CN109500074A - Dystopy suitable for clayed soil pollution amelioration elutes prosthetic device and restorative procedure - Google Patents
Dystopy suitable for clayed soil pollution amelioration elutes prosthetic device and restorative procedure Download PDFInfo
- Publication number
- CN109500074A CN109500074A CN201811614470.1A CN201811614470A CN109500074A CN 109500074 A CN109500074 A CN 109500074A CN 201811614470 A CN201811614470 A CN 201811614470A CN 109500074 A CN109500074 A CN 109500074A
- Authority
- CN
- China
- Prior art keywords
- water
- mud
- soil
- sludge
- elution
- 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
- 238000000034 method Methods 0.000 title claims abstract description 68
- 238000003900 soil pollution Methods 0.000 title claims abstract description 16
- XLYOFNOQVPJJNP-UHFFFAOYSA-N water Substances O XLYOFNOQVPJJNP-UHFFFAOYSA-N 0.000 claims abstract description 260
- 239000002689 soil Substances 0.000 claims abstract description 134
- 239000010802 sludge Substances 0.000 claims abstract description 102
- 238000010828 elution Methods 0.000 claims abstract description 93
- 239000002351 wastewater Substances 0.000 claims abstract description 76
- 239000003814 drug Substances 0.000 claims abstract description 64
- 238000006243 chemical reaction Methods 0.000 claims abstract description 55
- 239000002245 particle Substances 0.000 claims abstract description 54
- 238000003860 storage Methods 0.000 claims abstract description 41
- 230000018044 dehydration Effects 0.000 claims abstract description 34
- 238000006297 dehydration reaction Methods 0.000 claims abstract description 34
- 229910001385 heavy metal Inorganic materials 0.000 claims abstract description 20
- 230000000694 effects Effects 0.000 claims abstract description 19
- 238000012216 screening Methods 0.000 claims abstract description 18
- 238000004065 wastewater treatment Methods 0.000 claims abstract description 17
- 239000007788 liquid Substances 0.000 claims description 61
- 230000005484 gravity Effects 0.000 claims description 40
- 239000008399 tap water Substances 0.000 claims description 37
- 235000020679 tap water Nutrition 0.000 claims description 37
- 238000005406 washing Methods 0.000 claims description 36
- 238000011010 flushing procedure Methods 0.000 claims description 34
- 239000002002 slurry Substances 0.000 claims description 34
- 238000003825 pressing Methods 0.000 claims description 33
- 238000005189 flocculation Methods 0.000 claims description 28
- 239000012535 impurity Substances 0.000 claims description 28
- 238000001914 filtration Methods 0.000 claims description 26
- 230000008569 process Effects 0.000 claims description 25
- 239000003795 chemical substances by application Substances 0.000 claims description 24
- 239000003480 eluent Substances 0.000 claims description 24
- 239000012071 phase Substances 0.000 claims description 24
- 230000016615 flocculation Effects 0.000 claims description 22
- 238000002386 leaching Methods 0.000 claims description 19
- 239000000701 coagulant Substances 0.000 claims description 18
- 230000001376 precipitating effect Effects 0.000 claims description 16
- 239000002738 chelating agent Substances 0.000 claims description 15
- 239000013043 chemical agent Substances 0.000 claims description 15
- JEGUKCSWCFPDGT-UHFFFAOYSA-N h2o hydrate Chemical compound O.O JEGUKCSWCFPDGT-UHFFFAOYSA-N 0.000 claims description 15
- 239000000463 material Substances 0.000 claims description 15
- 230000009471 action Effects 0.000 claims description 14
- 239000003513 alkali Substances 0.000 claims description 14
- 239000007787 solid Substances 0.000 claims description 14
- 229910052783 alkali metal Inorganic materials 0.000 claims description 13
- 239000003153 chemical reaction reagent Substances 0.000 claims description 13
- 230000015271 coagulation Effects 0.000 claims description 12
- 238000005345 coagulation Methods 0.000 claims description 12
- 238000005067 remediation Methods 0.000 claims description 11
- 239000000356 contaminant Substances 0.000 claims description 10
- 239000003344 environmental pollutant Substances 0.000 claims description 10
- 238000011066 ex-situ storage Methods 0.000 claims description 10
- 231100000719 pollutant Toxicity 0.000 claims description 10
- 238000007873 sieving Methods 0.000 claims description 10
- 239000002699 waste material Substances 0.000 claims description 10
- KRKNYBCHXYNGOX-UHFFFAOYSA-N citric acid Chemical compound OC(=O)CC(O)(C(O)=O)CC(O)=O KRKNYBCHXYNGOX-UHFFFAOYSA-N 0.000 claims description 9
- 239000007790 solid phase Substances 0.000 claims description 7
- VEXZGXHMUGYJMC-UHFFFAOYSA-N Hydrochloric acid Chemical compound Cl VEXZGXHMUGYJMC-UHFFFAOYSA-N 0.000 claims description 6
- 238000010907 mechanical stirring Methods 0.000 claims description 6
- 239000007800 oxidant agent Substances 0.000 claims description 6
- 230000001590 oxidative effect Effects 0.000 claims description 6
- 239000002585 base Substances 0.000 claims description 5
- 238000004062 sedimentation Methods 0.000 claims description 5
- 238000013019 agitation Methods 0.000 claims description 4
- 230000015556 catabolic process Effects 0.000 claims description 4
- 238000006731 degradation reaction Methods 0.000 claims description 4
- 230000008021 deposition Effects 0.000 claims description 4
- 238000007599 discharging Methods 0.000 claims description 4
- 239000006185 dispersion Substances 0.000 claims description 4
- 238000002360 preparation method Methods 0.000 claims description 4
- 239000004094 surface-active agent Substances 0.000 claims description 4
- KCXVZYZYPLLWCC-UHFFFAOYSA-N EDTA Chemical compound OC(=O)CN(CC(O)=O)CCN(CC(O)=O)CC(O)=O KCXVZYZYPLLWCC-UHFFFAOYSA-N 0.000 claims description 3
- 238000013329 compounding Methods 0.000 claims description 3
- 238000001035 drying Methods 0.000 claims description 3
- 239000002920 hazardous waste Substances 0.000 claims description 3
- 239000004615 ingredient Substances 0.000 claims description 3
- 239000002957 persistent organic pollutant Substances 0.000 claims description 3
- 238000012797 qualification Methods 0.000 claims description 3
- 239000002910 solid waste Substances 0.000 claims description 3
- RCEAADKTGXTDOA-UHFFFAOYSA-N OS(O)(=O)=O.CCCCCCCCCCCC[Na] Chemical compound OS(O)(=O)=O.CCCCCCCCCCCC[Na] RCEAADKTGXTDOA-UHFFFAOYSA-N 0.000 claims description 2
- 238000005119 centrifugation Methods 0.000 claims description 2
- 238000005520 cutting process Methods 0.000 claims description 2
- 239000010801 sewage sludge Substances 0.000 claims description 2
- 229920002472 Starch Polymers 0.000 claims 1
- 239000002253 acid Substances 0.000 claims 1
- 238000004064 recycling Methods 0.000 claims 1
- 239000007921 spray Substances 0.000 claims 1
- 235000019698 starch Nutrition 0.000 claims 1
- 239000008107 starch Substances 0.000 claims 1
- 239000006228 supernatant Substances 0.000 claims 1
- 235000021419 vinegar Nutrition 0.000 claims 1
- 239000000052 vinegar Substances 0.000 claims 1
- 238000004069 wastewater sedimentation Methods 0.000 claims 1
- 230000008901 benefit Effects 0.000 abstract description 8
- 238000011109 contamination Methods 0.000 abstract description 8
- 238000005516 engineering process Methods 0.000 description 7
- QTBSBXVTEAMEQO-UHFFFAOYSA-N Acetic acid Chemical compound CC(O)=O QTBSBXVTEAMEQO-UHFFFAOYSA-N 0.000 description 6
- PXHVJJICTQNCMI-UHFFFAOYSA-N Nickel Chemical compound [Ni] PXHVJJICTQNCMI-UHFFFAOYSA-N 0.000 description 6
- 239000004927 clay Substances 0.000 description 6
- 238000012545 processing Methods 0.000 description 6
- 238000004140 cleaning Methods 0.000 description 5
- 238000011084 recovery Methods 0.000 description 5
- 239000004744 fabric Substances 0.000 description 4
- 238000005086 pumping Methods 0.000 description 4
- 238000003756 stirring Methods 0.000 description 4
- 239000004568 cement Substances 0.000 description 3
- 238000000265 homogenisation Methods 0.000 description 3
- 239000000203 mixture Substances 0.000 description 3
- 238000004537 pulping Methods 0.000 description 3
- 239000008400 supply water Substances 0.000 description 3
- XEEYBQQBJWHFJM-UHFFFAOYSA-N Iron Chemical compound [Fe] XEEYBQQBJWHFJM-UHFFFAOYSA-N 0.000 description 2
- 238000007664 blowing Methods 0.000 description 2
- 229910052793 cadmium Inorganic materials 0.000 description 2
- BDOSMKKIYDKNTQ-UHFFFAOYSA-N cadmium atom Chemical group [Cd] BDOSMKKIYDKNTQ-UHFFFAOYSA-N 0.000 description 2
- 239000012065 filter cake Substances 0.000 description 2
- 208000037805 labour Diseases 0.000 description 2
- 229910052759 nickel Inorganic materials 0.000 description 2
- 239000004576 sand Substances 0.000 description 2
- 238000004513 sizing Methods 0.000 description 2
- DGAQECJNVWCQMB-PUAWFVPOSA-M Ilexoside XXIX Chemical compound C[C@@H]1CC[C@@]2(CC[C@@]3(C(=CC[C@H]4[C@]3(CC[C@@H]5[C@@]4(CC[C@@H](C5(C)C)OS(=O)(=O)[O-])C)C)[C@@H]2[C@]1(C)O)C)C(=O)O[C@H]6[C@@H]([C@H]([C@@H]([C@H](O6)CO)O)O)O.[Na+] DGAQECJNVWCQMB-PUAWFVPOSA-M 0.000 description 1
- 230000002411 adverse Effects 0.000 description 1
- 238000013459 approach Methods 0.000 description 1
- QVGXLLKOCUKJST-UHFFFAOYSA-N atomic oxygen Chemical compound [O] QVGXLLKOCUKJST-UHFFFAOYSA-N 0.000 description 1
- 230000009286 beneficial effect Effects 0.000 description 1
- 230000015572 biosynthetic process Effects 0.000 description 1
- 238000005352 clarification Methods 0.000 description 1
- 230000006835 compression Effects 0.000 description 1
- 238000007906 compression Methods 0.000 description 1
- 238000010276 construction Methods 0.000 description 1
- 230000007812 deficiency Effects 0.000 description 1
- 238000013461 design Methods 0.000 description 1
- 238000003795 desorption Methods 0.000 description 1
- 239000003599 detergent Substances 0.000 description 1
- 238000011161 development Methods 0.000 description 1
- 238000004090 dissolution Methods 0.000 description 1
- 238000009826 distribution Methods 0.000 description 1
- MOTZDAYCYVMXPC-UHFFFAOYSA-N dodecyl hydrogen sulfate Chemical compound CCCCCCCCCCCCOS(O)(=O)=O MOTZDAYCYVMXPC-UHFFFAOYSA-N 0.000 description 1
- 229940079593 drug Drugs 0.000 description 1
- 239000008187 granular material Substances 0.000 description 1
- 230000036541 health Effects 0.000 description 1
- 230000006872 improvement Effects 0.000 description 1
- 229910052742 iron Inorganic materials 0.000 description 1
- 239000007791 liquid phase Substances 0.000 description 1
- 238000011068 loading method Methods 0.000 description 1
- 239000006210 lotion Substances 0.000 description 1
- 238000004519 manufacturing process Methods 0.000 description 1
- 229910052751 metal Inorganic materials 0.000 description 1
- 239000002184 metal Substances 0.000 description 1
- 239000011368 organic material Substances 0.000 description 1
- 230000003647 oxidation Effects 0.000 description 1
- 238000007254 oxidation reaction Methods 0.000 description 1
- 239000001301 oxygen Substances 0.000 description 1
- 229910052760 oxygen Inorganic materials 0.000 description 1
- 230000020477 pH reduction Effects 0.000 description 1
- 239000000843 powder Substances 0.000 description 1
- 239000002244 precipitate Substances 0.000 description 1
- 239000012716 precipitator Substances 0.000 description 1
- 238000004886 process control Methods 0.000 description 1
- 238000004080 punching Methods 0.000 description 1
- 238000000746 purification Methods 0.000 description 1
- 230000035484 reaction time Effects 0.000 description 1
- 230000008439 repair process Effects 0.000 description 1
- 238000011160 research Methods 0.000 description 1
- 230000000717 retained effect Effects 0.000 description 1
- 239000013049 sediment Substances 0.000 description 1
- 238000010334 sieve classification Methods 0.000 description 1
- 239000002893 slag Substances 0.000 description 1
- 229910052708 sodium Inorganic materials 0.000 description 1
- 239000011734 sodium Substances 0.000 description 1
- 239000003802 soil pollutant Substances 0.000 description 1
- 238000007711 solidification Methods 0.000 description 1
- 230000008023 solidification Effects 0.000 description 1
- 239000000126 substance Substances 0.000 description 1
- 239000013589 supplement Substances 0.000 description 1
- 238000005496 tempering Methods 0.000 description 1
- 230000007306 turnover Effects 0.000 description 1
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
- 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
-
- 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
- C02F1/58—Treatment of water, waste water, or sewage by removing specified dissolved compounds
- C02F1/62—Heavy metal compounds
-
- 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
- C02F1/72—Treatment of water, waste water, or sewage by oxidation
-
- 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
- C02F11/121—Treatment of sludge; Devices therefor by de-watering, drying or thickening by mechanical de-watering
- C02F11/122—Treatment of sludge; Devices therefor by de-watering, drying or thickening by mechanical de-watering using filter presses
-
- 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
- C02F11/14—Treatment of sludge; Devices therefor by de-watering, drying or thickening with addition of chemical agents
-
- C—CHEMISTRY; METALLURGY
- C02—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F2101/00—Nature of the contaminant
- C02F2101/10—Inorganic compounds
- C02F2101/20—Heavy metals or heavy metal compounds
Landscapes
- Engineering & Computer Science (AREA)
- Life Sciences & Earth Sciences (AREA)
- Environmental & Geological Engineering (AREA)
- Chemical & Material Sciences (AREA)
- Hydrology & Water Resources (AREA)
- Water Supply & Treatment (AREA)
- Organic Chemistry (AREA)
- Mechanical Engineering (AREA)
- Soil Sciences (AREA)
- Chemical Kinetics & Catalysis (AREA)
- General Chemical & Material Sciences (AREA)
- Treatment Of Sludge (AREA)
Abstract
The present invention relates to a kind of dystopys suitable for clayed soil pollution amelioration to elute prosthetic device and restorative procedure.Prosthetic device includes the soil particle diameter classification being made of wet crusher, collection stock tank, roller solution mud machine, Wet oscillating screen, collecting tank etc. and slurrying unit, the elution be made of elution slot, mud concentration basin, centrifugal dehydrator etc. and dewatering unit;The treatment unit for waste water that pond, effluent settling chamber etc. form is combined by waste water reaction, the sludge treating block being made of sludge storage pool, filter press etc.;It further include the constant pressure water supply unit and medicament configuration unit of auxiliary.Restorative procedure includes broken, slurrying, screening, elution, concentration, dehydration and matched wastewater treatment, Treatment of Sludge, water supply and dosing.Dystopy elution prosthetic device and restorative procedure are primarily adapted for use in each heavy metal species including clayed soil, organic or combined contamination soil reparation, have the advantages that applied widely, repairing effect is stable, operation operation is easy, wastewater recycle rate is high.
Description
Technical field
The invention belongs to contaminated sites recovery technique fields, and in particular to a kind of to can apply to including clayed soil
Each heavy metal species, organic or combined contamination soil reparation dystopy elution prosthetic device and restorative procedure.
Background technique
Soil is the basic eco-environmental elements of composition natural ecosystems and the substance base that the mankind depend on for existence and development
Plinth.Aggravation with mankind's activity to natural environment influence, produced pollution object is possible to logical during people's production and living
Cross various approach and enter soil, and be more than the receiving and detergent power of soil itself, so as to cause soil natural functional disturbance with
And the soil contamination problem that soil quality deteriorates, and then serious adverse effect may be generated to neighbouring human body and surrounding enviroment.
Therefore, it is necessary to take reasonable technological means to carry out contaminated soil remediation, to effectively control human body caused by soil pollution
Health and Ecological Environment Risk.
It is to dig out contaminated soil from contaminated area and be transferred to neighboringly that soil heterotopic, which elutes recovery technique,
In point or reactor, using water or other eluents, increased by grading, acidification dissolution, organic chelated or surfactant
The effects of molten, separates serious pollution soil constitution or the pollutant in soil is transferred to liquid phase from solid phase, then to containing pollutant
The soil restoring technology that is handled of leacheate.Soil heterotopic elution belongs to physical chemistry recovery technique, can be used for handling
Polluter includes heavy metal and half volatile organic contaminant, difficult volatile organic contaminant etc., has flexible operation, process
Controllably, the advantages that speed is fast, and soil whereabouts is extensive after reparation is repaired.
However, traditional soil heterotopic elution means are dirty for big partial size rank according to existing research and application at present
The reparation more economical and effective of soil is contaminated, the pollutant in gravel, sand, fine sand and similar soil is easier cleaned come out
And rehabilitation cost is controllable, and the then more difficult cleaning of the pollutant in the clayed soil of the small particles rank such as silty clay or clay, and
Rehabilitation cost is higher.It is reached generally, for particulate in soil (generally referring to powder/clay of the partial size less than 63-75 μm) content
The clayed soil even higher to 25%~30%, the effect and cost of traditional soil heterotopic elution all no longer have advantage.
Therefore, it is necessary to develop a kind of economical and effective, the dystopy of safety and stability elution reparation side for clayed soil pollution
Method and device.
Summary of the invention
It is an object of the invention to be directed to deficiency of the existing soil heterotopic elution technique on clayed soil pollution amelioration, mention
Prosthetic device and restorative procedure are eluted for a kind of dystopy suitable for clayed soil pollution amelioration.
The present invention can be realized by the inclusion of the technical solution of following steps:
A kind of dystopy suitable for clayed soil pollution amelioration of the present invention elutes prosthetic device, it includes soil particle diameter classification
With slurrying unit, Soil leaching and dewatering unit;
The soil particle diameter classification and slurrying unit, comprising: wet crusher, collection stock tank, roller solution mud machine, wet type vibration
Dynamic sieve, collecting tank;It is provided with high pressure water flushing pipeline at the feed hopper of wet crusher, collection slurry is provided with below wet crusher
Slot collects and is equipped with blender (translator and agitating paddle), Pulp pump in stock tank;Slurry pump discharge is connect with solution mud machine entrance;Roller
The drums inside for solving mud machine is equipped with high pressure water flushing pipeline;The outlet of roller solution mud machine is provided with conical screen;It is set below conical screen
It is equipped with Wet oscillating screen;Collecting tank is provided with below Wet oscillating screen;
The Soil leaching and dewatering unit, comprising: elution slot, mud concentration basin, centrifugal dehydrator;Sump bottom
Slurry outlet is connect with elution slot;It elutes slot and is equipped with elution adding of agent mouth;It elutes trench bottom slurry outlet and mud is concentrated
The connection of pond entrance;It elutes slot and is equipped with elution adding of agent mouth;(being additionally provided with quenched adding of agent mouth on elution slot);Mud concentration
The bottom concentration slurry outlet in pond is connect by pump with centrifugal dehydrator entrance;The purified liquor outlet and separating liquid collection of centrifugal dehydrator
The connection of liquid bath entrance;The outlet of separating liquid collecting tank is connect with mud concentration basin entrance;(i.e. heavy phase is solid for the slag-drip opening of centrifugal dehydrator
Body particle discharge ports) it is connect with belt conveyor.
Further, dystopy elution prosthetic device further includes treatment unit for waste water, sludge treating block;
The treatment unit for waste water, comprising: waste water reaction combines pond, effluent settling chamber, reuse sink;Mud concentration basin
Top concentration purified liquor outlet combined with waste water reaction pond waterwater entrance connect;The flocculation tank top in waste water reaction combination pond goes out
Mouth is connect with the entrance of effluent settling chamber;The bottom of effluent settling chamber is sludge bucket, and sludge bucket outlet is equipped with mud valve;Waste water
The upper clear supernate outlet of sedimentation basin is connect with reuse sink entrance;
The sludge treating block, comprising: sludge storage pool, filter press, pressing filtering liquid collecting tank;The bottom of effluent settling chamber
Sludge bucket outlet is connected by the sludge inlet of mud valve and sludge storage pool;The outlet of sludge storage pool base sludge and filter press
Sludge inlet connection;The pressing filtering liquid outlet of filter press is connect with pressing filtering liquid collecting tank entrance;The outlet of pressing filtering liquid collecting tank passes through pump
The waterwater entrance connection in pond is combined with waste water reaction.
Further, the wet crusher is the wet crusher of hammer;The roller solution mud machine is laterally to set
The roller solution mud machine for the drum type brake set, i.e. cylinder solution mud machine;High pressure is equipped on the cylinder interior central axis of cylinder solution mud machine
Water flushing pipeline is provided with several spray-holes in high pressure water flushing pipeline;The cylinder inner wall of cylinder solution mud machine is equipped with deflector;Cylinder
The cylinder outlet of solution mud machine is provided with conical screen;Conical screen and Wet oscillating screen are respectively provided with high pressure water flushing pipeline.
Further, waste water reaction combination pond is divided into three lattice, and the first lattice are dosing reactive tank, and the second lattice are coagulation
Slot, third lattice are flocculation tank, and every lattice are provided with blender (translator and agitating paddle);Dosing reactive tank is equipped with alkali/huge sum of money
The chemical agent for belonging to the removable pollutant such as agent for capturing/precipitating reagent or oxidant adds mouth, and coagulation tank is equipped with coagulant dosage
Mouthful, flocculation tank is equipped with flocculant concentration mouth.
Further, the sludge storage pool is equipped with flocculant concentration mouth;Blender (electrification is provided in sludge storage pool
Machine and agitating paddle);The filter press is Chamber Type Diaphragm Filter Press;The Chamber Type Diaphragm Filter Press have automatic pulling plate, blow and
The miscellaneous functions such as squeezing;The Chamber Type Diaphragm Filter Press includes high pressure water circular press subsystem;The prosthetic device further includes
Cycle of higher pressure water system;The cycle of higher pressure water system includes cycle of higher pressure water pot, high pressured water circuling pump (high-pressure compressing water
Pump);Cycle of higher pressure water pot and the high pressure water circular press subsystem of Chamber Type Diaphragm Filter Press connect: the high pressure of cycle of higher pressure water pot
It squeezes water out to connect by high pressured water circuling pump and the high-pressure compressing water water inlet of Chamber Type Diaphragm Filter Press, van-type diaphragm filters pressing
The high-pressure compressing water water outlet of machine is connect with the high-pressure compressing water water return outlet of cycle of higher pressure water pot.
Further, sump bottom slurry outlet is connect by pump with the mud entrance of elution slot;(elution slot can also be set
It sets below collecting tank, sump bottom mud directly can also be discharged into elution slot by the opening and closing gravity of spoil disposal slurry valve);Elution
Trench bottom slurry outlet is connect by pump with mud concentration basin;(mud concentration basin may also be arranged below elution slot, elute slot bottom
Portion's mud directly can also be discharged into mud concentration basin by the opening and closing gravity of spoil disposal slurry valve).
Further, elution slot is divided into three regions, and the top in first region is connected with the top of Two Areas,
The lower part of Two Areas is connected with trizonal lower part;Each region is equipped with blender (translator and stirring
Paddle);First region is equipped with quenched adding of agent mouth, and third region is equipped with elution adding of agent mouth.
Further, dystopy elution prosthetic device further includes the constant pressure water supply unit and medicament configuration list of auxiliary
Member;
The medicament configuration unit include: eluent grug feeding jar group, adjusting material grug feeding jar group, alkali/heavy metal chelating agent/
Precipitating reagent grug feeding jar group, coagulant grug feeding jar group and flocculant grug feeding jar group;Above-mentioned each grug feeding jar group includes connected up and down
Two-stage, higher level are medicament preparing tank, and junior is medicament storage jar (connecting with medication administration device);Eluent grug feeding jar group and elution slot
On elution adding of agent mouth connection;Adjusting material grug feeding jar group is connect with the quenched adding of agent mouth on elution slot;Chemical agent
The chemical agent that grug feeding jar group combines on the dosing reactive tank in pond with waste water reaction adds mouth connection, coagulant grug feeding jar group and useless
Coagulant dosage mouth connection on the coagulation tank in water reaction combination pond, flocculant grug feeding jar group combine the flocculation in pond with waste water reaction
Flocculant concentration mouth connection on slot.Electronic feed driving can also be set in medicament configuration region, be driven a vehicle by electronic feed auxiliary
Work of helping others carry out medicament promotion with add.
The constant pressure water supply unit includes two sets of constant pressure water supply equipments, respectively tap water constant pressure supply equipment and reuse
Water constant pressure water supply equipment;Tap water constant pressure supply equipment includes originally water pot, tap water constant pressure water supply pump group;Originally water pot passes through
Tap water constant pressure water supply pump group is connect with the water inlet of each medicament preparing tank respectively, and there are also one for the outlet of tap water constant pressure water supply pump group
The high pressure water of road and Wet oscillating screen rinse piping connection, tap water constant pressure water supply pump group outlet separately have all the way with cycle of higher pressure water
The high-pressure water inlet of tank connects;Recycle-water constant pressure water supply equipment includes reuse sink, recycle-water constant pressure water supply pump group, reuse sink
Pass through the recycle-water constant pressure water supply pump group high pressure water flushing pipeline with wet crusher, roller solution mud machine, Wet oscillating screen respectively
Connection.
A kind of Ex-situ washing remediation suitable for clayed soil pollution amelioration of the present invention, including soil breaking, slurrying,
The key steps such as screening, and elution, concentration and dehydration;Its main processes is as follows: soil is poured wet by high-pressure washing water
Formula crusher, by cutting and crushing at short grained thick mud;Thick mud is collected by collection stock tank, is lifted into circle by Pulp pump
Cylinder solution mud machine is dispersed into slime water by further disintegration by the sluicing and machine cuts of cylinder solution mud machine;Slime water from
The cylinder tail end of cylinder solution mud machine is discharged into conical screen and is tentatively sieved, and the large granular impurity on sieve greater than 5mm is by high pressure washing
Water rinses discharge, and sieving mud gravity falls into Wet oscillating screen and sieved again, high greater than the little particle impurity of 1mm on sieve
It presses flushing water to rinse discharge, after sieving mud falls into vibrating screen collecting tank, elution slot is promoted to by pump, then in elution slot
Elution occurs with eluent to react, enters mud concentration basin later, through gravity concentration, mud is concentrated and enters centrifugal dehydrator progress
Dehydration;It is discharged after the dewatered sludgd deposition of centrifugal dehydrator from mud discharging mouth, formation dehydration soil is simultaneously defeated by belt conveyor
It send to staging area to wait as soil after repairing and check and accept;The clear liquor overflow deviate from through centrifugal dehydrator enters separating liquid collection
Liquid bath is promoted through pump and is back to mud concentration basin;
Concentration clear liquid through mud concentration basin gravity concentration enters the waste water reaction combination pond for the treatment of unit for waste water;In waste water
After successively reacting with chemical agent, coagulant, flocculant in reaction combination pond, effluent settling chamber is flowed into, in gravity
Under, the solid particle (sludge) of heavy phase, which is settled and is deposited in the sludge bucket of effluent settling chamber, is then discharged into sludge storage pool;Light phase
Clear liquor overflow enter reuse sink, and provide reuse to the whole series elution prosthetic device by recycle-water constant pressure water supply pump group
Water;Sludge in sludge storage pool keep in and carry out it is quenched, it is quenched after sludge filter-press dehydration is completed by Chamber Type Diaphragm Filter Press
And press dewatering, dewatered sludge are discharged into bucket, pack and shift, outward transport disposition;The pressing filtering liquid that filter-press dehydration generates is then in filters pressing
Liquid collecting tank is back to waste water reaction and is combined pond and handled again after collecting by pump conveying.
Further, Ex-situ washing remediation of the invention further includes subsequent matched wastewater treatment, Treatment of Sludge etc.
Step;It further include matched constant pressure water supply, medicament is prepared and dosing.
A kind of Ex-situ washing remediation suitable for clayed soil pollution amelioration of the present invention, including following technique: (1) native
Earth grain size grading and pulping process;(2) Soil leaching and dewatering process;(3) waste water treatment process;(4) sludge treatment technique;
It (5) further include the constant pressure water supply technique and medicament configuration technique assisted;Wherein, soil particle diameter classification and pulping process mainly include
Wet type is broken, solves the process sections such as cement slurry making and solid-liquid screening;Soil leaching with dewatering process mainly include elution react, mud it is dense
The multilevel processing technologies such as contracting and separating and dehydrating;Waste water treatment process mainly includes dosing reaction, coagulation-flocculation and gravity precipitating etc.
Multilevel processing technology;Sludge treatment technique mainly includes that sludge is temporary, dosing is quenched and the process sections such as filter-press dehydration.
Ex-situ washing remediation suitable for clayed soil pollution amelioration of the invention, specific embodiment are as follows:
(1) soil particle diameter classification is with slurrying (i.e. broken, slurrying, screening): contaminated soil is miscellaneous by pretreatment removal bulk
Object (> 8cm), after being crushed big lumps, to wet crusher feed hopper uniform feeding;High pressure water flushing pipe is set in feed hopper
Road is smoothly fallen into wet crusher by high-pressure washing water assisted soil;Contaminated soil and high-pressure washing water are in the wet of hammer
Under the machine cuts effect of formula crusher, the thick mud of smaller particle size is formed;Thick mud is collected by collection stock tank, passes through slag
Stock pump is lifted into cylinder solution mud machine;Blender is set in collection stock tank, it is continuous or open on demand, avoid the impurity such as building waste with
And the soil particle agglomerate of relative bulk is in slot bottom over-deposit.Into cylinder solution mud machine thick mud in cylinder high pressure washing
The sluicing and machine cuts double action of water, the building waste impurity therein for being stained with soil particle smoothly realize impurity
With the dispersion of soil particle, the soil particle agglomerate of relative bulk therein, which further disintegrates, is dispersed to complete sliming, then
Through tentatively sieving with the conical screen of cylinder outlet connection, removal is greater than the large granular impurity of 5mm;The sieving mud gravity of conical screen
Wet oscillating screen is fallen into, further screening removal is greater than the little particle impurity of 1mm;It is logical at conical screen and Wet oscillating screen
Excessively high blow wash pipeline is adequately rinsed and is washed to the size particles impurity screened out using flushing water;By setting
Collecting tank below Wet oscillating screen is received and is completed through broken, slurrying and screening Soil slurry;Mud in collecting tank exists
Under the control of liquid level signal, the elution slot of subsequent Soil leaching technique is promoted to by pumping.
(2) Soil leaching and dehydration (elute, be concentrated and be dehydrated): the Soil slurry for entering elution slot is made in mechanical stirring
Under, it is sufficiently mixed contact with the eluent of investment elution slot and elution occurs and react.It is dirty according to target in soil to elute medicament
The difference of object is contaminated, the surfactants lists such as chelating agents or lauryl sodium sulfate such as hydrochloric acid, acetic acid, EDTA, citric acid may be selected
Solely or it is used in compounding.Under the action of eluent, the separated from contaminants being present in soil particle solid phase enters in leacheate.It is complete
Soil slurry at elution reaction enters mud concentration basin, and by gravity concentration, mud is concentrated in subsequent centrifugal dewatering technology section
(centrifugal dehydrator) completes dehydration, and concentration clear liquid enters the waste water reaction combination for the treatment of unit for waste water as waste water to be processed
Pond.The mud after reacting is come into full contact with first after gravity concentration technique is concentrated with eluent, then is carried out by centrifugal dehydrator
Mechanical dehydration reduces wastewater treatment load to increase dehydration efficiency.Under the action of centrifugal dehydrator operates centrifugal force, concentration
Mud formed sedimentation liquid and and then be separated into solid heavy phase and liquid light phase, after solid particle (sludge) deposition of heavy phase constantly from
Slag-drip opening (mud discharging mouth) discharge forms dehydration soil and is delivered to staging area as soil after repairing by belt conveyor and waits
It checks and accepts;The clear liquor overflow of light phase enters separating liquid collecting tank, is promoted through pump and is back to mud concentration basin.
(3) wastewater treatment: waste water enters the first lattice dosing reactive tank in waste water reaction combination pond, according to soil target stains
The difference of object and the eluent added, selection add chemical agent alkali/heavy metal chelating agent of corresponding removable pollutant/heavy
Shallow lake agent or oxidant, under the action of mechanical stirring, chemical agent is sufficiently mixed with waste water to be contacted and reacts, heavy metal-polluted
Dye object forms solid phase under the action of alkali/heavy metal chelating agent/precipitating reagent and separates with eluent ingredient, and organic pollutant is aoxidizing
Redox degradation occurs under the action of agent;The second lattice for completing the waste water gravity inflow waste water reaction combination pond of dosing reaction are mixed
Solidifying slot, third lattice flocculation tank, difference dosing coagulant, flocculant, so that the solid particle being likely to form after waste water dosing reaction
De- steady and flocculation is agglomerating;The waste water gravity for completing coagulation-flocculation flows into effluent settling chamber, under the effect of gravity, the solid of heavy phase
Grain is settled and is deposited in the sludge bucket of effluent settling chamber, is discharged into sludge storage pool by the opening and closing gravity of mud valve;Light phase
Clear liquor overflow enters reuse sink, and provides reuse to the whole series elution prosthetic device by recycle-water constant pressure water supply pump group
Water.Waste water after wastewater treatment can elute prosthetic device in the whole series with fully recovering.
(4) Treatment of Sludge: the sludge that wastewater treatment generates is kept in sludge storage pool, and stirring is provided in sludge storage pool
Machine.According to sludge storage number, before carrying out sludge press filtration dehydration, add flocculation medicament to sludge storage pool and open machinery and stir
It is quenched to mix completion sludge.Quenched good sludge completes the dehydration procedures such as filters pressing, squeezing and drying by Chamber Type Diaphragm Filter Press, takes off
Sewage sludge is discharged into bucket, is packed into jumbo bag and is simultaneously transferred to solid waste staging area, according to the property of sludge, periodically as hazardous waste or
General industry waste arrangement has the outward transport disposition of qualification unit;The pressing filtering liquid generated is dehydrated then after the collection of pressing filtering liquid collecting tank by pumping
The dosing reactive tank that conveying is back to waste water reaction combination pond is handled.
(5) constant pressure water supply and medicament configuration: constant pressure water supply includes that tap water supply and recycle-water supply water;Constant pressure water supply technique
It is realized by two sets of constant pressure water supply equipments, respectively tap water and recycle-water constant pressure water supply equipment, including originally water pot/recycle-water
Tank, tap water/recycle-water constant pressure water supply pump group and Isobarically Control cabinet etc., tap water are mainly used for medicament configuration and elute water supply
It is spare, tap water supply provided by originally water pot, tap water constant pressure water supply pump group each medicament preparing tank configuration medicament water,
High pressure washing water, the cycle of higher pressure water pot of Wet oscillating screen supply water (i.e. the high-pressure compressing water of Chamber Type Diaphragm Filter Press);It returns
The waste water that Soil leaching generates mainly is back to soil slurrying after processing with water, recycle-water is supplied water through reuse water pot, returned
The high pressure washing water of wet crusher, roller solution mud machine, Wet oscillating screen is provided with water constant pressure water supply pump group;Medicament configuration packet
Include medicament preparation, medicament storage and dosing;Medicament configuration is realized by the corresponding grug feeding jar group of various medicaments, including eluent, tune
Matter agent, alkali/heavy metal chelating agent/precipitating reagent, coagulant and flocculant etc., grug feeding jar group are divided into two-stage up and down, and higher level is medicament
Preparing tank, junior are medicament storage jar;The preparation of various medicaments carries out in each medicament preparing tank respectively;It can be according to operation just
Benefit matches lower mode in selection.
Beneficial effects of the present invention:
Dystopy elution prosthetic device of the invention and restorative procedure are primarily adapted for use in various heavy including clayed soil
Metal, organic or combined contamination soil reparation, with applied widely, repairing effect is stable, operation operation is easy, waste water returns
The features such as high with rate.
Compared with existing soil heterotopic elutes recovery technique, the present invention has the advantages that
(1) wet type crushing process is used.It is acted on by the machine cuts of crusher, by soil group common in clayed soil
Block is stained with the construction waste crushing of soil particle into uniformly tiny size, be next step solution cement slurry making create it is good
Condition, largely avoid tradition elution sieving technology using aggravation of soil or be stained with the building waste of soil particle as
A possibility that large granular materials are retained.
(2) using the clay sizing process of solution.When solving the operating of mud machine, rotary drum makes in cylinder mud constantly roll agitation, is leading
Under the sluicing and machine cuts effect of flowing scraper plate, the aggravation of soil in mud further disintegrates until complete sliming;Circle
High pressure water flushing pipeline is run through at cylinder center, carries out auxiliary solution mud by hydrodynamic cleaning;It is good to solve homogenization mud made of mud
Realize the dispersion of size particles in soil.
(3) two-stage solid-liquid screening technique is used.The homogenization mud that broken solution mud is formed, successively by solution mud machine tail end
Conical screen and Wet oscillating screen carry out solid-liquid screening, will be greater than the large granular impurity of 5mm and the little particle impurity greater than 1mm respectively
It is removed after high pressure washing water washing, reduces subsequent Soil leaching processing total amount, and reduce the load of single-stage screening, simultaneously
Large granular impurity and little particle impurity after washed can direct safe utilization, without being further processed.
(4) dosing elution technique is used.The homogenization mud of screened decrement fills in elution slot with corresponding eluent
Divide haptoreaction, soil pollutant is separated from soil particle solid phase and is entered in leacheate, realizes pollutant really from soil
The reparation purpose removed in ontology subtracts better than the contaminated soil in common soil Ex-situ washing remediation based on sieve classification
Hold technique.
(5) gravity concentration and centrifugal dewatering technology are used.The mud of completion elution reaction first forms after gravity concentration dense
Contracting mud, then soil water desorption is carried out by centrifugal dehydrator.Compared with other dewatering process, gravity concentration pretreatment is substantially reduced
The hydraulic loading of subsequent mechanical dehydration, and the dewatering of mud is improved, after mechanical dehydration soil moisture content is lower.This
Outside, centrifugal dehydration has many advantages, such as to continuously run, interval is rinsed and washing water quantity is few, charging moisture content tolerance is high, and
Under the conditions of the feed mud of special properties (particle diameter distribution, partial size density etc.), exists and do not have to add flocculation medicament is quenched to obtain
A possibility that obtaining preferable centrifugal dehydration effect.
(6) waste water treatment, recovery and utilization is used.The pollutant that wastewater treatment will remove out out of soil particle in leacheate
Again solidification generates precipitating (heavy-metal contaminated soil) or direct oxidation degradation (organic material contaminated soil), and treated, and waste water can
Fully recovering does not generate efflux wastewater when soil slurrying, normal operation.
Detailed description of the invention
Fig. 1 is the stream that a kind of dystopy suitable for clayed soil pollution amelioration of the present invention elutes prosthetic device and restorative procedure
Cheng Tu;
Fig. 2 is the section view for being equipped with high pressure water flushing pipeline in the present invention on the cylinder interior central axis of cylinder solution mud machine
Figure.
In figure: 1, wet crusher 2, feed hopper 3, collection stock tank 4, blender 5, Pulp pump 6, cylinder solution mud machine 7,
Cylinder 8, conical screen 9, Wet oscillating screen 10, vibrating screen collecting tank 11, elution slot 12, mud concentration basin 13, centrifugation are de-
Water dispenser 14, belt conveyor 15, separating liquid collecting tank 16, waste water reaction combine pond 17, dosing reactive tank 18, coagulation tank
19, flocculation tank 20, effluent settling chamber 21, sludge bucket 22, sludge storage pool 23, reuse sink 24, recycle-water constant pressure water supply pump
Group 25, Chamber Type Diaphragm Filter Press 26, cycle of higher pressure water pot 27, pressing filtering liquid collecting tank 28, originally water pot 29, tap water are permanent
Press water supply pump group 30, eluent grug feeding jar group 31, adjusting material grug feeding jar group 32, alkali/heavy metal chelating agent/precipitating reagent dosing
Tank group 33, coagulant grug feeding jar group 34, flocculant grug feeding jar group 35, electronic feed driving 36, high pressured water circuling pump 37,
High pressure water flushing pipe 38, high-pressure washing water
Specific embodiment
Specific implementation form of the invention is described in detail with reference to the accompanying drawings and examples.Protection model of the invention
It encloses and is not limited to specific embodiment, the range that claim of being subject to is defined.
Embodiment 1
As shown in Figure 1, a kind of dystopy suitable for clayed soil pollution amelioration of the present invention elutes prosthetic device, it includes soil
Earth grain size grading and slurrying unit, Soil leaching and dewatering unit, treatment unit for waste water, sludge treating block;
The soil particle diameter classification and slurrying unit, comprising: wet crusher 1, the collection stock tank 3, cylinder solution mud of hammer
Machine 6 (the roller solution mud machine for the drum type brake being laterally arranged), Wet oscillating screen 9, vibrating screen collecting tank 10;The charging of wet crusher
High pressure water flushing pipeline (connecting with 24 outlet conduit of recycle-water constant pressure water supply pump group) is provided in bucket 2;Below wet crusher
It is provided with collection stock tank 3, collects and is equipped with blender 4 (translator and agitating paddle), Pulp pump 5 in stock tank 3;The outlet of Pulp pump 5 and cylinder
Solve the connection of 6 entrance of mud machine;High pressure water flushing pipeline is provided on the cylinder interior central axis of cylinder solution mud machine 6 (such as Fig. 2 institute
Show, which protrudes into the cylinder interior of cylinder solution mud machine 6, runs through entire central axis, which rinses
It is provided with several spray-holes on pipeline 37, high-pressure washing water 38 can be ejected against cylinder inner wall;The high pressure water flushing pipe 37 with
24 outlet conduit of recycle-water constant pressure water supply pump group connection);7 inner wall of cylinder of cylinder solution mud machine 6 is equipped with deflector;Cylinder solution mud machine
6 outlet of cylinder 7 is provided with conical screen 8;Wet oscillating screen 9 is provided with below conical screen 8;It is provided with below Wet oscillating screen 9
Collecting tank, i.e. vibrating screen collecting tank 10;High pressure recycle-water flushing pipeline is equipped with above Wet oscillating screen 9 (to supply with recycle-water constant pressure
The connection of 24 outlet conduit of water pump group), while being additionally provided with high pressure tap water flushing pipeline and (being exported with tap water constant pressure water supply pump group 29
Pipeline connection);The high pressure washing sprinkler head of 9 top of Wet oscillating screen has multiple groups, wherein last group connection high pressure tap water punching
Pipeline is washed, last washing (water purification washing) together is carried out, it can be achieved that optimal cleaning effect by tap water;Cylinder solution mud machine
High pressure tap water flushing pipeline (connecting with 29 outlet conduit of tap water constant pressure water supply pump group) is equipped with above 6 conical screen 8.
The Soil leaching and dewatering unit, comprising: elution slot 11, mud concentration basin 12, centrifugal dehydrator 13;Elution
Slot 11 is located at 10 lower section of vibrating screen collecting tank;Elution slot 11 is divided into three regions being connected, the top in first region and the
The top of Two Areas is connected, and the lower part of Two Areas is connected with trizonal lower part;Each region is equipped with
Blender (translator and agitating paddle);First region is equipped with quenched adding of agent mouth, and third region is equipped with elution medicine
Agent adds mouth;Elution 11 bottom slurry outlet of slot is connect by pump with mud concentration basin 12;The bottom of mud concentration basin 12 is concentrated
Slurry outlet is connect by pump with 13 entrance of centrifugal dehydrator;The purified liquor outlet of centrifugal dehydrator 13 enters with separating liquid collecting tank 15
Mouth connection;The outlet of separating liquid collecting tank 15 is connect with 12 entrance of mud concentration basin;(i.e. heavy phase is solid for the slag-drip opening of centrifugal dehydrator 13
Body particle discharge ports) it is connect with 14 entrance of belt conveyor;
The treatment unit for waste water, comprising: waste water reaction combines pond 16, effluent settling chamber 20, reuse sink 23;Waste water
Reaction combination pond 16 is divided for three lattice, and the first lattice are dosing reactive tank 17, and the second lattice are coagulation tank 18, and third lattice are flocculation tank 19,
Every lattice are provided with blender (translator and agitating paddle);Dosing reactive tank is equipped with alkali/heavy metal chelating agent/precipitating reagent or oxygen
The chemical agents such as agent add mouth, and coagulation tank 18 is equipped with coagulant dosage mouth, and flocculation tank 19 is equipped with flocculant concentration mouth.Mud
The waterwater entrance that the top concentration purified liquor outlet of slurry concentration basin 12 combines pond 16 with waste water reaction (is located at the first lattice dosing reactive tank
17 tops) connection;19 upper outlet of flocculation tank in waste water reaction combination pond 16 is connect with the entrance of effluent settling chamber 20, and waste water is heavy
The bottom in shallow lake pond 20 is set there are four sludge bucket 21, and each outlet of sludge bucket 21 is equipped with mud valve;The top of effluent settling chamber 20
Purified liquor outlet is connect with 23 entrance of reuse sink;
The sludge treating block, comprising: sludge storage pool 22, Chamber Type Diaphragm Filter Press 25, pressing filtering liquid collecting tank 27;It is useless
The base sludge bucket outlet in water sedimentation pond 20 is connect by mud valve with the sludge inlet of sludge storage pool 22;22 bottom of sludge storage pool
Portion's sludge outlet is connect with 25 entrance of Chamber Type Diaphragm Filter Press;Sludge storage pool 22 is equipped with flocculant concentration mouth;Sludge storage pool 22
In be provided with blender (translator and agitating paddle);Chamber Type Diaphragm Filter Press 25 has the auxiliary such as automatic pulling plate, air blowing and squeezing
Function;The pressing filtering liquid outlet of Chamber Type Diaphragm Filter Press 25 is connect with 27 entrance of pressing filtering liquid collecting tank;Pressing filtering liquid collecting tank 27 exports
Waterwater entrance (i.e. 17 top of the first lattice dosing reactive tank) connection in pond 16 is combined with waste water reaction by pumping.
The elution prosthetic device further includes cycle of higher pressure water system;The cycle of higher pressure water system includes that high pressure is followed
Ring water pot 26, high pressured water circuling pump 36 (i.e. high-pressure compressing water pump);Chamber Type Diaphragm Filter Press 25 includes high pressure water circular press
System;Cycle of higher pressure water pot 26 connect (cycle of higher pressure water pot with the high pressure water circular press subsystem of Chamber Type Diaphragm Filter Press 25
26 high-pressure water inlet and tap water constant pressure water supply pump group 29 outlet connects, and the high-pressure compressing water out of cycle of higher pressure water pot 26 is logical
It crosses high pressured water circuling pump 36 to connect with the high-pressure compressing water water inlet of Chamber Type Diaphragm Filter Press 25, the height of Chamber Type Diaphragm Filter Press 25
Pressure squeeze water water outlet is connect with the high-pressure compressing water water return outlet of cycle of higher pressure water pot 26).Pass through 36 (high pressure of high pressured water circuling pump
Squeeze water pump) conveying 1.0~1.3MPa high-pressure compressing water, make high-pressure compressing water enter Chamber Type Diaphragm Filter Press 25 squeezing filter
Between plate and diaphragm, the gap of filter cake is destroyed using two-dimentional deflecting shear pressure filtering means dehydration, is changed grain structure, is kept its heavy
New arrangement, makes the water content of filter cake reach minimum.
The elution prosthetic device further includes the medicament configuration unit of auxiliary;The medicament configuration unit includes: leaching
Lotion grug feeding jar group 30, adjusting material grug feeding jar group 31, alkali/heavy metal chelating agent/precipitating reagent grug feeding jar group 32, coagulant grug feeding jar
Group 33 and flocculant grug feeding jar group 34;Above-mentioned each grug feeding jar group includes two-stage connected up and down, and higher level is medicament preparing tank, under
Grade is medicament storage jar;Medicament configuration region be provided with the driving of electronic feed can indirect labor carry out the promotion of medicament and add.
The elution prosthetic device further includes the constant pressure water supply unit of auxiliary;The constant pressure water supply unit includes two sets
Constant pressure water supply equipment, respectively tap water constant pressure supply equipment and recycle-water constant pressure water supply equipment;Tap water constant pressure supply equipment
Including originally water pot 28, tap water constant pressure water supply pump group 29;Originally water pot 28 by tap water constant pressure water supply pump group 29 respectively with
Each medicament preparing tank (i.e. eluent grug feeding jar group 30, adjusting material grug feeding jar group 31, alkali/heavy metal chelating agent/precipitating reagent grug feeding jar
Group 32, higher level's medicament preparing tank of coagulant grug feeding jar group 33, flocculant grug feeding jar group 34) water inlet connection, there are also all the way
Piping connection is rinsed with the high pressure water of Wet oscillating screen 9, separately has and is connect all the way with the high-pressure water inlet of cycle of higher pressure water pot 26;It returns
It include reuse sink 23, recycle-water constant pressure water supply pump group 24 with water constant pressure water supply equipment, reuse sink 23 passes through recycle-water constant pressure
Water supply pump group 24 rinses piping connection with the high pressure water of wet crusher 1, cylinder solution mud machine 6, Wet oscillating screen 9 respectively.
A kind of Ex-situ washing remediation suitable for clayed soil pollution amelioration of the present invention, it includes following technique: (1)
The soil particle diameter classification and pulping process that, the solution process sections such as cement slurry making and solid-liquid screening broken by wet type form;(2) anti-by eluting
It answers, mud is concentrated and the Soil leaching and dewatering process of the process sections such as separating and dehydrating composition;(3) by dosing reaction, coagulation-flocculation
The waste water treatment process formed with process sections such as gravity precipitatings;(4) temporary by sludge, dosing is quenched and the process sections such as filter-press dehydration
The sludge treatment technique of composition;It (5) additionally include the constant pressure water supply technique and medicament configuration technique assisted;Wherein, (1) wet type
Crushing process is realized by wet crusher;Clay sizing process is solved by the interior circle for setting central high pressure water flushing pipeline and inner wall deflector
Cylinder solution mud machine realizes that the sluicing and machine cuts when by solution mud machine cylinder operating act on, and solves aggravation of soil further
Body is dispersed into slime water;Two-stage solid-liquid screening technique is realized jointly by cylinder solution mud machine and Wet oscillating screen, is solved in mud machine
Finely dispersed mud is discharged into conical screen from cylinder tail end and is tentatively sieved, and the large granular impurity on sieve greater than 5mm is through high pressure
Flushing water is rinsed and is discharged after washing, and sieving mud gravity falls into Wet oscillating screen;High pressure water flushing pipe is set above vibrating screen
Road is further crushed soil particle by hydrodynamic cleaning, and the little particle impurity for being greater than 1mm on sieve is rinsed and is washed.
(2) elution reaction process is realized by elution slot 11;Mud concentration technology is realized by mud concentration basin 12;Separating and dehydrating technique by from
Heart dewaterer 13 is realized.(3) dosing reaction process, coagulation-flocculation technique combine pond 16 by waste water reaction and realize;Gravity precipitator
Skill is realized by effluent settling chamber 20;(4) sludge keeps in technique, dosing hardening and tempering process is realized by sludge storage pool 22;Filter-press dehydration work
Skill is realized by Chamber Type Diaphragm Filter Press 25.(5) constant pressure water supply technique by originally water pot 28, tap water constant pressure water supply pump group 29, return
It is realized with sink 23, recycle-water constant pressure water supply pump group 24 etc.;Medicament configuration technique is by each medicament preparing tank and each medicament storage jar
Deng realization.
Ex-situ washing remediation suitable for clayed soil pollution amelioration of the invention, specific embodiment are as follows:
The contaminated soil to be repaired for removing big sundries (> 8cm) by pretreatment, being crushed big lumps, passes through excavator
To 1 feed hopper of hammer wet crusher, 2 uniform feeding, high pressure water flushing pipeline is set in feed hopper 2, passes through the flushing of high pressure water
Assisted soil smoothly falls into the wet crusher 1 of hammer, while part water needed for the broken slurrying of offer.Fall into the wet of hammer
The contaminated soil and flushing water of formula crusher 1 under machine cuts effect, lay equal stress on by the broken thick mud for forming smaller particle size
Power is fallen into crusher collection stock tank 3.Blender 4 is set in crusher collection stock tank 3, and continuous or unlatching on demand avoids building waste
The soil particle agglomerate of equal impurity and relative bulk is in slot bottom over-deposit;The thick mud collected in crusher collection stock tank 3 is logical
It crosses Pulp pump 5 and is lifted into cylinder solution mud machine 6.The cylinder 7 of cylinder solution mud machine 6 is internally provided with deflector, when rotary drum,
Thick mud constantly rolls agitation in cylinder, therein to be stained with soil in the case where the sluicing of deflector and machine cuts act on
The building waste impurity of particle smoothly realizes the dispersion of impurity and soil particle, and the aggravation of soil of relative bulk therein is further
Disintegrate until complete sliming.The outlet of 6 cylinder 7 of cylinder solution mud machine is connected with conical screen 8, solve in mud mud large granular impurity (>
5mm) pass through the screening removal of conical screen 8.In addition, running through on the cylinder interior central axis of cylinder solution mud machine 6 has high pressure water flushing
Pipeline rinses auxiliary solution mud by high pressure water and carries out Washing to the large granular impurity screened out.Solution mud mud crosses taper
Gravity falls into Wet oscillating screen 9 and further sieves and remove little particle impurity (> 1mm) after sieve 8, is arranged above Wet oscillating screen 9
Four groups of high pressure water flushing pipelines, be further crushed by hydrodynamic cleaning soil particle and to sieve upper little particle impurity be rinsed and
Washing.Vibrating screen collecting tank 10 is fallen by the sieving mud of two-stage solid-liquid screening, subsequent elution technique is delivered to by pump.
It is delivered in elution slot 11 by broken, solution mud and the Soil slurry of screening by pumping, setting stirring in elution slot 11
Machine, Soil slurry are sufficiently mixed with the eluent of investment elution slot under mechanical agitation and contact and react.Elute medicine
Agent can be in the chelating agents such as hydrochloric acid, acetic acid, EDTA, citric acid and dodecyl sulphate according to the difference of soil target contaminant
It selects individually or is used in compounding in the surfactants such as sodium;Eluting reaction time is 2-4 hours.Complete the soil of elution reaction
Earth mud is lifted into mud concentration basin 12 by pump, by gravity concentration, be concentrated clear liquid flow into subsequent wastewater treatment system into
Row processing, concentration mud are promoted to centrifugal dehydrator 13 through pump, and under the action of centrifugal dehydrator 13 operates centrifugal force, mud is concentrated
Slurry forms sedimentation liquid and is separated into solid heavy phase and liquid light phase in turn, constantly arranges from slag-drip opening after the solids particles precipitate of heavy phase
Dehydration soil is formed out and staging area is delivered to as soil waiting after repairing by belt conveyor 14 checks and accepts;The clarification of light phase
Liquid flooding enters separating liquid collecting tank 15, is promoted through pump and is back to mud concentration basin 12.
Gravity is discharged into waste water reaction to the waste water that Soil leaching generates after overflow in the form of the concentration clear liquid of mud concentration basin 12
Pond 16 is combined, waste water reaction combination pond 16 is divided for three lattice, and every lattice are respectively provided with blender, and the first lattice are dosing reactive tank 17, according to
Soil target contaminant and the eluent added, selection add corresponding alkali/heavy metal chelating agent/precipitating reagent or oxidant,
Under the action of mechanical stirring, chemical agent is sufficiently mixed with waste water to be contacted and reacts, and heavy metal contaminants are in alkali/heavy metal
It forms solid phase under the action of agent for capturing/precipitating reagent to separate with eluent ingredient, organic pollutant occurs under the action of oxidant
Redox degradation.Second lattice and third lattice in waste water reaction combination pond 16 are respectively coagulation tank 18 and flocculation tank 19, complete to add
The waste water gravity of medicine reaction flows into coagulation tank 18 and flocculation tank 19, respectively dosing coagulant and flocculant, so that waste water dosing is anti-
Should after the de- steady and flocculation of the solid particle that is likely to form it is agglomerating.The waste water gravity for completing coagulation-flocculation flows into effluent settling chamber 20,
Under the effect of gravity, it the solid particles sediment of heavy phase and is deposited in the sludge bucket 21 of effluent settling chamber 20, passes through mud valve
Opening and closing gravity be discharged into sludge storage pool 22;The clear liquor overflow of light phase enters reuse sink 23, and is supplied by recycle-water constant pressure
Water pump group 24 provides recycle-water to the whole series elution prosthetic device.
Sludge (i.e. effluent settling chamber 20 settle down sludge) gravity that wastewater treatment generates be discharged into sludge storage pool 22 into
Row is temporary, and blender is arranged in sludge storage pool 22, according to sludge storage how much, before carrying out subsequent sludge press filtration processing, add wadding
Solidifying medicament simultaneously opens mechanical stirring to carry out sludge quenched.Complete quenched sludge by pump be delivered to Chamber Type Diaphragm Filter Press 25 into
Row dehydration, Chamber Type Diaphragm Filter Press 25 have the miscellaneous functions such as automatic pulling plate, air blowing and squeezing;Chamber Type Diaphragm Filter Press 25
Include high pressure water circular press subsystem, the high pressure water circular press subsystem of cycle of higher pressure water pot 26 and Chamber Type Diaphragm Filter Press 25
System connection, using the cycle of higher pressure water (high-pressure compressing water) in cycle of higher pressure water pot 26 in Chamber Type Diaphragm Filter Press 25 be located at pressure
The material squeezed between filter plate and diaphragm (filter cloth) carries out twice pressing;Chamber Type Diaphragm Filter Press 25 fed before this filters pressing (by into
The pressure of material material squeezes out the moisture in material, between material gap and filter cloth gap to realize material dewatering), filters pressing
After, restart high pressured water circuling pump 36 and carry out diaphragm pressing, cycle of higher pressure water (high-pressure compressing water) is filled with van-type diaphragm
Enter between Filter pressing board and diaphragm (filter cloth) in filter press 25, make diaphragm (filter cloth) inwardly bulging with pressure, form twice pressing,
Moisture in material is further squeezed out;It includes: compression, retrogressing, pressure maintaining, benefit that Chamber Type Diaphragm Filter Press 25, which carries process control,
The movements such as pressure, pulling plate, turnover panel opening and closing, by several dehydration procedure such as filters pressing, squeezing and drying, the sludge for completing dehydration is discharged into mud
Bucket is packed into jumbo bag and is transferred to solid waste staging area, according to sludge quality, periodically pacifies as hazardous waste or general industry waste
Row has the outward transport disposition of qualification unit;The pressing filtering liquid for carrying out sludge dewatering generation through Chamber Type Diaphragm Filter Press 25 then passes through pressing filtering liquid collection
After liquid bath 27 is collected, waste water dosing reactive tank 17 is back to by pump promotion and is handled.
A whole set of elution device includes two sets of constant pressure water supply equipments altogether, except a set of recycle-water constant pressure water supply of wastewater treatment end
Equipment, there are also a set of tap water constant pressure supply equipments;Tap water constant pressure supply equipment includes that originally water pot 28, tap water constant pressure supply
Water pump group 29 and Isobarically Control cabinet are mainly used for medicament configuration and elute the spare of water supply.Medicament configuration is corresponded to by various medicaments
Grug feeding jar group realize that including eluent grug feeding jar group 30, adjusting material grug feeding jar group 31, alkali/heavy metal chelating agent/precipitating reagent add
Medicinal cupping group 32, coagulant grug feeding jar group 33 and flocculant grug feeding jar group 34 etc.;Grug feeding jar group is divided into two-stage up and down, just according to operation
Benefit can choose with lower mode.Medicament configuration region is provided with 35 indirect labors of electronic feed driving and carries out medicament
It is promoted and is added.
Application Example:
Shanghai City northeast area has built dystopy Soil leaching prosthetic device described in a set of embodiment of the present invention 1, and
Showering improvement has been carried out using sticky contaminated soil of the dystopy Soil leaching prosthetic device to certain heavy metal pollution place.
For the contaminated soil of the contaminated site based on silty clay, main contamination index is cadmium (Cd), nickel (Ni), lead
(Pb).By 30 days trial operations, dystopy elution prosthetic device reached 3m3/ hr design treatment ability, contaminated soil is by broken
After broken, slurrying, screening, and elution, concentration and dehydration, main contamination index stablizes lower than target value, repairing effect is repaired.
Between trial run period, for wastewater eluting reclamation rate up to 100%, daily iron supplement tap water is mainly used for the configuration of medicament.
Numerical value has after numerical value, reparation target value and reparation before the reparation of the main contamination index of the contaminated soil of the contaminated site
Body is as shown in the table:
Main contamination index | Cadmium (Cd) | Nickel (Ni) | Lead (Pb) |
Before reparation (average, mg/kg) | 22 | 127 | 614 |
It repairs target value (mg/kg) | 9.5 | 71.4 | 400 |
After reparation (average, mg/kg) | 7.3 | 66.5 | 326 |
Claims (10)
1. a kind of dystopy suitable for clayed soil pollution amelioration elutes prosthetic device, it is characterised in that: the prosthetic device includes
Soil particle diameter classification and slurrying unit, Soil leaching and dewatering unit;
The soil particle diameter classification and slurrying unit, comprising: wet crusher, collection stock tank, roller solution mud machine, wet vibration
Sieve, collecting tank;It is provided with high pressure water flushing pipeline at the feed hopper of wet crusher, collection slurry is provided with below wet crusher
Slot collects and is equipped with blender, Pulp pump in stock tank;Slurry pump discharge is connect with solution mud machine entrance;The drums inside of roller solution mud machine
Equipped with high pressure water flushing pipeline;The outlet of roller solution mud machine is provided with conical screen;Wet oscillating screen is provided with below conical screen;It is wet
Collecting tank is provided with below formula vibrating screen;
The Soil leaching and dewatering unit, comprising: elution slot, mud concentration basin, centrifugal dehydrator;Sump bottom mud
Outlet is connect with elution slot;It elutes slot and is equipped with elution adding of agent mouth;Quenched adding of agent mouth is additionally provided on elution slot;Elution
Trench bottom slurry outlet is connect with mud concentration basin entrance;The bottom concentration slurry outlet of mud concentration basin is de- with centrifugation by pump
The connection of water dispenser entrance;The purified liquor outlet of centrifugal dehydrator is connect with separating liquid collecting tank entrance;The outlet of separating liquid collecting tank and mud
Starch the connection of concentration basin entrance;The slag-drip opening of centrifugal dehydrator is connect with belt conveyor.
2. dystopy according to claim 1 elutes prosthetic device, it is characterised in that: the prosthetic device further includes wastewater treatment
Unit, sludge treating block;
The treatment unit for waste water, comprising: waste water reaction combines pond, effluent settling chamber, reuse sink;Mud concentration basin it is upper
Portion's concentration purified liquor outlet combines the waterwater entrance connection in pond with waste water reaction;Waste water reaction combine pond flocculation tank upper outlet with
The entrance of effluent settling chamber connects;The bottom of effluent settling chamber is sludge bucket, and sludge bucket outlet is equipped with mud valve;Wastewater sedimentation
The upper clear supernate outlet in pond is connect with reuse sink entrance;
The sludge treating block, comprising: sludge storage pool, filter press, pressing filtering liquid collecting tank;The base sludge of effluent settling chamber
Bucket outlet is connected by the sludge inlet of mud valve and sludge storage pool;The sludge of sludge storage pool base sludge outlet and filter press
Entrance connection;The pressing filtering liquid outlet of filter press is connect with pressing filtering liquid collecting tank entrance;The outlet of pressing filtering liquid collecting tank is by pump and gives up
The waterwater entrance connection in water reaction combination pond.
3. dystopy according to claim 1 or 2 elutes prosthetic device, it is characterised in that: the wet crusher is hammer
The wet crusher of formula;The roller solution mud machine is the roller solution mud machine for the drum type brake being laterally arranged, i.e. cylinder solution mud machine;?
The cylinder interior central axis of cylinder solution mud machine is equipped with high pressure water flushing pipeline, if being provided with dry-spray in high pressure water flushing pipeline
Hole;The cylinder inner wall of cylinder solution mud machine is equipped with deflector;The cylinder outlet of cylinder solution mud machine is provided with conical screen;Conical screen and wet
Formula vibrating screen is respectively provided with high pressure water flushing pipeline.
4. dystopy according to claim 1 or 2 elutes prosthetic device, it is characterised in that: the waste water reaction combines pond
It is divided into three lattice, the first lattice are dosing reactive tank, and the second lattice are coagulation tank, and third lattice are flocculation tank, and every lattice are provided with blender,
Blender translator and agitating paddle;The chemical agent that dosing reactive tank is equipped with removable pollutant adds mouth, sets on coagulation tank
There is coagulant dosage mouth, flocculation tank is equipped with flocculant concentration mouth.
5. dystopy according to claims 1 and 2 elutes prosthetic device, it is characterised in that: the sludge storage pool is equipped with
Flocculant concentration mouth;Blender is provided in sludge storage pool;The filter press is Chamber Type Diaphragm Filter Press;The reparation dress
Setting further includes cycle of higher pressure water system;The cycle of higher pressure water system includes cycle of higher pressure water pot, high pressured water circuling pump;High pressure
The high-pressure compressing water out for recycling water pot is connected by high pressured water circuling pump and the high-pressure compressing water water inlet of Chamber Type Diaphragm Filter Press
It connects, the high-pressure compressing water water outlet of Chamber Type Diaphragm Filter Press is connect with the high-pressure compressing water water return outlet of cycle of higher pressure water pot.
6. dystopy according to claims 1 and 2 elutes prosthetic device, it is characterised in that: sump bottom slurry outlet is logical
Pump is crossed to connect with the mud entrance of elution slot;Alternatively, elution slot is arranged below collecting tank, sump bottom mud directly passes through
The opening and closing gravity of spoil disposal slurry valve is discharged into elution slot;Elution trench bottom slurry outlet is connect by pump with mud concentration basin;Alternatively,
For the setting of mud concentration basin below elution slot, the opening and closing gravity that elution trench bottom mud directly passes through spoil disposal slurry valve is discharged into mud
Concentration basin.
7. dystopy according to claims 1 and 2 elutes prosthetic device, it is characterised in that: elution slot is divided into three regions, the
The top in one region is connected with the top of Two Areas, and the lower part of Two Areas is connected with trizonal lower part
It is logical;Each region is equipped with blender;First region is equipped with quenched adding of agent mouth, and third region is equipped with elution medicine
Agent adds mouth.
8. dystopy according to claims 1 and 2 elutes prosthetic device, it is characterised in that: dress is repaired in the dystopy elution
Setting further includes the constant pressure water supply unit and medicament configuration unit assisted;
The medicament configuration unit includes: eluent grug feeding jar group, adjusting material grug feeding jar group, chemical agent grug feeding jar group, mixes
Solidifying agent grug feeding jar group and flocculant grug feeding jar group;Above-mentioned each grug feeding jar group includes two-stage connected up and down, and higher level matches for medicament
Tank processed, junior are medicament storage jar;Eluent grug feeding jar group is connect with the elution adding of agent mouth on elution slot;Adjusting material dosing
Tank group is connect with the quenched adding of agent mouth on elution slot;Chemical agent grug feeding jar group combines the dosing reaction in pond with waste water reaction
Chemical agent on slot adds mouth connection, and coagulant grug feeding jar group combines the coagulant dosage on the coagulation tank in pond with waste water reaction
Mouth connection, flocculant grug feeding jar group combine the connection of the flocculant concentration mouth on the flocculation tank in pond with waste water reaction;
The constant pressure water supply unit includes two sets of constant pressure water supply equipments, and respectively tap water constant pressure supply equipment and recycle-water is permanent
Press supply equipment;Tap water constant pressure supply equipment includes originally water pot, tap water constant pressure water supply pump group;Originally water pot is by originally
Water constant pressure water supply pump group is connect with the water inlet of each medicament preparing tank respectively, tap water constant pressure water supply pump group outlet there are also all the way with
The high pressure water of Wet oscillating screen rinses piping connection, the outlet of tap water constant pressure water supply pump group separately have all the way with cycle of higher pressure water pot
High-pressure water inlet connection;Recycle-water constant pressure water supply equipment includes reuse sink, recycle-water constant pressure water supply pump group, and reuse sink passes through
Recycle-water constant pressure water supply pump group rinses piping connection with the high pressure water of wet crusher, roller solution mud machine, Wet oscillating screen respectively.
9. a kind of Ex-situ washing remediation carried out using dystopy as described in claim 1 elution prosthetic device, feature
It is, this method includes soil breaking, slurrying, screening and Soil leaching, concentration and dehydration;This method technical process is as follows:
Soil pours wet crusher by high-pressure washing water, by cutting and crushing at short grained thick mud;Thick mud is received by collection stock tank
Collection, is lifted into cylinder solution mud machine by Pulp pump and is further solved by the sluicing and machine cuts of cylinder solution mud machine
Body is dispersed into slime water;Slime water is discharged into conical screen from the cylinder tail end of cylinder solution mud machine and is tentatively sieved, and 5mm is greater than on sieve
Large granular impurity rinsed and be discharged by high-pressure washing water, sieving mud gravity falls into Wet oscillating screen and is sieved again, on sieve
Little particle impurity greater than 1mm is rinsed by high-pressure washing water to be discharged, and after sieving mud falls into vibrating screen collecting tank, is promoted by pump
To elution slot, elution then occurs with eluent in elution slot and reacts, enters mud concentration basin later, it is dense through gravity concentration
Contracting mud enters centrifugal dehydrator and is dehydrated;It is discharged, is formed from mud discharging mouth after the dewatered sludgd deposition of centrifugal dehydrator
Dehydration soil is simultaneously delivered to staging area as soil waiting examination after repairing by belt conveyor;Through centrifugal dehydrator abjection
Clear liquor overflow enters separating liquid collecting tank, is promoted through pump and is back to mud concentration basin;
Concentration clear liquid after mud concentration basin gravity concentration enters the waste water reaction combination pond for the treatment of unit for waste water;It is anti-in waste water
It should combine after successively reacting with chemical agent, coagulant, flocculant in pond, flow into effluent settling chamber, under the effect of gravity,
The sludge settling of heavy phase is simultaneously deposited in the sludge bucket of effluent settling chamber and is then discharged into sludge storage pool;The clear liquor overflow of light phase
Recycle-water is provided to the whole series elution prosthetic device into reuse sink, and by recycle-water constant pressure water supply pump group;Sludge is in sludge
Kept in reservoir and carry out it is quenched, it is quenched after sludge filter-press dehydration and press dewatering are completed by Chamber Type Diaphragm Filter Press, it is de-
Sewage sludge is discharged into bucket, packs and shifts, outward transport disposition;The pressing filtering liquid that filter-press dehydration generates is then after the collection of pressing filtering liquid collecting tank
It is back to waste water reaction by pump conveying and is combined pond and handled again.
10. Ex-situ washing remediation as claimed in claim 9, it is characterised in that: specifically include following technical process:
(1) soil particle diameter classification and slurrying: contaminated soil was crushed big lumps by the bulk sundries of pretreatment removal > 8cm
Afterwards, to wet crusher feed hopper uniform feeding;By the high pressure water flushing pipeline at feed hopper, assisted using high-pressure washing water
Soil is smoothly fallen into wet crusher;Contaminated soil and high-pressure washing water are under the machine cuts effect of wet crusher, shape
At the thick mud of smaller particle size;Thick mud is collected by collection stock tank, is lifted into cylinder solution mud machine by Pulp pump;Collection slurry
Blender is set in slot, continuous or unlatching on demand;Into the waterpower of thick mud high-pressure washing water in cylinder of cylinder solution mud machine
It washes away and smoothly realizes impurity and soil with machine cuts double action, the building waste impurity therein for being stained with soil particle
The dispersion of grain, the soil particle agglomerate of relative bulk therein, which further disintegrates, is dispersed to complete sliming, passes through after and cylinder
The conical screen of outlet connection tentatively sieves, and removal is greater than the large granular impurity of 5mm;The sieving mud gravity of conical screen falls into wet type
Vibrating screen, further screening removal is greater than the little particle impurity of 1mm;At conical screen and Wet oscillating screen, pass through high pressure water
Flushing pipeline is adequately rinsed and is washed to the size particles impurity screened out using flushing water;By being located at wet type vibration
The collecting tank of dynamic sieve lower section, receives and completes through broken, slurrying and screening Soil slurry;Mud in collecting tank is in liquid level signal
Control under, by pump be promoted to subsequent elution slot;
(2) Soil leaching and dehydration: entering the Soil slurry of elution slot under mechanical agitation, the elution with investment elution slot
Agent is sufficiently mixed contact and elution reaction occurs;For eluent according to the difference of target contaminant in soil, selection includes hydrochloric acid, vinegar
Chelating agent or lauryl sodium sulfate surfactant including acid, EDTA, citric acid individually or are used in compounding;In eluent
Under effect, the separated from contaminants being present in soil particle solid phase enters in leacheate;Complete elution reaction Soil slurry into
Enter mud concentration basin, by gravity concentration, concentration mud enters centrifugal dehydrator and is carried out dehydrating, and concentration clear liquid is used as wait locate
Reason waste water enters the waste water reaction combination pond for the treatment of unit for waste water;Under the action of centrifugal dehydrator operates centrifugal force, mud is concentrated
Slurry forms sedimentation liquid and is separated into solid heavy phase and liquid light phase in turn, and shape constantly is discharged from mud discharging mouth after the sludgd deposition of heavy phase
Staging area is delivered to as soil waiting examination after repairing at dehydration soil and by belt conveyor;The supernatant liquid of light phase overflows
Stream enters separating liquid collecting tank, is promoted through pump and is back to mud concentration basin;
(3) wastewater treatment: waste water enters the first lattice dosing reactive tank in waste water reaction combination pond, according to soil target contaminant and
The difference of the eluent added, selection add chemical agent alkali/heavy metal chelating agent/precipitating reagent of corresponding removable pollutant
Or oxidant, under the action of mechanical stirring, chemical agent is sufficiently mixed with waste water to be contacted and reacts, heavy metal contaminants
It forms solid phase under the action of alkali/heavy metal chelating agent/precipitating reagent to separate with eluent ingredient, organic pollutant is in oxidant
Effect is lower to occur redox degradation;The waste water gravity for completing dosing reaction flows into the second lattice coagulation in waste water reaction combination pond
Slot, third lattice flocculation tank, difference dosing coagulant, flocculant, so that the solid particle being likely to form after waste water dosing reaction is de-
Steady and flocculation is agglomerating;The waste water gravity for completing coagulation-flocculation flows into effluent settling chamber, under the effect of gravity, the solid particle of heavy phase
In the sludge bucket for settling and being deposited in effluent settling chamber, sludge storage pool is discharged by the opening and closing gravity of mud valve;Light phase it is clear
Clear liquid flooding enters reuse sink, and provides recycle-water to the whole series elution prosthetic device by recycle-water constant pressure water supply pump group;
(4) Treatment of Sludge: wastewater treatment generate sludge in sludge storage pool keep in, according to sludge storage number, carrying out
Sludge press filtration dehydration before, to sludge storage pool add flocculation medicament and open mechanical stirring complete sludge it is quenched;Quenched good sludge
The dehydration procedure including filters pressing, squeezing and drying is completed by Chamber Type Diaphragm Filter Press, dewatered sludge is discharged into bucket, packs
And it is transferred to solid waste staging area, according to the property of sludge, periodically there is qualification as hazardous waste or general industry waste arrangement
Unit outward transport disposition;The pressing filtering liquid for being dehydrated generation is then back to waste water reaction by pump conveying after the collection of pressing filtering liquid collecting tank and combines
The dosing reactive tank in pond is handled;
The Ex-situ washing remediation further includes constant pressure water supply and medicament configuration;Medicament configuration includes medicament preparation, medicament
Storage and dosing, the preparation of various medicaments carry out in each medicament preparing tank respectively;Constant pressure water supply includes tap water supply and returns
It is supplied water with water;Tap water supply provides the configuration medicament of each medicament preparing tank by originally water pot, tap water constant pressure water supply pump group
It is the high-pressure compressing water of Chamber Type Diaphragm Filter Press with water, the high pressure washing water of Wet oscillating screen, the water supply of cycle of higher pressure water pot;
Recycle-water, which supplies water, provides wet crusher, roller solution mud machine, Wet oscillating screen by reuse water pot, recycle-water constant pressure water supply pump group
High pressure washing water.
Priority Applications (1)
Application Number | Priority Date | Filing Date | Title |
---|---|---|---|
CN201811614470.1A CN109500074A (en) | 2018-12-27 | 2018-12-27 | Dystopy suitable for clayed soil pollution amelioration elutes prosthetic device and restorative procedure |
Applications Claiming Priority (1)
Application Number | Priority Date | Filing Date | Title |
---|---|---|---|
CN201811614470.1A CN109500074A (en) | 2018-12-27 | 2018-12-27 | Dystopy suitable for clayed soil pollution amelioration elutes prosthetic device and restorative procedure |
Publications (1)
Publication Number | Publication Date |
---|---|
CN109500074A true CN109500074A (en) | 2019-03-22 |
Family
ID=65755542
Family Applications (1)
Application Number | Title | Priority Date | Filing Date |
---|---|---|---|
CN201811614470.1A Pending CN109500074A (en) | 2018-12-27 | 2018-12-27 | Dystopy suitable for clayed soil pollution amelioration elutes prosthetic device and restorative procedure |
Country Status (1)
Country | Link |
---|---|
CN (1) | CN109500074A (en) |
Cited By (17)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
CN110142287A (en) * | 2019-05-27 | 2019-08-20 | 安徽建筑大学 | Oxidation potential water leaching remediation method for soil polluted by persistent organic matters |
CN110251879A (en) * | 2019-07-05 | 2019-09-20 | 科盛环保科技股份有限公司 | A kind of decyanation system and method for cyanamide waste residue |
CN110563211A (en) * | 2019-10-18 | 2019-12-13 | 北京君驰华宇环境工程有限公司 | Mud-water separation and slurry concentration dehydration system for polluted soil leaching |
CN112159054A (en) * | 2020-10-09 | 2021-01-01 | 天津城建大学 | Method for removing heavy metal Cd in sludge by EDTA elution centrifugation |
CN112317524A (en) * | 2020-11-02 | 2021-02-05 | 北京高能时代环境技术股份有限公司 | Contaminated soil leaching treatment system and method |
CN112718838A (en) * | 2020-11-20 | 2021-04-30 | 上海胜丰环境能源科技有限公司 | Leaching system and process for high-concentration copper-polluted soil |
CN112718837A (en) * | 2020-11-20 | 2021-04-30 | 上海环境绿色生态修复科技有限公司 | Leaching system and process for mercury-polluted soil |
CN112828025A (en) * | 2020-11-27 | 2021-05-25 | 苏州精英环保有限公司 | Pollute soil drip washing and sewage treatment system that integrates |
CN112974509A (en) * | 2021-03-15 | 2021-06-18 | 湖南新九方科技有限公司 | Treatment method for heavy metal waste residue and soil mixed pollution medium |
CN113083875A (en) * | 2021-05-11 | 2021-07-09 | 江苏索尔雷米环保科技有限公司 | Soil ectopic chemical leaching treatment system |
CN112090952B (en) * | 2020-08-29 | 2021-07-27 | 山西大学 | Boiling type micro-foam soil pollution desorption device and method suitable for coking field |
CN113649406A (en) * | 2021-07-27 | 2021-11-16 | 上海琸域环境工程有限公司 | Slurry reaction tank for soil remediation |
CN114029331A (en) * | 2021-11-16 | 2022-02-11 | 吴海浪 | Soil remediation method |
CN115026116A (en) * | 2022-06-08 | 2022-09-09 | 上海市政工程设计研究总院(集团)有限公司 | Heavy metal pollution cohesive soil repair system |
CN115245955A (en) * | 2022-06-22 | 2022-10-28 | 福建安冠环境科技有限公司 | Method for cleaning petroleum-polluted soil by using surfactant |
CN115401063A (en) * | 2021-05-27 | 2022-11-29 | 郑州德森环境科技有限公司 | Automatic soil leaching system |
CN115611496A (en) * | 2022-11-04 | 2023-01-17 | 贵州航天乌江机电设备有限责任公司 | Harmless treatment device and method for waste drilling mud |
Citations (8)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
WO2013097461A1 (en) * | 2011-12-30 | 2013-07-04 | 深圳市能源环保有限公司 | Sewage and sludge treatment system and treatment method thereof |
CN204396456U (en) * | 2014-12-11 | 2015-06-17 | 北京建工环境修复股份有限公司 | A kind of Soil leaching repair system concentrating design concept based on decrement |
CN105772497A (en) * | 2016-04-12 | 2016-07-20 | 上海格林曼环境技术有限公司 | Soil ectopic leaching restoring complete equipment |
CN205710182U (en) * | 2016-04-12 | 2016-11-23 | 上海格林曼环境技术有限公司 | The wastewater treatment equipment of complete set of equipments is repaired in soil heterotopic drip washing |
CN106975652A (en) * | 2017-04-17 | 2017-07-25 | 北京建工环境修复股份有限公司 | A kind of feeding pulping repaired for Soil leaching and classification recovery system |
CN107127210A (en) * | 2017-04-17 | 2017-09-05 | 北京建工环境修复股份有限公司 | A kind of Soil leaching repair system and method |
CN207276463U (en) * | 2017-04-17 | 2018-04-27 | 北京建工环境修复股份有限公司 | A kind of Soil leaching mud thickening system |
CN209716032U (en) * | 2018-12-27 | 2019-12-03 | 上海市环境科学研究院 | Dystopy suitable for clayed soil pollution amelioration elutes prosthetic device |
-
2018
- 2018-12-27 CN CN201811614470.1A patent/CN109500074A/en active Pending
Patent Citations (8)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
WO2013097461A1 (en) * | 2011-12-30 | 2013-07-04 | 深圳市能源环保有限公司 | Sewage and sludge treatment system and treatment method thereof |
CN204396456U (en) * | 2014-12-11 | 2015-06-17 | 北京建工环境修复股份有限公司 | A kind of Soil leaching repair system concentrating design concept based on decrement |
CN105772497A (en) * | 2016-04-12 | 2016-07-20 | 上海格林曼环境技术有限公司 | Soil ectopic leaching restoring complete equipment |
CN205710182U (en) * | 2016-04-12 | 2016-11-23 | 上海格林曼环境技术有限公司 | The wastewater treatment equipment of complete set of equipments is repaired in soil heterotopic drip washing |
CN106975652A (en) * | 2017-04-17 | 2017-07-25 | 北京建工环境修复股份有限公司 | A kind of feeding pulping repaired for Soil leaching and classification recovery system |
CN107127210A (en) * | 2017-04-17 | 2017-09-05 | 北京建工环境修复股份有限公司 | A kind of Soil leaching repair system and method |
CN207276463U (en) * | 2017-04-17 | 2018-04-27 | 北京建工环境修复股份有限公司 | A kind of Soil leaching mud thickening system |
CN209716032U (en) * | 2018-12-27 | 2019-12-03 | 上海市环境科学研究院 | Dystopy suitable for clayed soil pollution amelioration elutes prosthetic device |
Non-Patent Citations (2)
Title |
---|
李传统等: "现代固体废物综合处理技术", vol. 1, 29 February 2008, 东南大学出版社, pages: 557 - 143 * |
杨守志等: "城市给水管道", vol. 1, 四川人民出版社, pages: 557 - 143 * |
Cited By (19)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
CN110142287B (en) * | 2019-05-27 | 2020-11-27 | 安徽建筑大学 | Oxidation potential water leaching remediation method for soil polluted by persistent organic matters |
CN110142287A (en) * | 2019-05-27 | 2019-08-20 | 安徽建筑大学 | Oxidation potential water leaching remediation method for soil polluted by persistent organic matters |
CN110251879A (en) * | 2019-07-05 | 2019-09-20 | 科盛环保科技股份有限公司 | A kind of decyanation system and method for cyanamide waste residue |
CN110563211A (en) * | 2019-10-18 | 2019-12-13 | 北京君驰华宇环境工程有限公司 | Mud-water separation and slurry concentration dehydration system for polluted soil leaching |
CN112090952B (en) * | 2020-08-29 | 2021-07-27 | 山西大学 | Boiling type micro-foam soil pollution desorption device and method suitable for coking field |
CN112159054A (en) * | 2020-10-09 | 2021-01-01 | 天津城建大学 | Method for removing heavy metal Cd in sludge by EDTA elution centrifugation |
CN112317524A (en) * | 2020-11-02 | 2021-02-05 | 北京高能时代环境技术股份有限公司 | Contaminated soil leaching treatment system and method |
CN112718838A (en) * | 2020-11-20 | 2021-04-30 | 上海胜丰环境能源科技有限公司 | Leaching system and process for high-concentration copper-polluted soil |
CN112718837A (en) * | 2020-11-20 | 2021-04-30 | 上海环境绿色生态修复科技有限公司 | Leaching system and process for mercury-polluted soil |
CN112828025A (en) * | 2020-11-27 | 2021-05-25 | 苏州精英环保有限公司 | Pollute soil drip washing and sewage treatment system that integrates |
CN112974509A (en) * | 2021-03-15 | 2021-06-18 | 湖南新九方科技有限公司 | Treatment method for heavy metal waste residue and soil mixed pollution medium |
CN113083875A (en) * | 2021-05-11 | 2021-07-09 | 江苏索尔雷米环保科技有限公司 | Soil ectopic chemical leaching treatment system |
CN115401063A (en) * | 2021-05-27 | 2022-11-29 | 郑州德森环境科技有限公司 | Automatic soil leaching system |
CN113649406A (en) * | 2021-07-27 | 2021-11-16 | 上海琸域环境工程有限公司 | Slurry reaction tank for soil remediation |
CN114029331A (en) * | 2021-11-16 | 2022-02-11 | 吴海浪 | Soil remediation method |
CN115026116A (en) * | 2022-06-08 | 2022-09-09 | 上海市政工程设计研究总院(集团)有限公司 | Heavy metal pollution cohesive soil repair system |
CN115245955A (en) * | 2022-06-22 | 2022-10-28 | 福建安冠环境科技有限公司 | Method for cleaning petroleum-polluted soil by using surfactant |
CN115611496A (en) * | 2022-11-04 | 2023-01-17 | 贵州航天乌江机电设备有限责任公司 | Harmless treatment device and method for waste drilling mud |
CN115611496B (en) * | 2022-11-04 | 2024-06-28 | 贵州航天乌江机电设备有限责任公司 | Harmless treatment device and treatment method for waste drilling mud |
Similar Documents
Publication | Publication Date | Title |
---|---|---|
CN109500074A (en) | Dystopy suitable for clayed soil pollution amelioration elutes prosthetic device and restorative procedure | |
CN105772497B (en) | A kind of soil heterotopic elution reparation complete set of equipments | |
CN104843955B (en) | A kind of oilfield drilling mud garbage is with brill processing system and processing method | |
CN109264898A (en) | A kind of flying dust multistage dechlorination and water lotion decalcification softening process and its system | |
CN205762942U (en) | The dystopy heavy-metal contaminated soil drip washing equipment of continuously-running | |
CN110270588A (en) | A kind of heavy-metal contaminated soil dystopy elution system and control system and method | |
CN109250877A (en) | A kind of shield residues processing technique | |
CN108002599A (en) | A kind of more material anaerobic fermented liquid solid-liquid separating methods and device containing kitchen garbage | |
CN104829070B (en) | A kind of oilfield drilling mud garbage is with brill processing system | |
CN109721191A (en) | A kind of sandstone building stones production wastewater treatment system | |
CN209583824U (en) | A kind of flying dust multistage dechlorination and water lotion decalcification melded system | |
CN209716032U (en) | Dystopy suitable for clayed soil pollution amelioration elutes prosthetic device | |
CN107840488A (en) | Washed-out sand muddy water device for cleansing and recycling and method | |
CN107298498A (en) | Industrial and mineral waste water high-efficiency purifies and recycled equipment | |
CN109794500A (en) | A kind of heavy-metal contaminated soil batch-type elution processing unit and method | |
KR101431161B1 (en) | Filtering, dehydrating equipment of sand and impurities | |
CN201458889U (en) | Sewage treatment device | |
SK279725B6 (en) | Method and apparatus for treating wastes from metallworking of ferromagnetic materials | |
CN213506500U (en) | Pile foundation construction slurry treatment system | |
CN206083405U (en) | Can handle high load capacity heavy metal combined pollution's multistage elution system of uniting | |
CN212042000U (en) | Heavy metal contaminated soil drip washing system | |
CN112588803A (en) | Restoration equipment and restoration method for engineering heavy metal arsenic and lead polluted soil | |
CN211679279U (en) | Heavy metal contaminated soil ex-situ elution system and control system | |
CN204644081U (en) | A kind of oilfield drilling mud waste is with brill treatment system | |
CN108409073A (en) | Ditch mud processing method |
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 |