CN102502956B - Municipal organic waste combined anaerobic treatment process and equipment - Google Patents

Municipal organic waste combined anaerobic treatment process and equipment Download PDF

Info

Publication number
CN102502956B
CN102502956B CN201110339482.XA CN201110339482A CN102502956B CN 102502956 B CN102502956 B CN 102502956B CN 201110339482 A CN201110339482 A CN 201110339482A CN 102502956 B CN102502956 B CN 102502956B
Authority
CN
China
Prior art keywords
solid
liquid
tank
anaerobic
making beating
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.)
Active
Application number
CN201110339482.XA
Other languages
Chinese (zh)
Other versions
CN102502956A (en
Inventor
何亮
王小韦
赵克
张晨光
解建波
Current Assignee (The listed assignees may be inaccurate. Google has not performed a legal analysis and makes no representation or warranty as to the accuracy of the list.)
Beijing environment Co.,Ltd.
BEIJING ENVIRONMENT ENGINEERING TECHNOLOGY Co.,Ltd.
Original Assignee
Beijing Sanitation Group Environmental Research Development Co Ltd
Priority date (The priority date 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 date listed.)
Filing date
Publication date
Application filed by Beijing Sanitation Group Environmental Research Development Co Ltd filed Critical Beijing Sanitation Group Environmental Research Development Co Ltd
Priority to CN201110339482.XA priority Critical patent/CN102502956B/en
Publication of CN102502956A publication Critical patent/CN102502956A/en
Application granted granted Critical
Publication of CN102502956B publication Critical patent/CN102502956B/en
Active legal-status Critical Current
Anticipated expiration legal-status Critical

Links

Images

Classifications

    • YGENERAL 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
    • Y02TECHNOLOGIES OR APPLICATIONS FOR MITIGATION OR ADAPTATION AGAINST CLIMATE CHANGE
    • Y02EREDUCTION OF GREENHOUSE GAS [GHG] EMISSIONS, RELATED TO ENERGY GENERATION, TRANSMISSION OR DISTRIBUTION
    • Y02E50/00Technologies for the production of fuel of non-fossil origin
    • Y02E50/30Fuel from waste, e.g. synthetic alcohol or diesel
    • YGENERAL 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
    • Y02TECHNOLOGIES OR APPLICATIONS FOR MITIGATION OR ADAPTATION AGAINST CLIMATE CHANGE
    • Y02WCLIMATE CHANGE MITIGATION TECHNOLOGIES RELATED TO WASTEWATER TREATMENT OR WASTE MANAGEMENT
    • Y02W10/00Technologies for wastewater treatment
    • Y02W10/20Sludge processing
    • YGENERAL 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
    • Y02TECHNOLOGIES OR APPLICATIONS FOR MITIGATION OR ADAPTATION AGAINST CLIMATE CHANGE
    • Y02WCLIMATE CHANGE MITIGATION TECHNOLOGIES RELATED TO WASTEWATER TREATMENT OR WASTE MANAGEMENT
    • Y02W30/00Technologies for solid waste management
    • Y02W30/20Waste processing or separation

Landscapes

  • Processing Of Solid Wastes (AREA)
  • Treatment Of Sludge (AREA)

Abstract

The invention discloses a municipal organic waste combined anaerobic treatment process and equipment. The process comprises a preprocessing step, an anaerobic digestion processing step and a swampiness processing step. Municipal organic wastes comprise heterogenous semifluid wastes and homogeneous solid-liquid wastes. The preprocessing step is characterized in that: circular pulping processing is firstly carried out on the heterogenous semifluid wastes, solid-liquid separation is then carried out on the circularly pulped materials and the homogeneous solid-liquid wastes, and the obtained slurry is used for the anaerobic digestion processing step. The invention also discloses equipment for the process. According to the process and the equipment, the municipal organic wastes are adopted as processing objects; the problems of homogenization of the municipal organic wastes, difficulty in feed-in and feed-out, and mixed feeding combined digestion are solved; the efficiency and the import substitution rate of a reactor are further improved through technology improvement on an anaerobic digestion tank; the aim of combined digestion is achieved; and a blank of domestic high solid wet type municipal organic waste combined anaerobic digestion processing complete technology process engineering is filled.

Description

A kind of municipal organic waste combined anaerobic treatment process and equipment
Technical field
The present invention relates to the process field of organic waste, a kind ofly specifically adopt high solid wet type anaerobic digestion techniques to carry out biological degradation to organic garbage of city and obtain resource utilization set technique and the equipment of biogas.
Background technology
Organic garbage of city mainly comprises heterogeneous body half fluidised form class rubbish (meal kitchen, fruits and vegetables rubbish) and homogeneous solid-liquid class rubbish (urban night soil, mud), and changing food waste is wherein mainly derived from the food residues that food-processing, food and beverage sevice and resident living etc. produce; Fruits and vegetables rubbish such as mainly refers in agricultural-food Transferring Base, the market of farm produce at the rubbish such as dish leaf that place produces, melon and fruit; Urban night soil and mud are respectively from public toilet or Residential areas septic tank and sewage work.Due to the continuous variation of organic garbage of city composition and the raising day by day of environmental quality requirement, conventional process mode such as sanitary landfill, burning and compost show various drawbacks gradually, and the organic garbage of city anaerobic digestion techniques that possesses efficient refuse processing and resource recovery double effects obtains pay attention to day by day.
At present, utilize anaerobic digestion techniques to process organic garbage of city and obtained abroad application quite widely, before the more than ten years, just had large-scale industrial production.In China, the history of Anaerobic Digestion municipal domestic organic refuse is also long-standing, is mainly used in the processing of feces of livestock and poultry, municipal sludge and high concentrated organic wastewater, the most typical little methane-generating pit in rural area that is applied as.In recent years, China in Beijing, the large-and-medium size cities such as Shanghai, Guangzhou, Shenzhen, or attempted utilizing anaerobic digestion techniques to process the organic garbage of city such as changing food waste, municipal sludge.But the domestic combined anaerobic digestion recycling treatment engineering that is directed to specially organic garbage of city does not also have what is heard, compared with developed countries, the through engineering approaches application level of Chinese municipal organic anaerobic digestion techniques is in urgent need to be improved.
At present, the research of Chinese municipal organic anaerobic digestion techniques is also in the preliminary stage, and the difficulty facing mainly contains the following aspects: the one, and organic garbage of city complicated component, physico-chemical property is inhomogeneous, variation range is larger, charging and discharging difficulty; The 2nd, urban night soil, mud and other organic garbage of city can not parallel feeding simultaneous digestions; The organic garbage of city such as meal kitchen, swill contain the composition that grease, inorganic salt etc. suppress anaerobic digestion; The 3rd, the efficiency of reactor is lower, and the residence time is long, conversion rate of organic matter is low, and anaerobic system domestic manufacture of key equipment rate is low.
Summary of the invention
The object of the invention is to overcome the shortcoming and defect of above-mentioned prior art, a kind of input and output material convenience, practicability and effectiveness are provided and can realize the Processes and apparatus that organic garbage of city is combined anaerobic treatment.
For achieving the above object, the present invention is by the following technical solutions:
A kind of municipal organic waste combined anaerobic treatment process, comprise pre-treatment step, Anaerobic Digestion step and natural pond moneyization treatment step, described organic garbage of city comprises heterogeneous body half fluidised form class rubbish and homogeneous solid-liquid class rubbish, described pre-treatment step is: heterogeneous body half fluidised form class rubbish first carries out circulation beating processing, described circulation beating is treated to: the material after making beating carries out solid-liquid separation, the slurries that obtain after solid-liquid separation re-start making beating and process, and reciprocation cycle repeatedly; Through circulation beating material after treatment, together carry out solid-liquid separation again with homogeneous solid-liquid class rubbish, gained slurries are used for carrying out Anaerobic Digestion step.
Further, described heterogeneous body half fluidised form class rubbish separable go out filtrate class rubbish, other parts are carried out circulation beating processing again after break process together with described filtrate class rubbish.
Further, the other parts in described heterogeneous body half fluidised form class rubbish except filtrate class rubbish are processed without making beating after break process, directly carry out solid-liquid separation, the outward transport of dewatering.
Further, described Anaerobic Digestion step comprises inanimate matter separation, pocket type oil removing, homogeneous and anaerobic ferment process, in described anaerobic ferment process, anaerobic fermentation tank enters material under adopting and above goes out the mode of biogas, natural pond liquid, and the bottom in anaerobic fermentation tank and top are equipped with respectively stirring technique, inside is furnished with Hydraulic Circulation heating treatment process.
Further, the liquid return of described natural pond liquid gained after processed enters homogenizing step for regulating material characteristic as making beating with process water or backflow.
A kind of organic waste combined anaerobic treatment process equipment, comprise the pretreatment unit that end contains solid-liquid separating machine, also comprise Anaerobic Digestion device and natural pond moneyization treatment unit, described pretreatment unit also comprises making beating tank, in described making beating tank, be provided with Hydraulic Circulation making beating reamer pump, making beating tank is communicated with the input terminus of described solid-liquid separating machine by the Hydraulic Circulation reamer pump of pulling an oar; The first liquid output terminal of solid-liquid separating machine is communicated with the input terminus of making beating tank by pipeline, valve, pump; The second liquid output terminal of solid-liquid separating machine is connected with Anaerobic Digestion device by pipeline, valve, pump.
Further, described Anaerobic Digestion device comprises inanimate matter separator, pocket type waste-oil scavenger, homogeneous tank, spiral pump and anaerobic fermentation tank, solid-liquid separating machine in pretreatment unit is connected successively with described inanimate matter separator, pocket type waste-oil scavenger, homogeneous tank, between described homogeneous tank and anaerobic fermentation tank bottom, by spiral pump, is connected.
Further, described anaerobically fermenting tank top is provided with the overhead for abolishing materials inside crust, and bottom is provided with for the mixed uniformly bottom stirrer of material, and inside is also provided with the Hydraulic Circulation agitator for maintaining steady temperature.
Further, the end of described natural pond moneyization treatment unit is provided with natural pond liquid pool, and described natural pond liquid pool is communicated with described making beating tank and homogeneous tank respectively through pump, pipeline and two valves.
Compared with prior art, the present invention has following beneficial effect:
1, pre-treatment adopts mechanical cycles beating process, has successfully solved the input and output material difficulty that exists in high solid digestion and material two hang-ups that homogenize; And will together carry out solid-liquid separation with homogeneous solid-liquid class rubbish again through circulation beating material after treatment, gained slurries are used for carrying out Anaerobic Digestion step, have realized the associating anaerobic treatment of organic garbage of city.
2, the design of inanimate matter separator efficiently solves inanimate matter in material and accumulates the reactor plugs problem causing.
3, for the high feature of China's organic waste oleaginousness, adopt pocket type waste-oil scavenger, guaranteed carrying out smoothly of anaerobic fermentation process.
4, stirring " broken shell " technology in top can effectively solve the crust problem of anaerobic reactor; It is constant that inner waterpower hydronics can utilize produced biogas self-energy to maintain temperature of reactor.
5, the natural pond liquid of anaerobically fermenting processing gained can reflux and maybe can reflux and carry out homogenization step for regulating material characteristic with process water as making beating, and resource can be effectively utilized.
6, in addition, for the unsettled feature of organic garbage of city supplied materials, the also other charging route of special design, even supplied materials biodegradability is poor, when material is after fragmentation, can process without making beating, directly material be sent into solid-liquid separating machine and dewatered and send outside, solve the unsettled problem of organic garbage of city supplied materials.
Below by drawings and Examples, technical scheme of the present invention is described in further detail.
Accompanying drawing explanation
Fig. 1 is municipal organic waste combined anaerobic treatment process schematic flow sheet of the present invention;
Fig. 2 is municipal organic waste combined anaerobic treatment process equipment of the present invention and process flow sheet.
Embodiment
Below in conjunction with accompanying drawing, the preferred embodiments of the present invention are described, should be appreciated that preferred embodiment described herein, only for description and interpretation the present invention, is not intended to limit the present invention.
Organic garbage of city comprises heterogeneous body half fluidised form class rubbish (changing food waste, fruits and vegetables rubbish etc.) and homogeneous solid-liquid class rubbish (urban night soil, domestic sludge etc.), municipal organic waste combined anaerobic treatment process of the present invention comprises pre-treatment step, Anaerobic Digestion step and natural pond moneyization treatment step, specifically as shown in Figure 1:
(1) pre-treatment step is:
First changing food waste enters storage bin or emergency stack stock ground, percolate diafiltration in storage bin or emergency stack stock ground is to collecting tank, the percolate of collecting tank pumps into making beating tank and carries out circulation beating processing, in storage bin or emergency stack stock ground remaining other high solid class rubbish after fragmentation, enter making beating tank carry out circulation beating processing, through the material after treatment of pulling an oar, enter solid-liquid separating machine and carry out solid-liquid separation, simultaneously, urban night soil, domestic sludge directly enters solid-liquid separating machine and carries out solid-liquid separation after simple process, after entering garbage collection box, making beating tank and the isolated oversize material of solid-liquid separating machine carry out landfill or compost treatment, the slurries (material after pulp) that solid-liquid separating machine is separated are for next step Anaerobic Digestion step.Circulation beating link in pre-treatment step homogenizes material, is convenient to the further processing of subsequent technique, has solved this difficult problem of input and output material difficulty simultaneously.
(2) Anaerobic Digestion step:
The slurries of separating through solid-liquid separating machine enter pocket type waste-oil scavenger through inanimate matter separator, skimming plant in pocket type waste-oil scavenger is removed top layer grease again, and the material after oil removing enters homogeneous tank again and by spiral pump, squeezes into anaerobic fermentation tank and carry out Anaerobic Digestion after stirring.Wherein, the input and output material of anaerobic fermentation tank adopts the mode of " bottom in and top out ", and (broken shell refers to broken long-play process for " broken shell " to be equipped with overhead, the scleroma layer that one deck that anaerobically fermenting pot liquid upper surface forms is comprised of stearates material), be equipped with bottom stirrer and evenly mix for material, be equipped with Hydraulic Circulation agitator for maintaining steady temperature.The fermentor tank residence time is designed to 20 days, charging solid content scope 8%-12%, and volume yield rate can reach 2.0.
(3) natural pond moneyization treatment step:
After Anaerobic Digestion, discharge biogas, cripple, natural pond liquid, the biogas that produces enters methane boiler through air storage bag, gas-cleaning installation, institute's heat-dissipating amount is heated up water for anaerobic fermentation tank heating and heating, also can sending and receiving electricity equipment utilization marsh gas power generation, the unnecessary gas that air storage bag is discharged is lighted emptying by torch on duty; The cripple of producing, natural pond liquid enter mud storage pool, and then through dewatering unit processing, solid part outward transport compost or landfill disposal, liquid portion enters natural pond liquid pool, the natural pond liquid of natural pond liquid pool can be back to making beating tank as pulling an oar with process water or being back to homogeneous tank for regulating material characteristic, the unnecessary car taken out outward transport.
The 2 pairs of municipal organic waste combined anaerobic treatment process of the present invention and equipment are elaborated by reference to the accompanying drawings more below:
First changing food waste in organic garbage of city is discharged into storage bin 101 and carries out preliminary solid-liquid separation, and storage bin 101 has collecting tank 102, and the unnecessary moisture of material enters collecting tank 102 through this seepage flow, directly by 1# submersible sewage pump 103, sends into making beating tank 104.Solid materials is being delivered to homocline crusher 106 via drag conveyer 105, abolishes plastics bag and crushes material to below particle diameter 150mm.Broken good material is sent into revolution shearing type crusher 108 via 1# scraper conveyor 107 and is crushed to below particle diameter 50mm, then via 1# reversible belt machine 109, is sent to 2# scraper conveyor 110, and by it, material is sent in making beating tank 104 and pulled an oar.Nucleus equipment in making beating tank 104 is Hydraulic Circulation making beating reamer pump 111, its main broken function has been coordinated with the turbine disk by turbine cutters in pump, sword is all with on every impeller limit on turbine cutters, along with the high speed rotating of turbine, the material that sucks pumping hole will together be cut repeatedly by impeller limit and the turbine disk, thereby be pulverized.Material after pulverizing can be sprayed by pump middle part stirring port, or operation switching valve, makes it to pump from outlet
During making beating, in making beating tank 104, first need to add a certain amount of process water, until interior two Hydraulic Circulations making beating of making beating tank 104 reamer pump 111 can normally be worked, two Hydraulic Circulation making beating reamer pumps 111 are pulled an oar simultaneously, adopt the mode of circulation beating, beating time 60 minutes.Circulation beating detailed process is as follows:
Its Matter Transfer process is: making beating tank 104 → solid-liquid separating machine 112 → collecting tank 102 → 1# submersible sewage pump 103 → making beating tank 104.Its valve and equipment operational procedure are: open → valve of valve 113 114 close → solid-liquid separating machine of open → valve 115 112 start → Hydraulic Circulation making beating reamer pump 111 move → Hydraulic Circulation making beating reamer pump 111 dischargings → 1# submersible sewage pumps 103 move.
Material is after 104 making beating of making beating tank, by 111 dischargings of Hydraulic Circulation making beating reamer pump, to solid-liquid separating machine 112, material is through solid-liquid separation, and solid residue is transported outward, liquid enters collecting tank 102 and again returns making beating tank 104 by 1# submersible sewage pump 103, so far completes a circulation.General beating time 10 minutes, discharging RCT 5 minutes, can complete pulp after four circulations substantially.
After making beating, by 111 dischargings of Hydraulic Circulation making beating reamer pump.Discharging process is as follows:
Material discharging process is: making beating tank 104 → solid-liquid separating machine 112 → slag stock pump 116 → inanimate matter separator 201 → pocket type waste-oil scavenger 202; Its valve and equipment operational procedure are: open → valve of valve 115 114 open → solid-liquid separating machine of close → valve 203 112 start → Hydraulic Circulation reamer pump 111 dischargings → slag stock pumps 116.
Material completes after making beating, all through solid-liquid separating machine 112, carries out solid-liquid separation (not shown) with urban night soil, domestic sludge in organic garbage of city, isolates and is greater than the outward transport of 4mm material extrusion dehydration; The material that is less than 4mm is delivered to pocket type waste-oil scavenger 202 by slag stock pump 116 through inanimate matter separator 201.
Material, by after 202 oil removings of pocket type waste-oil scavenger, enters homogeneous tank 204, and charging front opening grid agitator stirs 10~15 minutes, controls and feeds intake load or add reagent, maintains the pH value of charging at 6.8-7.5.Open anaerobic fermentation tank 208 overhead and bottom stirrer, open homogeneous tank 204 feed valves 205 and spiral pump feed valve 206, then open feed worm pump 207 to anaerobic fermentation tank 208 chargings.
In the selection of anaerobic fermentation tank 208 tank bodies, abandoned traditional Steel Concrete fermentor tank and welding cylinder of steel, selected assembled tank, assembled tank is compared traditional Steel Concrete fermentor tank and welding cylinder of steel, is not subject to seasonal effect in construction environment.The tank body material that enamel assembling technology adopts new and high technology to make, with the on-site consolidation mode final molding of rapid low consumption, the anaerobic reactor equipment of composition complete set, make the agent set of biogas engineering device reach advanced technology, preparation rationally, excellent property, rotproofness is good, maintenance is convenient, specious effect.Tank body material adopts the enamel layer prefabricated steel of high anticorrosion grade assembled in bolt mode, and bolt place adds special sealing material leakproof, and the protective layer of this kind of prefabricated steel formation can not only stop tank body corrosion, and has the function of antiacid alkali.
Anaerobic fermentation tank 208 input and output materials adopt " bottom in and top out " mode, material after the interior fermentation of anaerobic fermentation tank 208 flows out and enters cripple pond 301 from the overflow port on top, (open valve 302) sent into water extracter 304 through 2# submersible sewage pump 303 and dewatered, liquid (open valve 305) enters natural pond liquid pool 306, the outward transport of natural pond slag.The material of natural pond liquid pool 306 has three whereabouts: 1, through 3# submersible sewage pump 307, send into making beating tank 104 as process water (open valve 308), shut-off valve 309); 2, through 3# submersible sewage pump 307, squeeze into homogeneous tank 204 and regulate material characteristic (open valve 309, shut-off valve 308); 3, unnecessary waste liquid is directly transported outward and is taken away with taking out car.
In anaerobic fermentation tank 208 operational processs, when observing fermentation liquid level crust from viewing window, open overhead and abolish scum silica frost, when winter temperature is lower, open waterpower circulation stirring device and heating rod and heat to tank body, maintain constant anaeration in normal temperature environment, guarantee equipment steady running.Depending on material situation, after operation some cycles, open valve 310 carries out spoil disposal, and cripple enters cripple pond 301.
The biogas that anaerobic digestion process produces, after desulfurization dewatering device, enters air storage bag 311.Air storage bag 311 is provided with positive/negative pressure protector, and maximum positive voltage is 1Kpa.Institute's storing gas passes into methane boiler 312, produces heat and can be used for the heating of anaerobism equipment and warm oneself and heat up water, and unnecessary gas is lighted emptying by torch 313 on duty.
In addition, for the unsettled feature of municipal wastes supplied materials, the also other charging route of special design, even supplied materials biodegradability is poor, after material is via 108 fragmentations of revolution shearing type crusher, by 1# reversible belt machine 109, be sent to 2# reversible belt machine 117, and by it, directly material sent into solid-liquid separating machine 112 and dewatered and send outside.
The present invention has filled up domestic high solid wet type organic garbage of city combined anaerobic digestion and has processed complete this blank of technical matters through engineering approaches, using organic garbage of city as handling object, by pre-treatment machinery beating process, solve organic garbage of city and homogenize and input and output material difficult problem; By the heterogeneous bodies such as changing food waste half fluidised form class rubbish is processed and carried out solid-liquid separation with the homogeneous solid-liquid class rubbish such as municipal sludge and urban night soil through making beating, solved parallel feeding simultaneous digestion problem; By the technological transformation of anaerobic digestor has been improved to reactor efficiency and the localization rate of parts and components, reach the object of simultaneous digestion.
In sum, municipal organic waste combined anaerobic treatment process provided by the present invention and equipment are compared conventional art and aspect high solid wet type combination treatment and recycling, are had obvious advantage.
Finally it should be noted that: the foregoing is only the preferred embodiments of the present invention, be not limited to the present invention, although the present invention is had been described in detail with reference to previous embodiment, for a person skilled in the art, its technical scheme that still can record previous embodiment is modified, or part technical characterictic is wherein equal to replacement.Within the spirit and principles in the present invention all, any modification of doing, be equal to replacement, improvement etc., within all should being included in protection scope of the present invention.

Claims (9)

1. a municipal organic waste combined anaerobic treatment process, comprise pre-treatment step, Anaerobic Digestion step and natural pond moneyization treatment step, described organic garbage of city comprises heterogeneous body half fluidised form class rubbish and homogeneous solid-liquid class rubbish, it is characterized in that, described pre-treatment step is: heterogeneous body half fluidised form class rubbish first carries out circulation beating processing, described circulation beating is treated to: the material after making beating carries out solid-liquid separation, the slurries that obtain after solid-liquid separation re-start making beating and process, and reciprocation cycle repeatedly; Through circulation beating material after treatment, together carry out solid-liquid separation again with homogeneous solid-liquid class rubbish, gained slurries are used for carrying out Anaerobic Digestion step.
2. combined anaerobic treatment process according to claim 1, is characterized in that, described heterogeneous body half fluidised form class rubbish separable go out filtrate class rubbish, other parts are carried out circulation beating processing again after break process together with described filtrate class rubbish.
3. combined anaerobic treatment process according to claim 1, is characterized in that, the other parts in described heterogeneous body half fluidised form class rubbish except filtrate class rubbish are processed without making beating after break process, directly carry out solid-liquid separation, the outward transport of dewatering.
4. according to the combined anaerobic treatment process described in claim 1,2 or 3, it is characterized in that, described Anaerobic Digestion step comprises inanimate matter separation, pocket type oil removing, homogeneous and anaerobic ferment process, in described anaerobic ferment process, anaerobic fermentation tank enters material under adopting and above goes out the mode of biogas, natural pond liquid, and the bottom in anaerobic fermentation tank and top are equipped with respectively stirring technique, inside is furnished with Hydraulic Circulation heating treatment process.
5. combined anaerobic treatment process according to claim 4, is characterized in that, the liquid return of described natural pond liquid gained after processed enters homogenizing step for regulating material characteristic as making beating with process water or backflow.
6. an organic waste combined anaerobic treatment process equipment, comprise the pretreatment unit that end contains solid-liquid separating machine, also comprise Anaerobic Digestion device and natural pond moneyization treatment unit, it is characterized in that, described pretreatment unit also comprises making beating tank, in described making beating tank, be provided with Hydraulic Circulation making beating reamer pump, making beating tank is communicated with the input terminus of described solid-liquid separating machine by the Hydraulic Circulation reamer pump of pulling an oar; The first liquid output terminal of solid-liquid separating machine is communicated with the input terminus of making beating tank by pipeline, valve, pump; The second liquid output terminal of solid-liquid separating machine is connected with Anaerobic Digestion device by pipeline, valve, pump.
7. combined anaerobic treatment process equipment according to claim 6, it is characterized in that, described Anaerobic Digestion device comprises inanimate matter separator, pocket type waste-oil scavenger, homogeneous tank, spiral pump and anaerobic fermentation tank, solid-liquid separating machine in pretreatment unit is connected successively with described inanimate matter separator, pocket type waste-oil scavenger, homogeneous tank, between described homogeneous tank and anaerobic fermentation tank bottom, by spiral pump, is connected.
8. combined anaerobic treatment process equipment according to claim 7, it is characterized in that, described anaerobically fermenting tank top is provided with the overhead for abolishing materials inside crust, bottom is provided with for the mixed uniformly bottom stirrer of material, and inside is also provided with the Hydraulic Circulation agitator for maintaining steady temperature.
9. combined anaerobic treatment process equipment according to claim 8, is characterized in that, the end of described natural pond moneyization treatment unit is provided with natural pond liquid pool, and described natural pond liquid pool is communicated with described making beating tank and homogeneous tank respectively through pump, pipeline and two valves.
CN201110339482.XA 2011-11-01 2011-11-01 Municipal organic waste combined anaerobic treatment process and equipment Active CN102502956B (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
CN201110339482.XA CN102502956B (en) 2011-11-01 2011-11-01 Municipal organic waste combined anaerobic treatment process and equipment

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
CN201110339482.XA CN102502956B (en) 2011-11-01 2011-11-01 Municipal organic waste combined anaerobic treatment process and equipment

Publications (2)

Publication Number Publication Date
CN102502956A CN102502956A (en) 2012-06-20
CN102502956B true CN102502956B (en) 2014-04-30

Family

ID=46215107

Family Applications (1)

Application Number Title Priority Date Filing Date
CN201110339482.XA Active CN102502956B (en) 2011-11-01 2011-11-01 Municipal organic waste combined anaerobic treatment process and equipment

Country Status (1)

Country Link
CN (1) CN102502956B (en)

Families Citing this family (6)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN103350097B (en) * 2013-06-25 2016-02-24 重庆欣彦生物技术有限公司 Useless dirty ecological comprehensive treatment system
CN104673629B (en) * 2014-12-26 2016-12-07 贝尔芬格水处理技术(杭州)有限公司 A kind of anaerobic fermentation system and utilize its carry out mud digestion reaction produce biogas method
CN104907316B (en) * 2015-05-27 2017-11-24 北京世纪国瑞环境工程技术有限公司 A kind of kitchen garbage and civic feces total system and its method
CN107243497A (en) * 2017-06-16 2017-10-13 湖北帝朗环保科技有限公司 A kind of organic waste living area pulp degraded equipment and technological process
CN108517294A (en) * 2018-06-05 2018-09-11 爱土工程环境科技有限公司 A kind of debirs processing system and processing method
CN110813976A (en) * 2019-09-23 2020-02-21 河南恒天久大实业有限公司 Comprehensive treatment method for full recycling of municipal refuse

Citations (6)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN101224999A (en) * 2008-01-16 2008-07-23 宝林 Anaerobic digestion handling method for restaurant garbage
CN101337838A (en) * 2008-08-11 2009-01-07 鄂尔多斯市东胜区传祥垃圾处理有限责任公司 Combined anaerobic fermentation process for organic solid wastes
CN101574701A (en) * 2009-05-13 2009-11-11 北京健坤伟华新能源科技有限公司 Treatment method and system of restaurant waste
CN101906441A (en) * 2010-06-25 2010-12-08 南京大学 Material mixing and slag crushing method of anaerobic digestion reactor based on pulsating air pressure effect
CN101955388A (en) * 2010-09-02 2011-01-26 朱海生 Urban garbage and sludge resource comprehensive utilization system
CN102167486A (en) * 2011-02-25 2011-08-31 大连市市政设计研究院有限责任公司 Urban sludge, excrement and kitchen garbage combined treatment process

Family Cites Families (1)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JP5288730B2 (en) * 2007-05-28 2013-09-11 株式会社東芝 Method and apparatus for treating organic waste

Patent Citations (6)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN101224999A (en) * 2008-01-16 2008-07-23 宝林 Anaerobic digestion handling method for restaurant garbage
CN101337838A (en) * 2008-08-11 2009-01-07 鄂尔多斯市东胜区传祥垃圾处理有限责任公司 Combined anaerobic fermentation process for organic solid wastes
CN101574701A (en) * 2009-05-13 2009-11-11 北京健坤伟华新能源科技有限公司 Treatment method and system of restaurant waste
CN101906441A (en) * 2010-06-25 2010-12-08 南京大学 Material mixing and slag crushing method of anaerobic digestion reactor based on pulsating air pressure effect
CN101955388A (en) * 2010-09-02 2011-01-26 朱海生 Urban garbage and sludge resource comprehensive utilization system
CN102167486A (en) * 2011-02-25 2011-08-31 大连市市政设计研究院有限责任公司 Urban sludge, excrement and kitchen garbage combined treatment process

Non-Patent Citations (5)

* Cited by examiner, † Cited by third party
Title
JP特开2008-290041A 2008.12.04
Microbial community dynamics in mesophilic anaerobic co-digestion of mixed waste;Savaporn Supaphol,Sasha N.Jenkins,Pichamon Intomo,et al;《Bioresource Technology》;20110331;第102卷(第5期);第4021-4027页 *
Savaporn Supaphol,Sasha N.Jenkins,Pichamon Intomo,et al.Microbial community dynamics in mesophilic anaerobic co-digestion of mixed waste.《Bioresource Technology》.2011,第102卷(第5期),
沈剑山,颜晓英,蒋宏华.餐厨垃圾厌氧消化及综合利用技术.《云南师范大学学报》.2011,第31卷
餐厨垃圾厌氧消化及综合利用技术;沈剑山,颜晓英,蒋宏华;《云南师范大学学报》;20110930;第31卷;第220-224页 *

Also Published As

Publication number Publication date
CN102502956A (en) 2012-06-20

Similar Documents

Publication Publication Date Title
CN103381420B (en) Device and method for sewage collaborative reutilization comprehensive treatment
CN102531295B (en) Method for jointly treating different garbage
CN102502956B (en) Municipal organic waste combined anaerobic treatment process and equipment
CN206156994U (en) Silt and derivant recycled processing system during aquatic attitude was handled
CN102050546A (en) Method and device for comprehensive treatment of domestic sewage and organic waste
CN101792246B (en) Method for generating biogas through intensified hydrolysis and anaerobic digestion of municipal domestic organic refuse
CN103074381A (en) Efficient resourceful treatment method through separation and anaerobic fermentation for kitchen waste
CN103084380B (en) Municipal solid waste processing system and processing method
CN202860973U (en) Kitchen garbage treatment equipment
CN111054735A (en) Kitchen waste treatment system and treatment method
CN104498532A (en) Process for producing methane by mixing and fermenting organic wastes
CN108031697A (en) A kind of kitchen, method for processing kitchen waste
CN106957130A (en) A kind of processing method of sanitary sewage and organic solid castoff
CN112517615A (en) Organic matter combined anaerobic pretreatment device and method
CN103357653A (en) Household refuse and domestic sewage synchronous processing method
CN202963023U (en) Pretreatment device of biomass garbage
CN102500608A (en) Anaerobic treatment process for high-concentration kitchen waste
CN201572782U (en) Kitchen garbage pulverizing and decomposing device
CN101786771B (en) Equipped device for enhanced hydrolysis and anaerobic digestion of urban living organic garbage for producing biological fuel gas
CN204550559U (en) A kind of changing food waste is from stirring anaerobic digestion biogas production equipment
CN213559105U (en) Urban organic waste cooperative recycling treatment system
CN203140420U (en) Organic garbage disposal system
CN104673629A (en) Anaerobic fermentation system and method for producing biogas by carrying out sludge digestion reaction through anaerobic fermentation system
CN214289959U (en) Organic matter combined anaerobic pretreatment device
CN205999381U (en) A kind of anaerobic fermentation of kitchen waste processing system

Legal Events

Date Code Title Description
C06 Publication
PB01 Publication
C10 Entry into substantive examination
SE01 Entry into force of request for substantive examination
C14 Grant of patent or utility model
GR01 Patent grant
C56 Change in the name or address of the patentee
CP01 Change in the name or title of a patent holder

Address after: 101111 Beijing City, Tongzhou District Zhongguancun Tongzhou Science Park light mechanical and electrical integration industry base Branch East Three Street No. 18

Patentee after: Beijing Environment Engineering Technology Co., Ltd.

Address before: 101111 Beijing City, Tongzhou District Zhongguancun Tongzhou Science Park light mechanical and electrical integration industry base Branch East Three Street No. 18

Patentee before: Beijing Sanitation Group Environmental Research Development Co., Ltd.

TR01 Transfer of patent right

Effective date of registration: 20210621

Address after: 101111 No.18, Kechuang East 3rd Street, Tongzhou Park, Tongzhou Park, Zhongguancun Science and Technology Park, Tongzhou District, Beijing

Patentee after: BEIJING ENVIRONMENT ENGINEERING TECHNOLOGY Co.,Ltd.

Patentee after: Beijing environment Co.,Ltd.

Address before: 101111 No.18, Kechuang East 3rd Street, Tongzhou Park, Tongzhou Park, Zhongguancun Science and Technology Park, Tongzhou District, Beijing

Patentee before: BEIJING ENVIRONMENT ENGINEERING TECHNOLOGY Co.,Ltd.

TR01 Transfer of patent right