CN106363008A - Comprehensive urban garbage treatment station - Google Patents
Comprehensive urban garbage treatment station Download PDFInfo
- Publication number
- CN106363008A CN106363008A CN201610750140.XA CN201610750140A CN106363008A CN 106363008 A CN106363008 A CN 106363008A CN 201610750140 A CN201610750140 A CN 201610750140A CN 106363008 A CN106363008 A CN 106363008A
- Authority
- CN
- China
- Prior art keywords
- drying chamber
- rubbish
- heat
- conurbation
- garbage
- Prior art date
- Legal status (The legal status is an assumption and is not a legal conclusion. Google has not performed a legal analysis and makes no representation as to the accuracy of the status listed.)
- Granted
Links
- 239000010813 municipal solid waste Substances 0.000 title claims abstract description 61
- 238000001035 drying Methods 0.000 claims abstract description 50
- 239000002699 waste material Substances 0.000 claims abstract description 24
- 238000005520 cutting process Methods 0.000 claims abstract description 19
- 238000003860 storage Methods 0.000 claims abstract description 9
- 238000002485 combustion reaction Methods 0.000 claims abstract description 4
- 238000009826 distribution Methods 0.000 claims description 10
- 238000000034 method Methods 0.000 claims description 9
- 239000004035 construction material Substances 0.000 claims description 5
- 230000005611 electricity Effects 0.000 claims description 5
- 208000025865 Ulcer Diseases 0.000 claims description 4
- 239000003513 alkali Substances 0.000 claims description 4
- 239000000428 dust Substances 0.000 claims description 4
- 238000007920 subcutaneous administration Methods 0.000 claims description 4
- 231100000397 ulcer Toxicity 0.000 claims description 4
- 239000002245 particle Substances 0.000 claims description 3
- 238000009434 installation Methods 0.000 claims 1
- 230000005540 biological transmission Effects 0.000 abstract description 3
- 239000004566 building material Substances 0.000 abstract 2
- 238000010248 power generation Methods 0.000 abstract 1
- 239000007789 gas Substances 0.000 description 5
- 238000010438 heat treatment Methods 0.000 description 4
- 239000000463 material Substances 0.000 description 4
- 229910000831 Steel Inorganic materials 0.000 description 3
- 239000010959 steel Substances 0.000 description 3
- HGUFODBRKLSHSI-UHFFFAOYSA-N 2,3,7,8-tetrachloro-dibenzo-p-dioxin Chemical compound O1C2=CC(Cl)=C(Cl)C=C2OC2=C1C=C(Cl)C(Cl)=C2 HGUFODBRKLSHSI-UHFFFAOYSA-N 0.000 description 2
- RAHZWNYVWXNFOC-UHFFFAOYSA-N Sulphur dioxide Chemical compound O=S=O RAHZWNYVWXNFOC-UHFFFAOYSA-N 0.000 description 2
- 230000007613 environmental effect Effects 0.000 description 2
- 239000000126 substance Substances 0.000 description 2
- 238000004056 waste incineration Methods 0.000 description 2
- UGFAIRIUMAVXCW-UHFFFAOYSA-N Carbon monoxide Chemical compound [O+]#[C-] UGFAIRIUMAVXCW-UHFFFAOYSA-N 0.000 description 1
- 238000003915 air pollution Methods 0.000 description 1
- 238000007872 degassing Methods 0.000 description 1
- 201000010099 disease Diseases 0.000 description 1
- 208000037265 diseases, disorders, signs and symptoms Diseases 0.000 description 1
- 238000005516 engineering process Methods 0.000 description 1
- 230000007717 exclusion Effects 0.000 description 1
- 239000003546 flue gas Substances 0.000 description 1
- 231100000614 poison Toxicity 0.000 description 1
- 230000007096 poisonous effect Effects 0.000 description 1
- 238000002360 preparation method Methods 0.000 description 1
- 238000000746 purification Methods 0.000 description 1
- 239000000779 smoke Substances 0.000 description 1
- 238000005987 sulfurization reaction Methods 0.000 description 1
- 239000002918 waste heat Substances 0.000 description 1
- XLYOFNOQVPJJNP-UHFFFAOYSA-N water Substances O XLYOFNOQVPJJNP-UHFFFAOYSA-N 0.000 description 1
Classifications
-
- B—PERFORMING OPERATIONS; TRANSPORTING
- B09—DISPOSAL OF SOLID WASTE; RECLAMATION OF CONTAMINATED SOIL
- B09B—DISPOSAL OF SOLID WASTE NOT OTHERWISE PROVIDED FOR
- B09B3/00—Destroying solid waste or transforming solid waste into something useful or harmless
-
- B—PERFORMING OPERATIONS; TRANSPORTING
- B09—DISPOSAL OF SOLID WASTE; RECLAMATION OF CONTAMINATED SOIL
- B09B—DISPOSAL OF SOLID WASTE NOT OTHERWISE PROVIDED FOR
- B09B5/00—Operations not covered by a single other subclass or by a single other group in this subclass
Landscapes
- Engineering & Computer Science (AREA)
- Environmental & Geological Engineering (AREA)
- Processing Of Solid Wastes (AREA)
Abstract
The invention provides a comprehensive urban garbage treatment station. The comprehensive urban garbage treatment station comprises a skid-mounted device and a garbage storage chamber arranged on the skid-mounted device. A garbage pretreatment chamber is arranged above the garbage storage chamber. Garbage is subjected to continuous two-level drying in the garbage treatment chamber through a first-level drying chamber and a second-level drying chamber. The dried garbage is conveyed to a first crusher and a second crusher which are continuous through a first transmission system, and the dried garbage is crushed through the first crusher and the second crusher. The crushed garbage is conveyed to the positions of a first briquetting device and a first cutting device which are continuous through a second transmission system. Cut square blocks are conveyed into a closed combustion furnace to be incinerated, heat generated during incineration is transmitted to a power generation device through a first heat exchange device and a second heat exchange device, and waste generated through incineration is made into building materials through a second briquetting device and a second cutting device which are continuous. The garbage treatment station provided in the technical scheme can convert garbage into electric energy and convert incinerated waste into the building materials.
Description
Technical field
The present invention relates to technical field of waste treatment, a kind of more particularly to conurbation Biohazard Waste Disposal.
Background technology
The whole world produces 4.9 hundred million tons of rubbish every year, and only China just produces nearly 1.5 hundred million tons of municipal refuses every year.World's rubbish
Average annual growth is 8.42%, and Chinese rubbish rate of increase reaches more than 10%.Garbage disposal has become as life, produces and send out
The significant problem being faced in exhibition, how efficiently, energy-saving and environmental protection the presence of rubbish limits life and the development producing,
Process rubbish extremely urgent.Gradually it is taken seriously with environmental problem, the chance of industry development is provided for garbage disposal.
Waste incineration method is one of main method for the treatment of of urban garbage.Rubbish is processed with burning method and can eliminate various diseases
Substance, poisonous and harmful substance is converted into harmless object.Incinerator is furnished with good smoke and dust purifier, mitigates to air
Pollution.Garbage incineration equipment mainly includes burning rotary kiln, grate furnace, sulfuration pool furnace etc., because municipal refuse is multiple many
Sample, causes rubbish cannot fully thoroughly burn, and allows the harmful gass such as two English, sulfur dioxide not reach discharge standard.And
And the waste heat in garbage disposal is not fully utilized.
Content of the invention
In view of this, the main object of the present invention is to provide a kind of conurbation Biohazard Waste Disposal.
The technical solution used in the present invention is as follows:
A kind of conurbation Biohazard Waste Disposal, including skid, is arranged on the rubbish storage room in skid, described rubbish storage
The top of room is provided with rubbish pretreatment chamber, and rubbish is carried out even through first order drying chamber and second level drying chamber by Disposal Area
Continuous two-stage is dried, and the rubbish after drying is delivered to continuous first disintegrating machine and the second disintegrating machine by the first drive system, by the
One disintegrating machine and the second disintegrating machine carry out break process, and the rubbish after crushing is delivered to continuous first pressure through the second drive system
At block assembly and the first cutter sweep, the rubbish of small particle is squeezed into the length that thickness is 5～8cm by described first briquetting device
Stick, this long strip block cuts into, through the first cutter sweep, the square that length is 6cm again, and the square after cutting is delivered to closed combustion
Burn stove to be burned, the heat producing in burning passes to TRT through the first heat-exchanger rig and the second heat-exchanger rig, burns
Burn the waste material producing and make construction material through continuous second briquetting device and the second cutter sweep.
Further, described first drive system is arranged on rubbish pretreatment chamber, first order drying chamber and the second level and dries
The lower end of room, is provided with the first driving motor at described first drive system.
Further, described first disintegrating machine and the second disintegrating machine are arranged on a mobile platform, and this mobile platform is by
The two grades of positive bottom of drying chamber back and forth movements to the first briquetting device, when mobile platform movement is to second level drying chamber one end
When, the second disintegrating machine receives the rubbish of second level drying chamber conveying, when mobile platform movement is to first briquetting device one end, the
One disintegrating machine receives the rubbish of second level drying chamber conveying, the rate travel phase of the wherein first drive system and mobile platform
Join.
Further, the bottom of described first disintegrating machine and the second disintegrating machine is provided with the second drive system, this second biography
It is provided with the second driving motor at dynamic system.
Further, at described first heat-exchanger rig and the second heat-exchanger rig, the residual pressure recovering equipment that has surplus heat is set, should
Hot residual pressure recovering equipment is connected with TRT.
Further, it is provided with the first extruding power set at described first briquetting device, at described first cutter sweep
It is provided with the first cutting propelling plant, at described second briquetting device, be provided with the second extruding power set, described second cutting
It is provided with the second cutting propelling plant at device.
Further, the top of described incinerator is provided with heat distribution pipeline, and this heat distribution pipeline is respectively connecting to the first order and dries
Dry chamber and second level drying chamber, described heat distribution pipeline is provided with continuous dust arrester on the top of incinerator, and heat distribution pipeline exists
First order drying chamber and second level drying interior are respectively arranged with the first heat abstractor and the second heat abstractor, and described first dissipates
It is provided with thermal and the second heat abstractor and automatically adjust valve.
Further, be respectively arranged with described first order drying chamber and second level drying chamber the first dedusting depassing unit and
Second dedusting depassing unit.
Further, it is provided with power system at described TRT, this power system connects switch board, this switch board divides
Do not connect to the first driving motor, the second driving motor, mobile platform, first extruding power set, the first cutting propelling plant,
Second extruding power set and the second cutting propelling plant.
Further, described incinerator is provided with continuous dedusting off gas system, the upper end of described dedusting off gas system
It is provided with alkali subcutaneous ulcer system.
The present invention has the advantage that municipal refuse can be converted into electricity through burning by the technical scheme that the present invention provides
Power, the flue gas after burning through multistage dedusting degasification and removes dioxin, can directly discharge, and does not produce any dirt to surrounding
Dye.Heat energy in garbage processing procedure is used to generate electricity, and improves garbage disposal overall economic efficiency.Waste material is converted into building
The primary material of material.
Brief description
Fig. 1 is the structural representation of the present invention.
Specific embodiment
To describe the present invention, the illustrative examples of the here present invention below in conjunction with accompanying drawing and specific embodiment in detail
And explanation is used for explaining the present invention, but not as a limitation of the invention.
With reference to Fig. 1, it is an object of the invention to provide a kind of conurbation Biohazard Waste Disposal, including skid 28, it is arranged on sled
Fill the rubbish storage room 1 on 28, rubbish storage room 1 is the storeroom of closing, the rubbish in city passes through each terminal and collects
During the locker room 1 providing to the present invention, first pass through the stewing process of 3～5 days, the steel that the bottom of locker room 1 is made up of steel wire
Silk screen, the bottom of steel wire is collecting-tank, and its interior 60% moisture is removed in locker room 1 by rubbish, the water warp in collecting-tank
Discharge after purification, the top of described rubbish storage room 1 is provided with rubbish pretreatment chamber 4, and rubbish is by Disposal Area 4 through the first order
Drying chamber 6 and second level drying chamber 8 carry out continuous two-stage drying, and described first order drying chamber 6 and second level drying chamber 8 lead to respectively
Cross heat distribution pipeline 29 to connect to incinerator 19, by incinerator 19 be first order drying chamber 6 and second level drying chamber 8 provides heating power.
Rubbish after drying is delivered to continuous first disintegrating machine 10 and the second disintegrating machine 11 by the first drive system 3, is crushed by first
Machine 10 and the second disintegrating machine 11 carry out break process, broken after manage after rubbish be delivered to continuous the through the second drive system 12
At one briquetting device 15 and the first cutter sweep 17, described first disintegrating machine 10 and the second disintegrating machine 11 are arranged on a movement and put down
On platform, this mobile platform by back and forth movement between the positive bottom of second level drying chamber 8 to the first briquetting device 15, when mobile platform moves
When moving to second level drying chamber 8 one end, the second disintegrating machine 11 receives the rubbish of second level drying chamber 8 conveying, when mobile platform moves
When moving to first briquetting device 15 one end, the first disintegrating machine 10 receives the rubbish of second level drying chamber 8 conveying, the wherein first transmission
System 3 is matched with the rate travel of mobile platform.It is 5 that the rubbish of small particle is squeezed into thickness by described first briquetting device 15
The long strip block of～8cm, this long strip block cuts into, through the first cutter sweep 17, the square that length is 6cm again, and the square after cutting is defeated
Deliver to closed combustion furnace 19 to be burned, the heat producing in burning is through the first heat-exchanger rig 20 and the second heat-exchanger rig 21
Pass to TRT 23, burn the waste material producing and make and build through continuous second briquetting device 16 and the second cutter sweep 27
Build material, the residual pressure recovering equipment 22 that has surplus heat is set at described first heat-exchanger rig 20 and the second heat-exchanger rig 21, more than this heat
Push back receiving apparatus 22 to be connected with TRT 23.
In the present invention, it is provided with the first extruding power set 16, described first cutting at described first briquetting device 15
It is provided with the first cutting propelling plant 18 at device 17, at described second briquetting device 26, be provided with the second extruding power set
25, it is provided with the second cutting propelling plant 24 at described second cutter sweep 27.Wherein first extrudes power set 16 can be
First briquetting device 15 provides the extruding force of 5～10kp, and the second extruding power set 25 can provide for the second briquetting device 26
The extruding force of 25～30kp, due to considering clean-burning problem in burning phase, by the extruding force of the first briquetting device 15
Regulate and control to 5kp, the long strip block so squeezing out both had kept certain rigidity, and clean-burning requirement can be reached, useless
Material is carried out during construction material preparation it is contemplated that the rigid requirements of construction material, therefore adjusts the extruding force of the second briquetting device 26
Control 30kp.
Described first drive system 3 is arranged under rubbish pretreatment chamber 4, first order drying chamber 6 and second level drying chamber 8
End, is provided with the first driving motor 2 at described first drive system 4.Ensure that the purpose of continuous processing.Meanwhile, described first
The bottom of disintegrating machine 10 and the second disintegrating machine 11 is provided with the second drive system 12, is provided with second at this second drive system 12
Driving motor 13.Ensure that the rubbish after crushing can be delivered at the first briquetting device 15.
In the present invention, described heat distribution pipeline 29 is provided with continuous dust arrester 30, heating power on the top of incinerator 19
Pipeline 29 is respectively arranged with the first heat abstractor 31 and the second radiating dress in first order drying chamber 6 and second level drying chamber 8
Put 32, be provided with exhaust fan in the first heat abstractor 31 and the second heat abstractor 32 it is ensured that in first order drying chamber 6 He
Heating power in second level drying chamber 8 uniformly, is provided with described first heat abstractor 31 and the second heat abstractor 32 automatically
Control valve, can adjust the supply of heating power according to the actual needs.Meanwhile, described first order drying chamber 6 and the second level are dried
It is respectively arranged with the first dedusting depassing unit 5 and the second dedusting depassing unit 7 at room 8.Ensure that the gas of exclusion reaches discharge
Require.Continuous dedusting off gas system 34, the upper end setting of described dedusting off gas system 34 are provided with described incinerator 19
There is alkali subcutaneous ulcer system 33, described alkali subcutaneous ulcer system 33 is used for excluding dioxin.
It is provided with power system, this power system connects switch board, this switch board connects respectively at described TRT 23
To the first driving motor 2, the second driving motor 13, mobile platform, the first extruding power set 16, the first cutting propelling plant
18th, the second extruding power set 25 and the second cutting propelling plant 24.Waste incineration not only can be changed into electricity by the present invention
Can, itself is powered for whole Biohazard Waste Disposal using the electric energy that TRT 23 sends, and remaining electric energy is grid-connected to obtain economy
Income, meanwhile, divides waste material after a while to make construction material, has carried out secondary utilization.
The technical scheme above embodiment of the present invention being provided is described in detail, specific case used herein
The principle and embodiment of the embodiment of the present invention is set forth, the explanation of above example is only applicable to help understand this
The principle of inventive embodiments；Simultaneously for one of ordinary skill in the art, according to the embodiment of the present invention, in specific embodiment party
All will change in formula and range of application, in sum, this specification content should not be construed as limitation of the present invention.
Claims (10)
1. a kind of conurbation Biohazard Waste Disposal, including skid, is arranged on rubbish storage room in skid it is characterised in that institute
The top stating rubbish storage room is provided with rubbish pretreatment chamber, and rubbish is dried through first order drying chamber and the second level by Disposal Area
Dry chamber carries out continuous two-stage drying, and the rubbish after drying is delivered to continuous first disintegrating machine and second by the first drive system and breaks
Broken machine, carries out break process by the first disintegrating machine and the second disintegrating machine, and the rubbish after crushing is delivered to even through the second drive system
At the first continuous briquetting device and the first cutter sweep, the rubbish of small particle is squeezed into thickness and is by described first briquetting device
The long strip block of 5～8cm, this long strip block cuts into, through the first cutter sweep, the square that length is 6cm again, the square conveying after cutting
Burned to closed combustion furnace, the heat producing in burning passes to through the first heat-exchanger rig and the second heat-exchanger rig and sends out
Electric installation, burns the waste material producing and makes construction material through continuous second briquetting device and the second cutter sweep.
2. conurbation according to claim 1 Biohazard Waste Disposal is it is characterised in that described first drive system is arranged on
The lower end of rubbish pretreatment chamber, first order drying chamber and second level drying chamber, is provided with the first biography at described first drive system
Galvanic electricity machine.
3. conurbation according to claim 1 Biohazard Waste Disposal is it is characterised in that described first disintegrating machine and second breaks
Broken machine is arranged on a mobile platform, and this mobile platform is by fortune round between the positive bottom of second level drying chamber to the first briquetting device
Dynamic, when mobile platform movement is to second level drying chamber one end, the second disintegrating machine receives the rubbish of second level drying chamber conveying, when
When mobile platform movement is to first briquetting device one end, the first disintegrating machine receives the rubbish of second level drying chamber conveying, and wherein the
One drive system is matched with the rate travel of mobile platform.
4. the conurbation Biohazard Waste Disposal according to claim 1 or 3 is it is characterised in that described first disintegrating machine and
The bottom of sledging machine is provided with the second drive system, is provided with the second driving motor at this second drive system.
5. conurbation according to claim 1 Biohazard Waste Disposal is it is characterised in that described first heat-exchanger rig and
The residual pressure recovering equipment that has surplus heat is set at two heat-exchanger rigs, and this hot residual pressure recovering equipment is connected with TRT.
6. conurbation according to claim 1 Biohazard Waste Disposal is it is characterised in that arrange at described first briquetting device
There are the first extruding power set, at described first cutter sweep, be provided with the first cutting propelling plant, described second briquetting device
Place is provided with the second extruding power set, is provided with the second cutting propelling plant at described second cutter sweep.
7. conurbation according to claim 1 Biohazard Waste Disposal is it is characterised in that the top of described incinerator is provided with
Heat distribution pipeline, this heat distribution pipeline is respectively connecting to first order drying chamber and second level drying chamber, and described heat distribution pipeline is in incinerator
Top be provided with continuous dust arrester, heat distribution pipeline is respectively arranged with first order drying chamber and second level drying interior
One heat abstractor and the second heat abstractor, are provided with described first heat abstractor and the second heat abstractor and automatically adjust
Valve.
8. the conurbation Biohazard Waste Disposal according to claim 1 or 7 it is characterised in that described first order drying chamber and
It is respectively arranged with the first dedusting depassing unit and the second dedusting depassing unit at the drying chamber of the second level.
9. conurbation according to claim 1 Biohazard Waste Disposal is it is characterised in that be provided with electricity at described TRT
Force system, this power system connects switch board, and this switch board is respectively connecting to the first driving motor, the second driving motor, movement
Platform, the first extruding power set, the first cutting propelling plant, the second extruding power set and the second cutting propelling plant.
10. conurbation according to claim 1 Biohazard Waste Disposal is it is characterised in that the company of being provided with described incinerator
Continuous dedusting off gas system, the upper end of described dedusting off gas system is provided with alkali subcutaneous ulcer system.
Priority Applications (1)
| Application Number | Priority Date | Filing Date | Title |
|---|---|---|---|
| CN201610750140.XA CN106363008B (en) | 2016-08-28 | 2016-08-28 | A kind of conurbation Biohazard Waste Disposal |
Applications Claiming Priority (1)
| Application Number | Priority Date | Filing Date | Title |
|---|---|---|---|
| CN201610750140.XA CN106363008B (en) | 2016-08-28 | 2016-08-28 | A kind of conurbation Biohazard Waste Disposal |
Publications (2)
| Publication Number | Publication Date |
|---|---|
| CN106363008A true CN106363008A (en) | 2017-02-01 |
| CN106363008B CN106363008B (en) | 2019-05-10 |
Family
ID=57903591
Family Applications (1)
| Application Number | Title | Priority Date | Filing Date |
|---|---|---|---|
| CN201610750140.XA Active CN106363008B (en) | 2016-08-28 | 2016-08-28 | A kind of conurbation Biohazard Waste Disposal |
Country Status (1)
| Country | Link |
|---|---|
| CN (1) | CN106363008B (en) |
Cited By (2)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| CN108144944A (en) * | 2017-12-25 | 2018-06-12 | 郑州艾莫弗信息技术有限公司 | A kind of safe rubbish easily decomposes landfill pretreatment unit |
| CN108160673A (en) * | 2017-12-25 | 2018-06-15 | 郑州艾莫弗信息技术有限公司 | A kind of environment-friendly garbage fills pretreatment unit |
Citations (6)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| JPS60253712A (en) * | 1984-05-29 | 1985-12-14 | Maguma Kogyo Kk | Waste disposing plant |
| CN101949543A (en) * | 2010-09-17 | 2011-01-19 | 杨长银 | Household garbage treatment system |
| KR20110087073A (en) * | 2010-01-25 | 2011-08-02 | 한국하이테크 주식회사 | The electric generating system using burning the pellet |
| CN203484402U (en) * | 2013-09-27 | 2014-03-19 | 中环正仁(北京)环保投资有限公司 | Environment-friendly closed source circulation utilization garbage disposal generating system |
| CN203944637U (en) * | 2014-06-19 | 2014-11-19 | 国网四川省电力公司成都市新都供电分公司 | The aseptic combustion power generation system of a kind of power station garbage on water |
| CN204114952U (en) * | 2014-08-20 | 2015-01-21 | 福建正仁环保有限公司 | RDF burning electricity generation system prepared by a kind of clean and effective rubbish |
-
2016
- 2016-08-28 CN CN201610750140.XA patent/CN106363008B/en active Active
Patent Citations (6)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| JPS60253712A (en) * | 1984-05-29 | 1985-12-14 | Maguma Kogyo Kk | Waste disposing plant |
| KR20110087073A (en) * | 2010-01-25 | 2011-08-02 | 한국하이테크 주식회사 | The electric generating system using burning the pellet |
| CN101949543A (en) * | 2010-09-17 | 2011-01-19 | 杨长银 | Household garbage treatment system |
| CN203484402U (en) * | 2013-09-27 | 2014-03-19 | 中环正仁(北京)环保投资有限公司 | Environment-friendly closed source circulation utilization garbage disposal generating system |
| CN203944637U (en) * | 2014-06-19 | 2014-11-19 | 国网四川省电力公司成都市新都供电分公司 | The aseptic combustion power generation system of a kind of power station garbage on water |
| CN204114952U (en) * | 2014-08-20 | 2015-01-21 | 福建正仁环保有限公司 | RDF burning electricity generation system prepared by a kind of clean and effective rubbish |
Cited By (2)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| CN108144944A (en) * | 2017-12-25 | 2018-06-12 | 郑州艾莫弗信息技术有限公司 | A kind of safe rubbish easily decomposes landfill pretreatment unit |
| CN108160673A (en) * | 2017-12-25 | 2018-06-15 | 郑州艾莫弗信息技术有限公司 | A kind of environment-friendly garbage fills pretreatment unit |
Also Published As
| Publication number | Publication date |
|---|---|
| CN106363008B (en) | 2019-05-10 |
Similar Documents
| Publication | Publication Date | Title |
|---|---|---|
| CN103322574B (en) | Utilize method and the treatment system thereof of tunnel kiln brick sintering production line cooperative disposal house refuse | |
| CN106493148A (en) | A kind of solid organic castoff gasification and melting circulating disposal process | |
| CN102322642A (en) | Sludge drying and incinerating system on basis of incineration of waste grate furnace and treatment method thereof | |
| CN103483014B (en) | The dry treatment system of meal kitchen rubbish from cooking resource | |
| CN101457147B (en) | No-oxygen pyrolysis gasification processing device of urban domestic garbage and technique thereof | |
| CN102145343A (en) | Integrated garbage treatment and utilization method for effectively controlling dioxin | |
| CN105217916A (en) | A kind of innoxious sludge carbonization treatment process and process system thereof | |
| CN106350116A (en) | Traditional Chinese medicine residue gasification combustion heat supply device and method | |
| CN111750357A (en) | Vein industrial park system with waste incineration power plant as core | |
| CN106363008A (en) | Comprehensive urban garbage treatment station | |
| CN201964422U (en) | Novel pyrolyzing furnace for domestic garbage disposal, and garbage disposal system using same | |
| CN104907319A (en) | Garbage disposal device | |
| CN105903743B (en) | A kind of domestic garbage resource Terminal Treating | |
| CN106765135A (en) | A kind of biomass garbage source processing unit | |
| CN107662914B (en) | Method and treatment system for carbonizing household garbage by using tunnel kiln | |
| CN205175060U (en) | Rubbish drying equipment | |
| CN205115378U (en) | City domestic waste dry distillation system | |
| CN205299539U (en) | System for utilize cement kiln to deal with domestic waste in coordination | |
| CN204829929U (en) | Rubbish is pressed and is burned device futilely | |
| CN204661607U (en) | One way of life rubbish ultra-high frequency destructive distillation device | |
| CN204234452U (en) | Consumer waste incineration complete set of equipments | |
| CN106705051A (en) | Novel energy-saving garbage incinerator | |
| CN205717227U (en) | A kind of device utilizing solid waste incineration system waste heat to carry out waste oil paint can process | |
| CN104964287B (en) | Rubbish press dry incinerator | |
| CN201621704U (en) | Pyrolysis gasification device of domestic waste |
Legal Events
| Date | Code | Title | Description |
|---|---|---|---|
| C06 | Publication | ||
| PB01 | Publication | ||
| SE01 | Entry into force of request for substantive examination | ||
| SE01 | Entry into force of request for substantive examination | ||
| TA01 | Transfer of patent application right | ||
| TA01 | Transfer of patent application right |
Effective date of registration: 20190412 Address after: 310012 No. 11 Dongyue Street, Liujie Street, Xihu District, Hangzhou City, Zhejiang Province Applicant after: Zhejiang Xinhuang Environmental Engineering Co., Ltd. Address before: 437000 Group 8, Huangtiecun, Gaoqiao Town, Xianning District, Hubei Province Applicant before: Zhu Chao |
|
| GR01 | Patent grant | ||
| GR01 | Patent grant |