CN102219568A - Biological reaction equipment for accelerating domestic garbage landfilling stabilization process - Google Patents
Biological reaction equipment for accelerating domestic garbage landfilling stabilization process Download PDFInfo
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- CN102219568A CN102219568A CN2011100524357A CN201110052435A CN102219568A CN 102219568 A CN102219568 A CN 102219568A CN 2011100524357 A CN2011100524357 A CN 2011100524357A CN 201110052435 A CN201110052435 A CN 201110052435A CN 102219568 A CN102219568 A CN 102219568A
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- buffer layer
- biological reaction
- consumer waste
- landfill
- landfilling
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- 238000000034 method Methods 0.000 title claims abstract description 21
- 238000006243 chemical reaction Methods 0.000 title claims abstract description 19
- 230000006641 stabilisation Effects 0.000 title claims abstract description 15
- 238000011105 stabilization Methods 0.000 title claims abstract description 15
- 239000010813 municipal solid waste Substances 0.000 title abstract description 13
- 238000010169 landfilling Methods 0.000 title abstract 8
- XLYOFNOQVPJJNP-UHFFFAOYSA-N water Substances O XLYOFNOQVPJJNP-UHFFFAOYSA-N 0.000 claims abstract description 13
- 239000002699 waste material Substances 0.000 claims description 29
- 239000000872 buffer Substances 0.000 claims description 20
- 238000004056 waste incineration Methods 0.000 claims description 10
- 239000004576 sand Substances 0.000 claims description 9
- 239000004746 geotextile Substances 0.000 claims description 2
- 239000002245 particle Substances 0.000 claims description 2
- 239000007853 buffer solution Substances 0.000 abstract description 10
- 244000005700 microbiome Species 0.000 abstract description 4
- 230000015556 catabolic process Effects 0.000 abstract description 2
- 238000006731 degradation reaction Methods 0.000 abstract description 2
- 230000000694 effects Effects 0.000 abstract description 2
- 230000001133 acceleration Effects 0.000 abstract 1
- 230000000593 degrading effect Effects 0.000 abstract 1
- 230000000087 stabilizing effect Effects 0.000 abstract 1
- 238000010586 diagram Methods 0.000 description 4
- 239000000126 substance Substances 0.000 description 3
- 230000002596 correlated effect Effects 0.000 description 2
- 238000007599 discharging Methods 0.000 description 2
- 238000005516 engineering process Methods 0.000 description 2
- 239000000463 material Substances 0.000 description 2
- 150000007524 organic acids Chemical class 0.000 description 2
- 238000012545 processing Methods 0.000 description 2
- 238000009825 accumulation Methods 0.000 description 1
- 239000002253 acid Substances 0.000 description 1
- 230000002378 acidificating effect Effects 0.000 description 1
- 230000015572 biosynthetic process Effects 0.000 description 1
- 239000002361 compost Substances 0.000 description 1
- 230000006866 deterioration Effects 0.000 description 1
- 238000011161 development Methods 0.000 description 1
- 230000003203 everyday effect Effects 0.000 description 1
- 238000011835 investigation Methods 0.000 description 1
- 230000002906 microbiologic effect Effects 0.000 description 1
- 235000005985 organic acids Nutrition 0.000 description 1
- 238000011160 research Methods 0.000 description 1
- 230000000630 rising effect Effects 0.000 description 1
- 238000009827 uniform distribution Methods 0.000 description 1
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- 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
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- Processing Of Solid Wastes (AREA)
Abstract
The invention provides biological reaction equipment for accelerating a domestic garbage landfilling stabilization process, comprising a percolate recharging system and a landfilling reactor, wherein the percolate recharging system comprises a percolate collecting tank, a water pump and a plurality of water inlet and water outlet pipes; the landfilling reactor is internally provided with an acid buffer layer as well as a domestic garbage landfilling layer I and a domestic garbage landfilling layer II which are respectively positioned at the upper part and the lower part of the acid buffer layer, and the acid buffer layer is domestic garbage incineration residue. The equipment increases the humidity of the garbage landfilling body by percolate recharging, utilizes the acid buffer layer formed by the garbage incineration residue to regulate the pH environment in the garbage body, and creates a better living environment for degrading microorganisms of garbage, thus realizing acceleration of the degradation of garbage and accelerating the stabilizing process of the landfilling body. The equipment has low investment cost and remarkable effect.
Description
Technical field
The present invention relates to a kind of consumer waste filling and embedding device, is a kind of biological reaction apparatus that can quicken consumer waste filling and embedding stabilization process specifically.
Background technology
Though compost and incineration technology have obtained certain development, landfill remains the of paramount importance processing mode of domestic refuse, and the domestic refuse of China about 90% is to handle with land-fill method.In the starting stage of landfill yard operation, the organism in the domestic refuse is degraded gradually, has generated lot of organic acids.The sour environment of organic acid accumulation formation landfill yard has suppressed the microorganism active in the landfill yard, has influenced the degraded of domestic refuse and the stabilization process of landfill yard.
The resistates that produces behind the consumer waste incineration is a kind of refuse that contains the calcic class material of high density, has stronger sour surge capability.The sour buffer layer that is made of the consumer waste incineration resistates is set in household refuse landfill sites, not only can overcome the landfill yard sour environment of operation starting stage, reduce the influence of sour environment to the landfill yard microorganism, and can improve the degradation speed of domestic refuse, thereby accelerate the stabilization process of refuse landfill.This method is simple to operate, and processing cost is lower.
In existing research and the report, the still rarely seen method of utilizing the consumer waste incineration resistates to accelerate refuse landfill stabilization process as sour buffer layer.
Summary of the invention
The invention provides a kind of consumer waste filling and embedding reaction unit that can accelerate refuse landfill stabilization process, this device provides better p H environment for the microbiological deterioration domestic refuse, accelerates the stabilization process of landfill yard.
A kind of biological reaction apparatus that can quicken consumer waste filling and embedding stabilization process comprises leachate recirculation system and landfill reactor, and described leachate recirculation system comprises the leachate collection pond, water pump and some water inlets and water-drainage tube part.
Described landfill reactor comprises sour buffer layer and lays respectively at upper and lower consumer waste filling and embedding layer I of sour buffer layer and consumer waste filling and embedding layer II that described sour buffer layer is the consumer waste incineration resistates.The thickness of described sour buffer layer is 1: 4～6 with the total thickness ratio of two consumer waste filling and embedding layers.
Described sour buffer layer can be laid drainage type geotextile up and down, guarantees the structural stability of sour buffer layer.
As a kind of preferred, above described consumer waste filling and embedding layer II, be provided with the fine sand tectum, percolate uniform distribution of being convenient to recharge and the anaerobic environment that guarantees the landfill body.
The top of described landfill reactor also is provided with air chamber, and air chamber is positioned at fine sand tectum top, and what be convenient to landfill gas falls to arrange a mouthful discharge from gas.
The bottom of described landfill reactor is provided with metalling, and described metalling is that particle diameter is the gravel of 10-40mm, is convenient to the discharging and the collection of percolate.
The thickness of described fine sand tectum and metalling is 5～10cm.
The top of described landfill reactor is provided with percolate water-in and gas guide mouth.
When apparatus of the present invention are used, lay metalling at reactor bottom, consumer waste filling and embedding layer I inserted in the metalling top, and constantly compacting, reaches the requirement of the effective landfill height of reactor up to thickness.Consumer waste filling and embedding layer I lays sour buffer layer in the top, and constantly compacting makes its thickness reach the requirement of the effective landfill height of reactor.Acid buffer layer top is inserted domestic refuse once more, and constantly compacting, reaches the requirement of the effective landfill height of reactor up to consumer waste filling and embedding layer II.Then, sealed reactor after laying the fine sand layer above the consumer waste filling and embedding layer II.When operation device enters percolate in the leachate collection pond by valve, treats that leachate collection finishes, the be correlated with mensuration of physical and chemical index of the percolate sample that takes a morsel, investigation biological reaction apparatus running condition.Remaining percolate adopts water pump to recharge to landfill reactor.
The present invention is provided with sour buffer layer on the basis of recharging type landfill biological reaction apparatus, not only can increase the water ratio of rubbish body, improve microbic activity, and can utilize in the calcic class material in the sour buffer layer and the acidic substance in the landfill yard initial operating stage percolate, the acid of alleviating the landfill yard initial operating stage suppresses phenomenon, improve better p H environment for microorganism, accelerate the degraded of rubbish, quicken consumer waste filling and embedding stabilization process.
Description of drawings
The structural representation of Fig. 1 apparatus of the present invention.
Drawing reference numeral is described as follows: the 1-housing; The 2-metalling; 3-consumer waste filling and embedding layer I; 4-acid buffer layer; 5-consumer waste filling and embedding layer II; 6-fine sand tectum; The 7-air chamber; 8-percolate water-in; 9-gas guide mouth; The 10-water pump; 11-leachate collection pond; The 12-percolate discharge guiding pipe; The 13-valve.
Fig. 2 is the refuse landfill of employing apparatus of the present invention and the percolate pH value variation comparison diagram of pure household refuse landfill sites.
Fig. 3 is the refuse landfill of employing apparatus of the present invention and the percolate DOC value variation comparison diagram of pure household refuse landfill sites.
Embodiment
Embodiment 1
A kind of biological reaction apparatus that can quicken consumer waste filling and embedding stabilization process as shown in Figure 1, comprise leachate recirculation system and landfill reactor, described leachate recirculation system comprises water pump 10, leachate collection pond 11, percolate discharge guiding pipe 12 and valve 13, described landfill reactor comprises housing 1, the landfill reactor top is provided with gas guide mouth 9 and percolate water-in 8, and the inside of landfill reactor is provided with fine sand tectum 6, consumer waste filling and embedding layer II 5, sour buffer layer 4, consumer waste filling and embedding layer I 3 and metalling 2 from top to bottom successively.
Before the device operation, lay metalling 2 in the landfill reactor bottom earlier, be convenient to the discharging and the collection of landfill percolate.Consumer waste filling and embedding layer I inserted in metalling 2 tops, and constantly compacting, reaches 40% of the effective landfill height of reactor up to thickness.Consumer waste filling and embedding layer I lays consumer waste incineration resistates (sour buffer layer 4) in the top, and constantly compacting makes its thickness reach 20% of the effective landfill height of reactor.Acid buffer layer 4 tops are inserted domestic refuse once more, and constantly compacting, reach 40% of the effective landfill height of reactor up to consumer waste filling and embedding layer II.Then, above consumer waste filling and embedding layer II, lay fine sand tectum 6 back sealed reactors.Percolate water-in 8 and water pump 10, leachate collection pond 11, leachate collection pond 11 is connected with the landfill reactor bottom by percolate discharge guiding pipe 12, valve 13.
During the device operation, open valve 13 every day, percolate is entered in the leachate collection pond 11 by percolate discharge guiding pipe 12.Treat that leachate collection finishes, the be correlated with mensuration of physical and chemical index of the percolate sample that takes a morsel is investigated biological reaction apparatus running condition.Remaining percolate adopts water pump 10 to recharge to landfill reactor.
Fig. 2 is the refuse landfill of employing apparatus of the present invention and the percolate pH value variation comparison diagram of pure household refuse landfill sites.
As seen from Figure 2, the change procedure of two landfill yard reactor percolate pH is consistent substantially initial 80 days of operation, then presents distinct variation tendency afterwards.The landfill yard that contains consumer waste incineration resistates acid buffer layer, the pH value of its percolate rose to about 7.5 at 150 days after the slow for some time of rising, and kept this level subsequently always.This numerical value is similar to the pH value of sophisticated refuse landfill basically, illustrates that landfill yard has been in comparatively stable status.For pure household refuse landfill sites, the pH value of its percolate is in a process that slowly rises always, and its percolate pH value still maintains about 6.5 after 230 days in operation, reaches the level of ripe refuse landfill far away.
Fig. 3 is the refuse landfill of employing apparatus of the present invention and the percolate DOC value variation comparison diagram of pure household refuse landfill sites.
As seen from Figure 3, the change procedure of two landfill yard reactor percolate DOC and the variation tendency basically identical of pH.Contain that DOC presents comparatively significantly downtrending in the percolate from garbage filling field of consumer waste incineration resistates acid buffer layer after pH is increased to 7.5, move after 230 days, its DOC concentration drops to 2800mg/L and kept stable by the highest 22000mg/L, the DOC value basically identical of this value and ripe refuse landfill.Pure refuse landfill is after operation 230 days, and its DOC concentration still maintains about 20000mg/L, reaches the stabilization level far away.
The variation tendency of comprehensive pH and DOC as can be seen, the refuse landfill operation that contains consumer waste incineration resistates acid buffer layer reached stable status in about 150 days substantially, and pure refuse landfill operation is stable yet after 230 days.This shows, the stabilization process that the sour buffer layer that constitutes with the consumer waste incineration resistates can be accelerated landfill yard significantly is set in the landfill yard, thereby increase the storage capacity of refuse landfill, this is significant for the rare China of land resources.
Claims (9)
1. biological reaction apparatus that quickens consumer waste filling and embedding stabilization process, comprise leachate recirculation system and landfill reactor, described leachate recirculation system comprises leachate collection pond, water pump and some water inlets and water-drainage tube part, it is characterized in that: be provided with sour buffer layer in the described landfill reactor and lay respectively at upper and lower consumer waste filling and embedding layer I of sour buffer layer and consumer waste filling and embedding layer II; Described sour buffer layer is the consumer waste incineration resistates.
2. biological reaction apparatus as claimed in claim 1 is characterized in that: the thickness of described sour buffer layer is 1: 4～6 with the total thickness ratio of two consumer waste filling and embedding layers.
3. biological reaction apparatus as claimed in claim 2 is characterized in that: the thickness of described sour buffer layer is 1: 4 with the total thickness ratio of two consumer waste filling and embedding layers.
4. biological reaction apparatus as claimed in claim 1 is characterized in that: described sour buffer layer two-berth is provided with drainage type geotextile.
5. biological reaction apparatus as claimed in claim 1 is characterized in that: the top of described consumer waste filling and embedding layer II is provided with the fine sand tectum.
6. biological reaction apparatus as claimed in claim 5 is characterized in that: the tectal thickness of described fine sand is 5～10cm.
7. biological reaction apparatus as claimed in claim 1 is characterized in that: described landfill reactor bottom is provided with metalling, and described metalling is that particle diameter is the gravel of 10～40mm.
8. biological reaction apparatus as claimed in claim 7 is characterized in that: the thickness of described metalling is 5～10cm.
9. biological reaction apparatus as claimed in claim 1 is characterized in that: the top of described landfill reactor is provided with air chamber.
Priority Applications (1)
| Application Number | Priority Date | Filing Date | Title |
|---|---|---|---|
| CN2011100524357A CN102219568B (en) | 2011-03-04 | 2011-03-04 | Biological reaction equipment for accelerating domestic garbage landfilling stabilization process |
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| Application Number | Priority Date | Filing Date | Title |
|---|---|---|---|
| CN2011100524357A CN102219568B (en) | 2011-03-04 | 2011-03-04 | Biological reaction equipment for accelerating domestic garbage landfilling stabilization process |
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| Publication Number | Publication Date |
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| CN102219568A true CN102219568A (en) | 2011-10-19 |
| CN102219568B CN102219568B (en) | 2013-08-07 |
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| Application Number | Title | Priority Date | Filing Date |
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| CN2011100524357A Expired - Fee Related CN102219568B (en) | 2011-03-04 | 2011-03-04 | Biological reaction equipment for accelerating domestic garbage landfilling stabilization process |
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Cited By (3)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| CN105127174A (en) * | 2015-10-20 | 2015-12-09 | 南京大学 | Circulating sustainable domestic waste landfill site and treatment method thereof |
| CN107032503A (en) * | 2016-11-18 | 2017-08-11 | 陕西科技大学 | A kind of biological respinse wall for handling percolate and its application |
| CN110180858A (en) * | 2019-05-29 | 2019-08-30 | 台州学院 | A kind of processing method and processing device accelerating refuse landfill rubbish mineralising based on impulse electric field |
Citations (3)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| CN1085138A (en) * | 1993-10-04 | 1994-04-13 | 四川省成都洁世固体废物综合利用研究所 | The municipal refuse comprehensive utilization technique |
| CN1116971A (en) * | 1995-06-13 | 1996-02-21 | 绵阳城市垃圾无害化综合处理厂 | Municipal refuse treatment method and equipment |
| CN202030674U (en) * | 2011-03-04 | 2011-11-09 | 浙江工商大学 | Biological reaction unit for quickening domestic garbage landfilling stabilization process |
-
2011
- 2011-03-04 CN CN2011100524357A patent/CN102219568B/en not_active Expired - Fee Related
Patent Citations (3)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| CN1085138A (en) * | 1993-10-04 | 1994-04-13 | 四川省成都洁世固体废物综合利用研究所 | The municipal refuse comprehensive utilization technique |
| CN1116971A (en) * | 1995-06-13 | 1996-02-21 | 绵阳城市垃圾无害化综合处理厂 | Municipal refuse treatment method and equipment |
| CN202030674U (en) * | 2011-03-04 | 2011-11-09 | 浙江工商大学 | Biological reaction unit for quickening domestic garbage landfilling stabilization process |
Non-Patent Citations (4)
| Title |
|---|
| 《Journal of Hazardous Materials》 20080618 H.M.Lo, et al. "Biostabilization assessment of MSW co-disposed with MSWI fly ash in anaerobic bioreactors" 第1233－1242页 1－9 , 第162期 * |
| 《应用生态学报》 20060331 何若等 "生物反应器填埋场***渗滤液的脱氮性能" 第520－524页 1－9 第17卷, 第3期 * |
| H.M.LO, ET AL.: ""Biostabilization assessment of MSW co-disposed with MSWI fly ash in anaerobic bioreactors"", 《JOURNAL OF HAZARDOUS MATERIALS》 * |
| 何若等: ""生物反应器填埋场***渗滤液的脱氮性能"", 《应用生态学报》 * |
Cited By (3)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| CN105127174A (en) * | 2015-10-20 | 2015-12-09 | 南京大学 | Circulating sustainable domestic waste landfill site and treatment method thereof |
| CN107032503A (en) * | 2016-11-18 | 2017-08-11 | 陕西科技大学 | A kind of biological respinse wall for handling percolate and its application |
| CN110180858A (en) * | 2019-05-29 | 2019-08-30 | 台州学院 | A kind of processing method and processing device accelerating refuse landfill rubbish mineralising based on impulse electric field |
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| Publication number | Publication date |
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| CN102219568B (en) | 2013-08-07 |
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