[go: up one dir, main page]
More Web Proxy on the site http://driver.im/

CN109942161A - Sludge, excrement and kitchen garbage cooperate with anaerobic digestion process - Google Patents

Sludge, excrement and kitchen garbage cooperate with anaerobic digestion process Download PDF

Info

Publication number
CN109942161A
CN109942161A CN201910174596.XA CN201910174596A CN109942161A CN 109942161 A CN109942161 A CN 109942161A CN 201910174596 A CN201910174596 A CN 201910174596A CN 109942161 A CN109942161 A CN 109942161A
Authority
CN
China
Prior art keywords
anaerobic digestion
excrement
sludge
kitchen garbage
water
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.)
Pending
Application number
CN201910174596.XA
Other languages
Chinese (zh)
Inventor
宇鹏
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.)
Guangxi Teachers College
Original Assignee
Guangxi Teachers College
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 Guangxi Teachers College filed Critical Guangxi Teachers College
Priority to CN201910174596.XA priority Critical patent/CN109942161A/en
Publication of CN109942161A publication Critical patent/CN109942161A/en
Pending legal-status Critical Current

Links

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

Landscapes

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

Abstract

The invention discloses sludge, excrement and kitchen garbages to cooperate with anaerobic digestion process, pretreated kitchen garbage and sludge, excrement are uniformly mixed, moisture content is adjusted to 90%, it is cooled to 38 DEG C, the anaerobic digestion of mesophilic anaerobic digestion tank is sent into react 20 days, the biogas part of generation is used for steam boiler, and natural gas is made in remainder, and steam is heated for kitchen garbage pretreatment and pyrohydrolysis reaction;Biogas residue and biogas slurry is concentrated that solid content is made to reach 15%, it is reacted again through homogeneous pulp and pyrohydrolysis, material after reaction cools to 80 DEG C, Nutrition Soil is made lower than 40% through dehydration, desiccation to moisture content, the biogas slurry a part reflux generated in dehydration utilizes, and redundance is discharged into sewage treatment plant's processing.Present invention process energy integrated treatment sludge, excrement and kitchen garbage, can output natural gas and Nutrition Soil, the biogas slurry in technical process, which flows back, to be utilized, and is reduced externally discharge, is realized sludge, excrement and changing food waste into resources, emission reduction and harmless treatment.

Description

Sludge, excrement and kitchen garbage cooperate with anaerobic digestion process
Technical field
The invention belongs to sludge, excrement and kitchen garbage merging treatment technical field, especially sludge, excrement and kitchen rubbish Rubbish cooperates with anaerobic digestion process.
Background technique
The pollution of sludge, excrement and kitchen garbage is always the major issue of environment protection field.Sludge components are very complicated, it is wrapped Include the solid particles such as the silt particle, fiber, plant and animal residues being mixed into sanitary sewage or industrial wastewater and its condensation floccule, by Organic matter, heavy metal element and salt, a small amount of pathogenic microorganism, parasitism of zoogloea and its absorption that multiple-microorganism is formed The integrated solid materials such as worm's ovum.The key property of sludge is moisture content height, and high organic content, easy corruption is smelly, and Grain is thinner, and specific gravity is smaller, is in colloidal liquid.Mainly there are a variety of processing sides such as desiccation method, semi-oriented, compost, anaerobic digestion at present Method.Sludge is useful living resources, as can rationally utilizing can not only then turn waste into wealth, moreover it is possible to increase economic benefit, so, have Effect processing is disposed and is had important practical significance using the technology of sludge
Night soil-treatment is a global problem, solves bad, will seriously affect space and the quality of human lives.Excrement In organic matter and the substances such as nitrogen, phosphorus wherein, containing there are many enteron aisle germ, parasitic ovum and virus, development in the excrement of patient Middle national 70% disease with it is related.
Excrement have the characteristics that water content is big, content of organics is more, nitrogen, phosphorus, cause a disease opportunistic pathogen it is more, if direct emission, can make At water pollution, and the pernicious gas containing odor pollutants such as ammonia, hydrogen sulfide, mercaptan, thioethers is given out, causes health and environment dirty Dye problem.Stool problems are that city environmental protection must solve the problems, such as, the resource treatment technique of excrement for resource again It recycles and is of great significance.
Kitchen garbage is the sanitary waste that resident is formed during personal consumption, is easily rotted, and stench is distributed, and is passed Broadcast bacterium and virus.Kitchen garbage has the characteristics that water content is big, organic matter fat content is more, complicated component.City kitchen rubbish Rubbish quantity is very huge, and kitchen garbage full of nutrition is valuable renewable resource.
Currently, sludge generally with the methods of municipal sewage Combined Treatment, independent Anaerobic Digestion.Have individually to kitchen rubbish The processing technique of rubbish, individually to soiled litter processing technique, but individually processing method there are at high cost, complex managements, effect Bad, secondary pollution problems.
Summary of the invention
The object of the present invention is to provide a kind of sludge, excrement and kitchen garbages to cooperate with anaerobic digestion process, being capable of General Office Sludge, excrement and kitchen garbage are managed, natural gas and Nutrition Soil can be produced, the biogas slurry in technical process, which flows back, to be utilized, reduction pair Sludge, excrement and changing food waste into resources, emission reduction and harmless treatment are realized in outer discharge.
Sludge, excrement and kitchen garbage cooperate with anaerobic digestion process, comprising the following steps:
(1) kitchen garbage pre-processes: successively by multi-stage screening crushing, water-oil separating and slurrying;
(2) sludge, excrement pretreatment:
Sludge and excrement are stirred evenly, and mixed with the step (1) kitchen garbage pretreatment resulting material;
(3) Anaerobic Digestion is cooperateed with
It is uniformly mixed with step (2) resulting mixed material in blending tank through step (1) pretreated kitchen garbage, moisture content It adjusts to 90%, is cooled to 38 DEG C, is sent into the anaerobic digestion reaction that mesophilic anaerobic digestion tank carries out 20 days;Organic matter is in described Degradation in warm anaerobic digestor, the biogas part of generation are used for steam boiler, the steam of generation for kitchen garbage pretreatment and High-temperature hot hydrolysis heats, and natural gas is made after the remaining purified purification of biogas;Biogas residue and biogas slurry after anaerobic digestion is through machine Tool concentration makes solid content reach 15%, then through homogeneous pulp and pyrohydrolysis reaction to improve its dewatering, the reaction of pulp pyrohydrolysis Material afterwards cools to 80 DEG C, dehydration to moisture content 70%, then Nutrition Soil is made lower than 40% through desiccation to moisture content, takes off The biogas slurry a part generated during water, which flows back, to be utilized, and redundance is discharged into sewage treatment plant's processing.
It is that mechanical sorting machine removes sundries of the partial size greater than 50mm, crusberscreen that step (1) multi-stage screening, which crushes, Broken and heat water-spraying is carried out to material, and removes the sundries that partial size is greater than 25mm, vibrating screen screen-aperture is 3mm, oversize It is sieved again through vibrating screen after pulverizer crushes, undersize material removes the sundries such as tiny tile, sandstone, iron filings through desander.
Step (1) water-oil separating and slurrying are as follows: after material is heated to 50 ± 5 DEG C by steam heating, using Feed separation is light phase, heavy phase, solid slag three-phase by centrifuge separation;Light phase is by carrying out water-oil separating after being steam heated to 85 ± 5 DEG C For crude oil rouge and water phase, crude oil rouge moisture content≤3%, water phase oil content≤0.2%, water phase a part as high-temperature-hot-water reuse, Moisture content of the remainder for the step (3) mixed material adjusts;Solid slag mixes to obtain meal after being slurried material with heavy phase Kitchen rubbish pre-processes resulting material.
Mechanical stirring is used in step (3) the mesophilic anaerobic digestion tank.
Present invention process has the advantages that compared with prior art
(1) before high-temperature-hot-water solution is usually located at anaerobic digestion by other techniques, and high-temperature-hot-water solution is located at and detests by this technique It is to improve material dewatering performance with high-temperature-hot-water solution rather than improve anaerobic digestion performance after oxygen digestion.Before anaerobic digestion High-temperature-hot-water solution is carried out, can inhibit even to kill anaerobic digestion microorganism, cause subsequent anaerobic digestion process because of anaerobic digestion Microbial activity is insufficient and less effective.High-temperature-hot-water solution is carried out after anaerobic digestion and is avoided that this problem, moreover it is possible to be improved Material dewatering performance.
(2) this technique can be suitble to handle highly filled up to 10% organic solid waste.
(3) this technique can be suitably used for a plurality of types of wastes, as sludge, kitchen garbage, excrement, stalk, food market are organic Waste etc..
(4) can integrated treatment sludge, excrement and kitchen garbage, natural gas and Nutrition Soil can be produced, in technical process Biogas slurry flow back and utilize, reduce externally discharge, realize sludge, excrement and changing food waste into resources, emission reduction and harmless treatment.
Detailed description of the invention
Fig. 1 is the process flow chart that sludge, excrement and kitchen garbage of the present invention cooperate with anaerobic digestion process.
Specific embodiment
Below in conjunction with attached drawing to technology and detailed description of the invention, but do not constitute limiting the scope of the invention.
Present invention process process is as shown in Figure 1.The technique includes kitchen garbage pretreatment, sludge and excrement pretreatment, master Processing.
1, kitchen garbage pre-processes
Kitchen garbage pretreatment includes: discharging charging, multi-stage screening crushing, water-oil separating and slurrying.
(1) discharging is fed
The vehicle of kitchen garbage is loaded after weight bridge weighing, travels to discharging hall, kitchen garbage is poured into material-receiving device Kitchen garbage is delivered to mechanical sorting machine by the Shaftless screw conveyor of receiving hopper, receiving hopper bottom belt draining function.
It is escaped to reduce the smell that discharging generates, automatic hydraulic open-close cover is set at the top of receiving hopper, and it is fast that the discharging Room sets two pass Fast rolling screen door, the discharging Room and material-receiving device keep negative pressure, hopper region and other areas of pretreatment workshop by odor collection system Domain is separated by partition wall, and odor collection system is arranged to this region emphasis.
(2) multi-stage screening crushes
Mechanical sorting machine removes the sundries (such as metal, tile, vial, polybag) that partial size is greater than 50mm;Crusberscreen pair Material is crushed, heat water-spraying, and removes the sundries (such as bottle cap, small plastic bag, chopsticks) that partial size is greater than 25mm.This two fraction 95% or more sundries, obtains the homogenous mass based on organic matter in choosing removal material.Vibrating screen screen-aperture is 3mm, on sieve Object is sieved through vibrating screen again after pulverizer crushes, and undersize material removes the sundries such as tiny tile, sandstone, iron filings through desander, To meet the feed needs of oil-water separation system.
(3) water-oil separating and slurrying
Heater is passed through after material is heated to 50 ± 5 DEG C by steam, and feed separation is light phase, heavy phase, solid slag by horizontal centrifuge Three-phase.Light phase is temporarily stored into grease temporary storage tank, is promoted to heater by entering vertical centrifugal machine after being steam heated to 85 ± 5 DEG C through pump Water-oil separating is carried out, crude oil rouge (moisture content≤3%) is stored in grease holding vessel, and water phase (oil content≤0.2%) enters storage pool, A part is used as high-temperature-hot-water reuse, and residue is sent to the blending tank of main process task.After solid slag is slurried material by aquation beater With heavy phase by the blending tank that is pumped into main process task.
2, sludge, excrement pretreatment
Sludge, excrement pretreating process include discharging charging, homogenate.
(1) discharging is fed
After weight bridge weighing, sludge, excrement are transported to discharging hall by transport vehicle, pour into the reception feed bin for being installed on underground, connect Setting automatic hydraulic open-close cover prevents exhaust gas diffusion at the top of receiving warehouse.
(2) homogenate
Material is pumped to equal stock tank through screw conveyor and plunger by reception bin bottom rectangle heavy caliber discharge hole for discharge, if The blender for being placed in equal stock tank top stirs evenly sludge and excrement, then by being pumped into blending tank and pretreated kitchen garbage Mixing.
3, anaerobic digestion main process task technique is cooperateed with
Kitchen garbage, sludge and excrement are sent into blending tank with backflow biogas slurry after pretreatment are uniformly mixed respectively, moisture content It adjusts to 90%, is cooled to 38 DEG C through double-tube heat exchanger, the anaerobic digestion for being pumped into the progress 20 days of mesophilic anaerobic digestion tank is anti- It answers.Digester uses mechanical stirring.Organic matter is degraded in digester, and the biogas part of generation is used for steam boiler, generates steaming Vapour is heated for kitchen garbage pretreatment and high-temperature hot hydrolysis, and natural gas is made after the remaining purified purification of biogas.Anaerobism Postdigestive biogas residue and biogas slurry make solid content reach 15% through mechanical thickening, high-temperature-hot-water solution unit are pumped into, through homogeneous pulp It reacts with the pyrohydrolysis of high temperature and high pressure steam (150~170 DEG C of temperature, 0.5~0.8MPa of pressure) effect to improve its dehydration property Can, the material after the reaction of pulp pyrohydrolysis is cooled to 80 DEG C by cooling system, is dehydrated to moisture content about through centrifugal dehydrator 70%, it send through screw conveyor to drying bed, nutrition is made lower than 40% to moisture content using solar energy and boiler afterheat desiccation Soil.The biogas slurry a part generated in dehydration is discharged into sewage treatment plant's processing, and a part is back to homogenate pond.
The above-mentioned technique cooperatively processing sludge of the present embodiment, kitchen garbage, the total 300t/d of excrement, wherein sludge 245t/d, Kitchen garbage 50t/d, excrement 5t/d.Output biogas is 50Nm3Biogas/t material, 5.48 × 106Nm3/ a, Nutrition Soil 0.18t Nutrition Soil/t material, 1.98 × 104t/a.The biogas substitution coal of generation or the CO of petrochemical industry natural gas2Emission reduction is respectively 13.12kgCO2/ t material, 1436.64 t CO2/ a and 5.04kgCO2/ t material, 551.88t CO2/a;Nutrition Soil replacing fertilizer CO2Emission reduction is 46.26kg CO2/ t material, 5065.47t CO2/a.Degradation effect of organic compound is up to 60%.
These parameters illustrate present invention process with stable, degradation effect of organic compound is high, recycling is effective excellent Point.

Claims (4)

1. sludge, excrement and kitchen garbage cooperate with anaerobic digestion process, which comprises the following steps:
(1) kitchen garbage pre-processes: successively by multi-stage screening crushing, water-oil separating and slurrying;
(2) sludge, excrement pretreatment:
Sludge and excrement are stirred evenly, and mixed with the step (1) kitchen garbage pretreatment resulting material;
(3) Anaerobic Digestion is cooperateed with
It is uniformly mixed in blending tank through step (1) pretreated kitchen garbage with step (2) resulting mixed material, it is aqueous Rate is adjusted to 90%, is cooled to 38 DEG C, is sent into the anaerobic digestion reaction that mesophilic anaerobic digestion tank carries out 20 days;Organic matter is described Degradation in mesophilic anaerobic digestion tank, the biogas part of generation are used for steam boiler, and the steam of generation is pre-processed for kitchen garbage It is heated with high-temperature hot hydrolysis, natural gas is made after the remaining purified purification of biogas;Biogas residue and biogas slurry warp after anaerobic digestion Mechanical thickening makes solid content reach 15%, then through homogeneous pulp and pyrohydrolysis reaction to improve its dewatering, pulp pyrohydrolysis is anti- Material after answering cools to 80 DEG C, dehydration to moisture content 70%, then Nutrition Soil is made lower than 40% through desiccation to moisture content, The biogas slurry a part reflux generated in dehydration utilizes, and redundance is discharged into sewage treatment plant's processing.
2. institute's sludge as described in claim 1, excrement and kitchen garbage cooperate with anaerobic digestion process, which is characterized in that described It is that mechanical sorting machine removes sundries of the partial size greater than 50mm that step (1) multi-stage screening, which crushes, and crusberscreen carries out brokenly material Broken and heat water-spraying, and the sundries that partial size is greater than 25mm is removed, vibrating screen screen-aperture is 3mm, and oversize is crushed through pulverizer It is sieved again through vibrating screen afterwards, undersize material removes the sundries such as tiny tile, sandstone, iron filings through desander.
3. institute's sludge as described in claim 1, excrement and kitchen garbage cooperate with anaerobic digestion process, which is characterized in that described Step (1) water-oil separating and slurrying are as follows: after material is heated to 50 ± 5 DEG C by steam heating, using centrifuge separation by object Material is separated into light phase, heavy phase, solid slag three-phase;Light phase is crude oil rouge and water by carrying out water-oil separating after being steam heated to 85 ± 5 DEG C Phase, crude oil rouge moisture content≤3%, water phase oil content≤0.2%, water phase a part are used for as high-temperature-hot-water reuse, remainder The moisture content of step (3) mixed material adjusts;Solid slag mixes to obtain kitchen garbage pretreatment after being slurried material with heavy phase Resulting material.
4. institute's sludge as described in claim 1, excrement and kitchen garbage cooperate with anaerobic digestion process, which is characterized in that described Mechanical stirring is used in step (3) mesophilic anaerobic digestion tank.
CN201910174596.XA 2019-03-08 2019-03-08 Sludge, excrement and kitchen garbage cooperate with anaerobic digestion process Pending CN109942161A (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
CN201910174596.XA CN109942161A (en) 2019-03-08 2019-03-08 Sludge, excrement and kitchen garbage cooperate with anaerobic digestion process

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
CN201910174596.XA CN109942161A (en) 2019-03-08 2019-03-08 Sludge, excrement and kitchen garbage cooperate with anaerobic digestion process

Publications (1)

Publication Number Publication Date
CN109942161A true CN109942161A (en) 2019-06-28

Family

ID=67009412

Family Applications (1)

Application Number Title Priority Date Filing Date
CN201910174596.XA Pending CN109942161A (en) 2019-03-08 2019-03-08 Sludge, excrement and kitchen garbage cooperate with anaerobic digestion process

Country Status (1)

Country Link
CN (1) CN109942161A (en)

Cited By (9)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN110407411A (en) * 2019-08-01 2019-11-05 浙江天地环保科技有限公司 A kind of livestock and poultry feces anaerobic digestion biogas slurry pyrohydrolysis reclaiming system and method
CN110479733A (en) * 2019-07-25 2019-11-22 广东路通投资管理集团有限公司 A kind of rubbish from cooking high temperature microbe processing method
CN110538861A (en) * 2019-09-26 2019-12-06 中铁环境科技工程有限公司 Kitchen waste and sludge co-processing system and method
CN110803845A (en) * 2019-11-27 2020-02-18 长沙凯天工研院环保服务有限公司 Biological conditioner and method for improving dehydration performance of anaerobic digestion substances of kitchen waste
CN111606536A (en) * 2020-04-20 2020-09-01 同济大学 Method for sludge dewatering by synergistic reinforcement of anaerobic biological acidification of excess sludge and low-temperature hydrothermal coupling of kitchen waste
CN112759428A (en) * 2020-12-11 2021-05-07 上海然得环境科技有限公司 A equipment for producing fertilizer
CN113020211A (en) * 2021-03-08 2021-06-25 上海市城市建设设计研究总院(集团)有限公司 Kitchen waste and sludge synergistic anaerobic digestion system and method
CN115254921A (en) * 2022-05-10 2022-11-01 嘉兴市绿能环保科技有限公司 Kitchen waste treatment process
CN116114569A (en) * 2022-12-22 2023-05-16 国投信开水环境投资有限公司 Nutrient soil and preparation method and application thereof

Citations (3)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
EP0871597A1 (en) * 1995-01-14 1998-10-21 VESTERAGER, Niels Ole Method of treating a biomass in order to remove heavy metals with hydrogen sulphide
CN102836863A (en) * 2012-08-30 2012-12-26 北京世纪国瑞环境工程技术有限公司 Comprehensive treatment method for kitchen waste, town excrement and municipal sludge
CN104909530A (en) * 2015-05-25 2015-09-16 东南大学 Anaerobic digestion sludge conditioning system and method

Patent Citations (3)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
EP0871597A1 (en) * 1995-01-14 1998-10-21 VESTERAGER, Niels Ole Method of treating a biomass in order to remove heavy metals with hydrogen sulphide
CN102836863A (en) * 2012-08-30 2012-12-26 北京世纪国瑞环境工程技术有限公司 Comprehensive treatment method for kitchen waste, town excrement and municipal sludge
CN104909530A (en) * 2015-05-25 2015-09-16 东南大学 Anaerobic digestion sludge conditioning system and method

Non-Patent Citations (3)

* Cited by examiner, † Cited by third party
Title
冯启明等: "《非金属矿产加工与开发利用》", 31 December 2010, 地质出版社 *
汪国平: "《船舶与钢结构的涂装及防蚀技术》", 30 April 1993, 国防工业出版社 *
赵由才: "《农村生活垃圾处理与资源化利用技术》", 31 January 2018, 冶金工业出版社 *

Cited By (11)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN110479733A (en) * 2019-07-25 2019-11-22 广东路通投资管理集团有限公司 A kind of rubbish from cooking high temperature microbe processing method
CN110407411A (en) * 2019-08-01 2019-11-05 浙江天地环保科技有限公司 A kind of livestock and poultry feces anaerobic digestion biogas slurry pyrohydrolysis reclaiming system and method
CN110538861A (en) * 2019-09-26 2019-12-06 中铁环境科技工程有限公司 Kitchen waste and sludge co-processing system and method
CN110803845A (en) * 2019-11-27 2020-02-18 长沙凯天工研院环保服务有限公司 Biological conditioner and method for improving dehydration performance of anaerobic digestion substances of kitchen waste
CN111606536A (en) * 2020-04-20 2020-09-01 同济大学 Method for sludge dewatering by synergistic reinforcement of anaerobic biological acidification of excess sludge and low-temperature hydrothermal coupling of kitchen waste
US12006271B2 (en) 2020-04-20 2024-06-11 Tongji University Method for sludge dewatering using kitchen waste to synergistically enhance anaerobic biological acidification and low-temperature thermal hydrolysis of excess sludge
CN112759428A (en) * 2020-12-11 2021-05-07 上海然得环境科技有限公司 A equipment for producing fertilizer
CN112759428B (en) * 2020-12-11 2022-09-30 上海然得环境科技有限公司 A equipment for producing fertilizer
CN113020211A (en) * 2021-03-08 2021-06-25 上海市城市建设设计研究总院(集团)有限公司 Kitchen waste and sludge synergistic anaerobic digestion system and method
CN115254921A (en) * 2022-05-10 2022-11-01 嘉兴市绿能环保科技有限公司 Kitchen waste treatment process
CN116114569A (en) * 2022-12-22 2023-05-16 国投信开水环境投资有限公司 Nutrient soil and preparation method and application thereof

Similar Documents

Publication Publication Date Title
CN109942161A (en) Sludge, excrement and kitchen garbage cooperate with anaerobic digestion process
CN103008322B (en) Kitchen waste treatment system
CN102249477B (en) Processing method for oil-water separation of kitchen garbage
CN103706615B (en) One way of life refuse disposal system and method
CN205687770U (en) A kind of mud and the processing means of changing food waste
CN103084380B (en) Municipal solid waste processing system and processing method
CN112661372A (en) Household garbage, kitchen garbage, municipal excrement and municipal sludge co-treatment method
CN204747046U (en) Portable meal kitchen, surplus organic refuse collection in kitchen, transportation and online processing apparatus in succession
Zaher et al. Producing energy and fertilizer from organic municipal solid waste
CN102240659B (en) Equipment for integrally treating oil-water separation of kitchen garbage
CN105886330A (en) Municipal domestic solid waste integrated treatment process system
CN110695053A (en) Treatment system and method for various solid wastes in circulating industrial park
CN107460111A (en) Organic solid castoff processing system and its method of disposal based on subcritical hydrolysis
CN104907316B (en) A kind of kitchen garbage and civic feces total system and its method
JP3651836B2 (en) Organic waste treatment methods
JP5040641B2 (en) Organic waste slurry storage method and fuel conversion method, biomass fuel, and organic waste slurry storage device
CN106077029A (en) Domestic garbage resource integrated conduct method and processing system
CN211247719U (en) Processing system for various solid wastes in circulating industrial park
CN103551367B (en) Municipal living refuse comprehensive treatment method
CN115958051B (en) Cooperative treatment system and treatment method for food wastes and kitchen wastes
CN212703648U (en) Wet-type process treatment system for municipal domestic waste
CN217121247U (en) Kitchen garbage aerobic fermentation integration equipment
CN109467299A (en) A method of improving methane factor of created gase in excess sludge anaerobic digestion
GB2332196A (en) Process and apparatus for treatment of waste
CN212565795U (en) Kitchen waste hydrogen-rich energy combustion system

Legal Events

Date Code Title Description
PB01 Publication
PB01 Publication
SE01 Entry into force of request for substantive examination
SE01 Entry into force of request for substantive examination
RJ01 Rejection of invention patent application after publication

Application publication date: 20190628

RJ01 Rejection of invention patent application after publication