CN1900294A - Process for producing methane from city life organic waste - Google Patents
Process for producing methane from city life organic waste Download PDFInfo
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- CN1900294A CN1900294A CNA2005100441664A CN200510044166A CN1900294A CN 1900294 A CN1900294 A CN 1900294A CN A2005100441664 A CNA2005100441664 A CN A2005100441664A CN 200510044166 A CN200510044166 A CN 200510044166A CN 1900294 A CN1900294 A CN 1900294A
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- Y—GENERAL TAGGING OF NEW TECHNOLOGICAL DEVELOPMENTS; GENERAL TAGGING OF CROSS-SECTIONAL TECHNOLOGIES SPANNING OVER SEVERAL SECTIONS OF THE IPC; TECHNICAL SUBJECTS COVERED BY FORMER USPC CROSS-REFERENCE ART COLLECTIONS [XRACs] AND DIGESTS
- Y02—TECHNOLOGIES OR APPLICATIONS FOR MITIGATION OR ADAPTATION AGAINST CLIMATE CHANGE
- Y02E—REDUCTION OF GREENHOUSE GAS [GHG] EMISSIONS, RELATED TO ENERGY GENERATION, TRANSMISSION OR DISTRIBUTION
- Y02E50/00—Technologies for the production of fuel of non-fossil origin
- Y02E50/30—Fuel from waste, e.g. synthetic alcohol or diesel
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- 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
- Y02W10/00—Technologies for wastewater treatment
- Y02W10/20—Sludge processing
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Abstract
The technological process of producing methane with city domestic organic waste, including swill from restaurant and dining room, organic waste from vegetable market and food producing factory, excrement and plant stalks, includes the steps of collecting, sorting, crushing, sterilizing, acidification regulation, anaerobic fermentation and desulfurizing. The present invention makes it possible to utilize city domestic organic waste resource effectively.
Description
" technical field " the present invention relates to the production technique that a kind of biogas is produced, and particularly belonging to a kind of is the biogas reparation technology technology of raw material with the urban life organic waste.
" background technology " is along with quickening of urbanization process, the raising of living standards of the people, the quantity of urban life organic waste is increasing sharply, and is also more and more outstanding to the influence of environment, become one of the most serious public hazards in the world today, become the greatest contamination source of contaminate environment.Cleaning in time and processing urban life organic waste are to build graceful, clean and tidy, civilized modern city conditio sune qua non.The present most cities and towns of China still this type of organic waste as animal-feed, this disposal means can not satisfy the needs of environment protection and HUMAN HEALTH health.Handle this type of waste method at present in the world and be mainly landfill, compost and burning disposal, investment and land occupation are bigger, also cause secondary pollution easily.One of some effective that solves the pollution problem of urban life organic waste is exactly as a kind of resource recycling with it, for example, with the urban life organic waste is that raw material is produced biogas, reached the requirement of domestic rubbish disposal minimizing, resource utilization, innoxious, stabilization, the secondary pollution of having avoided organic waste in collection, transportation, transfer process, to cause; Rubbish is eliminated in the source, user surrounding environment is improved; Help the promotion and implementation of collection of urban life organic waste and resource reutilization.Through retrieval, discovery has formerly applies for a patent the handling problem that relates to the urban life organic waste: No. 91106919.4 patents " domestic waste basket case method anaerobic dry fermentation treatment process ", a kind of anaerobic dry fermentation treatment process about municipal wastes is disclosed, it is characterized in that municipal wastes is collected the porous basket case of packing into, company's basket is gone into the pond and is done fermentative processing, the biogas that fermentation produces provides domestic energy, and waste residue is made organic fertilizer.Other has No. 90103442.8 patents " closed container is handled the domestic refuse technology ", a kind of technology that adopts closed container to handle the domestic refuse after letter sorting is mainly disclosed, after being domestic refuse tank filling fermentation with letter sorting, the organic waste that produces becomes fertilizer, and the raw material of employing is mainly domestic refuse and the people urinates liquid dung.The shortcoming of above-mentioned patented technology is that biogas output is low, and labour intensity is big, and treatment capacity is little, can not form mass-producing, benefit production, so cause above-mentioned technology to be difficult to promote.Though above-mentioned patent application has been mentioned domestic refuse has been handled, but be dry process, treatment capacity very little, do not specify making aspect embodiment and corresponding processing step and the technical indicator yet, with regard to the processing and utilization of urban life organic waste, above-mentioned patent application and unexposed any content with practical value.In a word, above-mentioned formerly applying for a patent not with regard to the processing of urban life organic waste and utilization provides complete and processing method necessity.
" summary of the invention " purpose of the present invention promptly is to provide a kind of Technology of producing biogas with the urban life organic waste, to reach the purpose that the urban life organic waste is effectively handled and actively utilized.
Technology of producing biogas with the urban life organic waste disclosed in this invention, be the organic waste that hogwash, food market and food processing plant etc. that restaurant and each enterprises and institutions dining room produce are produced and the human faecal mass of resident living area, the organic waste centralized collection such as straw of city suburbs, carry out artificial and/or mechanical sorting, pulverizing, sterilization and disinfection, acidifying adjusting, anaerobically fermenting and desulfurization, thereby produce biogas; It is characterized in that, comprise the steps: raw material collection, letter sorting, pulverizing, sterilization and disinfection, acidifying adjusting, anaerobically fermenting, desulfurization, storage, wherein,
Step 1: raw material is collected; With tank car the organic waste that restaurant, dining room, food processing plant produce is collected, left in the storage pool; The organic waste collection of food market is deposited in the independent pond; The human faecal mass of resident living area collected leave in the independent storage pool;
Step 2: letter sorting; Earlier the organic waste that produces of the restaurant that step 1 is obtained, dining room, food processing plant carries out solid-liquid separation, and wherein soup is leached, and deposits standby; Solid substance and the iron plate in the organic waste of food market, plastics bag, wooden chopsticks, shell, glass, ceramics and the bone that separation is obtained sorts out again, obtains purified solid organic castoff;
Step 3: pulverize; Pure solid organic castoff with step 2 obtains is crushed to starchiness; And mix with the isolated soup of step 2, stir, obtain mixing the pulpous state feed liquid;
Step 4: sterilization and disinfection; The mixing pulpous state feed liquid that step 3 obtains is introduced in the sterilization pool, heated, kept 20～30 minutes, the germ in the feed liquid, parasitic ovum are killed, obtain aseptic feed liquid to 60～80 ℃;
Step 5: acidifying is regulated; The feed liquid that step 4 obtains being mixed with the human faecal mass of the resident living area of step 1 collection, add alkaline agent, is 5.8～6.2 to regulate its potential of hydrogen, squeezes in the acidification pool with pump then, carries out acidification;
Step 6: anaerobically fermenting; The acidifying feed liquid that step 5 obtains is introduced in the anaerobically fermenting pond, carried out anaerobically fermenting, with the collecting methane that produces;
Step 7: desulfurization; Step 6 is obtained biogas to be sent into thionizer and carries out desulfurization and handle;
Step 8: store; Biogas after step 7 desulfurization is introduced gas-holder to be stored.
Because Technology of producing biogas with the urban life organic waste disclosed in this invention, it is made raw material and is mainly organic waste that hogwash, food market and food processing plant etc. that restaurant and each enterprises and institutions dining room produce produce and the human faecal mass of resident living area, the organic wastes such as straw of city suburbs, therefore can handle in large quantity and utilize the organic waste that the city produces, the environmental pollution that causes eliminating this type of waste has positive effect, and has and produce continual and steady, high, the measured effect of matter of output.
The organic waste composition that " embodiment " urban life produces is comparatively complicated, concentrates and reclaims laggard pedestrian worker and/or mechanical sorting, obtains purified organic waste, carries out sterilization and disinfection, acidifying adjusting, anaerobically fermenting, desulfurization and storage again, wherein,
Raw material is collected: use special-purpose tank car, regularly organic wastes such as restaurant, each enterprises and institutions dining room, food processing plant are collected, and left in the storage pool; Organic waste collection in food market is deposited in the independent pond; The human faecal mass of resident living area collected leave in the independent storage pool.
Letter sorting: earlier the organic waste with the restaurant that collects, each enterprises and institutions dining room, food processing plant etc. utilizes centrifugal separator to carry out solid-liquid separation, and wherein soup is leached, and deposits standby; The composition that should not pulverize such as solid substance that separation is obtained and the iron plate in the organic waste of food market, plastics bag, wooden chopsticks, shell, glass, ceramics, bone sorts out again, obtains purified organic waste.
Pulverize: the pure solid organic castoff with previous step obtains, utilize pulverizer to be crushed to starchiness, and mix with isolated soup, stir.
Sterilization and disinfection: the mixed pulp pasty state feed liquid that previous step obtains is introduced in the sterilization pool, heated, kept 20 minutes to 70 ℃.Germ in the feed liquid, parasitic ovum etc. are killed, obtain aseptic feed liquid.
Acidifying is regulated: insert the part anaerobic species earlier in acidification pool, the feed liquid that previous step is obtained is mixed with the human faecal mass of resident living area again, add alkaline agent, to regulate its potential of hydrogen about 6.0, squeeze in the acidifying equalizing tank with pump then, carry out acidification.
Anaerobically fermenting: the acidifying feed liquid that previous step obtains is introduced in the anaerobic digester, carried out the anaeration in normal temperature fermentation, with the collecting methane that produces.
Biogas desulfurization: the biogas that previous step is obtained is sent into thionizer and is carried out desulfurization and handle.
Biogas stores: the biogas after the previous step desulfurization is introduced the gas-holder storage get final product, and keep certain pressure.
In addition, the solid substance that the natural pond liquid that can also utilize anaerobically fermenting to produce obtains after solid-liquid separation is produced solid organic fertilizer, utilizes the waste liquid that obtains to produce the liquid fertilising of dashing:
The natural pond liquid that obtains behind the anaerobically fermenting is carried out solid-liquid separation earlier, is raw material with the solid substance that obtains, and obtains solid organic fertilizer through the allotment of aerobic fermentation, endoplasm, oven dry sterilization, pelletizing forming again.
The natural pond liquid that obtains behind the anaerobically fermenting is carried out solid-liquid separation earlier, is raw material with the waste liquid that obtains, and obtains the liquid fertilising of dashing again through anaerobically fermenting, hydrolysis, allotment, filtration.
Above-mentioned dashing in the production craft step of fertilising about solid organic fertilizer and liquid state, the natural pond liquid that anaerobically fermenting produces is after solid-liquid separation, produce solid organic fertilizer and produce liquid other processing step basic identical with patent application formerly 200310114499.0 " is the fertilizer and the production technique thereof of making raw material with vinasse " towards fertilising, belong to existing known technology, so do not do repeat specification.
Technology of producing biogas with the urban life organic waste disclosed in this invention, can be in enormous quantities to the organic waste that urban life produces, successive is handled and utilize, not only offset except that environmental pollution and have positive effect, and turn waste into wealth, realize recycling economy, can be enterprise simultaneously and bring considerable economic.Therefore, the present invention has good economic benefit and social benefit, and the resource utilization, the benefit treatment technology that are suitable for as the urban life organic waste are promoted.
Claims (2)
1, a kind of Technology of producing biogas with the urban life organic waste, the straw of human faecal mass, city suburbs that is organic waste that hogwash, food market and food processing plant that restaurant and dining room produce are produced and resident living area is as the organic waste centralized collection, carry out artificial and/or mechanical sorting, pulverizing, sterilization and disinfection, acidifying adjusting, anaerobically fermenting and desulfurization, thereby produce biogas; It is characterized in that, comprise the steps:
Step 1: raw material is collected; With tank car the organic waste that restaurant, dining room, food processing plant produce is collected, left in the storage pool; The organic waste collection of food market is deposited in the independent pond; The human faecal mass of resident living area collected leave in the independent storage pool;
Step 2: letter sorting; Earlier the organic waste that produces of the restaurant that step 1 is obtained, dining room, food processing plant carries out solid-liquid separation, and wherein soup is leached, and deposits standby; Solid substance and the iron plate in the organic waste of food market, plastics bag, wooden chopsticks, shell, glass, ceramics and the bone that separation is obtained sorts out again, obtains purified solid organic castoff;
Step 3: pulverize; Pure solid organic castoff with step 2 obtains is crushed to starchiness; And mix with the isolated soup of step 2, stir, obtain mixing the pulpous state feed liquid;
Step 4: sterilization and disinfection; The mixing pulpous state feed liquid that step 3 obtains is introduced in the sterilization pool, heated, kept 20～30 minutes, the germ in the feed liquid, parasitic ovum are killed, obtain aseptic feed liquid to 60～80 ℃;
Step 5: acidifying is regulated; The feed liquid that step 4 obtains being mixed with the human faecal mass of the resident living area of step 1 collection, add alkaline agent, is 5.8～6.2 to regulate its potential of hydrogen, squeezes in the acidification pool with pump then, carries out acidification;
Step 6: anaerobically fermenting; The acidifying feed liquid that step 5 obtains is introduced in the anaerobically fermenting pond, carried out anaerobically fermenting, with the collecting methane that produces;
Step 7: desulfurization; Step 6 is obtained biogas to be sent into thionizer and carries out desulfurization and handle;
Step 8: store; Biogas after step 7 desulfurization is introduced gas-holder to be stored.
2, Technology of producing biogas with the urban life organic waste according to claim 1, its feature also is, comprise that also the solid substance that the natural pond liquid that utilizes anaerobically fermenting to produce obtains produces solid organic fertilizer after solid-liquid separation, utilize the waste liquid that obtains to produce the liquid fertilising of dashing:
The natural pond liquid that obtains behind the anaerobically fermenting is carried out solid-liquid separation earlier, is raw material with the solid substance that obtains, and obtains solid organic fertilizer through the allotment of aerobic fermentation, endoplasm, oven dry sterilization, pelletizing forming again;
The natural pond liquid that obtains behind the anaerobically fermenting is carried out solid-liquid separation earlier, is raw material with the waste liquid that obtains, and obtains the liquid fertilising of dashing again through anaerobically fermenting, hydrolysis, allotment, filtration.
Priority Applications (1)
| Application Number | Priority Date | Filing Date | Title |
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| CNB2005100441664A CN100557024C (en) | 2005-07-24 | 2005-07-24 | Produce the Technology of biogas with the urban life organic waste |
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| Application Number | Priority Date | Filing Date | Title |
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| CNB2005100441664A CN100557024C (en) | 2005-07-24 | 2005-07-24 | Produce the Technology of biogas with the urban life organic waste |
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| CN1900294A true CN1900294A (en) | 2007-01-24 |
| CN100557024C CN100557024C (en) | 2009-11-04 |
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Cited By (12)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| CN101857882A (en) * | 2010-06-11 | 2010-10-13 | 天津市环境保护科学研究院 | Process for producing biogas by two-stage anaerobic fermentation of crop stalk or livestock excrement |
| CN102151683A (en) * | 2010-12-02 | 2011-08-17 | 北京工商大学 | Damp and heat fermentation comprehensive harmless and resource processing system for kitchen waste |
| CN102247971A (en) * | 2011-05-05 | 2011-11-23 | 北京水气蓝德环保科技有限公司 | Process for treating kitchen waste by mechanical sorting and two-phase anaerobic fermentation |
| CN102286541A (en) * | 2011-07-14 | 2011-12-21 | 中城泓天(北京)环境科技发展有限公司 | Method for preparing biogas through food waste, urban sludge and urban excrement |
| CN102989748A (en) * | 2012-12-12 | 2013-03-27 | 郑州金土地能源科技有限公司 | Method for recycling kitchen waste |
| CN103787699A (en) * | 2014-02-14 | 2014-05-14 | 青岛吉曼新能源技术有限公司 | Treatment method and treatment device of town household garbage |
| CN103785669A (en) * | 2014-01-23 | 2014-05-14 | 天紫再生资源加工（天津）有限公司 | Domestic waste and straw reutilization comprehensive system |
| CN107353046A (en) * | 2016-05-09 | 2017-11-17 | 桐庐英力生态农业开发有限公司 | One kind utilizes food waste immersion organic fertilizer preparation method |
| CN108863475A (en) * | 2018-06-08 | 2018-11-23 | 广西大学 | The method for preparing selenium-enriched liquid organic fertilizer using the waste water and swine excrement in slaughterhouse |
| CN109081553A (en) * | 2018-08-22 | 2018-12-25 | 国诚集团有限公司 | A kind of municipal sewer mud purification method |
| CN109574717A (en) * | 2019-01-23 | 2019-04-05 | 镇江市中运城市环境治理有限公司 | A kind of production method and system preparing organic fertilizer using rubbish |
| CN112830840A (en) * | 2021-01-21 | 2021-05-25 | 聊城职业技术学院 | Composite microbial fertilizer and preparation method and application thereof |
-
2005
- 2005-07-24 CN CNB2005100441664A patent/CN100557024C/en not_active Expired - Fee Related
Cited By (14)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| CN101857882A (en) * | 2010-06-11 | 2010-10-13 | 天津市环境保护科学研究院 | Process for producing biogas by two-stage anaerobic fermentation of crop stalk or livestock excrement |
| CN102151683A (en) * | 2010-12-02 | 2011-08-17 | 北京工商大学 | Damp and heat fermentation comprehensive harmless and resource processing system for kitchen waste |
| CN102247971A (en) * | 2011-05-05 | 2011-11-23 | 北京水气蓝德环保科技有限公司 | Process for treating kitchen waste by mechanical sorting and two-phase anaerobic fermentation |
| CN102247971B (en) * | 2011-05-05 | 2012-11-14 | 北京水气蓝德环保科技有限公司 | Process for treating kitchen waste by mechanical sorting and two-phase anaerobic fermentation |
| CN102286541A (en) * | 2011-07-14 | 2011-12-21 | 中城泓天(北京)环境科技发展有限公司 | Method for preparing biogas through food waste, urban sludge and urban excrement |
| CN102989748A (en) * | 2012-12-12 | 2013-03-27 | 郑州金土地能源科技有限公司 | Method for recycling kitchen waste |
| CN103785669A (en) * | 2014-01-23 | 2014-05-14 | 天紫再生资源加工（天津）有限公司 | Domestic waste and straw reutilization comprehensive system |
| CN103787699A (en) * | 2014-02-14 | 2014-05-14 | 青岛吉曼新能源技术有限公司 | Treatment method and treatment device of town household garbage |
| CN103787699B (en) * | 2014-02-14 | 2016-02-24 | 青岛吉曼新能源技术有限公司 | The treatment process of a kind of villages and small towns domestic refuse and treatment unit |
| CN107353046A (en) * | 2016-05-09 | 2017-11-17 | 桐庐英力生态农业开发有限公司 | One kind utilizes food waste immersion organic fertilizer preparation method |
| CN108863475A (en) * | 2018-06-08 | 2018-11-23 | 广西大学 | The method for preparing selenium-enriched liquid organic fertilizer using the waste water and swine excrement in slaughterhouse |
| CN109081553A (en) * | 2018-08-22 | 2018-12-25 | 国诚集团有限公司 | A kind of municipal sewer mud purification method |
| CN109574717A (en) * | 2019-01-23 | 2019-04-05 | 镇江市中运城市环境治理有限公司 | A kind of production method and system preparing organic fertilizer using rubbish |
| CN112830840A (en) * | 2021-01-21 | 2021-05-25 | 聊城职业技术学院 | Composite microbial fertilizer and preparation method and application thereof |
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| Publication number | Publication date |
|---|---|
| CN100557024C (en) | 2009-11-04 |
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