CN108772408A - Municipal refuse comprehensive processing technique - Google Patents
Municipal refuse comprehensive processing technique Download PDFInfo
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- CN108772408A CN108772408A CN201810663505.4A CN201810663505A CN108772408A CN 108772408 A CN108772408 A CN 108772408A CN 201810663505 A CN201810663505 A CN 201810663505A CN 108772408 A CN108772408 A CN 108772408A
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- municipal refuse
- water
- comprehensive processing
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- 238000000034 method Methods 0.000 title claims abstract description 46
- 239000010813 municipal solid waste Substances 0.000 claims abstract description 33
- 239000000126 substance Substances 0.000 claims abstract description 22
- XLYOFNOQVPJJNP-UHFFFAOYSA-N water Substances O XLYOFNOQVPJJNP-UHFFFAOYSA-N 0.000 claims abstract description 21
- 230000008569 process Effects 0.000 claims abstract description 16
- 229910052751 metal Inorganic materials 0.000 claims abstract description 13
- 239000002184 metal Substances 0.000 claims abstract description 13
- 239000002351 wastewater Substances 0.000 claims abstract description 13
- 239000007787 solid Substances 0.000 claims abstract description 10
- 238000004065 wastewater treatment Methods 0.000 claims abstract description 9
- 238000009841 combustion method Methods 0.000 claims abstract description 7
- 239000002068 microbial inoculum Substances 0.000 claims description 20
- JVTAAEKCZFNVCJ-UHFFFAOYSA-N lactic acid Chemical compound CC(O)C(O)=O JVTAAEKCZFNVCJ-UHFFFAOYSA-N 0.000 claims description 14
- 241000894006 Bacteria Species 0.000 claims description 12
- QVGXLLKOCUKJST-UHFFFAOYSA-N atomic oxygen Chemical compound [O] QVGXLLKOCUKJST-UHFFFAOYSA-N 0.000 claims description 9
- 229910052760 oxygen Inorganic materials 0.000 claims description 9
- 239000001301 oxygen Substances 0.000 claims description 9
- 241000194108 Bacillus licheniformis Species 0.000 claims description 7
- 244000063299 Bacillus subtilis Species 0.000 claims description 7
- 235000014469 Bacillus subtilis Nutrition 0.000 claims description 7
- 241000108664 Nitrobacteria Species 0.000 claims description 7
- 239000004310 lactic acid Substances 0.000 claims description 7
- 235000014655 lactic acid Nutrition 0.000 claims description 7
- 239000007788 liquid Substances 0.000 claims description 6
- 239000010865 sewage Substances 0.000 claims description 6
- 241000193749 Bacillus coagulans Species 0.000 claims description 5
- 229940054340 bacillus coagulans Drugs 0.000 claims description 5
- 239000003795 chemical substances by application Substances 0.000 claims description 5
- 241000235342 Saccharomycetes Species 0.000 claims description 4
- 230000001580 bacterial effect Effects 0.000 claims description 3
- 239000000463 material Substances 0.000 claims description 3
- 238000003756 stirring Methods 0.000 claims description 3
- 238000009833 condensation Methods 0.000 claims description 2
- 230000005494 condensation Effects 0.000 claims description 2
- 241000726221 Gemma Species 0.000 claims 1
- 239000002131 composite material Substances 0.000 claims 1
- 230000000813 microbial effect Effects 0.000 claims 1
- 238000004064 recycling Methods 0.000 abstract description 8
- 239000002699 waste material Substances 0.000 abstract description 6
- 230000007613 environmental effect Effects 0.000 abstract description 5
- 230000009466 transformation Effects 0.000 abstract description 4
- 238000003672 processing method Methods 0.000 abstract description 3
- 239000002912 waste gas Substances 0.000 abstract description 3
- 239000002361 compost Substances 0.000 description 4
- 239000007789 gas Substances 0.000 description 4
- 238000009264 composting Methods 0.000 description 3
- 238000000926 separation method Methods 0.000 description 3
- 230000015572 biosynthetic process Effects 0.000 description 2
- 230000008859 change Effects 0.000 description 2
- 238000011038 discontinuous diafiltration by volume reduction Methods 0.000 description 2
- 230000000694 effects Effects 0.000 description 2
- 238000005516 engineering process Methods 0.000 description 2
- 238000001914 filtration Methods 0.000 description 2
- 230000036541 health Effects 0.000 description 2
- 238000004519 manufacturing process Methods 0.000 description 2
- 230000003647 oxidation Effects 0.000 description 2
- 238000007254 oxidation reaction Methods 0.000 description 2
- 238000003786 synthesis reaction Methods 0.000 description 2
- 238000004056 waste incineration Methods 0.000 description 2
- 241000193830 Bacillus <bacterium> Species 0.000 description 1
- OKTJSMMVPCPJKN-UHFFFAOYSA-N Carbon Chemical compound [C] OKTJSMMVPCPJKN-UHFFFAOYSA-N 0.000 description 1
- UGFAIRIUMAVXCW-UHFFFAOYSA-N Carbon monoxide Chemical compound [O+]#[C-] UGFAIRIUMAVXCW-UHFFFAOYSA-N 0.000 description 1
- 241000233866 Fungi Species 0.000 description 1
- 240000004808 Saccharomyces cerevisiae Species 0.000 description 1
- QAOWNCQODCNURD-UHFFFAOYSA-N Sulfuric acid Chemical compound OS(O)(=O)=O QAOWNCQODCNURD-UHFFFAOYSA-N 0.000 description 1
- 230000004913 activation Effects 0.000 description 1
- 239000004566 building material Substances 0.000 description 1
- AXCZMVOFGPJBDE-UHFFFAOYSA-L calcium dihydroxide Chemical compound [OH-].[OH-].[Ca+2] AXCZMVOFGPJBDE-UHFFFAOYSA-L 0.000 description 1
- 239000000920 calcium hydroxide Substances 0.000 description 1
- 229910001861 calcium hydroxide Inorganic materials 0.000 description 1
- 229910052799 carbon Inorganic materials 0.000 description 1
- 150000001875 compounds Chemical class 0.000 description 1
- 238000010276 construction Methods 0.000 description 1
- 230000037213 diet Effects 0.000 description 1
- 235000005911 diet Nutrition 0.000 description 1
- 239000010791 domestic waste Substances 0.000 description 1
- 238000011049 filling Methods 0.000 description 1
- 239000003546 flue gas Substances 0.000 description 1
- 235000013305 food Nutrition 0.000 description 1
- 229910001385 heavy metal Inorganic materials 0.000 description 1
- 238000011068 loading method Methods 0.000 description 1
- 230000035800 maturation Effects 0.000 description 1
- 238000002844 melting Methods 0.000 description 1
- 230000008018 melting Effects 0.000 description 1
- 230000002906 microbiologic effect Effects 0.000 description 1
- 238000004806 packaging method and process Methods 0.000 description 1
- 239000010893 paper waste Substances 0.000 description 1
- 239000002245 particle Substances 0.000 description 1
- 238000005325 percolation Methods 0.000 description 1
- 238000000197 pyrolysis Methods 0.000 description 1
- 239000002994 raw material Substances 0.000 description 1
- 239000002689 soil Substances 0.000 description 1
- 239000002910 solid waste Substances 0.000 description 1
- 239000010902 straw Substances 0.000 description 1
- 239000001117 sulphuric acid Substances 0.000 description 1
- 235000011149 sulphuric acid Nutrition 0.000 description 1
- 239000000725 suspension Substances 0.000 description 1
- 239000004753 textile Substances 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
- B09B3/40—Destroying solid waste or transforming solid waste into something useful or harmless involving thermal treatment, e.g. evaporation
-
- 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)
- Physics & Mathematics (AREA)
- Thermal Sciences (AREA)
- Processing Of Solid Wastes (AREA)
- Micro-Organisms Or Cultivation Processes Thereof (AREA)
Abstract
The invention discloses municipal refuse comprehensive processing techniques, include the following steps：(1) garbage classification：Rubbish is divided by solid substance not soluble in water, lightweight combustible and waste water by hydrometer method first, then solid substance not soluble in water is divided by metal and nonmetallic substance by magnetic method；(2) classification is handled：The lightweight combustible is filled after being burnt using combustion method；The waste water discharges after being handled by waste water treatment process；The metal is separated and recovered from using furnace process；The nonmetallic substance rebuild after being crushed.The present invention, which integrates, combines several waste disposal methods and waste water, waste gas processing method, realizes rubbish synthesization, economy, environmental protection treatment, and safety simultaneously is conducive to realize, is truly realized the recycling transformation of city integrated rubbish.
Description
Technical field
The present invention relates to a kind of municipal refuse comprehensive processing techniques, belong to technical field of waste treatment.
Background technology
In terms of global point, as economic is grown continuously and fast, living standards of the people improve rapidly, and urbanization process is not
It is disconnected to accelerate, but the environmental problem faced simultaneously is also on the rise, the especially processing of rubbish.How municipal solid wastes are solved
Problem, also one health of the mankind, clean living environment, have caused the great attention in the whole world.China's house refuse production in 2010
1.58 hundred million tons are measured, the accumulative stockpiling rubbish of surrounding city takes up an area ten thousand mu about more than 80, almost has in 661 cities up to 7,000,000,000 ton
2/3 city is surrounded by rubbish, and serious harm is produced to environment.
Domestic rubbish disposal mode includes mainly the side such as sanitary landfills, burning, compost, pyrolysis and comprehensive garbage disposal
Method.Although wherein filling technically simple maturation, Construction and operation expense is low, and treating capacity is big, needs to occupy a large amount of soils, site
Select Consideration extremely complex, recycling level is low, and there is also certain difficulty for loading embeading percolation liquid and biogas treatment；Rubbish
Burning is that solid waste is carried out to the process of pyrolytic and deep oxidation, has volume reduction, decrement larger, can recycle thermal energy
The advantages that, still, burning secondary pollution is serious, and especially incineration flue gas Zhong bioxin all causes environmental and human health impacts
Harm, some burning disposal projects are because the suspension that is strongly opposed to have to of the common people is built；Garbage compost processing is mainly used in
The higher rural garbage of China's content of organics, straw waste and vast small and medium-sized cities.Although composting technology can effective volume reduction
Decrement, reaches recycling effect, but compost is since there is also many problems, such as adaptability to raw material for the limitation of itself
Difference, heavy metal pollution problem is serious, and composting production sales volume is bad etc..
China's domestic waste be mainly derived from the daily daily life of family life, the food debris of diet, all kinds of devices,
The packaging bag of article, wrapping paper, large quantities of waste paper and textile, old metal etc., component of refuse is complicated, mostly composting.Mesh
Preceding garbage disposal still based on sanitary landfills, is aided with the modes such as waste incineration, compost.Wherein waste incineration is applied to south more
Developed area, and most parts of the north then use landfill disposal rubbish.It is this to handle rubbish only with single treatment mode
The waste disposal method that rubbish or landfill are combined with burning, or can not effectively be directed to garbage property and carry out thoroughly innoxious minimizing
Either recycling level is low or secondary pollution seriously cannot reach good treatment effect for processing.Therefore it needs to be directed to me
State's house refuse characteristic, using novel integrated conduct method, reach the abundant recycling of all the components in rubbish, minimizing,
Harmless treatment.
Invention content
General Office being carried out according to the characteristic of each sorting rubbish after garbage classification the purpose of the present invention is to provide a kind of
The municipal refuse comprehensive processing technique of reason.
The purpose of the present invention is what is be achieved through the following technical solutions：
Municipal refuse comprehensive processing technique, includes the following steps：
(1) garbage classification：First by hydrometer method by rubbish be divided into solid substance not soluble in water, lightweight combustible and
Waste water, then solid substance not soluble in water is divided by metal and nonmetallic substance by magnetic method；
(2) classification is handled：The lightweight combustible is filled after being burnt using combustion method；The waste water passes through wastewater treatment work
It is discharged after skill processing；The metal is separated and recovered from using furnace process；The nonmetallic substance rebuild after being crushed.
Further, the thermal energy generated after the combustion method burning can be used for producing electricl energy.
Further, the waste water treatment process includes the following steps：
(1) it adjusts：It adjusting pH value and is passed through oxygen, the adjusting pH value refers to adjusting pH value by adding acid-base material,
The range 7~9 of pH value；
(2) it handles and discharges：Complex microbial inoculum is added and carries out sewage disposal；It specifically refers to be added in every liter of sewage
5~8g complex microbial inoculums, and 30~40min is stirred, stirring while, is passed through oxygen, then is discharged after standing.
Further, the complex microbial inoculum includes following components of the dry cell weight than part：Nitrobacteria 20~28
Part, 15~18 parts of saccharomycete, 12~15 parts of bacillus subtilis, 30~36 parts of bacillus coagulans, bacillus licheniformis 14~
17 parts and 9~12 parts of lactic acid bacteria, and added and its parts by weight C toward above-mentioned microbial inoculum12H22O117~9 parts.
Further, the complex microbial inoculum includes following components of the dry cell weight than part：25 parts of nitrobacteria, ferment
11 parts of 16 parts of female bacterium, 13 parts of bacillus subtilis, 33 parts of bacillus coagulans, 15 parts of bacillus licheniformis and lactic acid bacteria, and
Toward the addition of above-mentioned microbial inoculum and its parts by weight C12H22O118 parts.
Further, the clear water that complex microbial inoculum elder generation temperature in use is 30~40 ° is prepared into liquid bacterial agent, and
It is 6~8 hours to keep the temperature, time.
The present invention, which integrates, combines several waste disposal methods and waste water, waste gas processing method, realizes rubbish synthesis
Change, economy, environmental protection treatment, safety are simultaneously conducive to realization, are truly realized the recycling transformation of city integrated rubbish.
Specific implementation mode
Embodiment 1
Municipal refuse comprehensive processing technique provided in this embodiment, includes the following steps：
(1) garbage classification：First by hydrometer method by rubbish be divided into solid substance not soluble in water, lightweight combustible and
Waste water, then solid substance not soluble in water is divided by metal and nonmetallic substance by magnetic method；The hydrometer method refers to basis
The weight of rubbish is classified, and rubbish is put in water, general solid substance not soluble in water can overweight water, this substance generally comprises
Metal, masonry etc.；The lightweight incendivity object is normally suspended in water, and the metal in solid substance not soluble in water generally passes through
Electromagnet can will be isolated.
(2) classification is handled：The lightweight combustible is filled after being burnt using combustion method, the thermal energy generated in the combustion method
Electric energy can be converted to by the prior art, and the smog for generation of burning can filter wherein harmful gas by filtering technique
Body, the filtering technique include that gas is passed through to water purifying module, oxidation module, active carbon module and irradiation modules successively to remove
Harmful substance, particle, peculiar smell of gas etc. are finally discharged into air, and the sewage after the processing gas of the water purifying module is logical
Subsequent waste water treatment process processing is crossed, pollution environment is prevented.
The waste water discharges after being handled by waste water treatment process；The waste water treatment process includes the following steps：(1) it adjusts
It saves pH value and is passed through oxygen, the adjusting pH value refers to by addition acid-base material adjusting pH value, the range 7~9 of pH value, preferentially
It is 8 to adjust pH value, and wherein pH value is adjusted using industrial sulphuric acid or calcium hydroxide and realized；The oxygen that is passed through refers to passing through exposure
Tracheae is passed through the realization that air realizes oxygen, also waste water is made to seethe, but the pH value and oxygen content in waste water take the lead in reaching micro-
Biological compound fungi agent control environment；
(2) it handles and discharges：Complex microbial inoculum is added and carries out sewage disposal；It specifically refers to be added in every liter of waste water
The complex microbial inoculum of 5~8g, and 30~40min is stirred, stirring while, is passed through oxygen, then stands (water and flocculate point
Until layer is apparent), wherein complex microbial inoculum elder generation temperature in use is prepared into liquid bacterial agent for 30~40 ° of clear water, and
It is 6~8 hours to keep the temperature, time, can C12H22O11Fully activation nitrobacteria, saccharomycete, bacillus subtilis, condensation
Bacillus, bacillus licheniformis and lactic acid bacteria keep wastewater treatment efficiency more preferable, the water discharged after sample process.
Wherein, the complex microbial inoculum includes following components of the dry cell weight than part：20~28 parts of nitrobacteria, ferment
15~18 parts of female bacterium, 12~15 parts of bacillus subtilis, 30~36 parts of bacillus coagulans, 14~17 parts of bacillus licheniformis and
9~12 parts of lactic acid bacteria, and added and its parts by weight C toward above-mentioned microbial inoculum12H22O117~9 parts.
Preferably, the complex microbial inoculum includes following components of the dry cell weight than part：25 parts of nitrobacteria, yeast
11 parts of 16 parts of bacterium, 13 parts of bacillus subtilis, 33 parts of bacillus coagulans, 15 parts of bacillus licheniformis and lactic acid bacteria and past
Above-mentioned microbial inoculum addition and its parts by weight C12H22O118 parts.
The metal is separated and recovered from using furnace process, and the furnace process includes that metal is carried out break process first
After be put into melting furnace fusing after detach, it is described separation be according between different metal fusing point fusing be separated by solid-liquid separation, liquid
It is cooled and shaped after separation, you can realization is recycling.
The nonmetallic substance rebuild after being crushed, and the nonmetallic substance generally comprises building materials and masonry etc., this
Kind substance can again be utilized by being molded again after being crushed, realize resource reutilization.
The present invention, which integrates, combines several waste disposal methods and waste water, waste gas processing method, realizes rubbish synthesis
Change, economy, environmental protection treatment, safety are simultaneously conducive to realization, are truly realized the recycling transformation of city integrated rubbish.
The above is only the preferred embodiment of the present invention, but scope of protection of the present invention is not limited thereto, any
The transformation and replacement that are carried out based on technical solution provided by the present invention and inventive concept should all cover the protection model in the present invention
In enclosing.
Claims (6)
1. municipal refuse comprehensive processing technique, it is characterised in that include the following steps：
(1) garbage classification：Rubbish is divided by solid substance not soluble in water, lightweight combustible by hydrometer method first and is given up
Water, then solid substance not soluble in water is divided by metal and nonmetallic substance by magnetic method；
(2) classification is handled：The lightweight combustible is filled after being burnt using combustion method；The waste water by waste water treatment process at
It is discharged after reason；The metal is separated and recovered from using furnace process；The nonmetallic substance rebuild after being crushed.
2. municipal refuse comprehensive processing technique according to claim 1, it is characterised in that：It is generated after the combustion method burning
Thermal energy can be used for producing electricl energy.
3. municipal refuse comprehensive processing technique according to claim 1, it is characterised in that：The waste water treatment process includes
Following steps：
(1) it adjusts：It adjusts pH value and is passed through oxygen, the adjusting pH value refers to adjusting pH value, pH value by adding acid-base material
Range 7~9；
(2) it handles and discharges：Complex microbial inoculum is added and carries out sewage disposal；Specifically refer in every liter of sewage be added 5~
8g complex microbial inoculums, and 30~40min is stirred, stirring while, is passed through oxygen, then is discharged after standing.
4. municipal refuse comprehensive processing technique according to claim 3, it is characterised in that：The complex microbial inoculum packet
Include following components of the dry cell weight than part：20~28 parts of nitrobacteria, 15~18 parts of saccharomycete, bacillus subtilis 12~15
Part, 30~36 parts of bacillus coagulans, 14~17 parts of bacillus licheniformis and 9~12 parts of lactic acid bacteria, and add toward above-mentioned microbial inoculum
Add and its parts by weight C12H22O117~9 parts.
5. municipal refuse comprehensive processing technique according to claim 3, it is characterised in that：The complex microbial inoculum packet
Include following components of the dry cell weight than part：25 parts of nitrobacteria, 16 parts of saccharomycete, 13 parts of bacillus subtilis, condensation gemma bar
11 parts of 33 parts of bacterium, 15 parts of bacillus licheniformis and lactic acid bacteria, and added and its parts by weight C toward above-mentioned microbial inoculum12H22O118 parts.
6. municipal refuse comprehensive processing technique according to claim 4 or 5, it is characterised in that：The microbial composite bacteria
Agent elder generation temperature in use is that 30~40 ° of clear water is prepared into liquid bacterial agent, and keeps the temperature, and the time is 6~8 hours.
Priority Applications (1)
| Application Number | Priority Date | Filing Date | Title |
|---|---|---|---|
| CN201810663505.4A CN108772408A (en) | 2018-06-25 | 2018-06-25 | Municipal refuse comprehensive processing technique |
Applications Claiming Priority (1)
| Application Number | Priority Date | Filing Date | Title |
|---|---|---|---|
| CN201810663505.4A CN108772408A (en) | 2018-06-25 | 2018-06-25 | Municipal refuse comprehensive processing technique |
Publications (1)
| Publication Number | Publication Date |
|---|---|
| CN108772408A true CN108772408A (en) | 2018-11-09 |
Family
ID=64026319
Family Applications (1)
| Application Number | Title | Priority Date | Filing Date |
|---|---|---|---|
| CN201810663505.4A Pending CN108772408A (en) | 2018-06-25 | 2018-06-25 | Municipal refuse comprehensive processing technique |
Country Status (1)
| Country | Link |
|---|---|
| CN (1) | CN108772408A (en) |
Cited By (1)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| CN113020223A (en) * | 2021-03-26 | 2021-06-25 | 广东省科学院资源综合利用研究所 | Method for recycling urban resident domestic garbage through full-recycling comprehensive treatment |
Citations (13)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| DK71987D0 (en) * | 1987-02-13 | 1987-02-13 | Nordiske Kabel Traad | PROCEDURE FOR CLEANING OIL AND CHEMICAL POLLUTANTS |
| CN1280887A (en) * | 1999-07-15 | 2001-01-24 | 赵石林 | Wet-type pretreating method for life garbage |
| TW200413116A (en) * | 2003-01-28 | 2004-08-01 | Steven Tse | Method and device to recycle and classify weighted garbage |
| CN101318195A (en) * | 2008-04-30 | 2008-12-10 | 北京恒业村科技有限公司 | Wet separation classification processing and reutilization method for domestic garbage |
| CN101716590A (en) * | 2009-12-09 | 2010-06-02 | 李兴 | Method for treating domestic garbage by water sorting |
| WO2011116656A1 (en) * | 2010-03-25 | 2011-09-29 | 河北省建筑材料工业设计研究院 | Combined treatment process of domestic garbage and sewage |
| CN102319722A (en) * | 2011-07-25 | 2012-01-18 | 重庆大学 | Mixed municipal domestic garbage resource treatment process |
| CN102391966A (en) * | 2011-11-17 | 2012-03-28 | 苏柯汉（潍坊）生物工程有限公司 | Composite bacteria for treating food waste percolate and preparation method thereof |
| CN102416398A (en) * | 2011-08-24 | 2012-04-18 | 深圳市艾科斯达投资有限公司 | Municipal solid waste compressive classification treatment method |
| CN103820427A (en) * | 2014-03-25 | 2014-05-28 | 钟华 | Preparation method of microbial water quality purifying fungicide |
| CN203621082U (en) * | 2013-12-19 | 2014-06-04 | 北京蓝天高兆环保科技有限公司 | Domestic garbage disposal system |
| CN104326561A (en) * | 2014-11-18 | 2015-02-04 | 华中农业大学 | Method for improving livestock and poultry breeding wastewater treatment efficiency via strengthening of multistage microorganisms |
| CN106591162A (en) * | 2015-10-15 | 2017-04-26 | 百米马（天津）有限公司 | Petroleum sewage treatment bacteria |
-
2018
- 2018-06-25 CN CN201810663505.4A patent/CN108772408A/en active Pending
Patent Citations (13)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| DK71987D0 (en) * | 1987-02-13 | 1987-02-13 | Nordiske Kabel Traad | PROCEDURE FOR CLEANING OIL AND CHEMICAL POLLUTANTS |
| CN1280887A (en) * | 1999-07-15 | 2001-01-24 | 赵石林 | Wet-type pretreating method for life garbage |
| TW200413116A (en) * | 2003-01-28 | 2004-08-01 | Steven Tse | Method and device to recycle and classify weighted garbage |
| CN101318195A (en) * | 2008-04-30 | 2008-12-10 | 北京恒业村科技有限公司 | Wet separation classification processing and reutilization method for domestic garbage |
| CN101716590A (en) * | 2009-12-09 | 2010-06-02 | 李兴 | Method for treating domestic garbage by water sorting |
| WO2011116656A1 (en) * | 2010-03-25 | 2011-09-29 | 河北省建筑材料工业设计研究院 | Combined treatment process of domestic garbage and sewage |
| CN102319722A (en) * | 2011-07-25 | 2012-01-18 | 重庆大学 | Mixed municipal domestic garbage resource treatment process |
| CN102416398A (en) * | 2011-08-24 | 2012-04-18 | 深圳市艾科斯达投资有限公司 | Municipal solid waste compressive classification treatment method |
| CN102391966A (en) * | 2011-11-17 | 2012-03-28 | 苏柯汉（潍坊）生物工程有限公司 | Composite bacteria for treating food waste percolate and preparation method thereof |
| CN203621082U (en) * | 2013-12-19 | 2014-06-04 | 北京蓝天高兆环保科技有限公司 | Domestic garbage disposal system |
| CN103820427A (en) * | 2014-03-25 | 2014-05-28 | 钟华 | Preparation method of microbial water quality purifying fungicide |
| CN104326561A (en) * | 2014-11-18 | 2015-02-04 | 华中农业大学 | Method for improving livestock and poultry breeding wastewater treatment efficiency via strengthening of multistage microorganisms |
| CN106591162A (en) * | 2015-10-15 | 2017-04-26 | 百米马（天津）有限公司 | Petroleum sewage treatment bacteria |
Non-Patent Citations (1)
| Title |
|---|
| 何莎: "水产养殖水体污染的微生物修复技术", 《江西农业》 * |
Cited By (1)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| CN113020223A (en) * | 2021-03-26 | 2021-06-25 | 广东省科学院资源综合利用研究所 | Method for recycling urban resident domestic garbage through full-recycling comprehensive treatment |
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