CN1668538A - Extinction type biological treatment machine for organic garbage - Google Patents

Extinction type biological treatment machine for organic garbage Download PDF

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Publication number
CN1668538A
CN1668538A CNA028296818A CN02829681A CN1668538A CN 1668538 A CN1668538 A CN 1668538A CN A028296818 A CNA028296818 A CN A028296818A CN 02829681 A CN02829681 A CN 02829681A CN 1668538 A CN1668538 A CN 1668538A
Authority
CN
China
Prior art keywords
organic garbage
housing
organic
porous carrier
digestion chamber
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.)
Granted
Application number
CNA028296818A
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Chinese (zh)
Other versions
CN1331783C (en
Inventor
宋昆元
严方
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Shanghai Gi Biotechnology Engineering Co ltd
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Shanghai Gi Biotechnology Engineering Co ltd
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Publication of CN1668538A publication Critical patent/CN1668538A/en
Application granted granted Critical
Publication of CN1331783C publication Critical patent/CN1331783C/en
Anticipated expiration legal-status Critical
Expired - Fee Related legal-status Critical Current

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Classifications

    • B—PERFORMING OPERATIONS; TRANSPORTING
    • B09—DISPOSAL OF SOLID WASTE; RECLAMATION OF CONTAMINATED SOIL
    • B09B—DISPOSAL OF SOLID WASTE
    • B09B3/00—Destroying solid waste or transforming solid waste into something useful or harmless
    • B09B3/60—Biochemical treatment, e.g. by using enzymes
    • B—PERFORMING OPERATIONS; TRANSPORTING
    • B09—DISPOSAL OF SOLID WASTE; RECLAMATION OF CONTAMINATED SOIL
    • B09B—DISPOSAL OF SOLID WASTE
    • B09B3/00—Destroying solid waste or transforming solid waste into something useful or harmless
    • B—PERFORMING OPERATIONS; TRANSPORTING
    • B09—DISPOSAL OF SOLID WASTE; RECLAMATION OF CONTAMINATED SOIL
    • B09B—DISPOSAL OF SOLID WASTE
    • B09B3/00—Destroying solid waste or transforming solid waste into something useful or harmless
    • B09B3/40—Destroying solid waste or transforming solid waste into something useful or harmless involving thermal treatment, e.g. evaporation
    • 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
    • C05F17/10—Addition or removal of substances other than water or air to or from the material during the treatment
    • C05F17/15—Addition or removal of substances other than water or air to or from the material during the treatment the material being gas
    • 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
    • C05F17/20—Preparation of fertilisers characterised by biological or biochemical treatment steps, e.g. composting or fermentation using specific microorganisms or substances, e.g. enzymes, for activating or stimulating the treatment
    • C—CHEMISTRY; METALLURGY
    • C05—FERTILISERS; MANUFACTURE THEREOF
    • C05F—ORGANIC FERTILISERS NOT COVERED BY SUBCLASSES C05B, C05C, e.g. FERTILISERS FROM WASTE OR REFUSE
    • C05F9/00—Fertilisers from household or town refuse
    • C05F9/02—Apparatus for the manufacture
    • 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
    • Y02P—CLIMATE CHANGE MITIGATION TECHNOLOGIES IN THE PRODUCTION OR PROCESSING OF GOODS
    • Y02P20/00—Technologies relating to chemical industry
    • Y02P20/141—Feedstock
    • Y02P20/145—Feedstock the feedstock being materials of biological origin
    • 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

Abstract

A device for decomposing organic garbage completely by biochemical treatment, includes a shell, a mixing apparatus, a motor and an inlet for organic garbage. A digestion cell which is covered by an oil jacket heating chamber with an electric heater, which is surrounded by insulated material, is formed inside the shell. A waste gas deodorization apparatus is arranged on the top back corner of the shell, on one side of which an air inlet is formed. The garbage mixing apparatus is installed on the support shaft of the digestion cell and drived by the motor. There exist porous carrier and many kinds of microbe supported on the porous carrier, herein, microbe including phototrophic bacteria, lactic acid, yeast and actinomycetes. Organic garbage is decomposed completely and no liquid or solid residue is discharged by using this device.

Description

Extinction type biological treatment machine for organic garbage
Elimination-type biologic processor of organic garbage
Technical field
The present invention relates to a kind of refuse disposal installation, more particularly to one kind is digested using many flora microorganisms to organic waste, is achieved innoxious digestion process, as a result can be realized the elimination-type biologic processor of organic garbage of noresidue discharge.Background technology
The acceleration developed with Chinese Urbanization, the reasonable disposal of urban biology rubbish has been included in the project for being badly in need of solving as a major subjects.Organic waste is a main component in domestic waste.In Shanghai, 13000 tons of house refuse is produced daily, and wherein organic waste occupies 1,200 1300 ton per days.Because organic waste is easily corrupt, it is difficult to transport, stores, produces the reasons such as stink, sewage harmful to health.And carry out refuse classification processing and carry out organic waste that to focus on be a good method, thus from twentieth century end many countries using microorganism to organic waste progress biological treatment, and achieved success.Organic garbage biological processor also arises at the historic moment.China has organic garbage biological processor to emerge and enters market in succession from the last century Mo city flourishing in Shanghai etc., this kind of organic garbage biological processor, usually using special strain, in artificial environment, the bio-digestion to organic waste is realized, but solid formation or liquid phase thing that the result of processing has remnants need to be discharged periodically.The content of the invention
It is an object of the invention to provide one kind organic waste, the elimination-type biologic processor of organic garbage of final noresidue discharge are handled using biological flora.
What the present invention was realized in：A kind of elimination-type biologic processor of organic garbage, including housing, mixing arrangement, motor, organic waste input port, it is characterized in that setting digestion chamber in housing and there is the oil lagging heating chamber of electric heater in digestion chamber's outsourcing, heat-insulation layer is set outside oil lagging, case top relief angle is provided with tail gas odor removal, air-in is set on the side plate of housing, and rubbish stirs mixing apparatus and is fixed on digestion chamber's frame axle and driven by motor.Confirm this Brief description of the drawings
Fig. 1:Left view cross section structure schematic diagram of the present invention
Fig. 2:Knot Chinese holly schematic diagram cuts open in vertical view office of the present invention
In figure：1, rubbish stirs mixing apparatus, 2, guidance panels, 3, air-ins, 4, organic wastes input ports, 5, tail gas odor removals, 6, heat-insulation layers, 7, oil lagging heating chambers, 8, electric cabinets, 9, motors, 10, housings, 11, digestion chambers.Embodiment
Contain BMS systems in the digestion chamber of the rubbish biological processor of the present invention.BMS systems are Best-Microorganism- System, it mainly by（A) porous carrier and（B) symbiotic co-existence is constituted in many flora microorganisms on porous carrier.Porous carrier
Currently preferred porous carrier is timber carrier, wherein having eliminated the composition for easily causing corruption, but retains cellulose, lignin and pentosan composition.The voidage of the present invention is 75-85 %, so that increase rubbish and the contact area of many flora microorganisms of BMS to greatest extent.
In addition, the timber carrier of the present invention has size and deep mixed hole, so that a certain degree of anaerobic zone, aerobic area and aerobic zone are formed, so as to provide suitable growing environment for different types of microorganism.Many flora microorganisms
Symbiotic co-existence is an aggregate being made up of a variety of floras in many flora microorganisms on porous carrier, wherein containing selected from following microorganism：Photosynthetic bacteria, lactic acid bacteria, saccharomycete, actinomyces etc..
Available for the present invention microorganism be not particularly limited, can be it is any have decompose, utilize the bacterium of the various pollutants such as organic matter, sulfide, nitrogen oxides, organophosphor in organic waste.For above-mentioned main several quasi-microorganisms, photosynthetic bacteria is mainly used in decomposing low fatty acid, aromatic compound；The material such as lactic acid bacteria main decomposition protein and glucose, lactic acid, acetic acid, propionic acid；Saccharomycete mainly has fabulous effect to high concentration organic garbage filter liquid；Gas chromatography of the actinomyces principal degradation including aromatic compound.
Representational microorganism example includes but is not limited to：It is beautiful for eliminating3Ammonifiers, nitrifier, denitrifying bacterium；Sulfide-oxidizing enzyme (such as Thiobacillus for eliminating sulfide）, thread sulphur bacteria (such as bayesian sulfur bacteria, Send out sulphur bacterium）, photosynthetic sulfur bacteria（Such as green sulphur bacteria, red sulfur bacteria）；Ammonifiers for denitrogenation dephosphorizing（Such as bacillus）, nitrifier, denitrifying bacterium, phosphobacteria（Such as Serratieae）.These microorganisms can be the conventional microbe species in this area, can also be separated and obtained under the environment such as place where the garage is piled up and waste water treatment plant with conventional method.
The BMS system response device simulating natural environment ecosystems, are present by being permitted the longer food chain that multiple-microorganism is constituted.Place occupy the BMS floras of carrier usually in a dormant state.When contacting organic waste, flora turns to active state by resting state quickly.Organic substance is adsorbed on thalline in very short time ＜ about 10-30 minute ＞ in organic waste, and solable matter is directly penetrating intracellular.Into in the presence of intracellular nutriment in the cell enzyme, through a series of biochemical reactions, organic matter is set to be converted into the simple inorganic matter such as carbon dioxide and water.Energy is produced simultaneously.The intermediate product synthetic cell material produced in energy and oxidizing process that microorganism is released using breathing, makes thalline amount reproduction.Microorganism constantly carries out organic matter in biological oxidation, environment and constantly reduced, and most organic waste is eliminated at last.
BMS systems used in the present invention have following main feature：
(D BMS system simulation natural ecological environments, its purification process and flow principle are different from traditional biological handling process, BMS systems not only can be with fast decoupled organic matter, the generation of the foreign odor such as suppression and removal of hydrogen sulfide, ammonia, and whole process can be made to be discharged without residual refuse.
(2) BMS biological treatment systems are different from traditional treating method for organic refuse；Oxygen transfer efficiency, coefficient of oxygen utilization, treatment effeciency, biomass and activity, the index such as economy are substantially better than traditional processing method.
(3) timber carrier of the invention, different from bio-carrier conventional at present, proportion is moderate in carrier, forms biological species, the rational ecosystem of distributed number.
(4) stirring and aerating system provide substantial oxygen source for microorganism species.
(5) equipment treatment effeciency is high, and floor space is small, and cost of investment is low, and integrated degree is high.Embodiment：
As shown in Figure 1, 2.A kind of elimination-type biologic processor of organic garbage, digestion chamber is set in housing, and is had in digestion chamber's outsourcing and set heat-insulation layer outside the oil lagging heating chamber of electric heater, oil lagging.Case top relief angle is provided with tail gas odor removal, air-in is set on the side plate of housing, rubbish stirs mixing apparatus and is fixed on digestion chamber's frame axle and driven by motor.Organic waste input port is located on the slope panel of case top, Electric cabinet, motor, guidance panel are located in the cavity between housing and digestion chamber, and guidance panel is arranged on the main view panel of housing, and electric cabinet is fixed on the backsight panel of housing.
A kind of method that organic garbage biological processor handles rubbish, comprises the following steps：A. symbiotic co-existence is added in many flora microorganisms on timber carrier in digestion chamber, add organic waste；B. digestion chamber is heated, temperature is 40 °C ± 2 °C, while driving mixing arrangement, the 2kw of motor power 2.:, mixing rotating speed is stirred by digestion chamber：4r. p. m, are controlled by operation industrial computer；C. fresh air is continually entered and using tail gas odor removal to tail gas deodorization by air-in in processing procedure.The beneficial effects of the invention are as follows：Using many flora microorganisms of BMS, the complete digestion of organic waste, no solid, liquid phase residue are carried out.Oil lagging digestion chamber is heated and attemperator, makes digestion chamber is heated to hook, and is conducive to the breeding of flora and is improved heat utilization efficiency.Digestion chamber is supplied and exhaust form, promotes the oxygen supply effect of digestion chamber's flora, in good time discharge vapor, to provide the living condition that flora is suitable.The organic waste specially designed stirs mixing apparatus and ensures that organic waste and air have good contact, promotes the digestion rate and reduction energy consumption of organic waste.Physical chemistry odor removal, improves the cleanliness factor of discharge tail gas, and result can realize that noresidue is discharged.Controlled using industrial computer, automaticity is high, ambient parameter modification in digestion chamber's is convenient, and excellent environment is provided for the breeding of flora.The various organic garbage treatment times see the table below：Title processing time
Vegetable melon and fruit class（Not fibre-bearing）< 6h
Melon and fruit class（Fibre-bearing）< 8h
Cereals< 8h
Meat< 16h
Bone class and other< 36h
Shell< 48h
Food processing factory's leftover bits and pieces and organic waste<24h is (under usual state） .

Claims (5)

  1. Claim
    1, a kind of elimination-type biologic processor of organic garbage, including housing, mixing arrangement, motor, organic waste input port, it is characterized in that, digestion chamber [11] are set in housing [10], and there is the oil lagging heating chamber [7] of electric electric heater in digestion chamber's outsourcing, heat-insulation layer [6] is set outside oil lagging, case top relief angle is provided with tail gas odor removal [5], air-in [3] is set on the side plate of housing, rubbish stirs mixing apparatus [1] and is fixed on digestion chamber's frame axle and is driven by motor [9].
    2nd, organic garbage biological processor according to claim 1, it is characterized in that, organic waste input port [4] is located on the slope panel of case top, electric cabinet [8], motor, guidance panel [2] are located in the cavity between housing and digestion chamber, guidance panel is arranged on the main view panel of housing, and electric cabinet is fixed on the backsight panel of housing.
    3rd, organic garbage biological processor as claimed in claim 1, it is characterised in that BMS systems are contained in described digestion chamber, the system by（A) porous carrier and（B) symbiotic co-existence is constituted in many flora microorganisms on porous carrier.
    4th, organic garbage biological processor as claimed in claim 3, it is characterised in that described porous carrier is timber carrier, voidage is 75-85 %.
    5th, organic garbage biological processor as claimed in claim 3, it is characterised in that described symbiotic co-existence contains following microorganism in many flora microorganisms on porous carrier：Photosynthetic bacteria, lactic acid bacteria, saccharomycete, square line bacterium.
CNB028296818A 2001-04-20 2002-09-27 Extinction type biological treatment machine for organic garbage Expired - Fee Related CN1331783C (en)

Applications Claiming Priority (2)

Application Number Priority Date Filing Date Title
CNB01112685XA CN1168546C (en) 2001-04-20 2001-04-20 Elimination-type biologic processor of organic garbage
PCT/CN2002/000681 WO2004028984A1 (en) 2001-04-20 2002-09-27 A device for decomposing organic garbage completely by biochemical treatment

Publications (2)

Publication Number Publication Date
CN1668538A true CN1668538A (en) 2005-09-14
CN1331783C CN1331783C (en) 2007-08-15

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CNB028296818A Expired - Fee Related CN1331783C (en) 2001-04-20 2002-09-27 Extinction type biological treatment machine for organic garbage

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CN (2) CN1168546C (en)
AU (1) AU2002338004A1 (en)
WO (1) WO2004028984A1 (en)

Cited By (3)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN103060231A (en) * 2012-12-26 2013-04-24 福建大用生态农业综合发展有限公司 Composite microecological bactericide used for eliminating stink in culturing farm
CN103656712A (en) * 2013-11-20 2014-03-26 日照海韵环保生物科技发展有限公司 Seaweed biological deodorant and preparation method thereof
CN105039221A (en) * 2015-08-07 2015-11-11 中国农业科学院哈尔滨兽医研究所 Cold water fish probiotics arthrobacter strain and application thereof

Families Citing this family (5)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN1168546C (en) * 2001-04-20 2004-09-29 上海金迪生物技术工程有限公司 Elimination-type biologic processor of organic garbage
TWI402423B (en) * 2006-02-28 2013-07-21 Entegris Inc System and method for operation of a pump
CN102699009A (en) * 2012-06-15 2012-10-03 上海科东自控工程有限公司 Microorganism garbage disposal machine
CN108994045A (en) * 2018-07-09 2018-12-14 淮阴师范学院 Utilize microorganism decomposition organic waste and the method for producing new energy
CN109553439A (en) * 2018-11-20 2019-04-02 龙岩维妮爵雅环保产品科技有限公司 A kind of refuse treatment plant

Family Cites Families (6)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JP3459048B2 (en) * 1991-12-24 2003-10-20 照夫 比嘉 Treatment of alcohol production waste liquid
JP3303892B2 (en) * 1993-07-12 2002-07-22 中部ドラム罐工業株式会社 High-speed fermentation processing equipment for garbage
JP2000167521A (en) * 1998-12-02 2000-06-20 Tanico Corp Apparatus for deodorizing garbage treatment machine, or the like
JP2001121121A (en) * 1999-10-29 2001-05-08 Sanyo Electric Co Ltd Organic matter treating apparatus
CN1194908C (en) * 2001-04-12 2005-03-30 章永泰 River mud repair material for sewage treatment
CN1168546C (en) * 2001-04-20 2004-09-29 上海金迪生物技术工程有限公司 Elimination-type biologic processor of organic garbage

Cited By (5)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN103060231A (en) * 2012-12-26 2013-04-24 福建大用生态农业综合发展有限公司 Composite microecological bactericide used for eliminating stink in culturing farm
CN103656712A (en) * 2013-11-20 2014-03-26 日照海韵环保生物科技发展有限公司 Seaweed biological deodorant and preparation method thereof
CN103656712B (en) * 2013-11-20 2016-04-13 日照贝斯特环保生物科技有限公司 A kind of seaweed bio deodorizer and preparation method thereof
CN105039221A (en) * 2015-08-07 2015-11-11 中国农业科学院哈尔滨兽医研究所 Cold water fish probiotics arthrobacter strain and application thereof
CN105039221B (en) * 2015-08-07 2019-04-16 中国农业科学院哈尔滨兽医研究所 One plant of cold water fish probiotics Arthrobacter strain and application thereof

Also Published As

Publication number Publication date
CN1168546C (en) 2004-09-29
WO2004028984A1 (en) 2004-04-08
CN1331783C (en) 2007-08-15
AU2002338004A1 (en) 2004-04-19
CN1382654A (en) 2002-12-04

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