CN106734118A - A kind of processing method of house refuse foul smell - Google Patents
A kind of processing method of house refuse foul smell Download PDFInfo
- Publication number
- CN106734118A CN106734118A CN201710086412.5A CN201710086412A CN106734118A CN 106734118 A CN106734118 A CN 106734118A CN 201710086412 A CN201710086412 A CN 201710086412A CN 106734118 A CN106734118 A CN 106734118A
- Authority
- CN
- China
- Prior art keywords
- rubbish
- foul smell
- processing method
- treatment
- refuse
- Prior art date
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- 238000003672 processing method Methods 0.000 title claims abstract description 21
- 239000010813 municipal solid waste Substances 0.000 claims abstract description 93
- 102000004190 Enzymes Human genes 0.000 claims abstract description 42
- 108090000790 Enzymes Proteins 0.000 claims abstract description 42
- 241000894006 Bacteria Species 0.000 claims abstract description 37
- 238000000855 fermentation Methods 0.000 claims abstract description 23
- 238000000034 method Methods 0.000 claims abstract description 16
- 239000011888 foil Substances 0.000 claims abstract description 15
- 229910001385 heavy metal Inorganic materials 0.000 claims abstract description 10
- 238000004458 analytical method Methods 0.000 claims abstract description 5
- 238000004064 recycling Methods 0.000 claims abstract description 5
- 238000012216 screening Methods 0.000 claims abstract description 5
- 239000007921 spray Substances 0.000 claims abstract description 4
- 239000000243 solution Substances 0.000 claims description 34
- 230000004151 fermentation Effects 0.000 claims description 8
- JVTAAEKCZFNVCJ-UHFFFAOYSA-N lactic acid Chemical compound CC(O)C(O)=O JVTAAEKCZFNVCJ-UHFFFAOYSA-N 0.000 claims description 8
- 239000003895 organic fertilizer Substances 0.000 claims description 8
- 238000006243 chemical reaction Methods 0.000 claims description 6
- 238000010790 dilution Methods 0.000 claims description 6
- 239000012895 dilution Substances 0.000 claims description 6
- 230000035484 reaction time Effects 0.000 claims description 6
- XLYOFNOQVPJJNP-UHFFFAOYSA-N water Substances O XLYOFNOQVPJJNP-UHFFFAOYSA-N 0.000 claims description 6
- 244000063299 Bacillus subtilis Species 0.000 claims description 4
- 241000233866 Fungi Species 0.000 claims description 4
- 230000034303 cell budding Effects 0.000 claims description 4
- 239000004310 lactic acid Substances 0.000 claims description 4
- 235000014655 lactic acid Nutrition 0.000 claims description 4
- 235000014469 Bacillus subtilis Nutrition 0.000 claims description 3
- 238000002156 mixing Methods 0.000 claims description 3
- 235000001674 Agaricus brunnescens Nutrition 0.000 claims description 2
- 239000000463 material Substances 0.000 claims description 2
- 238000001514 detection method Methods 0.000 claims 1
- 230000000694 effects Effects 0.000 abstract description 4
- 230000006641 stabilisation Effects 0.000 abstract description 3
- 238000011105 stabilization Methods 0.000 abstract description 3
- 239000007789 gas Substances 0.000 description 9
- CURLTUGMZLYLDI-UHFFFAOYSA-N Carbon dioxide Chemical compound O=C=O CURLTUGMZLYLDI-UHFFFAOYSA-N 0.000 description 4
- 238000005516 engineering process Methods 0.000 description 4
- 239000010791 domestic waste Substances 0.000 description 3
- QGZKDVFQNNGYKY-UHFFFAOYSA-N Ammonia Chemical compound N QGZKDVFQNNGYKY-UHFFFAOYSA-N 0.000 description 2
- 239000001569 carbon dioxide Substances 0.000 description 2
- 229910002092 carbon dioxide Inorganic materials 0.000 description 2
- 238000006555 catalytic reaction Methods 0.000 description 2
- DNJIEGIFACGWOD-UHFFFAOYSA-N ethanethiol Chemical compound CCS DNJIEGIFACGWOD-UHFFFAOYSA-N 0.000 description 2
- 239000007788 liquid Substances 0.000 description 2
- 239000002994 raw material Substances 0.000 description 2
- RWSOTUBLDIXVET-UHFFFAOYSA-N Dihydrogen sulfide Chemical group S RWSOTUBLDIXVET-UHFFFAOYSA-N 0.000 description 1
- NINIDFKCEFEMDL-UHFFFAOYSA-N Sulfur Chemical compound [S] NINIDFKCEFEMDL-UHFFFAOYSA-N 0.000 description 1
- 239000005864 Sulphur Substances 0.000 description 1
- 238000010521 absorption reaction Methods 0.000 description 1
- 150000001298 alcohols Chemical class 0.000 description 1
- 229910021529 ammonia Inorganic materials 0.000 description 1
- 230000001580 bacterial effect Effects 0.000 description 1
- 230000009286 beneficial effect Effects 0.000 description 1
- 239000002361 compost Substances 0.000 description 1
- 230000007812 deficiency Effects 0.000 description 1
- 238000001035 drying Methods 0.000 description 1
- 230000008030 elimination Effects 0.000 description 1
- 238000003379 elimination reaction Methods 0.000 description 1
- 238000003912 environmental pollution Methods 0.000 description 1
- 229910000037 hydrogen sulfide Inorganic materials 0.000 description 1
- 238000004519 manufacturing process Methods 0.000 description 1
- VUZPPFZMUPKLLV-UHFFFAOYSA-N methane;hydrate Chemical compound C.O VUZPPFZMUPKLLV-UHFFFAOYSA-N 0.000 description 1
- 238000001179 sorption measurement Methods 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
- 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
-
- C—CHEMISTRY; METALLURGY
- C05—FERTILISERS; MANUFACTURE THEREOF
- C05F—ORGANIC FERTILISERS NOT COVERED BY SUBCLASSES C05B, C05C, e.g. FERTILISERS FROM WASTE OR REFUSE
- C05F9/00—Fertilisers from household or town refuse
-
- Y—GENERAL TAGGING OF NEW TECHNOLOGICAL DEVELOPMENTS; GENERAL TAGGING OF CROSS-SECTIONAL TECHNOLOGIES SPANNING OVER SEVERAL SECTIONS OF THE IPC; TECHNICAL SUBJECTS COVERED BY FORMER USPC CROSS-REFERENCE ART COLLECTIONS [XRACs] AND DIGESTS
- Y02—TECHNOLOGIES OR APPLICATIONS FOR MITIGATION OR ADAPTATION AGAINST CLIMATE CHANGE
- Y02A—TECHNOLOGIES FOR ADAPTATION TO CLIMATE CHANGE
- Y02A40/00—Adaptation technologies in agriculture, forestry, livestock or agroalimentary production
- Y02A40/10—Adaptation technologies in agriculture, forestry, livestock or agroalimentary production in agriculture
- Y02A40/20—Fertilizers of biological origin, e.g. guano or fertilizers made from animal corpses
-
- Y—GENERAL TAGGING OF NEW TECHNOLOGICAL DEVELOPMENTS; GENERAL TAGGING OF CROSS-SECTIONAL TECHNOLOGIES SPANNING OVER SEVERAL SECTIONS OF THE IPC; TECHNICAL SUBJECTS COVERED BY FORMER USPC CROSS-REFERENCE ART COLLECTIONS [XRACs] AND DIGESTS
- Y02—TECHNOLOGIES OR APPLICATIONS FOR MITIGATION OR ADAPTATION AGAINST CLIMATE CHANGE
- Y02W—CLIMATE CHANGE MITIGATION TECHNOLOGIES RELATED TO WASTEWATER TREATMENT OR WASTE MANAGEMENT
- Y02W30/00—Technologies for solid waste management
- Y02W30/40—Bio-organic fraction processing; Production of fertilisers from the organic fraction of waste or refuse
Landscapes
- Engineering & Computer Science (AREA)
- Environmental & Geological Engineering (AREA)
- Chemical & Material Sciences (AREA)
- Organic Chemistry (AREA)
- Physics & Mathematics (AREA)
- Thermal Sciences (AREA)
- Processing Of Solid Wastes (AREA)
- Fertilizers (AREA)
Abstract
The invention discloses a kind of processing method of house refuse foul smell, belong to technical field of domestic garbage treatment.The processing method is comprised the following steps：Rubbish is picked up and slowly unclamped by a, startup garbage grab bucket machine, rubbish is loosely fallen, and uniformly sprays enzyme bacterium solution to rubbish while rubbish falls；B, on rubbish heap cover plastic foil carry out anaerobic fermentation treatment；C, plastic foil repeat step a and b are raised, until refuse odor is eliminated；D, the rubbish to having eliminated foul smell carry out screening process；E, recycling treatment is carried out to inorganic refuse；Rubbish to that cannot recycle is removed heavy metal treatment or minimizing treatment after carrying out heavy metal analysis.Processing method of the present invention can efficiently, stabilization, rapidly process the foul gas of domestic garbage treatment plant, high treating effect, investment and operating cost are low.
Description
Technical field
The present invention relates to technical field of domestic garbage treatment, and in particular to a kind of processing method of house refuse foul smell.
Background technology
During domestic waste comprehensively sorting, compost and landfill disposal, it is hydrogen sulfide, sulphur that can produce main component
The foul gas of alcohols, ammonia and VOC.The foul gas threshold concentration that domestic waste factory produces is low, right
Equipment and pipeline have aggressive, and also the daily life of normal production and nearby residents can be interfered, and produce tight
Health and the ecological environment harm of weight.
Technology development for urban garbage disposal factory foul gas mainly includes absorption and sorption, is catalyzed, burns
Burning and plasma technique etc..In recent years, biologic treating technique particularly bio-filter technology is because equipment is simple, treatment effeciency
High, investment and operating cost is low, non-secondary pollution the advantages of, be gradually applied to the treatment of gases containing stench sulphureous gases.At present, it is conventional
Biological treatment system has treatment effeciency low, difficult to realize up to standard when the gases containing stench sulphureous gases of domestic waste are processed
Discharge, the drawback such as system operation is unstable, processing cost is high.
The content of the invention
In order to overcome the deficiencies in the prior art, it is an object of the invention to provide a kind for the treatment of side of house refuse foul smell
Method, the processing method can efficiently, stabilization, rapidly process the foul gas of domestic garbage treatment plant, high treating effect, investment and
Operating cost is low.
To solve the above problems, the technical solution adopted in the present invention is as follows：
A kind of processing method of house refuse foul smell, it is comprised the following steps：
The rubbish that a, startup garbage grab bucket machine will be deposited in rubbish factory building is picked up and slowly unclamped, and rubbish is loosely fallen
To refuse collection hole；While rubbish falls, enzyme bacterium solution is uniformly sprayed to rubbish using flusher so that enzyme bacterium solution with
Rubbish is fully contacted carries out stack retting reaction；
B, being sprayed with covering plastic foil on the rubbish heap of enzyme bacterium solution, the biology enzyme in enzyme bacterium solution is carried out anaerobism with rubbish
Fermentation process；
After c, anaerobic fermentation treatment terminate, plastic foil, repeat step a and b are raised, until refuse odor is eliminated；
D, the rubbish to having eliminated foul smell in step c carry out screening process by inorganic refuse and organic fertilizer；
E, recycling treatment is carried out to inorganic refuse；Rubbish to that cannot recycle carries out heavy metal analysis, right
Detect that underproof rubbish is removed heavy metal treatment, to detecting that qualified rubbish is used as concrete after carrying out minimizing treatment
Raw material or the organic fertilizer for planting forest.
Used as the preferred embodiment of the present invention, the temperature in the step a in refuse collection hole is 10~30 DEG C, humidity
It is 40~80%.
Used as the preferred embodiment of the present invention, the reaction time of the anaerobic fermentation treatment in the step b is 5~10h.
Preferably, the reaction time of the anaerobic fermentation treatment in the step b is 6h.
Used as the preferred embodiment of the present invention, anaerobic fermentation treatment carries out refuse collection hole after 1~3h in the step b
Temperature rise to 40~60 DEG C.
Used as the preferred embodiment of the present invention, the enzyme bacterium solution is by lactic acid bacteria class, budding fungus, bacillus subtilis
Bacterium, lichengermium carry out what fermentation in parallel was made after mixing in UNICOM's tank.
Preferably, the enzyme bacterium solution presses 1：Enzyme bacterium solution is pressed after 100 ratio and water dilution：Rubbish=1:1 ratio uniform
It is sprayed onto on rubbish.
Preferably, also include using flusher to plastic foil uppermost spray enzyme bacterium solution in the step b, to eliminate effusion
Foul smell.
Preferably, the refuse leachate in the step b produced by anaerobic fermentation treatment is oozed by pipeline to rubbish
Processed in transparent liquid processing pond.
Compared to existing technology, the beneficial effects of the present invention are：
The processing method of house refuse foul smell of the present invention carries out biology and urges to rubbish at normal temperatures using enzyme bacterium solution
Change treatment to eliminate refuse odor, step operation is simple, compared with the processing method of prior art, in the factory building of same homalographic
Interior, the process cycle of refuse odor shortens to 5~10h from 72h, substantially reduces the process cycle of rubbish, can make house refuse
The garbage disposal ability for the treatment of plant improves 12 times, greatly reduces processing cost.The present invention can efficiently, stabilization, rapidly process
The foul gas of domestic garbage treatment plant, high treating effect, investment and operating cost are low.
Brief description of the drawings
Fig. 1 is the process chart of the processing method of house refuse foul smell of the present invention.
Specific embodiment
The present invention is described in further detail with reference to the accompanying drawings and detailed description.
As shown in figure 1, being a kind of processing method of house refuse foul smell of the present invention, it is comprised the following steps：
The rubbish that a, startup garbage grab bucket machine will be deposited in rubbish factory building is picked up and slowly unclamped, and rubbish is loosely fallen
To refuse collection hole；While rubbish falls, enzyme bacterium solution is uniformly sprayed to rubbish using flusher so that enzyme bacterium solution with
Rubbish is fully contacted carries out stack retting reaction；
B, being sprayed with covering plastic foil on the rubbish heap of enzyme bacterium solution, the biology enzyme in enzyme bacterium solution is carried out anaerobism with rubbish
Fermentation process；
After c, anaerobic fermentation treatment terminate, plastic foil, repeat step a and b are raised, until refuse odor is eliminated；
D, the rubbish to having eliminated foul smell in step c carry out screening process by inorganic refuse and organic fertilizer；
E, recycling treatment is carried out to inorganic refuse；Rubbish to that cannot recycle carries out heavy metal analysis, right
Detect that underproof rubbish is removed heavy metal treatment, to detecting that qualified rubbish is used as concrete after carrying out minimizing treatment
Raw material or the organic fertilizer for planting forest.
Preferably, in step a refuse collection hole in temperature for 10~30 DEG C, humidity be 40~80%, with this understanding,
The catalysis activity highest of biology enzyme.
The reaction time of the anaerobic fermentation treatment in step b is 5~10h.Preferably, the anaerobic fermentation treatment in step b
Reaction time be 6h.
Anaerobic fermentation treatment carries out the temperature in refuse collection hole after 1~3h and rises to 40~60 DEG C in step b.
Enzyme bacterium solution is to mix laggard in UNICOM's tank by lactic acid bacteria class, budding fungus, bacillus subtilis, lichengermium
Row fermentation in parallel is made.The number of viable of the enzyme bacterium solution can reach 2,300,000,000/milliliter, and the bacterial activity of the bacterium solution is good,
It is activated after adding water dilution, the organic molecule in rubbish can be decomposed, is entered rubbish and macerate ripe yeastiness.It is preferred that
Ground, enzyme bacterium solution presses 1：Enzyme bacterium solution is pressed after 100 ratio and water dilution：Rubbish=1:1 ratio uniform is sprayed onto on rubbish.
Also include using flusher to plastic foil uppermost spray enzyme bacterium solution in step b, to eliminate the foul smell of effusion.Work as life
When thing enzyme molecule is sprayed device and is sprayed at the top of plastic foil, biological enzyme molecule is fully contacted with the foul smell molecule for escaping, and makes
Obtain foul smell molecule and resolve into carbon dioxide and water, to reach elimination foul smell, can effectively prevent refuse odor from escaping around influence and occupy
The life of the people.
Refuse leachate in step b produced by anaerobic fermentation treatment is by pipeline to refuse leachate processing pond
Treatment, it is ensured that secondary environmental pollution and foul smell will not be produced to disturb residents.
Embodiment：
The house refuse Odor control of certain destructor plant comprises the following steps：
A, daily 133 15 tons of garbage truck pour into 2000 tons of house refuse in dump pit in the refuse-unloading Room, and 5
The garbage grab bucket machine of ton picks up rubbish, moves to the top in refuse collection hole, and then grab bucket is come up, and rubbish is loosely fallen
Under, enzyme bacterium solution is sprayed to grab bucket and the rubbish for falling by the flusher positioned at refuse collection hole corner, so that enzyme bacterium solution and rubbish
Be fully contacted temperature be 10~30 DEG C, humidity be 40~80% under conditions of carry out stack retting reaction.In the refuse-unloading Room daily
Receive 2000 tons of rubbish, it is necessary to install many loop wheel machines and grab bucket, coordinate biology enzyme sprinkling system.Wherein, enzyme bacterium solution is by lactic acid
Mushroom, budding fungus, bacillus subtilis, lichengermium carry out what fermentation in parallel was made after mixing in UNICOM's tank.Enzyme bacterium
Liquid presses 1：Enzyme bacterium solution is pressed after 100 ratio and water dilution：Rubbish=1:1 ratio uniform is sprayed onto on rubbish.Daily 2000 tons
Rubbish needs the dilution enzyme bacterium solution of 2000kg altogether.It is above-mentioned it is aerobic macerate it is ripe during, the moisture in rubbish is constantly evaporated, rubbish
The overall storage of rubbish is reduced.
B, complete that above-mentioned rubbish is aerobic and macerate ripe technique after, be sprayed with covering plastic foil on the rubbish heap of enzyme bacterium solution, enter
The treatment of row garbage anaerobic fermentation；After reaction 2h, the temperature of garbage disposal factory building rises to 40 DEG C；After reaction 6h, the rubbish in plastic foil
Rubbish carries out catalytic reaction by biology enzyme, and garbage odor molecule is broken down into carbon dioxide and hydrone, and refuse odor is most of
Eliminate.
After c, anaerobic fermentation treatment terminate, plastic foil is raised, repeat step a and b in 5 days, until refuse odor is eliminated.
D, the rubbish to having eliminated foul smell in step c carry out screening process by inorganic refuse and organic fertilizer.
E, recycling treatment is carried out to inorganic refuse；Rubbish to that cannot recycle carries out heavy metal analysis, right
Detect that underproof rubbish is removed heavy metal treatment, the rubbish to detecting qualified is sent to garbage drying room to be carried out at minimizing
It is used as concrete material or the organic fertilizer for planting forest after reason.
Above-mentioned implementation method is only the preferred embodiment of the present invention, it is impossible to limit the scope of protection of the invention with this,
The change and replacement of any unsubstantiality that those skilled in the art is done on the basis of of the invention belong to institute of the present invention
Claimed scope.
Claims (9)
1. a kind of processing method of house refuse foul smell, it is characterised in that：Comprise the following steps：
The rubbish that a, startup garbage grab bucket machine will be deposited in rubbish factory building is picked up and slowly unclamped, and rubbish is loosely fallen to rubbish
In rubbish collection pit；While rubbish falls, enzyme bacterium solution is uniformly sprayed to rubbish using flusher, so that enzyme bacterium solution and rubbish
Being fully contacted carries out stack retting reaction；
B, being sprayed with covering plastic foil on the rubbish heap of enzyme bacterium solution, the biology enzyme in enzyme bacterium solution is carried out anaerobic fermentation with rubbish
Treatment；
After c, anaerobic fermentation treatment terminate, plastic foil, repeat step a and b are raised, until refuse odor is eliminated；
D, the rubbish to having eliminated foul smell in step c carry out screening process by inorganic refuse and organic fertilizer；
E, recycling treatment is carried out to inorganic refuse；Rubbish to that cannot recycle carries out heavy metal analysis, to detection
Underproof rubbish is removed heavy metal treatment, to detecting that qualified rubbish is used as concrete material after carrying out minimizing treatment
Or for planting the organic fertilizer of forest.
2. the processing method of house refuse foul smell according to claim 1, it is characterised in that：Rubbish is received in the step a
Temperature in collection hole is 10~30 DEG C, humidity is 40~80%.
3. the processing method of house refuse foul smell according to claim 1, it is characterised in that：Anaerobism in the step b
The reaction time of fermentation process is 5~10h.
4. the processing method of house refuse foul smell according to claim 3, it is characterised in that：Anaerobism in the step b
The reaction time of fermentation process is 6h.
5. the processing method of house refuse foul smell according to claim 3, it is characterised in that：Anaerobism hair in the step b
The temperature that ferment treatment carries out refuse collection hole after 1~3h rises to 40~60 DEG C.
6. the processing method of house refuse foul smell according to claim 1, it is characterised in that：The enzyme bacterium solution is by lactic acid
Mushroom, budding fungus, bacillus subtilis, lichengermium carry out what fermentation in parallel was made after mixing in UNICOM's tank.
7. the processing method of house refuse foul smell according to claim 6, it is characterised in that：The enzyme bacterium solution presses 1：100
The dilution of ratio and water after press enzyme bacterium solution：Rubbish=1:1 ratio uniform is sprayed onto on rubbish.
8. the processing method of house refuse foul smell according to claim 1, it is characterised in that：Also include in the step b
Using flusher to plastic foil uppermost spray enzyme bacterium solution, to eliminate the foul smell of effusion.
9. the processing method of house refuse foul smell according to claim 1, it is characterised in that：Anaerobism hair in the step b
Refuse leachate produced by ferment treatment is processed by pipeline to refuse leachate processing pond.
Priority Applications (1)
| Application Number | Priority Date | Filing Date | Title |
|---|---|---|---|
| CN201710086412.5A CN106734118B (en) | 2017-02-17 | 2017-02-17 | Treatment method of household garbage odor |
Applications Claiming Priority (1)
| Application Number | Priority Date | Filing Date | Title |
|---|---|---|---|
| CN201710086412.5A CN106734118B (en) | 2017-02-17 | 2017-02-17 | Treatment method of household garbage odor |
Publications (2)
| Publication Number | Publication Date |
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| CN106734118A true CN106734118A (en) | 2017-05-31 |
| CN106734118B CN106734118B (en) | 2020-03-20 |
Family
ID=58958578
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|---|---|---|---|
| CN201710086412.5A Active CN106734118B (en) | 2017-02-17 | 2017-02-17 | Treatment method of household garbage odor |
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Cited By (4)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| CN107597786A (en) * | 2017-11-02 | 2018-01-19 | 成都三洲康洁生物科技有限责任公司 | Method for consumer waste filling and embedding processing |
| CN109158403A (en) * | 2018-08-07 | 2019-01-08 | 刘树云 | House refuse biology high temperature drying method for treating |
| CN110436974A (en) * | 2019-09-05 | 2019-11-12 | 湖南人文科技学院 | A kind of non-pollution processing method and system of afforestation rubbish |
| CN111167834A (en) * | 2020-01-10 | 2020-05-19 | 吕爱军 | System and method for heating garbage entering factory in garbage power plant |
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| CN111167834A (en) * | 2020-01-10 | 2020-05-19 | 吕爱军 | System and method for heating garbage entering factory in garbage power plant |
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