CN1021432C - Quick composting dynamic fermentation device for municipal refuse - Google Patents
Quick composting dynamic fermentation device for municipal refuse Download PDFInfo
- Publication number
- CN1021432C CN1021432C CN88101327A CN88101327A CN1021432C CN 1021432 C CN1021432 C CN 1021432C CN 88101327 A CN88101327 A CN 88101327A CN 88101327 A CN88101327 A CN 88101327A CN 1021432 C CN1021432 C CN 1021432C
- Authority
- CN
- China
- Prior art keywords
- fermentation cabin
- fermentation
- rubbish
- discharging machine
- spiral discharging
- 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.)
- Expired - Fee Related
Links
- 238000000855 fermentation Methods 0.000 title claims abstract description 73
- 230000004151 fermentation Effects 0.000 title claims abstract description 73
- 238000009264 composting Methods 0.000 title claims description 10
- 238000007599 discharging Methods 0.000 claims abstract description 31
- 239000002699 waste material Substances 0.000 claims description 10
- 238000009423 ventilation Methods 0.000 claims description 5
- 239000004575 stone Substances 0.000 claims description 3
- 230000001413 cellular effect Effects 0.000 claims description 2
- 239000010813 municipal solid waste Substances 0.000 abstract description 50
- 239000000463 material Substances 0.000 abstract description 39
- 238000000034 method Methods 0.000 abstract description 12
- 238000005516 engineering process Methods 0.000 abstract description 4
- 230000003203 everyday effect Effects 0.000 abstract description 4
- 239000002361 compost Substances 0.000 description 5
- 241000894006 Bacteria Species 0.000 description 4
- 238000000354 decomposition reaction Methods 0.000 description 3
- 241000186361 Actinobacteria <class> Species 0.000 description 2
- 240000004808 Saccharomyces cerevisiae Species 0.000 description 2
- QVGXLLKOCUKJST-UHFFFAOYSA-N atomic oxygen Chemical compound [O] QVGXLLKOCUKJST-UHFFFAOYSA-N 0.000 description 2
- 238000004519 manufacturing process Methods 0.000 description 2
- 244000005700 microbiome Species 0.000 description 2
- 239000003895 organic fertilizer Substances 0.000 description 2
- 239000005416 organic matter Substances 0.000 description 2
- 229910052760 oxygen Inorganic materials 0.000 description 2
- 239000001301 oxygen Substances 0.000 description 2
- 230000003068 static effect Effects 0.000 description 2
- XLYOFNOQVPJJNP-UHFFFAOYSA-N water Substances O XLYOFNOQVPJJNP-UHFFFAOYSA-N 0.000 description 2
- 241000196324 Embryophyta Species 0.000 description 1
- 241000233866 Fungi Species 0.000 description 1
- 240000002853 Nelumbo nucifera Species 0.000 description 1
- 235000006508 Nelumbo nucifera Nutrition 0.000 description 1
- 108010066057 cabin-1 Proteins 0.000 description 1
- 229920002678 cellulose Polymers 0.000 description 1
- 239000001913 cellulose Substances 0.000 description 1
- 238000006243 chemical reaction Methods 0.000 description 1
- 238000010276 construction Methods 0.000 description 1
- 230000002950 deficient Effects 0.000 description 1
- 238000004134 energy conservation Methods 0.000 description 1
- 238000010907 mechanical stirring Methods 0.000 description 1
- 102000004169 proteins and genes Human genes 0.000 description 1
- 108090000623 proteins and genes Proteins 0.000 description 1
- 230000001105 regulatory effect Effects 0.000 description 1
- 230000000630 rising effect Effects 0.000 description 1
- 239000002689 soil Substances 0.000 description 1
- 210000002700 urine Anatomy 0.000 description 1
Images
Classifications
-
- Y—GENERAL TAGGING OF NEW TECHNOLOGICAL DEVELOPMENTS; GENERAL TAGGING OF CROSS-SECTIONAL TECHNOLOGIES SPANNING OVER SEVERAL SECTIONS OF THE IPC; TECHNICAL SUBJECTS COVERED BY FORMER USPC CROSS-REFERENCE ART COLLECTIONS [XRACs] AND DIGESTS
- Y02—TECHNOLOGIES OR APPLICATIONS FOR MITIGATION OR ADAPTATION AGAINST CLIMATE CHANGE
- Y02A—TECHNOLOGIES FOR ADAPTATION TO CLIMATE CHANGE
- Y02A40/00—Adaptation technologies in agriculture, forestry, livestock or agroalimentary production
- Y02A40/10—Adaptation technologies in agriculture, forestry, livestock or agroalimentary production in agriculture
- Y02A40/20—Fertilizers of biological origin, e.g. guano or fertilizers made from animal corpses
Landscapes
- Processing Of Solid Wastes (AREA)
- Fertilizers (AREA)
Abstract
The invention provides a device and a simple and quick treatment process for quick treatment of municipal refuse. The device consists of a garbage conveying mechanism and a fermentation bin which is provided with a spiral discharging mechanism and has a rectangular (or conical) inverted cone masonry structure. The rapid processing technology is realized by the processing device. After the fermentation bin is filled with garbage materials, the first fermentation period is four days (96 hours). Then, the spiral discharging machine can be started every day to discharge the bottom material layer (1/4 which occupies the whole fermentation material layer) in the fermentation bin, thereby realizing the continuous treatment of the garbage.
Description
The present invention relates to a kind of municipal wastes fast processing equipment.
Treatment of urban garbage always is a significant problem in the urban construction.Some cities have been faced with the condition that is surrounded by rubbish because rubbish can not get dealing carefully with.At present, the method for watering, sanitary landfill method and biological compost method are burnt in the general employing of processing of municipal wastes.Burn the method for watering, the meeting atmosphere pollution; The sanitary landfill rule can take a large amount of soils.The biological compost method that present world developed country generally adopts-fast dynamic zymotechnique, then be with municipal wastes after pre-sorting, insert in the large fermentation tank, and mechanical stirring device is set in fermentor tank, the rubbish material that places in the fermentor tank is ceaselessly stirred, to quicken the organic decomposition in the rubbish material, reach it and fully ferment, and make it to become organic fertilizer.Dynamically the subject matter of zymotechnique existence is fast: its device fabrication costliness, and need expend a large amount of energy in the treating processes, thereby cause the processing cost height, afford to make, and with not rising.
In view of the problem of above-mentioned existence, the purpose of this invention is to provide a kind of simple in structure, municipal wastes rapid composting and fermenting equipment that production cost is low, energy-conservation.
The municipal wastes rapid composting and fermenting equipment includes a garbage conveyor structure and a fermentation cabin that is provided with discharging mechanism is formed.
The garbage conveyor structure comprises a vertical lift, conveyor, rubbing board unloading machine and separatory funnel etc.
Fermentation cabin is the rectangular tiles stone structure (also can be the cone masonry structure of reverse taper) of a reverse taper, is provided with supplementary feed at the top of fermentation cabin and regulates pipeline, in the bottom of fermentation cabin, is provided with ventilation plant and screw rod discharging machine.The screw rod discharging machine is contained on the round dolly of fermentation cabin bottom, during discharging, can rotation, and again can be reciprocating by means of round dolly, the interior bed of material of cutting fermentation cabin.
The dynamic zymotechnique flow process of municipal wastes high-rate composting realizes that by means of whole fermentation unit its concrete technical process is as follows:
Will be through after the rubbish after the pre-sorting be in vertical lift, conveyor, rubbing board unloading machine, separatory funnel are packed fermentation cabin into, air feed is also regulated moisture, after ferment 96 hours (four round the clock), the rubbish material that is in lowermost layer has reached innoxious sanitary index through fully fermentation.At this moment, start the screw rod discharging machine, cutting and discharge the fermentation cabin bottom bed of material (for the whole bed of material that ferments in the fermentation cabin 1/4th).Meanwhile, the bed of material on incised layer top constantly rolls when the screw rod discharging machine rotates and automatically falls to the bottom according to its deadweight, adds new rubbish material simultaneously in fermentation cabin.After fermenting once more in 24 hours, start the screw rod discharging machine and carry out the discharging second time, discharge other 1/4th bed of materials that ferment in the fermentation cabin.So go round and begin again, all can go out once rubbish material every day, thereby formed the continuous processing of rubbish through fermenting in four days.
The present invention compares with existing urban waste disposal equipment and technical process, not only its device structure simple, be easy to make, and its technical process is simple and easy, is convenient to realize that the serialization of rubbish handles.
Accompanying drawing 1 has provided structural representation of the present invention
For the ease of understanding the present invention, the existing embodiment that provides in reference to the accompanying drawings is described in detail:
The municipal wastes rapid composting and fermenting equipment includes a garbage conveyor structure and a fermentation cabin that is provided with discharging mechanism is formed.
The garbage conveyor structure includes a vertical lift 1 and a rotary conveyor 2 that is connected mutually with vertical lift 1.On rotary conveyor 2, be provided with rubbing board unloading machine 3 and separatory funnel 4.
Fermentation cabin 5 is the rectangular tiles stone structure (can also be the cone masonry structure of reverse taper) of a reverse taper, and after delivering from godown for ease of the bottom material in the fermentation cabin 5, upper materials falls, and the back draught of fermentation cabin 5 is 4 degree.For making competent oxygen and moisture are arranged in the fermentation cabin 5, be provided with supplementary feed at the top of fermentation cabin 5 and regulate pipeline 6, the ventilation hole 7 that the bottom in fermentation cabin 5 is provided with cellular (lotus root shape), ventilation hole 7 communicates with the blower fan 9 that is arranged at fermentation cabin 5 outsides.Side at fermentation cabin 5 outer bottoms is provided with the reciprocal dolly 8 that screw rod discharging machine 10 is housed, and is provided with outfeed belt conveyor 11 at its opposite side.During discharging, but 10 rotations of screw rod discharging machine can be made back and forth movement by means of round dolly 8 again, cut the bottom rubbish bed of material in the fermentation cabin 5, and material is discharged on the rotary conveyor 11.
The rubbish high-rate composting is to utilize microorganisms such as bacterium in the rubbish, fungi, actinomycetes, yeast that organism in the rubbish is carried out biological chemistry to decompose.According to test, 10,000,000,000 bacteriums and millions of actinomycetes, yeast are arranged in one kilogram of rubbish approximately, therefore as long as the top condition of its needs being provided for these microorganisms, just can reach the purpose of rapid decomposing organic matter.In static fermentation technology, the fermentation of rubbish high-rate composting is finished in fermentation cabin, and its cycle was generally ten days.In 24 hours, in the rubbish windrow of bottom, because the oxygen supply abundance, the organism in the rubbish produces thermopositive reaction in the fermentation cabin, and temperature rises rapidly, about 60 ℃ high-temperature zone occurred.At this moment, the thermophilic bacterium in the rubbish pursues active, has replaced thermophilic bacteria gradually, and further decomposing organic matter, protein and part Mierocrystalline cellulose.Second day, lower floor continued to keep high temperature, and its warm area rises to the middle level.The 3rd day, except that in, lower floor continue to keep the high temperature, warm area rises to the upper strata scrap heap bed of material again, and begins to set up and keep the high temperature balance.The 4th day, downtrending appearred in the scrap heap bed of material in lower floor, and by the 5th day to the tenth day, lower floor's temperature descended gradually, and material properties enters steady state, and fermentation promptly comes to an end.At this moment, show that the innoxious sanitary index of the rubbish after the fermentation (compost) reaches, and can be used as the organic fertilizer use through sample examination.
The dynamic zymotechnique of municipal wastes high-rate composting, principle and practice according to static fermentation technology, with the rubbish bed of material in the fermentation cabin be divided into four layers (be discharging machine whenever go out a defective material be in the fermentation cabin rubbish bed of material after the fermentation 1/4th), after the rubbish in the fermentation cabin has been carried out disposable being filled with, continuously fermented four days, (during this period, organic decomposition volume-diminished in the rubbish in the fermentation cabin, should add new rubbish material), at this moment, lower floor's rubbish bed of material fully ferments in the fermentation cabin, and has reached innoxious sanitary index.At this moment, can start discharging machine, discharge the bottom rubbish bed of material in the fermentation cabin (for the fermentation back rubbish bed of material 1/4th).During discharging because the rotation of spiral discharging machine, the whole rubbish material layer in the fermentation cabin, up-down vibration thereupon, make simultaneously be in fermenting of upper strata the rubbish bed of material automatically drop down onto the bottom of fermentation cabin according to its deadweight.Meanwhile constantly in fermentation cabin, add new rubbish material, make it to keep normal state of saturation.After fermentation in a day, second day, then can start discharging machine again and discharge the bottom bed of material.The whole dischargings of putting into for the first time in the fermentation cabin through four days dischargings of rubbish finish, and the new rubbish material that is replenished during discharging in first day has reached innoxious sanitary index also through four days fermentation.So go round and begin again, all can add once new rubbish material every day, goes out once to have passed through fermentation in four days, reached the organic compost of innoxious sanitary index.
Its concrete operating process is as follows:
Will be through the vertical lift 1 of the rubbish after the pre-sorting, conveyor 2, rubbing board unloading machine 3, separatory funnel 4, pack into and fill up fermentation cabin 5.Start blower fan 9, air feed in fermentation cabin 5, and regulate pipeline 6 by the supplementary feed that is arranged at fermentation cabin 5 tops and in fermentation cabin 5, add water (it is desirable to human urine), to regulate its moisture.After four days (96 hours) fermentation, because organic decomposition in the rubbish, the volume of the fermented product (rubbish) in the fermentation cabin 5 reduces about 1/4~1/3 space.Reinforced, with new this space of rubbish material filling.At this moment, the upper strata in the fermentation cabin 5 is a virgin material, and lower floor finishes for fermenting, and has reached innoxious sanitary index.At this moment, start screw rod discharging machine 10,10 rotations on one side of screw rod discharging machine, make back and forth movement by means of round dolly 8 on one side, the rubbish bed of material that the fermentation of bottoms has finished in the cutting fermentation cabin 5, (be lower floor's fermented product 1/4), and it is discharged on the rotary conveyor 11.When 10 dischargings of screw rod discharging machine, the whole rubbish material layer in the fermentation cabin 5 moves up and down, and automatically drops down onto the bottom of fermentation cabin 5 under screw rod discharging machine 10 rotates.In fermentation cabin 5, add new rubbish material, treat that fermentation cabin is filled after, start blower fan 9 air feed in fermentation cabin 5, and add water, to regulate its moisture.Through fermentation once more in a day, started screw rod discharging machine 10 in second day once more, discharge the bottom bed of material (also be lower floor's fermented product 1/4).So go round and begin again, all can go out every day once through the organic compost four days, that reached innoxious sanitary index that ferments.
Claims (1)
- A kind of vertical lift (1) that contains, conveyor (2), rubbing board unloading machine (3), separatory funnel (4), fermentation cabin (5), blower fan (9), spiral discharging machine (10), the municipal wastes rapid composting and fermenting equipment of outfeed belt conveyor (11), it is characterized in that this fermentation cabin (5) is the cone masonry structure of the rectangular tiles stone structure or the reverse taper of a reverse taper, be provided with a supply at the top of fermentation cabin (5) and regulate pipeline (6), be provided with cellular ventilation hole (7) in the bottom of fermentation cabin (5), ventilation hole (7) blower fan (9) outside with being arranged at fermentation cabin (5) communicates, outer setting in fermentation cabin (5) has reciprocal dolly (8), spiral discharging machine (10) is installed on the reciprocal dolly (8), spiral discharging machine (10) both can rotation, can make reciprocal cutting movement by means of reciprocal dolly again.
Priority Applications (1)
Application Number | Priority Date | Filing Date | Title |
---|---|---|---|
CN88101327A CN1021432C (en) | 1988-03-09 | 1988-03-09 | Quick composting dynamic fermentation device for municipal refuse |
Applications Claiming Priority (1)
Application Number | Priority Date | Filing Date | Title |
---|---|---|---|
CN88101327A CN1021432C (en) | 1988-03-09 | 1988-03-09 | Quick composting dynamic fermentation device for municipal refuse |
Publications (2)
Publication Number | Publication Date |
---|---|
CN1035654A CN1035654A (en) | 1989-09-20 |
CN1021432C true CN1021432C (en) | 1993-06-30 |
Family
ID=4831713
Family Applications (1)
Application Number | Title | Priority Date | Filing Date |
---|---|---|---|
CN88101327A Expired - Fee Related CN1021432C (en) | 1988-03-09 | 1988-03-09 | Quick composting dynamic fermentation device for municipal refuse |
Country Status (1)
Country | Link |
---|---|
CN (1) | CN1021432C (en) |
Cited By (1)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
CN100368349C (en) * | 2005-03-29 | 2008-02-13 | 中国农业大学 | Disposal method of domestic garbage and its special fermentation bin |
Families Citing this family (7)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
JP3303892B2 (en) * | 1993-07-12 | 2002-07-22 | 中部ドラム罐工業株式会社 | High-speed fermentation processing equipment for garbage |
JP2771127B2 (en) * | 1995-03-22 | 1998-07-02 | 茂次 中島 | Three-dimensional multi-stage multipurpose fermenter |
CN103074207B (en) * | 2013-01-25 | 2014-08-20 | 何志发 | Automatic cycle device and automatic cycle method of fermentation tank |
CN103263066A (en) * | 2013-05-22 | 2013-08-28 | 安徽天邦生物技术有限公司 | Fermentation tank device for three-dimensional solid state fermentation of soybean meals |
CN103662757B (en) * | 2013-12-06 | 2015-12-02 | 简厚诚 | For the pay-off of potting |
CN108585968A (en) * | 2018-04-21 | 2018-09-28 | 临沂清宇环境资源综合利用研究院有限公司 | A kind of equipment detaching labile organic compound Rapid Fermentation in house refuse |
CN114751193A (en) * | 2022-04-27 | 2022-07-15 | 李元喜 | Full-automatic straw fermentation process |
-
1988
- 1988-03-09 CN CN88101327A patent/CN1021432C/en not_active Expired - Fee Related
Cited By (1)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
CN100368349C (en) * | 2005-03-29 | 2008-02-13 | 中国农业大学 | Disposal method of domestic garbage and its special fermentation bin |
Also Published As
Publication number | Publication date |
---|---|
CN1035654A (en) | 1989-09-20 |
Similar Documents
Publication | Publication Date | Title |
---|---|---|
Rees | The fate of carbon compounds in the landfill disposal of organic matter | |
US5269634A (en) | Apparatus and method for sequential batch anaerobic composting of high-solids organic feedstocks | |
CN109759417B (en) | Environment-friendly microbial garbage treatment device and garbage treatment method | |
CN208200773U (en) | Community's environmental protection compact organic waste quick composting composting arrangement | |
EP1042254B1 (en) | Odor-free composting method and installation | |
CN1021432C (en) | Quick composting dynamic fermentation device for municipal refuse | |
CN212335050U (en) | Compost fermentation system applied to household garbage comprehensive treatment system | |
US7150987B2 (en) | Organic waste processing method and device therefor | |
CN201268670Y (en) | Column plate type composting reactor | |
CN100368349C (en) | Disposal method of domestic garbage and its special fermentation bin | |
CN112441851A (en) | Municipal sludge and kitchen garbage coprocessing preparation fertilizer production system | |
WO2011076444A1 (en) | Device and method for fermenting, post-rotting and intensive-rotting processing products | |
KR100732492B1 (en) | Tower type unstirred compost device and method | |
KR100271906B1 (en) | Method for processing kitchen refuse into livestock feed | |
CN2303840Y (en) | Fermentation tank for life garbage in city | |
JP3489134B2 (en) | Composting method and apparatus for kitchen waste | |
CN206512083U (en) | The device of biogas is reclaimed in sludge anaerobic fermentation | |
CN212532797U (en) | Vertical quick biological stabilizing device | |
KR100321827B1 (en) | Plant for processing kitchen refuge | |
EP1215187B1 (en) | A process and system for treating solid city waste | |
KR100299069B1 (en) | The methord and system of composting organic fertiliter with sewage sludge and food waste | |
CN215250476U (en) | Kitchen garbage secondary fermentation micro-oxygen decomposition equipment | |
KR101797104B1 (en) | Apparatus for comfosting | |
CN109622572A (en) | A kind of technique producing building materials collaboration processing house refuse | |
CN2571756Y (en) | Compound fertilizer preparation device by supermicrotreatment two-stage fermenting organic humified material in urban refuse |
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 | ||
C19 | Lapse of patent right due to non-payment of the annual fee | ||
CF01 | Termination of patent right due to non-payment of annual fee |