CN207671889U - A kind of dystrophication sediment in-situ decrement decontamination apparatus based on pore water guide - Google Patents
A kind of dystrophication sediment in-situ decrement decontamination apparatus based on pore water guide Download PDFInfo
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- CN207671889U CN207671889U CN201721571187.6U CN201721571187U CN207671889U CN 207671889 U CN207671889 U CN 207671889U CN 201721571187 U CN201721571187 U CN 201721571187U CN 207671889 U CN207671889 U CN 207671889U
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Abstract
The utility model provides a kind of dystrophication sediment in-situ decrement decontamination apparatus based on pore water guide, including D.C. regulated power supply, peristaltic pump, electric dehydration decontaminate electrode.Two opposite are arranged in parallel of electric dehydration decontamination electrode are inserted into bed mud, and electric dehydration decontamination electrode includes water guide electrode plate, the poly (methyl methacrylate) plate with holes set on water guide electrode plate both sides, the strainer on the outside of poly (methyl methacrylate) plate with holes, the overlying water isolation cover for being covered on water guide electrode plate.The plain conductor that water guide electrode plate is equipped with vertical guiding gutter and is connect with D.C. regulated power supply, water guide electrode plate bottom is equipped with the pore water memory being connected to guiding gutter, pore water memory is connect with row's conduit outside pore water, and conduit is arranged outside pore water and is connected with peristaltic pump.The utility model field work ability is strong, and the separation in situ of pollutants in sediments is good with removal effect, and power consumption is few, and operating cost is low, safeguards simply, and no chemical agent pollution and solid waste generate, and are influenced on river and lake Benthic ecology environment small.
Description
Technical field
The utility model is related to fwaater resources protection and water environment treatment field, specifically a kind of river based on pore water guide
Lake polluted bed mud sludge reduction onsite decontamination apparatus.
Background technology
Bed mud is the important component in important the accumulation library and aquatic ecosystem of dystrophication object, is recycled in regulation and control substance
With ecological process most important effect is played with service.In the case where external source pollution input gradually obtains control, how to have
Effect, which controls endogenous pollution of substrate sludge release, becomes Water Environment In Lakes improvement, and aquatic ecosystem restores basic with bio-diversity conservation
Premise, and current Ecological Civilization Construction and river length of carrying out in an all-round way make the realistic problem that must be faced.
River and lake sediments quality is loose, and muddy water reciprocation is strong, is the active region of pollution release and endogenous control
Key area.Dystopy dredging and covering in situ is mainly taken to solve the problems, such as that endogenous pollution of substrate sludge discharges both at home and abroad, wherein to dredge
Dredge quick, can substantially cut down pollution release iron, but of high cost, the mud amount after dredging is big, moisture content it is high (>90%), dirty
Complicated component is contaminated, subsequent processing is difficult.Covering in situ quickly can inhibit sediment pollution to discharge, and improve water transparency, but take stopgap measures
It does not effect a permanent cure, it is more difficult to cut down bed mud endogenous polyamine total amount, increase lake surface sediments volume instead, reduce the water body depth of water, influence bottom and dwell life
State environment.Therefore, such as how low cost detaches and removes the pollutant in bed mud with the mode of few disturbance ecology environment, is river and lake
Internal loading control obtains long-acting and actual effect key problem in technology.
Pore water is that the important preservation medium of pollutants in sediments and core discharge source.By the high bed mud hole of pollutant concentration
Gap water is detached and is removed, and the total amount and release iron of endogenous pollution of substrate sludge can be effectively cut down.Currently, open both at home and abroad
Some bed muds or the in situ sampling of soil pore water and the technique device of removing.The patent of Publication No. CN 103323290A
A kind of sampler for sediment pore water sampling in rivers or lakes is disclosed, is received by the stainless steel mesh of sampling pipe lower part
Collect pore water, is stored at the conical head of sampling bottom of the tube.The patent of Publication No. CN 105547757A discloses a kind of original
Position Sediment Pore Water is classified active sampler, collects pore water by the ceramic head mounted on different height plastic tube, realizes
Classification actively samples.Application No. is the patent of CN201710096949.X disclose pin-connected panel in situ elution with EKG is electronic cooperates with
The device and method of heavy metal-polluted soil is removed, device includes ekg electrode fixed plate, ekg electrode protection board, ekg electrode, leacheate
The compositions such as permeable tank, heavy metal-polluted soil solution collecting tank, under electric field or so, the pore water after being eluted to farmland soil heavy metals
Carry out collection and discharge in situ.
The utility model people has found by research in the process of implementing the utility model：It is existing based on pore water guide
There are larger deficiencies for riverbed sludge in-situ repairing device or technology：(1) stress to inhibit pore water by dredging or covering in situ
Pollution release, and it is indirect detach from bed mud medium and removes using pore water as pollution sources, therefore, the total amount of endogenous pollution
It cuts down few；(2) pore water sampler with sieve and ceramic head is developed, although pore water can be detached, amount is few, and efficiency is low, and
It is not related to the separation and removal of pollutants in sediments；(3) ekg electrode can take off the agricultural land soil pore water of no overlying water
It removes, but ekg electrode is in direct contact soil, electrode guiding gutter is easy to be blocked by soil particle, and EKG protection boards plug cumbersome, shadow
The sealing performance for ringing device, in addition, the device does not account for the intrusion of bed mud overlying water, and its avoids overlying water and hole
The problems such as exchange of water.
To sum up, fast and effeciently separation and removal internal contamination are the technical bottlenecks of dystrophication remedying sludge.How
Main preservation medium and the release source for catching this endogenous pollution of substrate sludge object of pore water, in electric field migration and gravitational field migration
Under effect, pollutants in sediments is quickly subjected to migration in situ, collection, storage with pore water and concentrates discharge, is cut from source
Subtract sediment pollution total amount and release iron, shorten repairing efficiency, will be the new approaches for solving sediment pollution internal loading, there is pole
Big environment, economical, societal benefits and application prospect.
Utility model content
The utility model provides a kind of dystrophication sediment in-situ decrement decontamination apparatus based on pore water guide, without dredging
Dig dystrophication bed mud, it is not necessary to covering material be added, be not required to input chemical agent；Rely primarily on low-voltage direct electric field and gravitational field
Sediments pollutant is carried out lateral transfer in situ with pore water and is collected with longitudinal, by containing high density pollution object by effect
Pore water carry out centrally stored with outer row, reduce bed mud hole water content, cut down the total amount of the releasable pollutant of bed mud, complete
The mud of pollutants in sediments-water separation and removal, realize the target of sediments decrement and decontamination.The device field work ability
By force, the separation in situ of pollutants in sediments is good with removal effect, and power consumption is few, and operating cost is low, safeguards simple, no chemical agent
Pollution and solid waste generate, and are influenced on river and lake Benthic ecology environment small.
To achieve the above object, the technical solution adopted in the utility model is：
A kind of dystrophication sediment in-situ based on pore water guide is reduced decontamination apparatus, including D.C. regulated power supply, compacted
Dynamic pump, electric dehydration decontaminate electrode, and two opposite are arranged in parallel of electric dehydration decontamination electrode are inserted into bed mud, electric dehydration decontamination
Electrode include water guide electrode plate, set on water guide electrode plate both sides poly (methyl methacrylate) plate with holes, be set to poly (methyl methacrylate) plate with holes on the outside of
Strainer, be covered on the overlying water isolation cover of water guide electrode plate, overlying water isolation cover is the body structure that Open Side Down, overlying water
The engaging portion of isolation cover and poly (methyl methacrylate) plate with holes and water guide electrode plate is sealed waterproof, and the lower side of overlying water isolation cover is straight
It connects and is placed in bed mud, and keep certain distance, the lower side that overlying water isolation cover is inserted into bed mud apparent away from water guide electrode plate surrounding
It is deeper than the top edge in bed mud of poly (methyl methacrylate) plate with holes and water guide electrode plate, water guide electrode plate is equipped with vertical guiding gutter
And plain conductor, plain conductor and the water proof wire in the water proof wire casing of overlying water isolation cover top of water guide electrode plate connect
It connects, water proof wire is connect with D.C. regulated power supply, and water guide electrode plate bottom is equipped with the pore water memory being connected to guiding gutter, hole
Gap water memory is connect with row's conduit outside pore water, and conduit is arranged outside pore water and is connected with peristaltic pump.
Further, overlying water isolation cover lower side driving depth be 5cm, overlying water isolation cover 3-7 lower side away from
From water guide electrode plate 3-1 all around each 10cm.
Further, poly (methyl methacrylate) plate with holes, which is middle and lower part, hole, top non-porous structure, poly (methyl methacrylate) plate and strainer with holes
Trepanning height it is identical with width.
Further, poly (methyl methacrylate) plate with holes, which is middle and lower part 20cm, hole, and top 5-10cm is non-porous, for sealing water guide electricity
Pole plate and the intrusion for preventing overlying water.
Further, organic glass panel aperture with holes is no more than 5mm, and thickness is no more than 3mm, and aperture of filter screen and thickness are not
More than 1mm.
Further, the electric dehydration decontamination electrode further includes the T-type handle being connected with pore water memory, and being used for will
Electric dehydration decontaminates electrode and is inserted into bed mud.
Further, overlying water isolation cover is organic glass material.
Further, conduit is arranged outside pore water with peristaltic pump to be connected by rubber hose, will be stored in pore water automatically and deposit
The pore water of reservoir and its contained pollutant carry out collection China and foreign countries and arrange.
Further, further include the liquid-collecting barrel being connect with peristaltic pump by rubber hose.
Further, pore water memory uses the structure of top square column and lower part inverted triangle taper, convenient for storage
It is plugged in pore water and bed mud.
As the above scheme is adopted, the utility model has the advantages that：
(1) inversion type overlying water isolation cover is used, removing pore water for electric dehydration decontamination electrode creates relative closure
Environment, blocked overlying water from it is vertical with laterally to electric dehydration decontaminate electrode intrusion, it is ensured that expeditiously removing containing height
The pore water of concentration pollutant improves the applicability of the in-situ immobilization of whole device.
(2) strainer, poly (methyl methacrylate) plate with holes are applied in combination with water guide electrode plate, fixed and smooth water guide electrode plate
Meanwhile being filtered by dual intercepting, effectively prevent sediment particles from invading and block the guiding gutter of water guide electrode plate, it is ensured that efficiently to receive
Collect pore water, reduces and avoid to greatest extent the discharge of solid content.
(3) vertical water guide electrode plate can play the multiple actions such as electromigration, electric osmose and gravity transfer, not only accelerate dirt
The separation and migration for contaminating object, the transverse direction for being also convenient for pore water collect with vertical, greatly improve sediment in-situ electric dehydration and remove
Dirty efficiency.
(4) in the presence of overlying water, electric dehydration abatement processes in situ is carried out to the sediments of high-moisture percentage, are being realized
While bed mud pore water and pollutant are reduced；Due to the hydrostatic pressure of overlying water, sediments porosity will reduce automatically, promote
Original position into bed mud is closely knit and minimizing, further weakens the releasability of pollutants in sediments.
(5) low-voltage dc power supply is used to carry out electric dehydration decontamination in situ, bed mud disturbance is small, and Benthic ecology environment influences
It is small.The repeatable usability of device is strong, and consumption electric energy is few, and operation expense is low, efficient, is conducive to obtain sediment pollution release
The actual effect of control with it is long-acting, there is huge economic, society and environmental benefit.
Description of the drawings
Fig. 1 is the operation principle of dystrophication sediment in-situ decrement decontamination apparatus of the utility model based on pore water guide
Schematic diagram；
Fig. 2 is the structural representation of dystrophication sediment in-situ decrement decontamination apparatus of the utility model based on pore water guide
Figure；
Fig. 3 is the structural schematic diagram of water guide electrode plate in the utility model.
In figure：1-riverbed sludge, 2-overlying waters, 3-electric dehydrations decontaminate electrode, and 4-D.C. regulated power supplies, 5-is anti-
Water conducting wire, 6-peristaltic pumps, 7-liquid-collecting barrels, 8-rubber hose, 3-1-water guide electrode plate, 3-2-poly (methyl methacrylate) plates with holes, 3-
3-strainers, 3-4-pore water memory arrange conduit outside 3-5-pore water, 3-6-water proof wire casing, 3-7-overlying water every
Cover absolutely, 3-8-T-type handle, 3-1-1-plain conductor, 3-1-2-guiding gutter.
Specific implementation mode
Below in conjunction with the attached drawing in the utility model, the technical solution in the utility model is carried out clearly and completely
Description.
It please refers to Fig.1 and Fig. 2, dystrophication sediment in-situ of the utility model based on pore water guide is reduced decontamination apparatus
One of embodiment, including D.C. regulated power supply 4, liquid-collecting barrel 7, peristaltic pump 6, electric dehydration decontaminate electrode 3, and electric dehydration is removed
Dirty electrode 3 is connected with D.C. regulated power supply 4 and peristaltic pump 6.It includes T-type handle 3-8, water proof wire that electric dehydration, which decontaminates electrode 3,
Casing 3-6, overlying water isolation cover 3-7, poly (methyl methacrylate) plate 3-2 with holes, water guide electrode plate 3-1, strainer 3-3, pore water memory
Conduit 3-5 is arranged outside 3-4, pore water.
Water guide electrode plate 3-1 is General-purpose electrode, you can does cathode, can also do anode, there is 2 water guide electricity in the present embodiment
Pole plate 3-1, it is opposite to be arranged in parallel, it connect be connected with the anode and cathode of D.C. regulated power supply 4 respectively, D.C. regulated power supply 4 has
There are digital display function, and voltage and current adjustment.It please gather with reference to figure 3, water guide electrode plate 3-1 is equipped with vertical guiding gutter 3-1-
2 and plain conductor 3-1-1, has both draining and electrode function, by electric osmose and the quick guide bed mud pore water of gravity, and according to
The pollutant in removal bed mud is detached by electromigration.Plain conductor 3-1-1 is pierced by after water guide electrode plate 3-1 and D.C. regulated power supply
4 are connected.Pore water memory 3-4 is set to the bottoms water guide electrode plate 3-1, is connected to guiding gutter 3-1-2.Pore water memory 3-4
It is connect with conduit 3-5 is arranged outside pore water, conduit 3-5 is arranged outside pore water and is connected by rubber hose 8 with peristaltic pump 6, will be deposited automatically
It is stored in the pore water of hole pore water memory 3-4 and its contained pollutant carries out collection China and foreign countries and arranges.As shown in Figure 1, pore water is deposited
The structure of top square column and lower part inverted triangle taper can be used in reservoir 3-4, convenient for being plugged in storage pore water and bed mud.Such as
Shown in Fig. 2, T-type handle 3-8 is connected with pore water memory 3-4, and Electrode Operation is decontaminated for entire sediment in-situ electric dehydration.
The making of the hard materials such as stainless steel can be used in T-type handle 3-8.
It is the smaller filter of the larger poly (methyl methacrylate) plate 3-2 with holes in aperture and aperture successively outside the both sides water guide electrode plate 3-1
Net 3-3.Poly (methyl methacrylate) plate 3-2 with holes, which is middle and lower part, a hole, top non-porous structure, poly (methyl methacrylate) plate 3-2 with holes and strainer 3-3's
The height of trepanning is identical with width.Poly (methyl methacrylate) plate 3-2 with holes is mainly used for fixed and smooth water guide electrode plate 3-1.It is logical
The double filtration for crossing poly (methyl methacrylate) plate 3-2 with holes and strainer 3-3 intercepts, it is therefore prevented that sediments in electric dehydration depolluting processes
Grain is lost in intrusion with pore water and blocks the guiding gutter 3-1-2 of water guide electrode plate 3-1.
Overlying water isolation cover 3-7 is the body structure that Open Side Down, is covered at the top of water guide electrode plate 3-1, including top plate
And the lower side extended downwardly along top plate surrounding.The top plate and poly (methyl methacrylate) plate 3-2 with holes and water guide electricity of overlying water isolation cover 3-7
The engaging portion of pole plate 3-1 is sealed waterproof.The lower side of overlying water isolation cover 3-7 is placed directly in bed mud, and away from water guide electricity
Pole plate 3-1 surroundings keep certain distance.The lower side that overlying water isolation cover 3-7 is inserted into bed mud will obviously be deeper than organic glass with holes
The top edge in bed mud of plate 3-2 and water guide electrode plate 3-1 can avoid overlying water and completely cuts off cover 3-7's by overlying water in this way
Side wall directly invades electric dehydration decontamination electrode.It is equipped with water proof wire casing 3-6, water proof wire at the top of overlying water isolation cover 3-7
Water proof wire 5, the waterproof in the plain conductor 3-1-1 and water proof wire casing 3-6 of water guide electrode plate 3-1 are equipped in casing 3-6
Conducting wire 5 connects, and water proof wire 5 is connect with D.C. regulated power supply 4.Water proof wire casing 3-6 is for ensureing water guide electrode plate 3-1's
Plain conductor 3-1-1 and the water proof wire 5 that the is attached thereto Electrical Safety in overlying water, prevent from leaking electricity.
Electric dehydration decontamination electrode 3 is inserted into bed mud 1, after connecting D.C. regulated power supply 4, electrolysis water occurs inside bed mud
Reaction generates H+And OH-, H+Increase can promote the dissolving, desorption and a large amount of release of pollutants in sediments, improve pore water rapidly
The concentration of middle pollutant.
Under DC electric field effect, metal ion, NH in sediments4 +、H+Deng cationic guide water power pole plate 3-1's
Cathode is oriented electromigration, PO4 3-, Cl-、SO4 2-、OH-The anode of equal anion then guide water power pole plate 3-1 orients electromigration.
It, can also be with pore water together, from water guide electrode under electroosmotic effect into the pollutant of pore water while electromigration occurs
The anode of plate 3-1 is to cathode directional migration.Therefore, under electromigration and the double action of electric osmose, pollutant and hole are realized
Water is from the separation in sediments medium.
Move to electric dehydration decontamination electrode 3 near pollutants in sediments or pore water molecule, pass sequentially through strainer 3-3 and
Poly (methyl methacrylate) plate 3-2 with holes, into the guiding gutter 3-1-2 of water guide electrode plate 3-1, then under the effect of gravity, along guiding gutter
3-1-2 imports pore water memory 3-4.In the case that cold, guiding gutter pore water memory 3-4 can also be by water guide electricity
Pore water above pole plate 3-1 in bed mud carries out centralized collection discharge.
Illustrate its specific implementation process below in conjunction with Fig. 1, Fig. 2 and Fig. 3：
1. understanding pending waters regimen and 1 pollution situation of riverbed sludge, including the depth of water of overlying water 2, flow velocity, bed mud 1
The basic parameters such as hole water content and distribution, pollutant kind, content and distribution.Hydrologic condition based on pending waters and bottom
Mud 1 pollutes bearing features, determines that electric dehydration decontamination electrode 3 is inserted into the depth of bed mud 1 and the lift etc. of peristaltic pump 6.Generally
For, 0-10cm bed muds 1 hole water content in surface layer is high, moisture content 60%-80%；Increase with the depth of bed mud 1, pore water
Content is generally on a declining curve, and when the thickness of bed mud 1 is more than 30cm, moisture content is generally below 50%.To improve the de- of bed mud 1
Water decontaminates efficiency, and general recommendations selection pollutant concentration is high, pore water discharges active surface layer 20cm bed muds 1 and handled.
2. after selected pending area, by the T-type handle 3-8 that is connected with pore water memory 3-4, electric dehydration is decontaminated
Electrode 3 is inserted into bed mud 1, generally enters water degree according to the depth of water of pending waters overlying water 2 and T-type handle 3-8, confirms electronic
Whether dehydration decontamination electrode 3 is inserted into set depth.To reduce influence of the DC electric field to Benthic ecology environment, electric dehydration is removed
The power-on voltage of dirty electrode 3 is usually no more than 30V, and the spacing of two neighboring electric dehydration decontamination electrode 3 is no more than 2.0m, voltage
Gradient controls within 1V/cm.
3. it is organic glass material that electric dehydration, which decontaminates the overlying water isolation cover 3-7 installed at 3 top of electrode, for Open Side Down
Body structure, overlying water isolation cover 3-7 lower side be placed directly in bed mud 1, driving depth 5cm, overlying water isolation cover
The lower side of 3-7 is apart from water guide electrode plate 3-1 all around each 10cm, to prevent overlying water 2 from passing through overlying water isolation cover 3-7's
Side wall invades and streams and decontaminate electrode 3 into electric dehydration.In addition, overlying water isolation cover 3-7 and poly (methyl methacrylate) plate 3-2 with holes
It is sealed water-proofing treatment with the engaging portion of water guide electrode plate 3-1, cuts off the direct hydraulic connection of overlying water 2 and pore water.
4. connecting D.C. regulated power supply 4, cell reaction occurs for the pore water inside pending bed mud 1, generates H+And OH-, H+
Increase can improve sediments acidity, promote the dissolving, desorption and a large amount of release of pollutants in sediments, pollutants in sediments given
Separation, and enter pore water.
5. under DC electric field effect, metal ion, NH in bed mud 14 +、H+Deng the moon of cationic guide water power pole plate 3-1
Pole is oriented migration, PO4 3-, Cl-、SO4 2-、OH-The anode directional migration of equal anion then guide water power pole plate 3-1.Occurring
While electromigration, into the pollutant of pore water, can also with pore water under electroosmotic effect from the anode of water guide electrode plate 3-1
To cathode directional migration.By the double action of electromigration and electric osmose, pollutant is had with pore water from pending bed mud 1
Effect separation.
6. the two-sided of water guide electrode plate 3-1 is paid the utmost attention to be vertically arranged with uniform guiding gutter 3-1-2.Water guide electrode plate
3-1 belongs to General-purpose electrode, you can do anode, can also do cathode, the internal metal wirings 3-1-1 of water guide electrode plate 3-1 with it is anti-
Water wire socket 3-6 is connected, and for powering to water guide electrode plate 3-1, water guide electrode plate 3-1 can be processed by conductive materials such as graphite
It forms.
7. under DC electric field effect, moving to the pollutant or pore water near electric dehydration decontamination electrode 3, passing sequentially through
Strainer 3-3 and poly (methyl methacrylate) plate 3-2 with holes, into the guiding gutter 3-1-2 of water guide electrode plate 3-1.Strainer 3-3 is Fiber Materials,
Aperture is no more than 1mm with thickness；The apertures poly (methyl methacrylate) plate 3-2 with holes are no more than 5mm, and thickness is no more than 3mm.Strainer 3-3 with
Poly (methyl methacrylate) plate 3-2 trepannings height with holes is identical as the depth of pending bed mud 1, general 20cm.
8. water guide electrode plate 3-1 front with reverse side by two pieces of identical poly (methyl methacrylate) plate 3-2 with holes be fixed with
Smooth, the outside of poly (methyl methacrylate) plate 3-2 with holes is strainer 3-3.Poly (methyl methacrylate) plate 3-2 with holes, which is middle and lower part 20cm, hole, top
5-10cm is non-porous, the intrusion for sealing water guide electrode plate 3-1 He preventing overlying water 1.
9. the double filtration by poly (methyl methacrylate) plate 3-2 with holes and strainer 3-1 intercepts, effectively electric dehydration is prevented to decontaminate
Sediments particle is lost in intrusion with pore water and blocks the guiding gutter 3-1-2 of water guide electrode plate 3-1 in the process.
10. under electric field or gravity, migrates to the bed mud pore water near water guide electrode plate 3-1, continue on and lead
The guiding gutter 3-1-2 of water power pole plate 3-1 imports pore water memory 3-4.Pore water memory 3-4 using top square column and
The structure of lower part inverted triangle taper, convenient for being plugged in storage pore water and bed mud 1.
11. the rectangular place in top of pore water memory 3-4, conduit 3-5 is arranged outside lateral connection pore water.It is arranged outside pore water
Conduit 3-5 is connected with peristaltic pump 6 by rubber hose 8, will be stored in the pore water of pore water memory 3-4 and its contained automatically
Pollutant detached from 1 medium of bed mud with collection China and foreign countries arrange.
12. sediment in-situ electric dehydration decontamination electrode 3 is powered by D.C. regulated power supply 4 and water proof wire 5.Direct current
Regulated power supply 4 has digital display function, and voltage and current adjustment.To save energy consumption, electric dehydration decontaminates between the generally use of electrode 3
Powered-on mode of having a rest is run.During power-off, the guiding gutter 3-1-2 of water guide electrode plate 3-1 can rely on gravity to collect water guide electricity
Pore water above pole plate 3-1 in bed mud 1.
13. in operational process, when the water outlet of the pore water of peristaltic pump 6 significantly reduces, you can stop electric dehydration decontamination behaviour
Make, electric dehydration decontamination electrode 3 is extracted by T-type handle 3-8, after suitably rinsing, carries on work.
14. the present apparatus electric dehydration decontamination electrode 3 have generalization and can normalized characteristic, anode or the moon can be also served as
Pole.In concrete practice, combination or the concentration of multiple electric dehydration decontamination electrodes 3 can be carried out, just substantially increases list in this way
The processing area of a electric dehydration decontamination electrode 3, and by centrally connected power supply and unified pump drainage pore water, improve the operation effect of device
Benefit.
Above description is only a specific implementation of the present invention, but the scope of protection of the utility model is not limited to
It is any to belong to those skilled in the art within the technical scope disclosed by the utility model in this, the change that can be readily occurred in
Change or replace, should be covered within the scope of the utility model.Therefore, the scope of protection of the utility model should be with power
Subject to the protection domain that profit requires.
Claims (10)
1. a kind of dystrophication sediment in-situ based on pore water guide is reduced decontamination apparatus, including D.C. regulated power supply, wriggling
Pump, electric dehydration decontaminate electrode, and two opposite are arranged in parallel of electric dehydration decontamination electrode are inserted into bed mud, it is characterised in that：Electricity
Dynamic dehydration decontamination electrode include water guide electrode plate, set on water guide electrode plate both sides poly (methyl methacrylate) plate with holes, be set to it is with holes organic
Strainer on the outside of glass plate, the overlying water isolation cover for being covered on water guide electrode plate, overlying water isolation cover is the babinet that Open Side Down
The engaging portion of structure, overlying water isolation cover and poly (methyl methacrylate) plate with holes and water guide electrode plate is sealed waterproof, overlying water isolation
The lower side of cover is placed directly in bed mud, and keeps certain distance, overlying water isolation cover to be inserted into bed mud away from water guide electrode plate surrounding
Lower side be obviously deeper than the top edge in bed mud of poly (methyl methacrylate) plate with holes and water guide electrode plate, water guide electrode plate is equipped with
Vertical guiding gutter and plain conductor, plain conductor and the overlying water isolation of water guide electrode plate are covered in the water proof wire casing of top
Water proof wire connects, and water proof wire is connect with D.C. regulated power supply, and water guide electrode plate bottom is equipped with the hole being connected to guiding gutter
Water memory, pore water memory connect with row's conduit outside pore water, conduit are arranged outside pore water and is connected with peristaltic pump.
2. the dystrophication sediment in-situ based on pore water guide is reduced decontamination apparatus as described in claim 1, feature exists
In：The lower side driving depth of overlying water isolation cover is 5cm, and the lower side of overlying water isolation cover 3-7 is apart from water guide electrode plate 3-1
Each 10cm all around.
3. the dystrophication sediment in-situ based on pore water guide is reduced decontamination apparatus as described in claim 1, feature exists
In：Poly (methyl methacrylate) plate with holes, which is middle and lower part, a hole, top non-porous structure, the height of the trepanning of poly (methyl methacrylate) plate and strainer with holes and
Width is identical.
4. the dystrophication sediment in-situ based on pore water guide is reduced decontamination apparatus as claimed in claim 3, feature exists
In：Poly (methyl methacrylate) plate with holes, which is middle and lower part 20cm, hole, and top 5-10cm is non-porous, for sealing water guide electrode plate and preventing overlying
The intrusion of water.
5. the dystrophication sediment in-situ based on pore water guide is reduced decontamination apparatus as described in claim 1, feature exists
In：Organic glass panel aperture with holes is no more than 5mm, and thickness is no more than 3mm, and aperture of filter screen is no more than 1mm with thickness.
6. the dystrophication sediment in-situ based on pore water guide is reduced decontamination apparatus as described in claim 1, feature exists
In：The electric dehydration decontamination electrode further includes the T-type handle being connected with pore water memory, for electric dehydration to be decontaminated electricity
Bed mud is inserted into pole.
7. the dystrophication sediment in-situ based on pore water guide is reduced decontamination apparatus as described in claim 1, feature exists
In：Overlying water isolation cover is organic glass material.
8. the dystrophication sediment in-situ based on pore water guide is reduced decontamination apparatus as described in claim 1, feature exists
In：Conduit is arranged outside pore water with peristaltic pump to be connected by rubber hose, automatically by be stored in pore water memory pore water and
Pollutant contained by it carries out collection China and foreign countries and arranges.
9. the dystrophication sediment in-situ based on pore water guide is reduced decontamination apparatus as described in claim 1, feature exists
In：It further include the liquid-collecting barrel being connect with peristaltic pump by rubber hose.
10. the dystrophication sediment in-situ based on pore water guide is reduced decontamination apparatus as described in claim 1, feature exists
In：Pore water memory uses the structure of top square column and lower part inverted triangle taper, convenient in storage pore water and bed mud
Plug.
Priority Applications (1)
| Application Number | Priority Date | Filing Date | Title |
|---|---|---|---|
| CN201721571187.6U CN207671889U (en) | 2017-11-22 | 2017-11-22 | A kind of dystrophication sediment in-situ decrement decontamination apparatus based on pore water guide |
Applications Claiming Priority (1)
| Application Number | Priority Date | Filing Date | Title |
|---|---|---|---|
| CN201721571187.6U CN207671889U (en) | 2017-11-22 | 2017-11-22 | A kind of dystrophication sediment in-situ decrement decontamination apparatus based on pore water guide |
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Cited By (4)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| CN107746163A (en) * | 2017-11-22 | 2018-03-02 | 长江水利委员会长江科学院 | A kind of dystrophication sediment in-situ decrement decontamination apparatus based on pore water guide |
| CN109045847A (en) * | 2018-09-18 | 2018-12-21 | 北京中岩大地科技股份有限公司 | A kind of apparatus and method of factory's waste residue dehydration decontamination |
| CN109179966A (en) * | 2018-09-18 | 2019-01-11 | 北京中岩大地科技股份有限公司 | A kind of apparatus and method that direct current decontaminates the dehydration of factory's waste residue in conjunction with gravity |
| CN109731905A (en) * | 2019-03-01 | 2019-05-10 | 长江水利委员会长江科学院 | A kind of autonomous controllably soil or the electronic acidification device for dissociation of pollutants in sediments and method |
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2017
- 2017-11-22 CN CN201721571187.6U patent/CN207671889U/en active Active
Cited By (4)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| CN107746163A (en) * | 2017-11-22 | 2018-03-02 | 长江水利委员会长江科学院 | A kind of dystrophication sediment in-situ decrement decontamination apparatus based on pore water guide |
| CN109045847A (en) * | 2018-09-18 | 2018-12-21 | 北京中岩大地科技股份有限公司 | A kind of apparatus and method of factory's waste residue dehydration decontamination |
| CN109179966A (en) * | 2018-09-18 | 2019-01-11 | 北京中岩大地科技股份有限公司 | A kind of apparatus and method that direct current decontaminates the dehydration of factory's waste residue in conjunction with gravity |
| CN109731905A (en) * | 2019-03-01 | 2019-05-10 | 长江水利委员会长江科学院 | A kind of autonomous controllably soil or the electronic acidification device for dissociation of pollutants in sediments and method |
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