CN108484320A - A kind of organic solid waste high-temperature aerobic fermentation processing method - Google Patents
A kind of organic solid waste high-temperature aerobic fermentation processing method Download PDFInfo
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- CN108484320A CN108484320A CN201810318203.3A CN201810318203A CN108484320A CN 108484320 A CN108484320 A CN 108484320A CN 201810318203 A CN201810318203 A CN 201810318203A CN 108484320 A CN108484320 A CN 108484320A
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- Prior art keywords
- pile
- aerobic fermentation
- solid waste
- organic solid
- tunning
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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
- C05F3/00—Fertilisers from human or animal excrements, e.g. manure
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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
- 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
- C05G3/80—Soil conditioners
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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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- Chemical & Material Sciences (AREA)
- Life Sciences & Earth Sciences (AREA)
- Organic Chemistry (AREA)
- Engineering & Computer Science (AREA)
- Pest Control & Pesticides (AREA)
- Health & Medical Sciences (AREA)
- Soil Sciences (AREA)
- Biochemistry (AREA)
- Biotechnology (AREA)
- Chemical Kinetics & Catalysis (AREA)
- General Chemical & Material Sciences (AREA)
- Microbiology (AREA)
- Molecular Biology (AREA)
- Processing Of Solid Wastes (AREA)
- Fertilizers (AREA)
Abstract
Present invention aims at a kind of organic solid waste high-temperature aerobic fermentation processing method is provided, static pile composting technology can be solved the problems, such as.Implementation steps:A) batch mixing:Organic solid waste and conditioning material are mixed in proportion to 0.25 0.75t/m of bulk density3;B) cloth:Tunning oversize is taped against a pile top layer by mixed material cloth to pile middle layer by tunning oversize cloth to pile bottom;C) overlay film:Cover proofed breathable fabric, isolating bar pile and atmospheric environment;D) aerobic fermentation:Pass through bottom aerating system intermittent aerating;E) it sieves:After 7 42 days, coating is rolled, tunning is moved into adjustable screening system, screenings is transported outward as product, and oversize returns to cloth material process and participates in next period.Under the premise of the present invention keeps static bar buttress formula compost advantage, technique is optimized, and have both dynamic compost feature, improve treatment effeciency, reduced to realize that floor space, investment are synchronous with operating cost.
Description
Technical field
The present invention relates to a kind of organic solid waste high-temperature aerobic fermentation processing methods.More specifically:It is related in processing procedure
In pass through simple batch mixing state modulator, unique pile Reactor structure, aeration pattern, screening control model, covering waterproof
Under breathable fabric environment, the efficient of target material, emission reduction processing are realized;Without turning, realize similar with turning
Effect;And realizing one kind of the regulation and control of practical residence time under the conditions of different compost materials, Various Seasonal, novel to cover waterproof saturating
Gas fabric compost method.
Background technology
Solid waste is the mankind generated during production and life activity it is general no longer there is original value and by
The solid-state or semisolid substance of discarding can be divided into organic solid waste, two class of inoganic solids waste, wherein organic solid by composition
Waste can be divided into 7 kinds of fundamental types again:1. sludge;2. animal wastes;3. crop residues;4. food production waste;5. work
Industry organic waste;6. timber processes waste;7. house refuse.
It is that yield is huge that organic solid waste, which has first common feature,:By 2012 end of the year whole nation urban wastewater treatment firms
Nearly 30,000,000 tons of sludge annual output (equivalent 80% moisture content);State Environmental Protection Administration pollutes feelings in 2002 to scale animal and poultry cultivation
Condition investigation result shows that Chinese festiva feces of livestock and poultry amount is about 1,900,000,000 tons;National agricultural crop straw theoretical resources amount is 8.20 within 2009
Hundred million tons (air-drying, water content 15%);Since nineteen eighty, the domestic waste in China is with the annual growth rate of 8%-10%
Increase, having reached within 2001 1.5 hundred million t, produce are discarded in food production waste, industrial organic wastes, timber processing in addition
It measures huge.
It is that high-temperature aerobic fermentation process is preferably used to handle that organic solid waste, which has second common feature,:For organic solid waste
Harm needs progress minimizing, innoxious, stabilization processes preferably to be adopted since organic matter and moisture are higher in organic solid waste
Individually processing or mixed processing are carried out with high-temperature aerobic fermentation technical finesse.Current all organic solid wastes have high-temperature aerobic fermentation
Case is run, and sludge, animal wastes, agricultural waste material etc. dominate work using high-temperature aerobic fermentation as harmless treatment
Skill.
The principal mode of organic solid waste high-temperature aerobic fermentation processing has slot type, bar buttress formula, container type etc..Earlier industry heap
Fertile system much uses static pile composting technology, because there is such technology investment to save, treatment scale is adjustable, horizontal layout
The features such as flexible, on the U.S., Canada and other places, largely static Windows composting system also remains operational state at present.But due to
A static pile compositing system takes up a large area, climate influences the problems such as big, secondary pollution is not easy to control, the degree of automation is low,
It is restricted in most said conditions application.
Invention content
In view of this, the main purpose of the present invention is to provide a kind of organic solid waste high-temperature aerobic fermentation processing method,
It can solve main problem existing for static pile composting technology.
In order to achieve the above objectives, the technical scheme is that as follows realizing:
A) batch mixing:Organic solid waste is mixed according to a certain percentage with conditioning material to bulk density 0.25-0.75t/m3;
B) cloth:It, later will be among mixed material cloth to pile by tunning oversize cloth to the pile bottom
Layer, then tunning oversize is routed to a pile topmost;
C) overlay film:Upper proofed breathable fabric is covered above pile, and a pile is made to be isolated with atmospheric environment;
D) aerobic fermentation:By being laid on an aerating system for pile bottom in advance according to default monitoring system indication signal to item
Pile intermittent aerating;
E) it sieves:After 7-42 days, proofed breathable fabric is rolled, is moved tunning by method mechanically or manually
It is sieved to adjustable screening system, tunning screenings transports outward recycling, tunning sieve as final products
Upper object returns to cloth material process and participates in next fermentation period.
A kind of the characteristics of organic solid waste high-temperature aerobic fermentation processing method mixing process of the invention be only to organic solid waste and
Conditioning material mixed, control parameter is only bulk density, be different from Traditional compost method to organic solid waste, conditioning material and
Three kinds of materials such as compost product are mixed, and most important control parameter is the indexs such as moisture content, C/N, pH value.
A kind of the characteristics of organic solid waste high-temperature aerobic fermentation processing method cloth process of the invention is to form " sandwich chalk
Power " carton pile Reactor structure, that is, mixed material are in a pile center, and surrounding wraps up tunning oversize;Tunning sieves
Upper object is layed in a pile heap body bottom, and uniform gas distribution effect can be undertaken using its larger porosity;Tunning oversize is laid with
The features such as can utilizing its gap structure and relatively low moisture content at the top of pile heap body, reduces the condensation of proofed breathable fabric lower surface
Water drips the influence to heap body central mixing material.
Above a kind of organic solid waste high-temperature aerobic fermentation processing method pile of the present invention the characteristics of covering proofed breathable fabric
Pile heap body is in supercharging thermal environment when being aeration, also reduces foul smell loss amount in fermentation process.
A kind of the characteristics of organic solid waste high-temperature aerobic fermentation processing method aerobic fermentation process of the invention is aerating system
Start and stop are obtained according to three common result of calculations of parameter such as monitoring system heap temperature, outdoor temperature, aerating system drag overall are preset
It arrives.
A kind of organic solid waste high-temperature aerobic fermentation processing method of the present invention sieves a kind of alternative as turning, aerobic
Fermentation time and tunning screenings ratio are related to material fermentation degree, by adjusting aerobic fermentation time and adjustable knotter screen
The screening ratio of subsystem, realizes the regulation and control of practical residence time under the conditions of different compost materials, Various Seasonal.
The compost product screenings that the present invention obtains is Nutrition Soil, before every pollutant index meets relevant criterion
It puts, can be used as soil agent modifying agent, can be used for urban lawn, flower planting, afforestation, deserta, green barren hill etc.
Aspect also can need to be added a certain amount of synergy inorganic fertilizer according to soil regime and peasant, then be made after sufficiently mixing
Particle uses after packaging.
Description of the drawings
Attached drawing described herein is used to provide further understanding of the present invention, and is constituted part of this application, this hair
Bright illustrative embodiments and their description do not constitute improper limitations of the present invention, in the accompanying drawings for explaining the present invention:
Attached drawing 1 shows a kind of process flow chart of the embodiment of the present invention.
Attached drawing 2 shows a kind of pile Reactor structure figure of the embodiment of the present invention.
Wherein:1. indicating proofed breathable fabric coating;2. indicating tunning oversize;3. indicating mixed material;④
Indicate aerating system.
Specific implementation mode
It is below with reference to the accompanying drawings and in conjunction with the embodiments, next that the present invention will be described in detail.
As shown in Figure 1, 2, a kind of organic solid waste high-temperature aerobic fermentation processing method is realized as follows:
A) batch mixing:Organic solid waste is mixed according to a certain percentage with conditioning material to bulk density 0.25-0.75t/m3;
B) cloth:It, later will be in 3 cloth of mixed material to pile by 2 cloth of tunning oversize to the pile bottom
Interbed, then tunning oversize 2 is routed to a pile topmost;
C) overlay film:Upper proofed breathable fabric 1 is covered above pile, and a pile is made to be isolated with atmospheric environment;
D) aerobic fermentation:By be laid in advance the aerating system of pile bottom 4 according to default monitoring system indication signal to
Pile intermittent aerating;
E) it sieves:After 7-42 days, proofed breathable fabric 1 is rolled, is moved tunning by method mechanically or manually
It moves adjustable screening system to be sieved, tunning screenings transports outward recycling, tunning as final products
Oversize 2 returns to cloth material process and participates in next fermentation period.
From the above description, it can be seen that the above embodiment of the present invention achieves that:
Make static bar buttress formula composting technology under the premise of keeping intrinsic advantage, overcoming climate influences big, secondary dirt
The inadequate natural endowments such as not easy to control are contaminated, the adverse effect generated to heap body after covering proofed breathable fabric is overcome, simplifies batch mixing
Process and control require, have the feature required by dynamic turning, improve treatment effeciency, to realize floor space,
Investment is synchronous with operating cost to be reduced.
Obviously, those skilled in the art should be understood that each subsystem of the above-mentioned present invention or each step can be with recruitments
The devices such as journey machinery, conveying equipment, general purpose instrument control system realize that they can be fully integrated in a system, or
Person is integrated in multiple subsystem composition projects respectively.In this way, the present invention is not limited to any specific subsystems to combine.
The above is the preferred embodiments of the present invention, is not intended to restrict the invention, for the technology of this field
For personnel, the invention may be variously modified and varied.All within the spirits and principles of the present invention, any made by repair
Change, equivalent replacement, improvement etc., should all be included in the protection scope of the present invention.
Claims (6)
1. a kind of organic solid waste high-temperature aerobic fermentation processing method provided by the invention includes the following steps:
A) batch mixing:Organic solid waste is mixed according to a certain percentage with conditioning material to bulk density 0.25-0.75t/m3;
B) cloth:By tunning oversize cloth to the pile bottom, later by mixed material cloth to pile middle layer, then
Tunning oversize is routed to a pile topmost;
C) overlay film:Upper proofed breathable fabric is covered above pile, and a pile is made to be isolated with atmospheric environment;
D) aerobic fermentation:By being laid on an aerating system for pile bottom in advance according to default monitoring system indication signal between pile
It has a rest aeration;
E) it sieves:After 7-42 days, proofed breathable fabric is rolled, and tunning is moved to by method mechanically or manually can
It adjusts screening system to be sieved, tunning screenings transports outward recycling, tunning oversize as final products
It returns to cloth material process and participates in next fermentation period.
2. a kind of organic solid waste high-temperature aerobic fermentation processing method according to claim 1, it is characterized in that:Mixing process is only
Organic solid waste and conditioning material are mixed, control parameter is only bulk density.
3. a kind of organic solid waste high-temperature aerobic fermentation processing method according to claim 1, it is characterized in that:Cloth process shape
It is in a pile center at " chocolate cream " pile Reactor structure, that is, mixed material, surrounding wraps up tunning oversize.
4. a kind of organic solid waste high-temperature aerobic fermentation processing method according to claim 1, it is characterized in that:It is covered above pile
Lid proofed breathable fabric, pile heap body is in supercharging thermal environment when aeration, also reduces foul smell loss amount in fermentation process.
5. a kind of organic solid waste high-temperature aerobic fermentation processing method according to claim 1, it is characterized in that:Aerobic fermentation mistake
The start and stop of journey aerating system, it is total according to three parameters such as monitoring system heap temperature, outdoor temperature, aerating system drag overall are preset
It is obtained with result of calculation.
6. a kind of organic solid waste high-temperature aerobic fermentation processing method according to claim 1, it is characterized in that:Screening is used as and turns over
A kind of alternative of heap, aerobic fermentation time and compost product screenings ratio are related to material fermentation degree, by adjusting
The screening ratio of aerobic fermentation time and adjustable screening system are realized and are actually stopped under the conditions of different compost materials, Various Seasonal
Stay the regulation and control of time.
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Cited By (4)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
CN109956634A (en) * | 2019-03-14 | 2019-07-02 | 江苏雷蒙新材料有限公司 | The method for innocent treatment of excess sludge after a kind of organic chemical waste water biochemical treatment |
CN110663715A (en) * | 2019-11-04 | 2020-01-10 | 云峰机械(福建)有限公司 | Homogeneous inflating and foaming machine |
CN113149789A (en) * | 2021-04-07 | 2021-07-23 | 中国科学院西双版纳热带植物园 | Soil conditioner and preparation method thereof |
CN117655091A (en) * | 2023-03-01 | 2024-03-08 | 日照城投环境科技集团有限公司 | Organic solid waste treatment and carbon sink method for mediating land restoration thereof |
Citations (2)
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JP2008214129A (en) * | 2007-03-05 | 2008-09-18 | Hisayuki Kishi | Method and apparatus for fermentation composting treatment |
CN106187336A (en) * | 2016-07-19 | 2016-12-07 | 金发科技股份有限公司 | More than a kind of kitchen, Organic substance aerobic compost builds heaping method |
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2018
- 2018-04-11 CN CN201810318203.3A patent/CN108484320A/en active Pending
Patent Citations (2)
Publication number | Priority date | Publication date | Assignee | Title |
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JP2008214129A (en) * | 2007-03-05 | 2008-09-18 | Hisayuki Kishi | Method and apparatus for fermentation composting treatment |
CN106187336A (en) * | 2016-07-19 | 2016-12-07 | 金发科技股份有限公司 | More than a kind of kitchen, Organic substance aerobic compost builds heaping method |
Cited By (4)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
CN109956634A (en) * | 2019-03-14 | 2019-07-02 | 江苏雷蒙新材料有限公司 | The method for innocent treatment of excess sludge after a kind of organic chemical waste water biochemical treatment |
CN110663715A (en) * | 2019-11-04 | 2020-01-10 | 云峰机械(福建)有限公司 | Homogeneous inflating and foaming machine |
CN113149789A (en) * | 2021-04-07 | 2021-07-23 | 中国科学院西双版纳热带植物园 | Soil conditioner and preparation method thereof |
CN117655091A (en) * | 2023-03-01 | 2024-03-08 | 日照城投环境科技集团有限公司 | Organic solid waste treatment and carbon sink method for mediating land restoration thereof |
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Application publication date: 20180904 |