CN110340124A - A kind of contaminated soil remediation governing system - Google Patents
A kind of contaminated soil remediation governing system Download PDFInfo
- Publication number
- CN110340124A CN110340124A CN201910640659.6A CN201910640659A CN110340124A CN 110340124 A CN110340124 A CN 110340124A CN 201910640659 A CN201910640659 A CN 201910640659A CN 110340124 A CN110340124 A CN 110340124A
- Authority
- CN
- China
- Prior art keywords
- soil
- leacheate
- flocculation
- setting pot
- level
- 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.)
- Pending
Links
Classifications
-
- B—PERFORMING OPERATIONS; TRANSPORTING
- B09—DISPOSAL OF SOLID WASTE; RECLAMATION OF CONTAMINATED SOIL
- B09C—RECLAMATION OF CONTAMINATED SOIL
- B09C1/00—Reclamation of contaminated soil
- B09C1/02—Extraction using liquids, e.g. washing, leaching, flotation
-
- C—CHEMISTRY; METALLURGY
- C02—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F11/00—Treatment of sludge; Devices therefor
- C02F11/12—Treatment of sludge; Devices therefor by de-watering, drying or thickening
-
- C—CHEMISTRY; METALLURGY
- C02—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F9/00—Multistage treatment of water, waste water or sewage
-
- C—CHEMISTRY; METALLURGY
- C02—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F1/00—Treatment of water, waste water, or sewage
- C02F1/001—Processes for the treatment of water whereby the filtration technique is of importance
- C02F1/002—Processes for the treatment of water whereby the filtration technique is of importance using small portable filters for producing potable water, e.g. personal travel or emergency equipment, survival kits, combat gear
-
- C—CHEMISTRY; METALLURGY
- C02—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F1/00—Treatment of water, waste water, or sewage
- C02F1/38—Treatment of water, waste water, or sewage by centrifugal separation
-
- C—CHEMISTRY; METALLURGY
- C02—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F1/00—Treatment of water, waste water, or sewage
- C02F1/52—Treatment of water, waste water, or sewage by flocculation or precipitation of suspended impurities
Landscapes
- Life Sciences & Earth Sciences (AREA)
- Engineering & Computer Science (AREA)
- Environmental & Geological Engineering (AREA)
- Hydrology & Water Resources (AREA)
- Water Supply & Treatment (AREA)
- Chemical & Material Sciences (AREA)
- Organic Chemistry (AREA)
- Soil Sciences (AREA)
- Processing Of Solid Wastes (AREA)
Abstract
The invention discloses a kind of contaminated soil remediation governing systems, including sequentially connected cutting agency, material screening machine structure, elution mechanism, sorting mechanism, cyclonic separation mechanism, rabbling mechanism, flocculation setting pot and dewatering device.The present invention is handled by the physical method of the vibration screening to contaminated soil, so that contaminated soil is fragmented, guarantee that subsequent elution is abundant, roller leaching machine applies leacheate into contaminated soil, it is set to roll composite pollution soil, compared with existing penetration mode, not only sufficiently with pollutant therein interaction, and also it is high-efficient;Pollutant is transferred in leacheate by leacheate, then the liquid for including pollutant is extracted from soil media again, it is separated by solid-liquid separation, so as to heavier sandy soil or heavy metal etc. in cyclonic separation sewage, soil mixing without heavy pollutant obtains sludge after carrying out flocculation sand setting, obtains stabilization processes soil through dehydration and drying and stabilization processes.
Description
Technical field
The present invention relates to the present invention relates to soil protection technical fields, and in particular to a kind of contaminated soil elution repairing and treating
System.
Background technique
Soil leaching refers to and injects or penetrate into flushing liquor in the soil, it is made to flow through the soil layer that need to be administered, parses in soil
Pollutant, then to the flushing liquor containing pollutant carry out processing and reuse process.Leacheate can be water, chemical solvent or
Other fluids that pollutant may be eluted from soil.The absorption-of the changeable soil of the injection of leacheate and pollutant is de-
Attached characteristic, oxidation-reduction potential, interfacial tension, pH value and distribution, dissolution, precipitated form etc., to increase the molten of pollutant
Xie Du makes it form lotion with solution or chemically react, pollutant in soil is promoted to remove.The soil texture, pollution species
Type and occurrence status have a major impact the effect of Soil leaching.Soil douching technique can be used for radioactive substance, organic matter, again
The processing or pre-treatment of metal or other inorganic matter contaminated soils, the pollutant in gravel, sand, fine sand and similar soil more hold
Easily it is leached out, and the then more difficult elution of the pollutant in clay.Soil is rinsed there are many way of realization, including in-situ immobilization and
Showering.
The mechanism of soil fixing metal can be divided into two major classes: first is that being adsorbed on the surface of soil constitution with ionic state;Second is that
Form the precipitating of metallic compound.Its principle of Soil leaching is acted on the heavy metal in reagent and solid phase of soil, is formed molten
The heavy metal ion or metal complex of solution property, then rush pollutant to outside root layer with clear water, recycle containing certain coordination
The compound shower soil of body, is allowed to form more stable complex compound with heavy metal ion;Or with the solution with anion, such as
Carbonate, phosphate rinse soil, and heavy metal is made to form compound precipitation.The key problem in technology of this method is to find one kind to mention
The heavy metal of various forms is taken, and does not destroy the leacheate of soil texture.Currently, the leacheate for washed off soil is more, packet
Include organic or inorganic acid, alkali, salt and chelating agent.Blaylock etc. examines citric acid, malic acid, acetic acid, EDTA, DTPA to print
Spend the effect that leaf mustard absorbs Cd and Pb.Wu Longhua research discovery EDTA can obviously reduce soil to the absorptivity of copper, absorptivity with
Desorption efficiency and the logarithm of the EDTA amount of addition are in significant negatively correlated.Soil leaching, which is eluted or accumulated with column, elutes more practical and warp
Ji suitable for the soil remediation of the small pollution weight of area, but also easily causes secondary pollution, leads to the leaching loss of certain nutrients and sinks
It forms sediment, destroys soil microaggregate structure, while being easy to cause underground water pollution.
Current Soil leaching device mode is simply extensive, and leacheate is directly sprayed to the mode of Soil leaching, these are repaired
Multiple liquid or water profound can not enter inside soil, therefore the efficiency eluted is lower, and repairing effect is poor, water resource waste
Seriously, secondary pollution is caused without processing after pollutant in leacheate absorption soil.
Summary of the invention
In view of the deficiencies of the prior art, the present invention provide it is a kind of elution sufficiently, repairing effect is good, leacheate processing after clear liquid
The Soil leaching repair system recycled.
To achieve the goals above, the technical solution adopted by the present invention is as follows:
A kind of contaminated soil remediation governing system, including sequentially connected cutting agency, material screening machine structure, elution mechanism, sorting machine
Structure, cyclonic separation mechanism, rabbling mechanism, flocculation setting pot and dewatering device;
Contaminated soil in cutting agency is sieved into soil particle by material screening machine structure, and soil particle is sprayed in elution mechanism
Leacheate, the pollutant in soil are transferred in leacheate, and the soil for mixing leacheate enters sorting mechanism and sorted, point
Selecting mechanism will include that the leacheate of pollutant is extracted from soil media, and the leacheate containing pollutant enters eddy flow
Separating mechanism, cyclonic separation mechanism accelerate the soil sand fallout contained in leacheate, and sandy soil are deposited to cyclonic separation mechanism bottom
Portion is discharged, and bumpy flow enters after cyclonic separation mechanism is discharged from top to rabbling mechanism on the leacheate containing pollutant, passes through
Flocculation setting pot is entered after stirring, flocculant is added in flocculation setting pot, after the pollutant in leacheate carries out flocculation sand setting, wadding
The floccule body of retrogradation sand bottom of pond portion enters dewatering device and is dehydrated, the leacheate utilized again.
Further, the cutting agency is soil hopper, and the upper port of the soil hopper is contaminated soil inlet port;
The material screening machine structure is vibrating screen, and the import of the vibrating screen is connected with the outlet of the lower end of soil hopper;
Contaminated soil screens out the substances such as internal gravel through shaker vibration, and the outlet of self-excited oscillation sieve discharges to the first conveyer belt
On, contaminated soil is sent to elution mechanism through the first conveyer belt, and the elution mechanism is roller leaching machine.
Further, the mixture of soil and leacheate is discharged on the second conveyer belt from roller leaching machine, the mixture
It is sent to sorting mechanism through the second conveyer belt, the sorting mechanism is rolling-drum separator, the mixture process of soil and leacheate
Rolling-drum separator is separated by solid-liquid separation, and soil is gone out the discharge port discharge of rolling-drum separator, and the leacheate containing pollutant is through rolling
The liquid outlet of cylinder sorting machine is connected to cyclonic separation mechanism, and the cyclonic separation mechanism is hydrocyclone.
Further, the hydrocyclone is second cyclone, and the bottom of the hydrocyclone offers sandy soil and goes out
Mouthful, the top of cyclone is rotary fluid outlet, and the top rotary fluid outlet confluence of second cyclone enters rabbling mechanism.
Further, the rabbling mechanism is mixing agitator, is offered on the mixing agitator and second cyclone
Top rotary fluid export the inlet that communicates, the mixing agitator offers liquid outlet, the leacheate containing pollutant from
Liquid outlet discharge.
Further, the soil and rotary fluid that the rolling-drum separator sub-elects are mixed into mixing and blending machine, through stirring
Enter flocculation setting pot after mixing uniformly.
Further, the flocculation setting pot includes that level-one flocculation setting pot, second level flocculation setting pot and three-level flocculation are heavy
Sand pond;The import of connection mixing agitator liquid outlet is offered on the level-one flocculation setting pot, mixture enters one from import
Grade flocculation setting pot;Treatment fluid after level-one flocculates sand setting branches to second level flocculation by level-one flocculation setting pot upper end and sinks
Sand pond and three-level flocculation setting pot, the bottom of level-one flocculation setting pot, second level flocculation setting pot and three-level flocculation setting pot are opened
It is exported equipped with flocculate precipitate, three flocculate precipitate export pipelines are flowed to and are connected to dewatering device afterwards together.
Further, the second level flocculation setting pot and the clear liquid on three-level flocculation setting pot upper layer pass through two stage treatment unit
Roller leaching machine water supply pipe is flowed back into after processing.
Further, flocculate precipitate carries out sludge stabilization treatment after dehydration and drying, obtains stabilization processes soil
Earth.
Further, the bottom sandy soil outlet connection dehydration and drying tank of the hydrocyclone, it is husky after dehydration and drying
Soil is discharged from lower end, and the moisture and rotary fluid of disengaging converge.
Compared with prior art, obtained by the present invention to have the beneficial effect that:
The present invention has the characteristics of optimization of structure process, land classification high treating effect;The present invention passes through the vibration to contaminated soil
The physical method processing of dynamic screening guarantees subsequent elution sufficiently so that contaminated soil is fragmented, and roller leaching machine is to contaminated soil
Middle application leacheate, make its roll composite pollution soil, compared with existing penetration mode, not only with pollutant phase interaction therein
With abundant and high-efficient;The physics such as the desorption of pollutant in soil, chelating, dissolution or complexing, chemistry are made by leacheate
With, it is finally transferred to pollutant in leacheate, then the liquid for including pollutant is extracted from soil media again,
It is separated by solid-liquid separation, so as to heavier sandy soil or heavy metal etc. in cyclonic separation sewage, then again and without heavy pollutant
Soil mixing carry out flocculation sand setting after obtain sludge, through dehydration and drying and stabilization processes obtain stabilization processes soil.
Detailed description of the invention
Attached drawing 1 is process flow chart of the invention.
Specific embodiment
Below in conjunction with the attached drawing in the embodiment of the present application, technical solutions in the embodiments of the present application carries out clear, complete
Site preparation description, it is clear that described embodiments are only a part of embodiments of the present application, instead of all the embodiments.Below
Description only actually at least one exemplary embodiment be it is illustrative, never as to the application and its application or making
Any restrictions.Based on the embodiment in the application, those of ordinary skill in the art are not making creative work premise
Under every other embodiment obtained, shall fall in the protection scope of this application.
It should be noted that term used herein above is merely to describe specific embodiment, and be not intended to restricted root
According to the illustrative embodiments of the application.As used herein, unless the context clearly indicates otherwise, otherwise singular
Also it is intended to include plural form, additionally, it should be understood that, when in the present specification using term "comprising" and/or " packet
Include " when, indicate existing characteristics, step, operation, device, component and/or their combination.
Unless specifically stated otherwise, positioned opposite, the digital table of the component and step that otherwise illustrate in these embodiments
Up to the unlimited scope of the present application processed of formula and numerical value.Simultaneously, it should be appreciated that for ease of description, each portion shown in attached drawing
The size divided not is to draw according to actual proportionate relationship.For technology, side known to person of ordinary skill in the relevant
Method and equipment may be not discussed in detail, but in the appropriate case, and the technology, method and apparatus should be considered as authorizing explanation
A part of book.In shown here and discussion all examples, any occurrence should be construed as merely illustratively, and
Not by way of limitation.Therefore, the other examples of exemplary embodiment can have different values.It should also be noted that similar label
Similar terms are indicated in following attached drawing with letter, therefore, once it is defined in a certain Xiang Yi attached drawing, then subsequent attached
It does not need that it is further discussed in figure.
In the description of the present application, it is to be understood that the noun of locality such as " front, rear, top, and bottom, left and right ", " laterally, vertical,
Vertically, orientation or positional relationship indicated by level " and " top, bottom " etc. is normally based on orientation or position shown in the drawings and closes
System is merely for convenience of description the application and simplifies description, and in the absence of explanation to the contrary, these nouns of locality do not indicate that
It must have a particular orientation or be constructed and operated in a specific orientation with the device or element for implying signified, therefore cannot manage
Solution is the limitation to the application protection scope;The noun of locality " inside and outside " refers to inside and outside the profile relative to each component itself.
For ease of description, spatially relative term can be used herein, as " ... on ", " ... top ",
" ... upper surface ", " above " etc., for describing such as a device shown in the figure or feature and other devices or spy
The spatial relation of sign.It should be understood that spatially relative term is intended to comprising the orientation in addition to device described in figure
Except different direction in use or operation.For example, being described as if the device in attached drawing is squeezed " in other devices
It will be positioned as " under other devices or construction after part or construction top " or the device of " on other devices or construction "
Side " or " under other devices or construction ".Thus, exemplary term " ... top " may include " ... top " and
" in ... lower section " two kinds of orientation.The device can also be positioned with other different modes and (is rotated by 90 ° or in other orientation), and
And respective explanations are made to the opposite description in space used herein above.
In addition, it should be noted that, limiting components using the words such as " first ", " second ", it is only for be convenient for
Corresponding components are distinguished, do not have Stated otherwise such as, there is no particular meanings for above-mentioned word, therefore should not be understood as to this
Apply for the limitation of protection scope.
As shown in Fig. 1, a kind of contaminated soil remediation governing system, including sequentially connected cutting agency, material screening machine structure,
Elute mechanism, sorting mechanism, cyclonic separation mechanism, rabbling mechanism, flocculation setting pot and dewatering device;
Contaminated soil in cutting agency is sieved into soil particle by material screening machine structure, and soil particle is sprayed in elution mechanism
Leacheate, the pollutant in soil are transferred in leacheate, and the soil for mixing leacheate enters sorting mechanism and sorted, point
Selecting mechanism will include that the leacheate of pollutant is extracted from soil media, and the leacheate containing pollutant enters eddy flow
Separating mechanism, cyclonic separation mechanism accelerate the soil sand fallout contained in leacheate, and sandy soil are deposited to cyclonic separation mechanism bottom
Portion is discharged, and bumpy flow enters after cyclonic separation mechanism is discharged from top to rabbling mechanism on the leacheate containing pollutant, passes through
Flocculation setting pot is entered after stirring, flocculant is added in flocculation setting pot, after the pollutant in leacheate carries out flocculation sand setting, wadding
The floccule body of retrogradation sand bottom of pond portion enters dewatering device and is dehydrated, the leacheate utilized again.
The cutting agency is soil hopper, and the upper port of the soil hopper is contaminated soil inlet port;
The material screening machine structure is vibrating screen, and the import of the vibrating screen is connected with the outlet of the lower end of soil hopper;
Contaminated soil screens out the substances such as internal gravel through shaker vibration, and the outlet of self-excited oscillation sieve discharges to the first conveyer belt
On, contaminated soil is sent to elution mechanism through the first conveyer belt, and the elution mechanism is roller leaching machine.
The mixture of soil and leacheate is discharged on the second conveyer belt from roller leaching machine, and the mixture is through the second transmission
Band is sent to sorting mechanism, and the soil of the roller leaching machine internal chamber wall adherency also enters sorting mechanism after rinsing, and described point
Select mechanism for rolling-drum separator, the mixture of soil and leacheate is separated by solid-liquid separation by rolling-drum separator, and soil is through going out to be rolled
The discharge port discharge of cylinder sorting machine, the leacheate containing pollutant are connected to cyclonic separation mechanism through the liquid outlet of rolling-drum separator,
The cyclonic separation mechanism is hydrocyclone.
The hydrocyclone is second cyclone, and the bottom of the hydrocyclone offers sandy soil outlet, cyclone
Top be rotary fluid outlet, second cyclone top rotary fluid outlet confluence enter rabbling mechanism.The hydrocyclone
Bottom sandy soil outlet connection dehydration and drying tank, by dehydration and drying after sandy soil from lower end be discharged, the moisture and rotary fluid of disengaging
Confluence.
The rabbling mechanism is mixing agitator, and the top eddy flow with second cyclone is offered on the mixing agitator
Liquid exports the inlet communicated, and the mixing agitator offers liquid outlet, and the leacheate containing pollutant is discharged from liquid outlet.
The soil and rotary fluid that the rolling-drum separator sub-elects are mixed into mixing and blending machine, agitated uniformly laggard
Enter the setting pot that flocculates.
The flocculation setting pot includes level-one flocculation setting pot, second level flocculation setting pot and three-level flocculation setting pot;It is described
The import of connection mixing agitator liquid outlet is offered on level-one flocculation setting pot, mixture enters level-one flocculation sand setting from import
Pond;Treatment fluid after level-one flocculates sand setting branches to second level flocculation setting pot and three-level by level-one flocculation setting pot upper end
Flocculate setting pot, and it is heavy that the bottom of level-one flocculation setting pot, second level flocculation setting pot and three-level flocculation setting pot offers flocculation
Starch outlet, three flocculate precipitate export pipelines are flowed to and are connected to dewatering device afterwards together.Second level flocculation setting pot and
The clear liquid on three-level flocculation setting pot upper layer flows back into roller leaching machine water supply pipe, waterpower rotation after two stage treatment cell processing
The water of device and the setting pot that flocculates is flowed by extracting again using recirculated water use is formed, and reduces water resource waste.
Flocculate precipitate carries out sludge stabilization treatment after dehydration and drying, obtains stabilization processes soil.At stablizing
The purpose of reason is exactly the organic substance degraded in sludge, is further reduced sludge moisture content, kills bacterium in sludge sludge, disease
Substance etc., eliminate stink, this be sludge can recycling effective use committed step.The method of sludge stabilizing mainly has heap
Extensive use of chemical fertilizer, drying, anaerobic digestion etc..
The present invention is handled by the physical method of the vibration screening to contaminated soil, so that contaminated soil is fragmented, is guaranteed
Sufficiently, roller leaching machine applies leacheate into contaminated soil for subsequent elution, so that it is rolled composite pollution soil, with existing infiltration
Mode is compared, not only sufficiently with pollutant therein interaction, and also it is high-efficient;By leacheate to pollutant in soil
The physics, chemical action such as desorption, chelating, dissolution or complexing, are finally transferred to pollutant in leacheate, then again including
The liquid of pollutant is extracted from soil media, is separated by solid-liquid separation, so as to heavier sandy soil in cyclonic separation sewage or
Heavy metal etc. then mixes again with the soil without heavy pollutant and obtains sludge after carrying out flocculation sand setting, through dehydrating
Stabilization processes soil is obtained with stabilization processes.
Claims (10)
1. a kind of contaminated soil remediation governing system, it is characterised in that: including sequentially connected cutting agency, material screening machine structure, leaching
Washing machine structure, sorting mechanism, cyclonic separation mechanism, rabbling mechanism, flocculation setting pot and dewatering device;
Contaminated soil in cutting agency is sieved into soil particle by material screening machine structure, and soil particle is sprayed in elution mechanism
Leacheate, the pollutant in soil are transferred in leacheate, and the soil for mixing leacheate enters sorting mechanism and sorted, point
Selecting mechanism will include that the leacheate of pollutant is extracted from soil media, and the leacheate containing pollutant enters eddy flow
Separating mechanism, cyclonic separation mechanism accelerate the soil sand fallout contained in leacheate, and sandy soil are deposited to cyclonic separation mechanism bottom
Portion is discharged, and bumpy flow enters after cyclonic separation mechanism is discharged from top to rabbling mechanism on the leacheate containing pollutant, passes through
Flocculation setting pot is entered after stirring, flocculant is added in flocculation setting pot, after the pollutant in leacheate carries out flocculation sand setting, wadding
The floccule body of retrogradation sand bottom of pond portion enters dewatering device and is dehydrated, the leacheate utilized again.
2. a kind of contaminated soil remediation governing system according to claim 1, it is characterised in that: the cutting agency is soil
Earth hopper, the upper port of the soil hopper are contaminated soil inlet port;
The material screening machine structure is vibrating screen, and the import of the vibrating screen is connected with the outlet of the lower end of soil hopper;
Contaminated soil screens out the substances such as internal gravel through shaker vibration, and the outlet of self-excited oscillation sieve discharges to the first conveyer belt
On, contaminated soil is sent to elution mechanism through the first conveyer belt, and the elution mechanism is roller leaching machine.
3. a kind of contaminated soil remediation governing system according to claim 2, it is characterised in that: soil and leacheate it is mixed
Object is closed to be discharged on the second conveyer belt from roller leaching machine, which is sent to sorting mechanism through the second conveyer belt, and described point
Select mechanism for rolling-drum separator, the mixture of soil and leacheate is separated by solid-liquid separation by rolling-drum separator, and soil is through going out to be rolled
The discharge port discharge of cylinder sorting machine, the leacheate containing pollutant are connected to cyclonic separation mechanism through the liquid outlet of rolling-drum separator,
The cyclonic separation mechanism is hydrocyclone.
4. a kind of contaminated soil remediation governing system according to claim 3, it is characterised in that: the hydrocyclone is
Second cyclone, the bottom of the hydrocyclone offer sandy soil outlet, and the top of cyclone is rotary fluid outlet, second level rotation
The top rotary fluid outlet confluence for flowing device enters rabbling mechanism.
5. a kind of contaminated soil remediation governing system according to claim 4, it is characterised in that: the rabbling mechanism is mixed
Blender is closed, is offered on the mixing agitator and exports the inlet communicated with the top rotary fluid of second cyclone, it is described
Mixing agitator offers liquid outlet, and the leacheate containing pollutant is discharged from liquid outlet.
6. a kind of contaminated soil remediation governing system according to claim 5, it is characterised in that: the rolling-drum separator point
The soil and rotary fluid selected are mixed into mixing and blending machine, agitated uniformly rear into flocculation setting pot.
7. a kind of contaminated soil remediation governing system according to claim 6, it is characterised in that: the flocculation setting pot packet
Include level-one flocculation setting pot, second level flocculation setting pot and three-level flocculation setting pot;The company of offering on the level-one flocculation setting pot
The import of logical mixing agitator liquid outlet, mixture enter level-one flocculation setting pot from import;After level-one flocculates sand setting
Treatment fluid branches to second level flocculation setting pot and three-level flocculation setting pot, level-one flocculation sand setting by level-one flocculation setting pot upper end
The bottom in pond, second level flocculation setting pot and three-level flocculation setting pot offers flocculate precipitate outlet, three flocculate precipitates
Export pipeline is flowed to is connected to dewatering device afterwards together.
8. a kind of contaminated soil remediation governing system according to claim 7, it is characterised in that: the second level flocculation sand setting
The clear liquid on pond and three-level flocculation setting pot upper layer flows back into roller leaching machine water supply pipe after two stage treatment cell processing.
9. a kind of contaminated soil remediation governing system according to claim 7, it is characterised in that: flocculate precipitate is by de-
Sludge stabilization treatment is carried out after water is dry, obtains stabilization processes soil.
10. a kind of contaminated soil remediation governing system according to claim 4, it is characterised in that: the hydrocyclone
Bottom sandy soil outlet connection dehydration and drying tank, by dehydration and drying after sandy soil from lower end be discharged, the moisture and rotary fluid of disengaging
Confluence.
Priority Applications (1)
Application Number | Priority Date | Filing Date | Title |
---|---|---|---|
CN201910640659.6A CN110340124A (en) | 2019-07-16 | 2019-07-16 | A kind of contaminated soil remediation governing system |
Applications Claiming Priority (1)
Application Number | Priority Date | Filing Date | Title |
---|---|---|---|
CN201910640659.6A CN110340124A (en) | 2019-07-16 | 2019-07-16 | A kind of contaminated soil remediation governing system |
Publications (1)
Publication Number | Publication Date |
---|---|
CN110340124A true CN110340124A (en) | 2019-10-18 |
Family
ID=68176518
Family Applications (1)
Application Number | Title | Priority Date | Filing Date |
---|---|---|---|
CN201910640659.6A Pending CN110340124A (en) | 2019-07-16 | 2019-07-16 | A kind of contaminated soil remediation governing system |
Country Status (1)
Country | Link |
---|---|
CN (1) | CN110340124A (en) |
Cited By (7)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
CN110842017A (en) * | 2019-11-27 | 2020-02-28 | 智优株式会社 | Modularized mobile soil leaching system |
CN110877044A (en) * | 2019-11-04 | 2020-03-13 | 衢州学院 | Leaching type soil remediation device |
CN110918637A (en) * | 2019-12-20 | 2020-03-27 | 煜环环境科技有限公司 | Stirring and mixing system and process for soil remediation |
CN111515232A (en) * | 2020-04-09 | 2020-08-11 | 张晨 | Treatment method for organic pollution of soil |
CN111842456A (en) * | 2020-07-28 | 2020-10-30 | 吉林省环境科学研究院 | Novel soil treatment system |
CN112845553A (en) * | 2020-12-28 | 2021-05-28 | 华东理工大学 | Method and device for restoring heavy metal contaminated soil |
CN114273410A (en) * | 2021-10-29 | 2022-04-05 | 郑惠华 | Device and method for repairing industrial heavy metal cadmium contaminated soil |
Citations (5)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
CN103316907A (en) * | 2013-06-07 | 2013-09-25 | 东江环保股份有限公司 | Heavy-metal-polluted site soil leaching remediation method and device |
CN204220613U (en) * | 2014-10-28 | 2015-03-25 | 浙江博世华环保科技有限公司 | A kind of Soil leaching equipment |
CN204620627U (en) * | 2015-03-18 | 2015-09-09 | 江苏盖亚环境工程有限公司 | A kind of soil heterotopic elution circuit |
JP2015171709A (en) * | 2014-02-24 | 2015-10-01 | 清水建設株式会社 | Arsenic-contaminated soil washing method |
CN207343444U (en) * | 2017-03-23 | 2018-05-11 | 湖北保灵华环保科技有限公司 | A kind of heavy-metal contaminated soil elutes repair system |
-
2019
- 2019-07-16 CN CN201910640659.6A patent/CN110340124A/en active Pending
Patent Citations (5)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
CN103316907A (en) * | 2013-06-07 | 2013-09-25 | 东江环保股份有限公司 | Heavy-metal-polluted site soil leaching remediation method and device |
JP2015171709A (en) * | 2014-02-24 | 2015-10-01 | 清水建設株式会社 | Arsenic-contaminated soil washing method |
CN204220613U (en) * | 2014-10-28 | 2015-03-25 | 浙江博世华环保科技有限公司 | A kind of Soil leaching equipment |
CN204620627U (en) * | 2015-03-18 | 2015-09-09 | 江苏盖亚环境工程有限公司 | A kind of soil heterotopic elution circuit |
CN207343444U (en) * | 2017-03-23 | 2018-05-11 | 湖北保灵华环保科技有限公司 | A kind of heavy-metal contaminated soil elutes repair system |
Non-Patent Citations (1)
Title |
---|
温泉 等: "《水土修复技术》", 31 October 2017, 吉林大学出版社 * |
Cited By (7)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
CN110877044A (en) * | 2019-11-04 | 2020-03-13 | 衢州学院 | Leaching type soil remediation device |
CN110842017A (en) * | 2019-11-27 | 2020-02-28 | 智优株式会社 | Modularized mobile soil leaching system |
CN110918637A (en) * | 2019-12-20 | 2020-03-27 | 煜环环境科技有限公司 | Stirring and mixing system and process for soil remediation |
CN111515232A (en) * | 2020-04-09 | 2020-08-11 | 张晨 | Treatment method for organic pollution of soil |
CN111842456A (en) * | 2020-07-28 | 2020-10-30 | 吉林省环境科学研究院 | Novel soil treatment system |
CN112845553A (en) * | 2020-12-28 | 2021-05-28 | 华东理工大学 | Method and device for restoring heavy metal contaminated soil |
CN114273410A (en) * | 2021-10-29 | 2022-04-05 | 郑惠华 | Device and method for repairing industrial heavy metal cadmium contaminated soil |
Similar Documents
Publication | Publication Date | Title |
---|---|---|
CN110340124A (en) | A kind of contaminated soil remediation governing system | |
CN105057340B (en) | A kind of chromium-polluted soil dystopy elution renovation technique and its device | |
CN104843955B (en) | A kind of oilfield drilling mud garbage is with brill processing system and processing method | |
CN104874599A (en) | Soil ex-situ leaching system and method thereof | |
CN104525556B (en) | Movable device and movable method for leaching composite polluted soil | |
CN109013683B (en) | A kind of soil restoring device by heavy-metal contaminated soil | |
CN105268737A (en) | Heavy metal contaminated soil remediation equipment and remediation process thereof | |
CN104889150A (en) | Technology for chemical leaching remediation of heavy metal polluted soil | |
CN106077060A (en) | A kind of heavy-metal contaminated soil processing means and process technique thereof | |
CN106391685A (en) | Ex-situ sorting, cleaning and repairing device for chromium-polluted soil and cleaning and repairing technology using ex-situ sorting, cleaning and repairing device | |
CN105750316A (en) | Method for washing and remedying soil at different positions in engineering multi-level sieving manner | |
CN109940034A (en) | Method for repairing heavy metal contaminated soil by flotation | |
WO2020192046A1 (en) | Flotation process for treating coal slime by using salt-containing wastewater | |
CN106111684A (en) | A kind of preprocess method promoting soil washing desorption performance and device | |
CN106881341A (en) | A kind of heavy-metal contaminated soil leaching repairing method | |
CN208912333U (en) | A kind of multistage multistage hydrocyclone separation technology device | |
KR20120064803A (en) | Hybrid type soil washing facility and method for separation and remediation of contaminated soil | |
CN106583438A (en) | Remediation system and method for poisonous and harmful soil | |
CN104829070A (en) | Oil and gas field drilling fluid waste treatment-while-drilling system | |
CN211679279U (en) | Heavy metal contaminated soil ex-situ elution system and control system | |
CN211528001U (en) | Device for rapidly detecting water quality type of mine | |
CN206083405U (en) | Can handle high load capacity heavy metal combined pollution's multistage elution system of uniting | |
CN109092881A (en) | A kind of polycyclic aromatic hydrocarbon-heavy-metal contaminated soil elution device and repair system | |
CN106927546A (en) | A kind of soil argillaceous sand stone is separated and sewage disposal system, method | |
CN107321779A (en) | A kind of organic material contaminated soil wet method prosthetic device and technique |
Legal Events
Date | Code | Title | Description |
---|---|---|---|
PB01 | Publication | ||
PB01 | Publication | ||
SE01 | Entry into force of request for substantive examination | ||
SE01 | Entry into force of request for substantive examination | ||
RJ01 | Rejection of invention patent application after publication | ||
RJ01 | Rejection of invention patent application after publication |
Application publication date: 20191018 |