CN105180171A - Garbage treatment method and garbage treatment equipment - Google Patents
Garbage treatment method and garbage treatment equipment Download PDFInfo
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- CN105180171A CN105180171A CN201510679162.7A CN201510679162A CN105180171A CN 105180171 A CN105180171 A CN 105180171A CN 201510679162 A CN201510679162 A CN 201510679162A CN 105180171 A CN105180171 A CN 105180171A
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- garbage
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- 238000000034 method Methods 0.000 title claims abstract description 52
- 239000010813 municipal solid waste Substances 0.000 title claims abstract description 32
- 239000002689 soil Substances 0.000 claims abstract description 50
- 239000002912 waste gas Substances 0.000 claims abstract description 33
- 239000004568 cement Substances 0.000 claims abstract description 30
- 238000005188 flotation Methods 0.000 claims abstract description 17
- 239000002351 wastewater Substances 0.000 claims abstract description 15
- 238000006065 biodegradation reaction Methods 0.000 claims abstract description 12
- 238000001914 filtration Methods 0.000 claims abstract description 10
- 239000010902 straw Substances 0.000 claims abstract description 8
- 239000002699 waste material Substances 0.000 claims description 15
- 241000219782 Sesbania Species 0.000 claims description 11
- XLYOFNOQVPJJNP-UHFFFAOYSA-N water Substances O XLYOFNOQVPJJNP-UHFFFAOYSA-N 0.000 claims description 9
- 238000001816 cooling Methods 0.000 claims description 8
- 240000007594 Oryza sativa Species 0.000 claims description 4
- 235000007164 Oryza sativa Nutrition 0.000 claims description 4
- 238000013019 agitation Methods 0.000 claims description 4
- 230000001580 bacterial effect Effects 0.000 claims description 4
- 241001233061 earthworms Species 0.000 claims description 4
- 230000008676 import Effects 0.000 claims description 4
- 238000004898 kneading Methods 0.000 claims description 4
- 238000002156 mixing Methods 0.000 claims description 4
- 238000002360 preparation method Methods 0.000 claims description 4
- 235000009566 rice Nutrition 0.000 claims description 4
- 230000005611 electricity Effects 0.000 claims description 3
- 238000010438 heat treatment Methods 0.000 claims description 3
- 241000196324 Embryophyta Species 0.000 claims description 2
- 230000017260 vegetative to reproductive phase transition of meristem Effects 0.000 claims description 2
- 244000275012 Sesbania cannabina Species 0.000 claims 1
- 238000004519 manufacturing process Methods 0.000 abstract description 4
- 238000000855 fermentation Methods 0.000 abstract description 3
- 230000004151 fermentation Effects 0.000 abstract description 3
- 238000000354 decomposition reaction Methods 0.000 abstract description 2
- 239000002994 raw material Substances 0.000 abstract description 2
- 239000002910 solid waste Substances 0.000 abstract description 2
- 230000000694 effects Effects 0.000 description 5
- 238000003912 environmental pollution Methods 0.000 description 4
- 240000003537 Ficus benghalensis Species 0.000 description 3
- 239000000126 substance Substances 0.000 description 3
- 238000004056 waste incineration Methods 0.000 description 3
- 244000166124 Eucalyptus globulus Species 0.000 description 2
- 241000218922 Magnoliophyta Species 0.000 description 2
- 241000361919 Metaphire sieboldi Species 0.000 description 2
- 241001148470 aerobic bacillus Species 0.000 description 2
- 238000009395 breeding Methods 0.000 description 2
- 230000001488 breeding effect Effects 0.000 description 2
- 239000002184 metal Substances 0.000 description 2
- 238000003756 stirring Methods 0.000 description 2
- 241000894006 Bacteria Species 0.000 description 1
- 235000004936 Bromus mango Nutrition 0.000 description 1
- 240000007228 Mangifera indica Species 0.000 description 1
- 235000014826 Mangifera indica Nutrition 0.000 description 1
- 235000009184 Spondias indica Nutrition 0.000 description 1
- 238000009825 accumulation Methods 0.000 description 1
- 230000009286 beneficial effect Effects 0.000 description 1
- 238000006243 chemical reaction Methods 0.000 description 1
- 230000007812 deficiency Effects 0.000 description 1
- 238000005516 engineering process Methods 0.000 description 1
- 230000007613 environmental effect Effects 0.000 description 1
- 230000002427 irreversible effect Effects 0.000 description 1
- 238000009285 membrane fouling Methods 0.000 description 1
- 238000012986 modification Methods 0.000 description 1
- 230000004048 modification Effects 0.000 description 1
- 239000000618 nitrogen fertilizer Substances 0.000 description 1
- 235000015097 nutrients Nutrition 0.000 description 1
- 238000003672 processing method Methods 0.000 description 1
- 238000011084 recovery Methods 0.000 description 1
- 150000003839 salts Chemical class 0.000 description 1
- 238000002791 soaking Methods 0.000 description 1
- 238000003900 soil pollution Methods 0.000 description 1
- 239000007787 solid Substances 0.000 description 1
- 230000001131 transforming effect Effects 0.000 description 1
- 238000009423 ventilation Methods 0.000 description 1
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
- Y02E—REDUCTION OF GREENHOUSE GAS [GHG] EMISSIONS, RELATED TO ENERGY GENERATION, TRANSMISSION OR DISTRIBUTION
- Y02E20/00—Combustion technologies with mitigation potential
- Y02E20/12—Heat utilisation in combustion or incineration of waste
Landscapes
- Processing Of Solid Wastes (AREA)
Abstract
The invention relates to a treatment method of solid waste, in particular to a garbage treatment method and garbage treatment equipment. The garbage treatment method comprises steps that garbage is crushed, dewatered and continuously incinerated, the produced residues are poured into a flotation tank to be soaked, waste gas is filtered through porous soil blocks, and meanwhile, the residues are subjected to flotation and biodegradation. In the garbage treatment equipment, a garbage crusher, a garbage dewaterer, a feeding roller and a continuous incinerator are connected sequentially, a chimney is arranged at the top of the continuous incinerator and connected with a horizontal sub-chimney through a branched pipe connector, and the sub-chimney is filled with a plurality of porous soil blocks and mounted above a cement pit. The production cost is lower, and all that is required is to perform improvement on an original garbage incineration field; raw materials of the porous soil blocks used for filtering the waste gas are widely existing yellow mud and common straw in rural areas, the waste gas and wastewater obtained after garbage incineration are fixed and subjected to biological fermentation, decomposition and fixation.
Description
Technical field
The present invention relates to a kind of processing method of solid waste, especially a kind of waste disposal method and its treatment facility.
Background technology
Along with the process of urbanization is constantly accelerated, the form of garbage disposal is more severe.Trash processing way conventional at present comprises burning, landfill, sorting recovery and biodegradation, and this several processing mode respectively has pluses and minuses:
Burn, the time of piling up is short, and the processing time is short, and floor space is few, can provide the addition products such as electric power, but environmental pollution is larger;
Landfill, the time of piling up is long, and the processing time is short, and floor space is large, waste soil, and environmental pollution is larger;
Sorting is reclaimed, and the time of piling up is long, and the processing time is long, and floor space greatly, needs a large amount of labour or equipment, and environmental pollution is less and can provide the addition products such as metal;
Biodegradation, the time of piling up is long, and the processing time is long, and floor space is large, and need manually to keep an eye on and regulate, environmental pollution is minimum.
For meeting the life Production requirement of people, garbage disposal needs a kind ofly to reduce accumulation time, processing time and can not cause the waste disposal method of irreversible membrane fouling to environment and soil.
Summary of the invention
For the deficiencies in the prior art, the invention provides a kind of efficient and the waste disposal method of environmental protection and treatment facility.
Technical scheme of the present invention is:
A kind of waste disposal method, comprises the following steps:
Step one, by refuse breaking;
Step 2, the garbage dewatering that step one was processed;
Step 3, puts into continous way incinerator and burns by the rubbish of step 2 process;
Step 4, burns the waste gas produced and lowers the temperature and be in charge of process, meanwhile pour the residue that step 3 burning produces into floation tank and soak by step 3;
Step 5, is filtered the waste gas of step 4 process by porous soil block, meanwhile the residue of step 4 process is carried out flotation;
Step 6, waste gas step 5 being completed filtration is discharged and porous soil block is carried out biodegradation, and all kinds of Recyclables meanwhile step 5 floatingly selected carry out reclaiming and passed in porous soil block and carry out biodegradation in the lump with porous soil block by the waste water that flotation produces.
Concrete, in described step 4, the method for waste gas cooling is: waste gas is imported chimney, in chimney outer felt around water cooling tube.
Concrete, the method being in charge of process in described step 4 is: after waste gas is imported chimney, connects a point pipe joint at chimney end, and point pipe joint connects some sub-chimneys.
Concrete, the method that in described step 5, waste gas is filtered by porous soil block is: fill at sub-chimney internal diameter the yellow mud block that some diameters are 15-20 centimetre, waste gas is imported sub-chimney.
Concrete, in described step 5, the preparation method of porous soil block is: add stalk after mixing of being watered by yellow mud, straw kneading is agglomerating, dry or dry.
Concrete, biodegradable method in described step 6 is: pour in cement pit by the porous soil block completing filtration in step 5, waste water step 5 flotation produced imports cement pit, porous soil block and waste water are uniformly mixed and add aerobic bacterial classification, mud in cement pit takes out after one week to two weeks and is piled into mount by air agitation process, in mount, put into some earthworms the some sesbanias of mount surface grafting, treat that sesbania first time Post flowering at least plants a large-scale arbor seedling on mount.
The principle of waste disposal method of the present invention is:
Fast garbage conversion can be become waste gas and residue by burning, avoiding a large amount of sanitary fills;
Burning the waste gas that produces by being distributed in some sub-chimneys, increasing the contact area of waste gas, the stalk that waste gas can progressively be included by porous soil block and porous soil block or straw are adsorbed;
Burn the residue that produces by soaking, water miscible ash content (salt) is dissolved in water, and other are convenient to the metal of flotation, insoluble oxide etc. and are reclaimed by flotation;
By biodegradation, the porous soil block adsorbing a large amount of harmful substance is processed, the flotation waste water having dissolved ash content can't be absorbed by bacterium during the fermentation, but by stir and most of grey branch that ventilates is blended in mud, be finally convenient to the plantation of sesbania and arbor;
Plantation sesbania contributes to conserving water and soil and providing nitrogenous fertilizer thus build more complicated biotic environment, thus harmful substance is degraded further and fix;
Plantation arbor realizes diversity of organism further, and then promotes the degraded of harmful substance and fix, and arbor has more powerful fixation to mount.
A kind of refuse treatment plant, comprise refuse grinder, garbage dewatering, feeding roller-way, continous way incinerator, chimney, floation tank and cement pit, described refuse grinder, garbage dewatering, feeding roller-way, continous way incinerator connects successively, described continous way incinerator top is provided with some chimneys, described chimney is connected with some horizontally disposed sub-chimneys by a point pipe joint, some porous soil blocks are filled with in described sub-chimney, described sub-chimney adopts disparting type structure and adopts buckle fastening, described sub-chimney is arranged on above cement pit, slag-drip opening is provided with bottom described continous way incinerator, described slag-drip opening connects floation tank, described floation tank connects cement pit by pipeline.
Concrete, wound form water cooling tube outside described chimney, its effect is that waste gas is lowered the temperature, and avoids the disintegration of porous soil block and burning, also plays the effect utilizing waste-gas heat.
Concrete, described sub-chimney internal diameter is 20-30 centimetre, and described sub-chimney length is 10-15 rice, and described sub-chimney quantity is no less than 50, and its effect effectively increases waste gas surface area.
Concrete, described porous soil block diameter is 15-20 centimetre, is convenient to fill.
Concrete, be at least provided with a kind of agitating device and a kind of air-breather in described cement pit, its effect is convenient to aerobic bacteria breeding to decompose mud.
Concrete, described continous way incinerator is connected with at least one in heating system, electricity generation system, and its effect is effectively utilized by the heat energy produced of burning away the refuse.
Beneficial effect of the present invention is: production cost of the present invention is lower, by carrying out transforming on original waste incineration field, raw material for the porous soil block of filtering exhaust are the common stalk in the yellow mud that extensively exists and rural area and straw, process is also very simple, by the waste gas after waste incineration and wastewater solid being decided and passing through biological fermentation, decomposition, fixing, not only can preventing pollution environment can also effectively utilize waste incineration after various nutrients improve ecological environment further.
Accompanying drawing explanation
Fig. 1 is equipment structure chart of the present invention.
In figure, 1, refuse grinder; 2, garbage dewatering; 3, feeding roller-way; 4, continous way incinerator; 5, chimney; 6, sub-chimney; 7, slag-drip opening; 8, floation tank; 9, cement pit.
Detailed description of the invention
Below in conjunction with embodiment and accompanying drawing, the specific embodiment of the present invention is described further:
Embodiment 1: as shown in Figure 1:
A kind of refuse treatment plant, comprise refuse grinder 1, garbage dewatering 2, feeding roller-way 3, continous way incinerator 4, chimney 5, floation tank 8 and cement pit 9, described refuse grinder 1, garbage dewatering 2, feeding roller-way 3, continous way incinerator 4 connects successively, described continous way incinerator 4 top is provided with 1 chimney 5, described chimney 5 is connected with 50 horizontally disposed sub-chimneys 6 by a point pipe joint, some porous soil blocks (packed space is at least 60% of sub-chimney volume) are filled with in described sub-chimney 6, described sub-chimney 6 adopts 4 disparting type structures and adopts buckle fastening, described sub-chimney 6 is arranged on above cement pit 9, slag-drip opening 7 is provided with bottom described continous way incinerator 4, described slag-drip opening 7 connects floation tank 8, described floation tank 8 connects cement pit 9 by pipeline.
Wound form water cooling tube outside described chimney 5, described sub-chimney 6 internal diameter is 20-30 centimetre, and described sub-chimney 6 length is 10-15 rice, and described porous soil block diameter is 15-20 centimetre, be provided with spiral agitator and breather pipe in described cement pit 9, described continous way incinerator 4 is connected with heating system.
A kind of waste disposal method, comprises the following steps:
Step one, by refuse breaking;
Step 2, the garbage dewatering that step one was processed;
Step 3, puts into continous way incinerator 4 by the rubbish of step 2 process and burns;
Step 4, burns the waste gas produced and lowers the temperature and be in charge of process, meanwhile pour the residue that step 3 burning produces into floation tank 8 and soak by step 3;
Step 5, is filtered the waste gas of step 4 process by porous soil block, meanwhile the residue of step 4 process is carried out flotation;
Step 6, waste gas step 5 being completed filtration is discharged and porous soil block is carried out biodegradation, and all kinds of Recyclables meanwhile step 5 floatingly selected carry out reclaiming and passed in porous soil block and carry out biodegradation in the lump with porous soil block by the waste water that flotation produces.
In described step 5, the preparation method of porous soil block is: add straw kneading after mixing of being watered by yellow mud agglomerating, dry or dry.
Biodegradable method in described step 6 is: pour in cement pit 9 by the porous soil block completing filtration in step 5, waste water step 5 flotation produced imports cement pit 9, porous soil block and waste water are uniformly mixed and add aerobic bacterial classification, mud in cement pit takes out after two weeks and is piled into mount (mount is hemispherical by air agitation process, height one meter is good), and in mount, some earthworms (earthworm weight about 30 grams) are put into the some sesbanias of mount surface grafting (the every 200 square centimeters of plantations in a mount surface sesbania seedling), treat that sesbania first time Post flowering plants a large-scale arbor seedling (general employing spire banyan on mount, great Ye banyan, mango).
Embodiment 2: as shown in Figure 1:
A kind of refuse treatment plant, comprise refuse grinder 1, garbage dewatering 2, feeding roller-way 3, continous way incinerator 4, chimney 5, floation tank 8 and cement pit 9, described refuse grinder 1, garbage dewatering 2, feeding roller-way 3, continous way incinerator 4 connects successively, described continous way incinerator 4 top is provided with 3 chimneys 5, every root chimney 5 is connected with 20 horizontally disposed sub-chimneys 6 (sub-chimney adds up to 60) respectively by a point pipe joint, some porous soil blocks (packed space is at least 65% of sub-chimney volume) are filled with in described sub-chimney 6, described sub-chimney 6 adopts disparting type structure and adopts buckle fastening, described sub-chimney 6 is arranged on above cement pit 9, slag-drip opening 7 is provided with bottom described continous way incinerator 4, described slag-drip opening 7 connects floation tank 8, described floation tank 8 connects cement pit 9 by pipeline.
Wound form water cooling tube outside described chimney 5, described sub-chimney 6 internal diameter is 20-30 centimetre, and described sub-chimney 6 length is 10-15 rice, and described porous soil block diameter is 15-20 centimetre, be provided with in described cement pit 9 and stir pestle and ventilation pump, described continous way incinerator 4 is connected with electricity generation system.
A kind of waste disposal method, comprises the following steps:
Step one, by refuse breaking;
Step 2, the garbage dewatering that step one was processed;
Step 3, puts into continous way incinerator 4 by the rubbish of step 2 process and burns;
Step 4, burns the waste gas produced and lowers the temperature and be in charge of process, meanwhile pour the residue that step 3 burning produces into floation tank 8 and soak by step 3;
Step 5, is filtered the waste gas of step 4 process by porous soil block, meanwhile the residue of step 4 process is carried out flotation;
Step 6, waste gas step 5 being completed filtration is discharged and porous soil block is carried out biodegradation, and all kinds of Recyclables meanwhile step 5 floatingly selected carry out reclaiming and passed in porous soil block and carry out biodegradation in the lump with porous soil block by the waste water that flotation produces.
In described step 5, the preparation method of porous soil block is: add straw kneading after mixing of being watered by yellow mud agglomerating, dry or dry.
Biodegradable method in described step 6 is: pour in cement pit 9 by the porous soil block completing filtration in step 5, waste water step 5 flotation produced imports cement pit 9, porous soil block and waste water are uniformly mixed and add aerobic bacterial classification, within one week, (processing time only should calculate the fine day time in air agitation process, and must have more than 3 days continuous sunny) after the mud in cement pit taken out and be piled into mount (mount be hemispherical, height one meter is good), and in mount, some earthworms (earthworm weight about 30 grams) are put into the some sesbanias of mount surface grafting (the every 200 square centimeters of plantations in a mount surface sesbania seedling), treat that sesbania first time Post flowering plants a large-scale arbor seedling (adopting eucalyptus) on mount.
Embodiment 1 be applicable to average temperature of the whole year 20 degrees Celsius, annual rainfall 1700 millimeters, the annual sunshine time area of 1600 hours use, Typical Representative is the Northern Guangdong Province in Guangdong, this area's agricultural is flourishing, produce a large amount of straws, be convenient to manufacture the porous soil block described in embodiment 1, in addition, are all applicable to the growth of the large-scale arbors such as spire banyan at its temperature, rainfall and sunshine, are also applicable to the breeding of aerobic bacteria.
Embodiment 2 is applicable to average temperature of the whole year and is 20 degrees Celsius and the difference of monthly mean temperature is no more than 20 degrees Celsius, annual rainfall 1700 millimeters, annual number at the sunshine area of 1600 hours uses, Typical Representative is the Delta of Pearl River in Guangdong, this area's industry is flourishing, but land resource is in short supply, so by reducing the aerobic fementation time and being fixed by the eucalyptus that plantation grows fast.
What describe in above-described embodiment and description just illustrates principle of the present invention and most preferred embodiment; without departing from the spirit and scope of the present invention; the present invention also has various changes and modifications, and these changes and improvements all fall in the claimed scope of the invention.
Claims (10)
1. a waste disposal method, is characterized in that: comprise the following steps:
Step one, by refuse breaking;
Step 2, the garbage dewatering that step one was processed;
Step 3, puts into continous way incinerator and burns by the rubbish of step 2 process;
Step 4, burns the waste gas produced and lowers the temperature and be in charge of process, meanwhile pour the residue that step 3 burning produces into floation tank and soak by step 3;
Step 5, is filtered the waste gas of step 4 process by porous soil block, meanwhile the residue of step 4 process is carried out flotation;
Step 6, waste gas step 5 being completed filtration is discharged and porous soil block is carried out biodegradation, and all kinds of Recyclables meanwhile step 5 floatingly selected carry out reclaiming and passed in porous soil block and carry out biodegradation in the lump with porous soil block by the waste water that flotation produces.
2. waste disposal method according to claim 1, is characterized in that: in described step 4, the method for waste gas cooling is: waste gas is imported chimney, in chimney outer felt around water cooling tube.
3. waste disposal method according to claim 1, is characterized in that: the method being in charge of process in described step 4 is: after waste gas is imported chimney, connects a point pipe joint at chimney end, and point pipe joint connects some sub-chimneys.
4. waste disposal method according to claim 1, is characterized in that: the method that in described step 5, waste gas is filtered by porous soil block is: fill at sub-chimney internal diameter the yellow mud block that some diameters are 15-20 centimetre, waste gas is imported sub-chimney.
5. waste disposal method according to claim 1, is characterized in that: in described step 5, the preparation method of porous soil block is: add stalk after mixing of being watered by yellow mud, straw kneading is agglomerating, dry or dry.
6. waste disposal method according to claim 1, it is characterized in that: the biodegradable method in described step 6 is: the porous soil block completing filtration in step 5 is poured in cement pit, waste water step 5 flotation produced imports cement pit, porous soil block and waste water are uniformly mixed and add aerobic bacterial classification, mud in cement pit takes out after one week to two weeks and is piled into mount by air agitation process, some earthworms are put into the some sesbanias of mount surface grafting in mount, treat that sesbania first time Post flowering at least plants a large-scale arbor seedling on mount.
7. a refuse treatment plant, it is characterized in that: comprise refuse grinder, garbage dewatering, feeding roller-way, continous way incinerator, chimney, floation tank and cement pit, described refuse grinder, garbage dewatering, feeding roller-way, continous way incinerator connects successively, described continous way incinerator top is provided with some chimneys, described chimney is connected with some horizontally disposed sub-chimneys by a point pipe joint, some porous soil blocks are filled with in described sub-chimney, described sub-chimney adopts disparting type structure and adopts buckle fastening, described sub-chimney is arranged on above cement pit, slag-drip opening is provided with bottom described continous way incinerator, described slag-drip opening connects floation tank, described floation tank connects cement pit by pipeline.
8. refuse treatment plant according to claim 7, is characterized in that: wound form water cooling tube outside described chimney.
9. refuse treatment plant according to claim 7, is characterized in that: described sub-chimney internal diameter is 20-30 centimetre, and described sub-chimney length is 10-15 rice, and described sub-chimney quantity is no less than 50.
10. refuse treatment plant according to claim 7, is characterized in that: described porous soil block diameter is 15-20 centimetre; Or, in described cement pit, be at least provided with a kind of agitating device and a kind of air-breather; Or described continous way incinerator is connected with at least one in heating system, electricity generation system.
Priority Applications (1)
| Application Number | Priority Date | Filing Date | Title |
|---|---|---|---|
| CN201510679162.7A CN105180171B (en) | 2015-10-19 | 2015-10-19 | A kind of waste disposal method and its processing equipment |
Applications Claiming Priority (1)
| Application Number | Priority Date | Filing Date | Title |
|---|---|---|---|
| CN201510679162.7A CN105180171B (en) | 2015-10-19 | 2015-10-19 | A kind of waste disposal method and its processing equipment |
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| CN105180171A true CN105180171A (en) | 2015-12-23 |
| CN105180171B CN105180171B (en) | 2017-12-08 |
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| CN201510679162.7A Active CN105180171B (en) | 2015-10-19 | 2015-10-19 | A kind of waste disposal method and its processing equipment |
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Cited By (3)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| CN106311716A (en) * | 2016-08-05 | 2017-01-11 | 奚正文 | Garbage treatment machine |
| CN107774674A (en) * | 2016-08-30 | 2018-03-09 | 陕西鑫能环境科技股份有限公司 | A kind of consumer waste incineration pretreatment unit and electricity generation system |
| CN108716684A (en) * | 2018-05-23 | 2018-10-30 | 安徽省农业科学院土壤肥料研究所 | A kind of field straw combustion method that smoke-producing amount is few |
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| CN2456034Y (en) * | 2000-12-19 | 2001-10-24 | 中国科学院广州能源研究所 | Chimney of incinerator with flue purification |
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| GB2478797A (en) * | 2010-03-19 | 2011-09-21 | Advanced Plasma Power Ltd | Treatment of wastes using two plasma chambers |
| CA2832892A1 (en) * | 2010-05-07 | 2011-11-10 | Advanced Plasma Power Limited | Waste treatment |
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| CN203533565U (en) * | 2013-09-26 | 2014-04-09 | 深圳市汇清科技有限公司 | Household refuse incineration and auxiliary smoke processing system |
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| CN2456034Y (en) * | 2000-12-19 | 2001-10-24 | 中国科学院广州能源研究所 | Chimney of incinerator with flue purification |
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| Publication number | Priority date | Publication date | Assignee | Title |
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| CN106311716A (en) * | 2016-08-05 | 2017-01-11 | 奚正文 | Garbage treatment machine |
| CN107774674A (en) * | 2016-08-30 | 2018-03-09 | 陕西鑫能环境科技股份有限公司 | A kind of consumer waste incineration pretreatment unit and electricity generation system |
| CN108716684A (en) * | 2018-05-23 | 2018-10-30 | 安徽省农业科学院土壤肥料研究所 | A kind of field straw combustion method that smoke-producing amount is few |
Also Published As
| Publication number | Publication date |
|---|---|
| CN105180171B (en) | 2017-12-08 |
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