CN204747056U - Pollute processing system of building rubbish - Google Patents
Pollute processing system of building rubbish Download PDFInfo
- Publication number
- CN204747056U CN204747056U CN201520417841.2U CN201520417841U CN204747056U CN 204747056 U CN204747056 U CN 204747056U CN 201520417841 U CN201520417841 U CN 201520417841U CN 204747056 U CN204747056 U CN 204747056U
- Authority
- CN
- China
- Prior art keywords
- pond
- ponds
- conveyer belt
- type conveyer
- heavy
- Prior art date
- Legal status (The legal status is an assumption and is not a legal conclusion. Google has not performed a legal analysis and makes no representation as to the accuracy of the status listed.)
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- 238000005406 washing Methods 0.000 claims abstract description 21
- 238000001914 filtration Methods 0.000 claims abstract description 12
- 239000007788 liquid Substances 0.000 claims abstract description 12
- 239000010802 sludge Substances 0.000 claims abstract description 10
- 239000006228 supernatant Substances 0.000 claims abstract description 10
- 238000003756 stirring Methods 0.000 claims abstract description 9
- 238000011084 recovery Methods 0.000 claims abstract description 7
- 239000002699 waste material Substances 0.000 claims description 30
- 238000004140 cleaning Methods 0.000 claims description 24
- 238000004062 sedimentation Methods 0.000 claims description 14
- 230000001376 precipitating Effects 0.000 claims description 5
- 238000007599 discharging Methods 0.000 abstract 1
- 230000005484 gravity Effects 0.000 abstract 1
- 239000000126 substance Substances 0.000 abstract 1
- 239000002689 soil Substances 0.000 description 17
- 238000000034 method Methods 0.000 description 10
- 239000004094 surface-active agent Substances 0.000 description 10
- 239000012141 concentrate Substances 0.000 description 5
- 238000005516 engineering process Methods 0.000 description 5
- 239000002245 particle Substances 0.000 description 5
- 238000004064 recycling Methods 0.000 description 5
- 238000011010 flushing procedure Methods 0.000 description 3
- 239000000463 material Substances 0.000 description 3
- 230000002572 peristaltic Effects 0.000 description 3
- 239000004575 stone Substances 0.000 description 3
- 230000032258 transport Effects 0.000 description 3
- 239000003673 groundwater Substances 0.000 description 2
- 239000007800 oxidant agent Substances 0.000 description 2
- 230000001590 oxidative Effects 0.000 description 2
- 238000005067 remediation Methods 0.000 description 2
- 238000004642 transportation engineering Methods 0.000 description 2
- 238000010276 construction Methods 0.000 description 1
- 230000000694 effects Effects 0.000 description 1
- 239000003344 environmental pollutant Substances 0.000 description 1
- 239000000284 extract Substances 0.000 description 1
- 238000006062 fragmentation reaction Methods 0.000 description 1
- 239000000203 mixture Substances 0.000 description 1
- 239000005416 organic matter Substances 0.000 description 1
- 230000003534 oscillatory Effects 0.000 description 1
- 231100000719 pollutant Toxicity 0.000 description 1
- 238000000247 postprecipitation Methods 0.000 description 1
- 239000002002 slurry Substances 0.000 description 1
- 239000007921 spray Substances 0.000 description 1
- XLYOFNOQVPJJNP-UHFFFAOYSA-N water Substances O XLYOFNOQVPJJNP-UHFFFAOYSA-N 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
- Y02W—CLIMATE CHANGE MITIGATION TECHNOLOGIES RELATED TO WASTEWATER TREATMENT OR WASTE MANAGEMENT
- Y02W30/00—Technologies for solid waste management
- Y02W30/50—Reuse, recycling or recovery technologies
- Y02W30/58—Construction or demolition [C&D] waste
Abstract
Pollute processing system of building rubbish, including the crushing and screening system, the roller -type conveyer belt, high -pressure rinse -system, mixing system deals with system and washing liquid recovery system including just heavy pond, two mud that sink ponds, be equipped with high -pressure rinse -system above the roller -type conveyer belt, high -pressure rinse -system connection washing liquid chemicals tank, roller -type conveyer belt below is equipped with the reaction, and the reaction connects just heavy pond, two heavy ponds through the pipeline in proper order, and the settled sludge in the two heavy ponds carries to plate and frame filter press, plate and frame filter press's filter -pressing liquid and the supernatant management way in the two heavy ponds are connected to recovery filtration system, the reaction is equipped with mixing system. The building rubbish that sees through the grid stirs in the reaction, and stirring back mud gets into the first pond that sinks by the pipeline, just sinking and accomplishing gravity in the pond and deposit the mud that the contains little rubble natural mummification in back of discharging, the supernatant gets into two and sinks ponds, and two settled sludge that sink in the ponds carry to plate and frame filter press, filter -pressing liquid and two sink and retrieve filtration system in the ponds.
Description
Technical field
The utility model relates to the process of solid-state castoff, especially pollutes the treatment system of building waste.
Background technology
Contaminated site showering (ex-situremediation) technology refers to be excavated by contaminated soil or underground water from the position occurring to pollute or extracts, and carries out the technology of administering after transport again.Implementing contaminated site, in showering process, not only to need to administer contaminated soil and groundwater, also need the building waste to adhering to contaminated soil to clean simultaneously.At present, for the building waste adhering to contaminated soil, main employing is manually carried out sorting and cleaning, and wastes time and energy.
In organic polluted soil and groundwater remediation, oxidant and be widely used with surfactant enhanced remediation technology but, can produce a large amount of surfactant wash liquid containing organic pollution in soil washing repair process, directly discharge may cause secondary pollution to environment.Exploiting economy, Surfactant cleaning solution recycling efficiently, remove the organic matter in cleaning solution, and realize the recovery and reuse technology of surfactant, the secondary pollution of discarded cleaning solution, the simultaneously recycling of surfactant not only can be avoided also effectively can to reduce rehabilitation cost.
Repair on-the-spot operating efficiency and the recycling of surfactant to improve, this is designed a set of screening flushing integration apparatus and replaces manually completing the sorting to contaminated building waste and cleaning.
Summary of the invention
The utility model object is, proposes a kind for the treatment of system polluting building waste.More reasonable structure is reliable, and the secondary pollution of discarded cleaning solution, the simultaneously recycling of surfactant not only can be avoided also effectively can to reduce rehabilitation cost.
The technical solution of the utility model is, pollutes the treatment system of building waste, comprises pulverizing-screening system, roller type conveyer belt, high-pressure washing system, stirring system, comprises preliminary sedimentation tank, the sludge treatment system of second pond and cleaning solution recovery system; High-pressure washing system is provided with above roller type conveyer belt, high-pressure washing system connects cleaning solution pharmacy jar, be provided with reactive tank below roller type conveyer belt, reactive tank connects preliminary sedimentation tank, second pond successively by pipeline, and the precipitating sludge in second pond is delivered to plate and frame type filter-press; Supernatant in the pressing filtering liquid of plate and frame type filter-press and second pond is connected to recovery filtration system through pipeline; Reactive tank is provided with stirring system.
Contaminated building waste is by after pulverizing-screening system, the building waste of Screening Network top greater particle size is to roller band, high-pressure washing system is provided with above roller type conveyer belt, high-pressure washing system connects cleaning solution pharmacy jar, topple over after staying the building waste high pressure washing above roller band to concentrate and stack, be provided with scrub raffinate accumulator tank below roller type conveyer belt, scrub raffinate enters preliminary sedimentation tank by pipeline; Through Screening Network comparatively small particle diameter building waste by conveyer belt, enter grid, after staying the building waste high pressure washing above grid, topple over concentrate stack, the building waste through grid stirs in reactive tank, stir after mud enter preliminary sedimentation tank by pipeline; Complete gravitational settling in preliminary sedimentation tank and discharge rear natural mummification containing the mud of small crushed stone, supernatant enters second pond, and the precipitating sludge in second pond is delivered to plate and frame type filter-press, completes disposal.Supernatant in pressing filtering liquid and second pond reclaims filtration system through pipeline to cleaning solution, pumps in cleaning solution pharmacy jar and re-use after process.
The utility model beneficial effect: the application of cleaning solution pharmacy jar, high-pressure washing system and post precipitation pond, by peristaltic pump, plate and frame type filter-press and cleaning solution are delivered to bottom thickened sludge reclaim supporting the use of the series of processes devices such as filter and avoid the secondary pollution of discarded cleaning solution, the simultaneously recycling of surfactant also effectively can reduce rehabilitation cost.The utility model is a kind of mechanical structure, has higher efficiency and disposal ability, is applicable to process various pollution building waste (comprising contaminated soil) on a large scale.
Accompanying drawing explanation
Fig. 1 is the utility model structural representation.
Detailed description of the invention
See Fig. 1, wherein: 1. building waste (contaminated soil) breaker, 2. building waste (contaminated soil) screening plant, 3. conveyer belt, 4. cleaning solution pharmacy jar, 5. high-pressure washing system, 6. roller type conveyer belt, 7. scrub raffinate accumulator tank, 8. grid, 9. stirring system, 10. reactive tank, 11. preliminary sedimentation tanks, 12. second ponds, 13. plate and frame type filter-presses, 14. cleaning solutions reclaim filter.
The construction waste crushing device (employing disintegrating machine) that the utility model connects successively, conveyer belt are to building waste screening plant (adopting oscillatory type screening plant); Conveyer belt will need material to be processed (building waste of Screening Network top greater particle size) to be sent to roller type conveyer belt again; And be provided with high-pressure washing system above roller type conveyer belt, high-pressure washing system connects the liquid (oxidant adds surfactant) that cleaning solution pharmacy jar provides, material above roller type conveyer belt becomes normal material after removing pollutant, after cleaning solution washing, mixture flows out to below from roller gap and is provided with scrub raffinate accumulator tank and reactive tank, and scrub raffinate accumulator tank connects preliminary sedimentation tank by pipeline; By the comparatively small particle diameter of Screening Network by conveyer belt to grid, after staying the building waste high pressure washing above grid, topple over to concentrate and stack; Building waste through grid fully stirs in reactive tank, by pipeline to preliminary sedimentation tank; In preliminary sedimentation tank, complete gravitational settling discharge rear natural mummification containing the mud of small crushed stone, supernatant enters second pond.Precipitating sludge in second pond transports to plate and frame type filter-press by peristaltic pump, completes disposal.Supernatant in pressing filtering liquid and second pond reclaims filtration system through conveyance conduit to cleaning solution, pumps in cleaning solution pharmacy jar 4 and re-use after process.
The course of work of the present utility model:
(1) contaminated building waste (contaminated soil) short transportation by lighter is transported to screening flushing integration apparatus stockyard to keep in, and properly protect;
(2) contaminated building waste (contaminated soil) is dropped into crushing and screening integration apparatus 12, after fragmentation and screening (aperture is 20mm), be greater than 20mm building waste (contaminated soil) through conveyer belt 3, be sent to roller type conveyer belt 6, building waste (contaminated soil) (together with the contaminated soil) that be less than 20mm enters grid 8 through conveyer belt 3;
(3) diameter is greater than the building waste (contaminated soil) of 20mm on roller type conveyer belt 6, slow rolls forward, carries out spray process through high-pressure washing system 5, concentrates and stack after standard discharge.The scrub raffinate collected in scrub raffinate accumulator tank 7, enters preliminary sedimentation tank 11 by conveyance conduit;
(4) diameter is less than the building waste (contaminated soil) of 20mm through conveyer belt 3, enter grid 8 (grid gap is 10mm), grid is provided with high-pressure washing system 5, be greater than 10mm particle to be rinsed totally, topple over and discharge and concentrate stacking, the building waste (together with contaminated soil) and the surfactant flushing liquid that are less than 10mm enter in reactive tank 10 through grid, are fully stirred in reactive tank by stirring system 9; Mud after abundant stir process
Be delivered to preliminary sedimentation tank 11 through reactive tank slurry transportation pipeline, carry out gravitational settling;
(5) in preliminary sedimentation tank, complete gravitational settling get rid of rear natural mummification containing the mud of small crushed stone, supernatant enters second pond 12, and the precipitating sludge in second pond transports to plate and frame type filter-press 13 by peristaltic pump, completes final disposal;
(6) supernatant in the pressing filtering liquid that produces of plate and frame type filter-press 13 and second pond reclaims filtration system through conveyance conduit to cleaning solution, and process pumps in pharmacy jar 4 and re-starts utilization after reclaiming.
Claims (1)
1. pollute the treatment system of building waste, it is characterized in that comprising pulverizing-screening system, roller type conveyer belt, high-pressure washing system, stirring system, comprise preliminary sedimentation tank, the sludge treatment system of second pond and cleaning solution recovery system; High-pressure washing system is provided with above roller type conveyer belt, high-pressure washing system connects cleaning solution pharmacy jar, be provided with reactive tank below roller type conveyer belt, reactive tank connects preliminary sedimentation tank, second pond successively by pipeline, and the precipitating sludge in second pond is delivered to plate and frame type filter-press; Supernatant in the pressing filtering liquid of plate and frame type filter-press and second pond is connected to recovery filtration system through pipeline; Reactive tank is provided with stirring system.
Priority Applications (1)
| Application Number | Priority Date | Filing Date | Title |
|---|---|---|---|
| CN201520417841.2U CN204747056U (en) | 2015-06-16 | 2015-06-16 | Pollute processing system of building rubbish |
Applications Claiming Priority (1)
| Application Number | Priority Date | Filing Date | Title |
|---|---|---|---|
| CN201520417841.2U CN204747056U (en) | 2015-06-16 | 2015-06-16 | Pollute processing system of building rubbish |
Publications (1)
| Publication Number | Publication Date |
|---|---|
| CN204747056U true CN204747056U (en) | 2015-11-11 |
Family
ID=54461812
Family Applications (1)
| Application Number | Title | Priority Date | Filing Date |
|---|---|---|---|
| CN201520417841.2U Active CN204747056U (en) | 2015-06-16 | 2015-06-16 | Pollute processing system of building rubbish |
Country Status (1)
| Country | Link |
|---|---|
| CN (1) | CN204747056U (en) |
Cited By (3)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| CN106391682A (en) * | 2016-10-28 | 2017-02-15 | 大连德联投资控股有限公司 | Soil organic remediation system for city environmental sanitation refuse landfills and working method of soil organic remediation system |
| CN109133312A (en) * | 2017-06-15 | 2019-01-04 | 湖北省宏源药业科技股份有限公司 | It is a kind of to carbonate continuous neutralization reaction device and its reaction process |
| CN110038893A (en) * | 2019-05-31 | 2019-07-23 | 丁乙飞 | A kind of circulating photocatalysis soil repair system and its restorative procedure |
-
2015
- 2015-06-16 CN CN201520417841.2U patent/CN204747056U/en active Active
Cited By (5)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| CN106391682A (en) * | 2016-10-28 | 2017-02-15 | 大连德联投资控股有限公司 | Soil organic remediation system for city environmental sanitation refuse landfills and working method of soil organic remediation system |
| CN106391682B (en) * | 2016-10-28 | 2022-03-15 | 大连德联投资控股有限公司 | Soil organic remediation system for urban sanitation refuse landfill and working method thereof |
| CN109133312A (en) * | 2017-06-15 | 2019-01-04 | 湖北省宏源药业科技股份有限公司 | It is a kind of to carbonate continuous neutralization reaction device and its reaction process |
| CN110038893A (en) * | 2019-05-31 | 2019-07-23 | 丁乙飞 | A kind of circulating photocatalysis soil repair system and its restorative procedure |
| CN110038893B (en) * | 2019-05-31 | 2021-11-30 | 广州市番禺环境科学研究所有限公司 | Circulating type photocatalytic soil remediation system and remediation method thereof |
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Legal Events
| Date | Code | Title | Description |
|---|---|---|---|
| C14 | Grant of patent or utility model | ||
| GR01 | Patent grant |