERED BY SUBCLASSES C10G, C10K; LIQUEFIED PETROLEUM GAS; ADDING MATERIALS TO FUELS OR FIRES TO REDUCE SMOKE OR UNDESIRABLE DEPOSITS OR TO FACILITATE SOOT REMOVAL; FIRELIGHTERS
- C10L5/00—Solid fuels
- C10L5/02—Solid fuels such as briquettes consisting mainly of carbonaceous materials of mineral or non-mineral origin
- C10L5/04—Raw material of mineral origin to be used; Pretreatment thereof
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- C—CHEMISTRY; METALLURGY
- C10—PETROLEUM, GAS OR COKE INDUSTRIES; TECHNICAL GASES CONTAINING CARBON MONOXIDE; FUELS; LUBRICANTS; PEAT
- C10L—FUELS NOT OTHERWISE PROVIDED FOR; NATURAL GAS; SYNTHETIC NATURAL GAS OBTAINED BY PROCESSES NOT COVERED BY SUBCLASSES C10G, C10K; LIQUEFIED PETROLEUM GAS; ADDING MATERIALS TO FUELS OR FIRES TO REDUCE SMOKE OR UNDESIRABLE DEPOSITS OR TO FACILITATE SOOT REMOVAL; FIRELIGHTERS
- C10L5/00—Solid fuels
- C10L5/40—Solid fuels essentially based on materials of non-mineral origin
- C10L5/46—Solid fuels essentially based on materials of non-mineral origin on sewage, house, or town refuse
-
- C—CHEMISTRY; METALLURGY
- C02—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F1/00—Treatment of water, waste water, or sewage
- C02F1/52—Treatment of water, waste water, or sewage by flocculation or precipitation of suspended impurities
-
- C—CHEMISTRY; METALLURGY
- C02—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F1/00—Treatment of water, waste water, or sewage
- C02F1/58—Treatment of water, waste water, or sewage by removing specified dissolved compounds
- C02F1/62—Heavy metal compounds
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- C—CHEMISTRY; METALLURGY
- C02—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F2101/00—Nature of the contaminant
- C02F2101/10—Inorganic compounds
- C02F2101/20—Heavy metals or heavy metal compounds
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- C—CHEMISTRY; METALLURGY
- C04—CEMENTS; CONCRETE; ARTIFICIAL STONE; CERAMICS; REFRACTORIES
- C04B—LIME, MAGNESIA; SLAG; CEMENTS; COMPOSITIONS THEREOF, e.g. MORTARS, CONCRETE OR LIKE BUILDING MATERIALS; ARTIFICIAL STONE; CERAMICS; REFRACTORIES; TREATMENT OF NATURAL STONE
- C04B2235/00—Aspects relating to ceramic starting mixtures or sintered ceramic products
- C04B2235/02—Composition of constituents of the starting material or of secondary phases of the final product
- C04B2235/30—Constituents and secondary phases not being of a fibrous nature
- C04B2235/34—Non-metal oxides, non-metal mixed oxides, or salts thereof that form the non-metal oxides upon heating, e.g. carbonates, nitrates, (oxy)hydroxides, chlorides
- C04B2235/3427—Silicates other than clay, e.g. water glass
- C04B2235/3436—Alkaline earth metal silicates, e.g. barium silicate
- C04B2235/3454—Calcium silicates, e.g. wollastonite
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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
- 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
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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
- 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
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- Y02P—CLIMATE CHANGE MITIGATION TECHNOLOGIES IN THE PRODUCTION OR PROCESSING OF GOODS
- Y02P40/00—Technologies relating to the processing of minerals
- Y02P40/60—Production of ceramic materials or ceramic elements, e.g. substitution of clay or shale by alternative raw materials, e.g. ashes
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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
- Y02W30/40—Bio-organic fraction processing; Production of fertilisers from the organic fraction of waste or refuse
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Abstract
The invention belongs to technical field of waste treatment, the specifically method of comprehensive utilization of one way of life rubbish, step is as follows: after house refuse electricity consumption magnetic screening goes out metallics recovery, remaining refuse classification is building waste, organic waste and inorganic refuse, building waste is used for making insulating brick, organic waste is used for making fertilizer after harmless treatment, and inorganic refuse carries out being mixed for burning electricity generation with coal grain after pulverizing.Categorized consumer waste is recoverable metal, building waste, inorganic refuse and organic waste several types by the method for the present invention, and then use different processing modes, metallics can be recycled, insulating brick, fertilizer can also be prepared respectively, it is applied individually to burn additionally due to isolated inorganic refuse, the calorific value burned is higher, it is less to burn the pollutant produced, it is possible to realizes the recycling of house refuse and reduces the purpose of environmental hazard.
Description
Technical field
The present invention relates to technical field of waste treatment, having is the method for comprehensive utilization of one way of life rubbish.
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.In a lot of situations, burn
Change heat energy produced by rubbish to can be used for generating electricity, heating.But waste incineration also has operating cost high, and incinerating combustion value is low, waste gas
In carry the shortcomings such as a large amount of pollutant.So carrying out rational pretreatment before waste incineration, recycle its recyclable part
After burn being used for, then can effectively reduce its harm and reduce and burn cost.
Summary of the invention
The technical problem to be solved in the present invention is to provide the method for comprehensive utilization of one way of life rubbish, can realize house refuse
Resource reutilization and reduce its pollution on the environment.
For solve above-mentioned technical problem, the present invention by the following technical solutions:
The method of comprehensive utilization of one way of life rubbish, be house refuse electricity consumption magnetic screening is gone out metallics reclaim after, its
Remaining refuse classification is building waste, organic waste and inorganic refuse, and building waste is used for making insulating brick, and organic waste is through nothing
Evilization is used for making fertilizer after processing, inorganic refuse carries out being mixed for burning electricity generation with coal grain after pulverizing.
Further improvement as technique scheme:
Described building waste makes the process of insulating brick: building waste 1) is ground into the granule of particle diameter 1~5mm, so
Mix with bamboo charcoal, sepiolite powder, wollastonite in powder and foaming agent afterwards, and be mixed into the water of mixture weight 20%~30%, to carry out
Foaming processes;2) by powdered to expanded perlite, calcined kaolin and glue powder polyphenyl particle co-grinding, then with step 1) obtain
The product mixing obtained, and it is mixed into the water of mixture weight 10%~15%, then make adobe;3) adobe is placed in heating environment
In, first it being warming up to 800 DEG C from from room temperature, the heating-up time is 30~60 minutes;It is warming up to 1000 DEG C again, the heating-up time from 800 DEG C
It is 60~90 minutes, and keeps the temperature 6 of 1000 DEG C~8 hours;Then being warming up to 1150 DEG C from 1000 DEG C, the heating-up time is 30
~60 minutes;Finally it is naturally cooling to room temperature, can be prepared by insulating brick.
Wherein, the weight portion of involved material is: building waste 50~60 parts, bamboo charcoal 5~10 parts, sepiolite powder 10~15
Part, wollastonite in powder 10~15 parts, foaming agent 5~10 parts, expanded perlite 8~13 parts, calcined kaolin 5~10 parts and rubber powder gather
Benzene granule 1~5 parts.
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.
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
Categorized consumer waste is that recoverable metal, building waste, inorganic refuse and organic waste are several by the method for the present invention
Type, and then use different processing modes, metallics can be recycled, moreover it is possible to prepare insulating brick, fertilizer respectively, this
Outward being applied individually to burn owing to having isolated inorganic refuse, the calorific value of burning is higher, it is less to burn the pollutant produced, it is possible to
Realize the recycling of house refuse and reduce the purpose of environmental hazard.
Detailed description of the invention
Below in conjunction with specific embodiment for instruction and explanation of the present invention.
Embodiment 1
The method of comprehensive utilization of one way of life rubbish, be house refuse electricity consumption magnetic screening is gone out metallics reclaim after, its
Remaining refuse classification is building waste, organic waste and inorganic refuse, and building waste is used for making insulating brick, and organic waste is through nothing
Evilization is used for making fertilizer after processing, inorganic refuse carries out being mixed for burning electricity generation with coal grain after pulverizing.
Described building waste makes the process of insulating brick: building waste 1) is ground into the granule of particle diameter 1~5mm, so
Mix with bamboo charcoal, sepiolite powder, wollastonite in powder and foaming agent afterwards, and be mixed into the water of mixture weight 20%, to carry out at foaming
Reason;2) by powdered to expanded perlite, calcined kaolin and glue powder polyphenyl particle co-grinding, then with step 1) product that obtains
Thing mixes, and is mixed into the water of mixture weight 13%, then makes adobe;3) adobe is placed in heating environment, first from from often
Temperature is warming up to 800 DEG C, and the heating-up time is 60 minutes;Being warming up to 1000 DEG C from 800 DEG C again, the heating-up time is 60 minutes, and keeps
The temperature of 1000 DEG C 7 hours;Then being warming up to 1150 DEG C from 1000 DEG C, the heating-up time is 60 minutes;Finally it is naturally cooling to room
Temperature, can be prepared by insulating brick.The weight portion of involved material is: building waste 50 parts, bamboo charcoal 8 parts, sepiolite powder 15 parts, silicon ash
Stone powder 10 parts, foaming agent 8 parts, expanded perlite 13 parts, calcined kaolin 5 parts and glue powder polyphenyl particle 3 parts.
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.The system of described heavy metal scavenger
Standby process is: adding iron chloride, aluminum chloride and manganese chloride in water, prepared iron concentration is 0.8mol/L, aluminium ion concentration
It is the mixed solution of 0.4mol/L for 0.9mol/L, manganese ion concentration, in the case of being stirred continuously, adds sodium hydroxide solution
Regulating to pH value is 8, takes precipitation after standing clarification, after washing precipitate 4 times with water, 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
The method of comprehensive utilization of one way of life rubbish, carries out house refuse tearing up, after broken bag processes, filters out metal
Material reclaims to be sold, and remaining refuse classification is organic waste and inorganic refuse, and organic waste is used for making after harmless treatment
Become fertilizer, for burning electricity generation after mixing with coal grain after inorganic refuse pulverizing.
Described building waste makes the process of insulating brick: building waste 1) is ground into the granule of particle diameter 1~5mm, so
Mix with bamboo charcoal, sepiolite powder, wollastonite in powder and foaming agent afterwards, and be mixed into the water of mixture weight 25%, to carry out at foaming
Reason;2) by powdered to expanded perlite, calcined kaolin and glue powder polyphenyl particle co-grinding, then with step 1) product that obtains
Thing mixes, and is mixed into the water of mixture weight 15%, then makes adobe;3) adobe is placed in heating environment, first from from often
Temperature is warming up to 800 DEG C, and the heating-up time is 30 minutes;Being warming up to 1000 DEG C from 800 DEG C again, the heating-up time is 80 minutes, and keeps
The temperature of 1000 DEG C 8 hours;Then being warming up to 1150 DEG C from 1000 DEG C, the heating-up time is 30 minutes;Finally it is naturally cooling to room
Temperature, can be prepared by insulating brick.The weight portion of involved material is: building waste 55 parts, bamboo charcoal 10 parts, sepiolite powder 10 parts, silicon
Limestone flour 13 parts, foaming agent 10 parts, expanded perlite 8 parts, calcined kaolin 8 parts and glue powder polyphenyl particle 5 parts.
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.The preparation of described heavy metal scavenger
Cheng Wei: adding iron chloride, aluminum chloride and manganese chloride in water, prepared iron concentration is 0.5mol/L, aluminium ion concentration is
1.2mol/L, manganese ion concentration are the mixed solution of 0.5mol/L, in the case of being stirred continuously, add sodium hydroxide solution and adjust
Saving to pH value is 7, takes precipitation after standing clarification, after washing precipitate 3 times with water, 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
The method of comprehensive utilization of one way of life rubbish, carries out house refuse tearing up, after broken bag processes, filters out metal
Material reclaims to be sold, and remaining refuse classification is organic waste and inorganic refuse, and organic waste is used for making after harmless treatment
Become fertilizer, for burning electricity generation after mixing with coal grain after inorganic refuse pulverizing.
Described building waste makes the process of insulating brick: building waste 1) is ground into the granule of particle diameter 1~5mm, so
Mix with bamboo charcoal, sepiolite powder, wollastonite in powder and foaming agent afterwards, and be mixed into the water of mixture weight 30%, to carry out at foaming
Reason;2) by powdered to expanded perlite, calcined kaolin and glue powder polyphenyl particle co-grinding, then with step 1) product that obtains
Thing mixes, and is mixed into the water of mixture weight 10%, then makes adobe;3) adobe is placed in heating environment, first from from often
Temperature is warming up to 800 DEG C, and the heating-up time is 50 minutes;Being warming up to 1000 DEG C from 800 DEG C again, the heating-up time is 90 minutes, and keeps
The temperature of 1000 DEG C 6 hours;Then being warming up to 1150 DEG C from 1000 DEG C, the heating-up time is 40 minutes;Finally it is naturally cooling to room
Temperature, can be prepared by insulating brick.The weight portion of involved material is: building waste 60 parts, bamboo charcoal 5 parts, sepiolite powder 12 parts, silicon ash
Stone powder 15 parts, foaming agent 5 parts, expanded perlite 11 parts, calcined kaolin 10 parts and glue powder polyphenyl particle 1 part.
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.The preparation of described heavy metal scavenger
Process is: adding iron chloride, aluminum chloride and manganese chloride in water, prepared iron concentration is 1mol/L, aluminium ion concentration is
0.8mol/L, manganese ion concentration are the mixed solution of 0.1mol/L, in the case of being stirred continuously, add sodium hydroxide solution and adjust
Saving to pH value is 8, takes precipitation after standing clarification, after washing precipitate 5 times with water, is dried and is 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 (5)
1. the method for comprehensive utilization of one way of life rubbish, it is characterised in that house refuse electricity consumption magnetic screening is gone out metallics and returns
After receipts, remaining refuse classification is building waste, organic waste and inorganic refuse, and building waste is used for making insulating brick, organic rubbish
Rubbish is used for making fertilizer after harmless treatment, and inorganic refuse carries out being mixed for burning electricity generation with coal grain after pulverizing.
Method of comprehensive utilization the most according to claim 1, it is characterised in that described building waste makes the process of insulating brick
For: 1) building waste is ground into the granule of particle diameter 1~5mm, then mixed with bamboo charcoal, sepiolite powder, wollastonite in powder and foaming agent
Close, and be mixed into the water of mixture weight 20%~30%, to carry out foaming process;2) by expanded perlite, calcined kaolin and
Glue powder polyphenyl particle co-grinding is powdered, then with step 1) product that obtains mixes, and be mixed into mixture weight 10%~
The water of 15%, then makes adobe;3) adobe being placed in heating environment, be first warming up to 800 DEG C from from room temperature, the heating-up time is
30~60 minutes;Being warming up to 1000 DEG C from 800 DEG C again, the heating-up time is 60~90 minutes, and keeps the temperature 6~8 of 1000 DEG C
Hour;Then being warming up to 1150 DEG C from 1000 DEG C, the heating-up time is 30~60 minutes;Finally it is naturally cooling to room temperature, can make
Obtain insulating brick;
The weight portion of involved material is: building waste 50~60 parts, bamboo charcoal 5~10 parts, sepiolite powder 10~15 parts, wollastonite
Powder 10~15 parts, foaming agent 5~10 parts, expanded perlite 8~13 parts, calcined kaolin 5~10 parts and glue powder polyphenyl particle 1~
5 parts.
Method of comprehensive utilization the most according to claim 1, it is characterised in that the process that described harmless treatment processes is:
Being put into by organic waste in the water of its weight 2~3 times, regulation pH value regulates to 9~11, and continuous aeration processes 12~24 hours,
Being stirred continuously organic waste in aeration process, then filter, filtering residue is used for making fertilizer, and filtrate puts into its weight 0.1%~1%
Heavy metal scavenger, under conditions of being stirred continuously react 30~60min, be subsequently adding flocculant flocculation sediment, on gained
Clear 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,.
Method of comprehensive utilization the most according to claim 3, it is characterised in that described in make the process of fertilizer and be: by gained
Filtering residue, agricultural crop straw and cattle manure mixing pile 100~150 centimetres of high stockpiles, spread last layer Testa oryzae at stockpile outer layer, then
Overlay 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
Obtain fertilizer;Deodorization process after the weight ratio of filtering residue, agricultural crop straw, cattle manure, Testa oryzae and copper sulfate be 30~50:50~
80:10~30:5~15:1~5.
Method of comprehensive utilization the most according to claim 1, it is characterised in that: described inorganic refuse be ground into particle diameter 1~
Mix with the coal grain that particle diameter is 10~20mm after the granule of 10mm, the weight ratio of inorganic refuse and coal grain be 1:0.05~
0.2。
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Cited By (4)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
CN108114968A (en) * | 2017-12-21 | 2018-06-05 | 杨恒武 | A kind of garbage classification processing method |
CN108996986A (en) * | 2018-07-05 | 2018-12-14 | 安徽建邦建材有限公司 | A kind of resistance to resistance to compression construction wall thermal insulation material preparation method |
CN109385317A (en) * | 2018-11-26 | 2019-02-26 | 安徽吉露科技有限公司 | A kind of preparation method of new energy materials |
CN110257124A (en) * | 2018-12-29 | 2019-09-20 | 王�锋 | The method of rubbish biomass burning block and preparation method thereof and systems of distributed heating systems and power generation |
Citations (4)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
CN1329950A (en) * | 2001-08-06 | 2002-01-09 | 北京华联达环保能源技术开发有限责任公司 | Process for comprehensive utilization of life garbage in urban area |
CN102515691A (en) * | 2011-12-26 | 2012-06-27 | 四川白塔新联兴陶瓷集团有限责任公司 | Light environment-friendly brick prepared from waste brick powder, and preparation method for light environment-friendly brick |
CN105562425A (en) * | 2016-02-23 | 2016-05-11 | 广西鸿生源环保股份有限公司 | Recycling treatment process and system for household garbage |
CN105618457A (en) * | 2015-12-25 | 2016-06-01 | 安徽继宏环保科技有限公司 | Disposal system for urban domestic waste |
-
2016
- 2016-06-24 CN CN201610481671.3A patent/CN106116640A/en active Pending
Patent Citations (4)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
CN1329950A (en) * | 2001-08-06 | 2002-01-09 | 北京华联达环保能源技术开发有限责任公司 | Process for comprehensive utilization of life garbage in urban area |
CN102515691A (en) * | 2011-12-26 | 2012-06-27 | 四川白塔新联兴陶瓷集团有限责任公司 | Light environment-friendly brick prepared from waste brick powder, and preparation method for light environment-friendly brick |
CN105618457A (en) * | 2015-12-25 | 2016-06-01 | 安徽继宏环保科技有限公司 | Disposal system for urban domestic waste |
CN105562425A (en) * | 2016-02-23 | 2016-05-11 | 广西鸿生源环保股份有限公司 | Recycling treatment process and system for household garbage |
Non-Patent Citations (1)
Title |
---|
"《现代能源与发电技术》" * |
Cited By (4)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
CN108114968A (en) * | 2017-12-21 | 2018-06-05 | 杨恒武 | A kind of garbage classification processing method |
CN108996986A (en) * | 2018-07-05 | 2018-12-14 | 安徽建邦建材有限公司 | A kind of resistance to resistance to compression construction wall thermal insulation material preparation method |
CN109385317A (en) * | 2018-11-26 | 2019-02-26 | 安徽吉露科技有限公司 | A kind of preparation method of new energy materials |
CN110257124A (en) * | 2018-12-29 | 2019-09-20 | 王�锋 | The method of rubbish biomass burning block and preparation method thereof and systems of distributed heating systems and power generation |
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