CN106734153A - For thermal desorption processing system in situ and method that contaminated soil is carried out with heat exchange pattern - Google Patents

For thermal desorption processing system in situ and method that contaminated soil is carried out with heat exchange pattern Download PDF

Info

Publication number
CN106734153A
CN106734153A CN201710035073.8A CN201710035073A CN106734153A CN 106734153 A CN106734153 A CN 106734153A CN 201710035073 A CN201710035073 A CN 201710035073A CN 106734153 A CN106734153 A CN 106734153A
Authority
CN
China
Prior art keywords
well
contaminated soil
heat
extraction
heated
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
Application number
CN201710035073.8A
Other languages
Chinese (zh)
Inventor
吕正勇
魏丽
冯国杰
朱湖地
万德山
李淑彩
苗竹
范吉强
Current Assignee (The listed assignees may be inaccurate. Google has not performed a legal analysis and makes no representation or warranty as to the accuracy of the list.)
Beijing Geoenviron Engineering and Technology Inc
Original Assignee
Beijing Geoenviron Engineering and Technology Inc
Priority date (The priority date 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 date listed.)
Filing date
Publication date
Application filed by Beijing Geoenviron Engineering and Technology Inc filed Critical Beijing Geoenviron Engineering and Technology Inc
Priority to CN201710035073.8A priority Critical patent/CN106734153A/en
Publication of CN106734153A publication Critical patent/CN106734153A/en
Pending legal-status Critical Current

Links

Classifications

    • BPERFORMING OPERATIONS; TRANSPORTING
    • B09DISPOSAL OF SOLID WASTE; RECLAMATION OF CONTAMINATED SOIL
    • B09CRECLAMATION OF CONTAMINATED SOIL
    • B09C1/00Reclamation of contaminated soil
    • B09C1/06Reclamation of contaminated soil thermally
    • BPERFORMING OPERATIONS; TRANSPORTING
    • B09DISPOSAL OF SOLID WASTE; RECLAMATION OF CONTAMINATED SOIL
    • B09CRECLAMATION OF CONTAMINATED SOIL
    • B09C1/00Reclamation of contaminated soil
    • B09C1/002Reclamation of contaminated soil involving in-situ ground water treatment
    • BPERFORMING OPERATIONS; TRANSPORTING
    • B09DISPOSAL OF SOLID WASTE; RECLAMATION OF CONTAMINATED SOIL
    • B09CRECLAMATION OF CONTAMINATED SOIL
    • B09C2101/00In situ

Abstract

The present invention discloses a kind of thermal desorption processing system in situ and method carried out with heat exchange pattern for contaminated soil, heated well, the extraction well of more than 1, the temperature monitoring well of more than 1 and the pressure monitoring well of more than 1 including located underground more than 1, exhaust treatment system and sewage disposal system of the extraction well connection positioned at ground, the surface in contaminated soil region is equipped with ground barrier layer, contaminated soil region is all around provided with water-stop curtain, and the depth of water-stop curtain is the impermeable stratum for reaching underground.The number of the heated well, extraction well, temperature monitoring well and pressure monitoring well meets 9:3:1:0.5, and the arrangement of the heated well, extraction well, temperature monitoring well, pressure monitoring well arranged using regular hexagon mode.The present invention can be prevented effectively from the diffusion of the Polluted area after thermal desorption in situ, the maintenance down probability caused by gas converting heat system jams when reducing system operation.

Description

The thermal desorption processing system in situ that is carried out with heat exchange pattern for contaminated soil and Method
Technical field
The present invention provides a kind of thermal desorption processing system in situ and method carried out with heat exchange pattern for contaminated soil, Belong to technical field of soil remediation.
Background technology
Thermal desorption technology in situ is that contaminated soil is heated to more than the boiling point of target contaminant, by control system temperature Selectively promote pollutant to gasify with residence time of material to volatilize, target contaminant separated with soil particle, removed.Heat is de- Attached process can make the physicochemical changes such as organic compound volatilization and the cracking in soil.When pollutant be converted into gaseous state it Afterwards, its mobility will be greatly improved, and the gaseous products for evaporating carry out purified treatment after collecting and capturing.
The object carried out handled by the system and method for thermal desorption in situ with heat exchange pattern is by volatile organic matter, half Contaminated soil and the underground water such as volatile organic matter, agricultural chemicals type organic, polycyclic aromatic hydrocarbon type organic.That is, with heat The system and method that conduction pattern carries out thermal desorption in situ are applied to all of organic contaminants soil and groundwater Repair.
On May 28th, 2016, State Council prints and distributes《Soil Pollution Control action plan》, referred to as " ten, soil "." soil ten Bar " Article 23 clear stipulaties:Improvement is carried out in former address in principle with recovery project, and is taken the necessary measures and prevented Polluted Soil Earth is excavated, stored up etc. and causing secondary pollution.Therefore, for organic by volatile organic matter, semi-volatile organic matter, pesticide The reparation of the contaminated soils such as thing, polycyclic aromatic hydrocarbon type organic and underground water, so thermal desorption technology application prospect right and wrong in situ It is often extensive.
At present, the country is had some and the Patents of thermal desorption in situ is carried out with heat exchange pattern, but these patents are in itself Focus on the thermal desorption process of particular technique, the pollutant for less being produced during attention thermal desorption is excessive and prevents cross pollution, It is not thorough to be also contemplated in processing equipment setting.
The content of the invention
The purpose of the present invention is directed to by organic pollutant contaminated soil and underground water add with heat exchange pattern Contaminated soil, is heated to temperature more than organic pollutant boiling point by thermal pollution soil, turns the phase of organic pollutant It is changed into gaseous state, so as to reach the purpose of rehabilitating soil and underground water.Under the collective effect of ground barrier layer and air-introduced machine, make dirt Dye soil region forms tiny structure, and gaseous organic pollutant is collected in extraction well, enters ground by high-temp waste gas extraction pipe Face processing system is processed, waste gas qualified discharge after treatment, and sewage is processed into sewage disposal system.In order to ensure in-situ heat Secondary pollution is not caused to environment in desorption process, it is heat rejection to form thermodynamic barrier in the surrounding in contaminated soil region and bottom; In order to ensure being smoothed out for follow-up Ground Processing System, the present invention is provided with steam-water separation equipment also in Ground Processing System It is standby.
The present invention provides a kind of thermal desorption processing system in situ carried out with heat exchange pattern for contaminated soil, including position Heated well, the extraction well of more than 1, the temperature monitoring well of more than 1 and the prison of the pressure of more than 1 in more than 1 of underground Well logging, positioned at the exhaust treatment system and sewage disposal system of ground, the surface in contaminated soil region spreads for the extraction well connection It is provided with ground barrier layer, contaminated soil region is all around provided with water-stop curtain, and the depth of water-stop curtain is to reach underground not Pervious bed.
The number of the heated well, extraction well, temperature monitoring well and pressure monitoring well meets 9:3:1:0.5, and it is described plus Hot well, extraction well, temperature monitoring well, the arrangement of pressure monitoring well are arranged using regular hexagon mode.
Respectively positioned at six summits and center of regular hexagon, heated well constitutes the side of regular hexagon to the heated well 0.91 times of a length of heated well radius of influence, the summit of the extraction well and central point are located at the regular hexagon that heated well is constituted The regular hexagon one that two corresponding point midways of the length of side, temperature monitoring well and pressure monitoring well location are constituted in heated well The midpoint of the individual length of side and the point midway of the regular hexagon central point line.
The depth of the heated well and extraction well meets and penetrates whole contaminated soil region, and reach contaminated soil region with The depth of lower 1-2m, to realize the underground heat rejection to contaminated soil region;The heated well is also about the contaminated soil area The periphery in domain is set one week, to realize the surrounding heat rejection to contaminated soil region;The ground barrier layer is that thickness is 10- The concrete layer of 30cm.
The exhaust treatment system includes the one-level steam-water separation equipment, gas converting heat system, the two grades of carbonated drinks that are sequentially connected with Separation equipment, gas purifying equipment, air-introduced machine and chimney;The sewage disposal system includes the regulation tank, the sewage that are sequentially connected with Heat-exchange system and sewage disposal device, one-level steam-water separation equipment, gas converting heat system, two grades of steam-water separation equipment and gas Cleaning equipment is all connected with adjusting tank.
The extraction well is connected with the one-level steam-water separation equipment by waste gas extraction pipe, the extraction well with it is described Connected by sewage pumping pipeline between regulation tank, the waste gas extraction pipe carries out being in tilted layout for 2%-5% or so, by extracting Well is downward-sloping to one-level steam-water separation equipment direction.
The mode of heating of the heated well is that electrical heating produces heat, then heat radiation is carried out to the soil of surrounding and heat is passed Lead, or the mode of heating of heated well is straight-through hot-air, then heat transfer is carried out to the soil of surrounding.
The depth of the heated well reaches the bottom clear area below contaminated soil region, and the heated well is intercepted in bottom surface The lower section of layer carries out pouring sealing using cement grout, and heated well is along logical longitudinally to center setting heating element heater or hot-air The periphery of road, the heating element heater or hot-air channel is heat conduction sand, and the outside of heat conduction sand is well casing.
The extraction well includes gas phase extraction well and multiphase extraction well, the depth of extraction well for reach contaminated soil region with Under bottom clear area, the extraction well carries out pouring sealing, extraction well edge in the lower section of ground barrier layer using cement grout And extracting screen casing is set longitudinally to center, the outside of the extracting screen casing sets quartz sand filtration layer, and extracting screen casing is exposed to ground The over top in face is provided with vacuum table, and waste gas extraction pipe and sewage pumping pipeline are also associated with the top of extracting screen casing.
The present invention also provides a kind of in-situ heat desorption processing method carried out with heat exchange pattern for contaminated soil, including Following steps:
1)Run the exhaust treatment system and sewage disposal system on ground;
2)Daily heating rate is 1 ~ 1.5 DEG C below 100 DEG C, and 100 DEG C increase temperature rise rate above according to temperature rise situation, use Heated well continues to heat, and temperature in use monitoring well and pressure monitoring well are monitored;
3)When the gas flow of exhaust treatment system is reduced to the 20% of maximum throughput, and 1 ~ 5 day time is maintained, to pollution Soil is sampled detection, if reaching reparation desired value, repairs and completes;If not up to, need other ancillary method with Strengthening the effect of thermal desorption in situ or being changed to other techniques carries out subsequent treatment.
The step 2)In, if the boiling temperature of pollutant is less than 100 DEG C, it is necessary to contaminated soil is heated in contaminated soil 10 DEG C or so more than to pollutant boiling point, and keep heating, extract, monitor 30 ~ 90 days;If the boiling of pollutant in contaminated soil Point temperature be higher than 100 DEG C, it is necessary to 10 DEG C or so that contaminated soil is heated to more than pollutant boiling point, and keep heating, extract, Monitoring 3 ~ 20 days.
Compared to prior art, the advantage of the invention is that:
1. enable to the present invention to use in organic contaminants place carries out thermal desorption in situ with heat exchange pattern Technique can be smoothed out;
2. the present invention can be prevented effectively from the Polluted area diffusion after thermal desorption treatment in situ;
3. present invention reduces the maintenance down probability caused by gas converting heat system jams during system operation;
4. the present invention carries out control and monitoring to in-situ heat desorption process, it is to avoid the unexpected generation during thermal desorption.
Brief description of the drawings
Fig. 1 is process chart of the invention;
Fig. 2 is the horizontal layout schematic diagram of contaminated site in the present invention;
Fig. 3 is the profile of heated well in the present invention;
Fig. 4 is the profile of longitudinal extraction well in the present invention;
Fig. 5 is the profile of horizontal extraction well in the present invention.
Specific embodiment
The invention will be further described with specific embodiment below in conjunction with the accompanying drawings, so that those skilled in the art can be with It is better understood from the present invention and can be practiced, but illustrated embodiment is not as a limitation of the invention.
The present invention provides a kind of thermal desorption processing system in situ and method carried out with heat exchange pattern for contaminated soil, It is achieved through the following technical solutions:
As shown in figure 1, the thermal desorption processing system bag in situ carried out with heat exchange pattern for contaminated soil that the present invention is provided Include heated well 1 located underground, extraction well 2, monitoring well 3(Including temperature monitoring well and pressure monitoring well), and positioned on the ground Exhaust treatment system, sewage disposal system, energy supply system 4(If being then supply of electric power system with electric power as power resources System and power cable;If being then hot air generating system and hot-air supply line with hot-air as power resources;If with Heat medium heat transfer is power resources, then be medium heating system and the heat medium circulatory system, for a whole set of processing system provides power, Main connection heated well)With monitoring system 5(The operation of a whole set of processing system of monitoring, main connection temperature monitoring well and pressure prison Well logging).
Thermal desorption system in situ of the invention additionally uses contaminated soil region and intercepts measure and ground obstruct measure, wherein The floor surface that ground obstruct measure is specially in contaminated soil region lays ground barrier layer 6, and thickness is not limited, complete nothing The damaged obstruct for realizing floor surface, specifically can preferably lay with 10-30cm thick heat resistance concrete layer or gas Bubble light insulating concrete layer is realized intercepting, and forms heat rejection barrier with the floor surface in contaminated soil region, and prevent heat Amount loss is excessive with pollutant.The obstruct measure of contaminated soil region is specially four below contaminated soil region and in addition Zhou Jinhang heat rejections, to be specifically as follows be set to the depth of heated well and extraction well and reach the cleaning below contaminated soil region Region(It is specifically as follows and digs the depth that depth reaches 1-2m below contaminated soil region), with the following shape in contaminated soil region Into Base Heat baffle area 7, and the circle of interval setting one heated well in the clean soil of the periphery in contaminated soil region is close to, should Need to be spaced the 1-2 distance of heat transfer radius between one circle heated well of periphery setting and contaminated soil region, a circle adds The clean soil region that hot well is heated forms surrounding thermal resistance septal area 8, is realized to the four of contaminated soil region by above means Heat rejection is realized in week and bottom, prevents pollutant excessive.
The present invention can also set one and enclose in the spacing of the outer weekly interval 1.5-3m of the heated well of contaminated soil region periphery Water-stop curtain 9, the depth of water-stop curtain can reach underground impermeable stratum 10, make impermeable stratum 10 and the sealing curtain for all around setting Curtain 9 is engaged, to intercept the flowing of underground water.
The heated well located underground, extraction well, temperature monitoring well, the arrangement of pressure monitoring well use positive six Side shape arrangement, as shown in Fig. 2 wherein heated well is arranged at six summits and the central point of regular hexagon, and heated well is constituted The length of side of regular hexagon be 0.8-0.91 times of the heated well radius of influence.The summit of the extraction well and central point are located at heating Two corresponding point midways of the length of side of regular hexagon that well is constituted, and then make the regular hexagon that extraction well also constituted It is larger compared with heated well.Temperature monitoring well and pressure monitoring well location are in one length of side of the regular hexagon that heated well is constituted Point and the point midway of the regular hexagon central point line, the regular hexagon that temperature monitoring well and pressure monitoring well are constituted will be compared with The regular hexagon that extraction well is constituted is some larger, and the number between heated well, extraction well, temperature monitoring well and pressure monitoring well Amount ratio meets heated well:Extraction well:Temperature monitoring well:Pressure monitoring well=9:3:1:0.5, number and setting according to more than Position rule can set each well body in specific contaminated site.The pressure monitoring well is arranged at dirt mostly in arrangement Contaminate the surrounding of soil region, small part is uniformly arranged in contaminated soil region, in specific setting, due to temperature monitoring well and The set location of pressure monitoring well is identical rule, therefore, can be flexible in the case where the two number proportionate relationship is met Arrangement.Above heated well, extraction well, temperature monitoring well, the arrangement of pressure monitoring well than more uniform, be prevented from heating, In extractive process produce dead angle problem occur, make heating, extracting more fully, and can be relatively good realize pressure and temperature Monitoring.
The mode of heating of the heated well is to be provided with electrically heated rod in electrical heating, i.e. heated well, then to the soil of surrounding Carry out heat radiation and heat transfer.The mode of heating of the heated well can also be hot-air, and the source of hot-air is fuel combustion The hot-air or other manner of generation are by changing thermogenetic hot-air.The mode of heating of the heated well can also be heat medium Heat transfer, i.e., the pipeline by medium heating system and medium in heated well is transferred heat in contaminated soil.
The heated well cross-section structure is as shown in figure 3, it is downward from the surface of ground 24 in pending contaminated soil region Dig, bottom clear area 27 is reached up through contaminated soil region 28, specific depth is to reach contaminated soil region below 28 The depth of 1-2m, the cleaning soil depth of the 1-2m just constitutes Base Heat baffle area 7.The top in the contaminated soil region 28 The ground barrier layer 6 that is constituted for the refractory concrete layer of 10-30cm of the thickness that is equipped with of the surface of ground 24, the heating Well carries out sealing and constitutes cement grout portion 25 in the lower section of ground barrier layer 6 using cement grout.Heated well 1 is along longitudinal center Place sets heating element heater, hot-air channel or heat medium passage 29, the heating element heater, hot-air channel or heat medium passage 29 Periphery is heat conduction sand 26, and the outside of heat conduction sand is the well casing of metal material, is used to support whole well body internal heating element, heat empty Gas passage or heat medium passage 29, heat conduction sand 26, and outwards conduct heat.The thickness of the heat conduction sand 26(Radially)For 75 ~ 100mm, heat is conducted for the heat produced after absorbing heating element heater or hot-air exchange and to surrounding soil.
The extraction well includes gas phase extraction well and multiphase extraction well, when the Groundwater in contaminated soil region to be repaired When position is less than restoring area, extraction well uses gas phase extraction well;When the groundwater level in contaminated soil region to be repaired is located at When in restoring area, extraction well using the extracting of dewatering well and gas phase be combined into together with the multiphase extraction well that is formed.
As shown in Figure 4 and Figure 5, when contaminated soil region 28, depth is not blocked up for the cross-section structure of the extraction well, such as 10m with It is interior, generally using longitudinal extraction well, as shown in figure 4, it is downward from the surface of ground 24 in pending contaminated soil region 28 Dig, until reaching bottom clear area 27, specific depth is the depth for reaching contaminated soil region 1-2m below 28, the 1-2m's Cleaning soil depth constitutes Base Heat baffle area 7.The thickness that the surface of ground 24 in the contaminated soil region 28 is equipped with It is the ground barrier layer 6 that the refractory concrete layer of 10-30cm is constituted, the extraction well is used in the lower section of ground barrier layer 6 Cement grout carries out sealing and constitutes cement grout portion 25.Internal longitudinally central place sets extracting screen casing 30, the extracting screen casing 30 It is outside quartz sand filtration layer 31 is set, do not enter extracting screen casing 30 to ensure silt during extracting, prevent subsequently Face processing system(Exhaust treatment system and sewage disposal system)Block.The over top that extracting screen casing 30 is exposed to ground is set There is vacuum table 32, to show the negative pressure value in extraction well at any time.The top for extracting screen casing 30 is also connected with the waste gas of outside setting Extraction pipe 18 and sewage pumping pipeline 19, the waste gas extraction pipe 18, sewage pumping pipeline 19 are extracted with extraction well 2 respectively The pump-line of setting, pumping conduit are connected in screen casing 30.
The automatic Underground water water level of energy is provided with the bottom of multiphase extraction well and according to groundwater level automatic start-stop The water pump with compressed air as power, and by extract extracting screen casing in pumping conduit connect sewage pumping pipeline, and then It is connected with the sewage disposal system of ground.
If relatively deep such as more than the 10m in contaminated soil region to be repaired, then need the scattered level for setting more than 1 to extract Well, extraction pipe uses carbon steel pipe, structure as shown in figure 5, the depth that the depth of horizontal extraction well is horizontal extraction pipe 32 is In ground barrier layer 1 meter -3 meters or so of position below 6(In contaminated soil region 28), and horizontal extraction well well head Part needs to be sealed using cement grout in the bottom of bottom surface barrier layer.The reason for using horizontal extraction well is that vapor is adding Ramped up after heat and risen, be pooled to the lower section of ground barrier layer, to prevent in ground barrier layer higher-pressure region formed below.Level is extracted Well set its do not calculate in being described above 9:3:1:In 0.5 number design, it belongs to additional technology segment, in dirt Setting horizontal extraction well in the case of dye soil region relatively depth can preferably realize extracting.
Multiple thermocouples are provided with described temperature monitoring well, 1 thermocouple typically is set every 1.5 meters;Temperature monitoring The depth of well needs to reach the bottom in contaminated soil region, that is, reach and touch and be more than Base Heat baffle area, temperature prison In sieve aperture is provided with longitudinal well casing of below ground in well logging, it digs downwards from pending contaminated soil region surface, and The ground that the thickness being equipped with the surface at the top of well, contaminated soil region is constituted for the refractory concrete layer of 10-30cm Face barrier layer, and use the side of cement seal, the part more than ground to pass through metal hose under the barrier layer of ground It is connected to be connected exhaust treatment system with the waste gas extraction pipe on ground, and prevents high-temp waste gas the four of the temperature monitoring well borehole wall Week forms higher-pressure region and temperature short-channel, it is ensured that system operatio safety.
Described pressure monitoring well is located at contaminated soil region neighboring mostly, uniformly divides in contaminated soil region on a small quantity Cloth.1 pressure probe is provided with described temperature and pressure power monitoring well, set location is the depth of the 0-3m below the barrier layer of ground Degree, shows to judge whether restoring area runs under negative pressure, if can cause two to environment by pressure monitoring well internal pressure Secondary pollution;Shown by the pressure of place surrounding and judge whether Polluted area spreads, and pass through the pressure monitoring in contaminated site Well pressure display judges whether ground barrier layer has infringement.Pressure monitoring well uses cement under the ground barrier layer at the top of it Pour sealing.
As shown in figure 1, described exhaust treatment system includes the one-level steam-water separation equipment 11, gas converting heat being sequentially connected with System 12, two grades of steam-water separation equipment 13, gas purifying equipment 14, air-introduced machine 15 and chimneys 16, through chimney 16 to qualified discharge 17, the extraction well 2 is connected with the one-level steam-water separation equipment 11 by waste gas extraction pipe 18.When considering that sharp to waste heat With waste gas extraction pipe 18 and one-level steam-water separation equipment 11 need to carry out isothermal holding, if not considering UTILIZATION OF VESIDUAL HEAT IN, waste gas is taken out Carry pipeline 18 and one-level steam-water separation equipment 11 need not carry out isothermal holding, and in setting waste gas extraction pipe 18 need into Row 2%-5%'s or so is in tilted layout, downward-sloping to 11 directions of one-level steam-water separation equipment from extraction well, is beneficial to waste gas extracting Condensate liquid in pipeline 18 is to the water conservancy diversion of one-level steam-water separation equipment 11.The bottom of one-level steam-water separation equipment 11 offers pipeline, It is connected with the regulation tank 20 of sewage disposal system, is discharged from one-level steam-water separation equipment 11 at any time in order to condensate liquid.By one The high-temp waste gas of level steam-water separation equipment 11 by temperature after the heat exchange of gas converting heat system close to normal temperature, afterwards again by two grades of vapour Water separation equipment 13, by after gas purifying equipment purification and in air-introduced machine 15(Roots blower)Draft effect under, through chimney 16 qualified discharges.The bottom outlet of sewer and gas of the condensation-water drain of gas converting heat system 12, two grades of steam-water separation equipment 13 The outlet of sewer of body cleaning equipment 14 is connected with the regulation tank 20 of sewage disposal system.
In to contaminated soil heating process, indigenous microorganism can be with the increased activity of temperature in the range of 10 ~ 45 DEG C Enhancing, ethnic quantity increases.The accumulation under roots blower air-extraction function of these indigenous microorganisms is arrived in gas converting heat system and blocked Gas converting heat system, gas converting heat system can just be continued to run with after block clearing must be shut down when clogging is serious.Changed in gas Steam-water separation equipment is set before hot systems, most indigenous microorganism is entered into sewage disposal system with condensed water, subtract The probability of small gas heat-exchange system blocking accident.
As shown in figure 1, the sewage disposal system includes being sequentially connected with regulation tank 20, liquid heat exchange system 21 and sewage Reason equipment 22.Connected by sewage pumping pipeline 19 between the sewage disposal system and extraction well 2(Correspondence carries out multiphase extracting Or be required to be equipped with this equipment during groundwater extraction).Inflow sewage after being processed through sewage disposal device 22 is received and is managed or up to standard Discharge 23.
The desorption processing method of the thermal desorption system in situ heated with heat exchange pattern specifically includes following step Suddenly:
1)The exhaust treatment system and sewage disposal system on ground are run first;
2)Daily heating rate is 1 ~ 1.5 DEG C below 100 DEG C, and 100 DEG C can suitably increase temperature rise speed above according to temperature rise situation Rate, such as heating rate are 2-3 DEG C, and while being begun to warm up using heated well at the beginning, extraction well is to proceed by extracting, and Temperature in use monitoring well and pressure monitoring well are monitored;
If the boiling temperature of pollutant is less than 100 DEG C, it is necessary to contaminated soil is heated to more than pollutant boiling point in contaminated soil 10 DEG C or so, and keep heating, extract, monitor 30 ~ 90 days(Depending on number of days is according to pollutant concentration and reparation desired value);If The boiling temperature of pollutant is higher than 100 DEG C, it is necessary to 10 DEG C for contaminated soil being heated to more than pollutant boiling point in contaminated soil Left and right, and keep heating, extract, monitor 3 ~ 20 days(Depending on number of days is according to pollutant concentration and reparation desired value);
3)When the gas flow of exhaust treatment system is reduced to the 20% of maximum throughput and maintain 1 ~ 5 day time, to ensure dirt Dye thing is thoroughly taken out.Detection is sampled to contaminated soil, if reaching reparation desired value, that is, is considered as reparation and is completed;If not reaching Arrive, then needing other ancillary method strengthening the effect of thermal desorption in situ or be changed to other techniques carries out subsequent treatment, For example can be with return to step 2)Process proceed heating extracting or can be using being repaired by the way of in situ injection.It is dirty Directly by extracting the automatic control of pump, and with intensification, sewage extracting amount meeting nature is gradually reduced for the judgement up to standard of water treatment system, Finally it is reduced to zero.
Embodiment described above is only the preferred embodiment lifted to absolutely prove the present invention, protection model of the invention Enclose not limited to this.Equivalent substitute or conversion that those skilled in the art are made on the basis of the present invention, in the present invention Protection domain within.Protection scope of the present invention is defined by claims.

Claims (10)

1. a kind of thermal desorption processing system in situ carried out with heat exchange pattern for contaminated soil, it is characterised in that including position Heated well, the extraction well of more than 1, the temperature monitoring well of more than 1 and the prison of the pressure of more than 1 in more than 1 of underground Well logging, positioned at the exhaust treatment system and sewage disposal system of ground, the surface in contaminated soil region spreads for the extraction well connection It is provided with ground barrier layer, contaminated soil region is all around provided with water-stop curtain, and the depth of water-stop curtain is to reach underground not Pervious bed.
2. the thermal desorption processing system in situ carried out with heat exchange pattern for contaminated soil according to claim 1, its It is characterised by, the number of the heated well, extraction well, temperature monitoring well and pressure monitoring well meets 9:3:1:0.5, and it is described plus Hot well, extraction well, temperature monitoring well, the arrangement of pressure monitoring well are arranged using regular hexagon mode.
3. the thermal desorption processing system in situ carried out with heat exchange pattern for contaminated soil according to claim 2, its It is characterised by, respectively positioned at six summits and center of regular hexagon, heated well constitutes regular hexagon to the heated well The length of side is 0.91 times of the heated well radius of influence, and the summit of the extraction well and central point are located at positive six side that heated well is constituted Two corresponding point midways of the length of side of shape, the regular hexagon that temperature monitoring well and pressure monitoring well location are constituted in heated well One midpoint of the length of side and the point midway of the regular hexagon central point line.
4. the thermal desorption processing system in situ carried out with heat exchange pattern for contaminated soil according to claim 1, its It is characterised by, the depth satisfaction of the heated well and extraction well penetrates whole contaminated soil region, and reaches contaminated soil region The depth of following 1-2m, to realize the underground heat rejection to contaminated soil region;The heated well is also about the contaminated soil The periphery in region is set one week, to realize the surrounding heat rejection to contaminated soil region;The ground barrier layer is that thickness is 10- The concrete layer of 30cm.
5. the thermal desorption processing system in situ carried out with heat exchange pattern for contaminated soil according to claim 1, its It is characterised by, the exhaust treatment system includes the one-level steam-water separation equipment, gas converting heat system, the two grades of carbonated drinks that are sequentially connected with Separation equipment, gas purifying equipment, air-introduced machine and chimney;The sewage disposal system includes the regulation tank, the sewage that are sequentially connected with Heat-exchange system and sewage disposal device, one-level steam-water separation equipment, gas converting heat system, two grades of steam-water separation equipment and gas Cleaning equipment is all connected with adjusting tank.
6. the thermal desorption processing system in situ carried out with heat exchange pattern for contaminated soil according to claim 5, its It is characterised by, the extraction well is connected with the one-level steam-water separation equipment by waste gas extraction pipe, the extraction well and institute State regulation tank between connected by sewage pumping pipeline, the waste gas extraction pipe carries out being in tilted layout for 2%-5% or so, by taking out Carry well downward-sloping to one-level steam-water separation equipment direction.
7. the thermal desorption processing system in situ carried out with heat exchange pattern for contaminated soil according to claim 1, its It is characterised by, the mode of heating of the heated well produces heat for electrical heating, then heat radiation is carried out to the soil of surrounding and heat is passed Lead, or the mode of heating of heated well is straight-through hot-air, then heat transfer is carried out to the soil of surrounding.
8. the thermal desorption processing system in situ carried out with heat exchange pattern for contaminated soil according to claim 1, its It is characterised by, the depth of the heated well reaches the bottom clear area below contaminated soil region, the heated well hinders in bottom surface The lower section of interlayer carries out pouring sealing using cement grout, and heated well sets heating element heater or hot-air along longitudinally to center The periphery of passage, the heating element heater or hot-air channel is heat conduction sand, and the outside of heat conduction sand is well casing;The extraction well includes gas Phase extraction well and multiphase extraction well, the depth of extraction well are to reach the bottom clear area below contaminated soil region, the extracting Well carries out pouring sealing in the lower section of ground barrier layer using cement grout, and extraction well sets extracting sieve along longitudinally to center Pipe, the outside of the extracting screen casing sets quartz sand filtration layer, and the over top that extracting screen casing is exposed to ground is provided with vacuum table, Waste gas extraction pipe and sewage pumping pipeline are also associated with the top of extracting screen casing.
9. a kind of in-situ heat desorption processing method carried out with heat exchange pattern for contaminated soil, it is characterised in that including with Under several steps:
1)Run the exhaust treatment system and sewage disposal system on ground;
2)Daily heating rate is 1 ~ 1.5 DEG C below 100 DEG C, and 100 DEG C increase temperature rise rate above according to temperature rise situation, use Heated well continues to heat, and temperature in use monitoring well and pressure monitoring well are monitored;
3)When the gas flow of exhaust treatment system is reduced to the 20% of maximum throughput, and 1 ~ 5 day time is maintained, to pollution Soil is sampled detection, if reaching reparation desired value, repairs and completes;If not up to, need other ancillary method with Strengthening the effect of thermal desorption in situ or being changed to other techniques carries out subsequent treatment.
10. the in-situ heat desorption processing method carried out with heat exchange pattern for contaminated soil according to claim 9, its It is characterised by, the step 2)In, if the boiling temperature of pollutant is less than 100 DEG C, it is necessary to contaminated soil is added in contaminated soil More than heat to pollutant boiling point 10 DEG C or so, and keep heating, extract, monitor 30 ~ 90 days;If pollutant in contaminated soil Boiling temperature be higher than 100 DEG C, it is necessary to 10 DEG C or so that contaminated soil is heated to more than pollutant boiling point, and keep heating, take out Carry, monitor 3 ~ 20 days.
CN201710035073.8A 2017-01-18 2017-01-18 For thermal desorption processing system in situ and method that contaminated soil is carried out with heat exchange pattern Pending CN106734153A (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
CN201710035073.8A CN106734153A (en) 2017-01-18 2017-01-18 For thermal desorption processing system in situ and method that contaminated soil is carried out with heat exchange pattern

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
CN201710035073.8A CN106734153A (en) 2017-01-18 2017-01-18 For thermal desorption processing system in situ and method that contaminated soil is carried out with heat exchange pattern

Publications (1)

Publication Number Publication Date
CN106734153A true CN106734153A (en) 2017-05-31

Family

ID=58947184

Family Applications (1)

Application Number Title Priority Date Filing Date
CN201710035073.8A Pending CN106734153A (en) 2017-01-18 2017-01-18 For thermal desorption processing system in situ and method that contaminated soil is carried out with heat exchange pattern

Country Status (1)

Country Link
CN (1) CN106734153A (en)

Cited By (24)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN107520246A (en) * 2017-09-26 2017-12-29 上海格林曼环境技术有限公司 Burning heat transfer and residual neat recovering system for the thermal desorption reparation of contaminated site original position
CN107552554A (en) * 2017-09-26 2018-01-09 上海格林曼环境技术有限公司 Extracting condensation and Separate System of Water-jet for the thermal desorption reparation of contaminated site original position
CN107626730A (en) * 2017-09-26 2018-01-26 上海格林曼环境技术有限公司 A kind of extracting gang of wells for contaminated site in-situ immobilization engineering
CN107671116A (en) * 2017-11-16 2018-02-09 北京高能时代环境技术股份有限公司 A kind of improved organic material contaminated soil or underground water In-situ resistance heating hot repair complex system and hot restorative procedure
CN107685073A (en) * 2017-09-26 2018-02-13 上海格林曼环境技术有限公司 A kind of concentrated combustion formula original position thermal desorption prosthetic device for contaminated site
CN107685072A (en) * 2017-09-26 2018-02-13 上海格林曼环境技术有限公司 A kind of method of concentrated combustion formula original position thermal desorption reparation for contaminated site
CN107952789A (en) * 2017-11-14 2018-04-24 中国环境科学研究院 Thermal desorption system, thermal desorption-oxidation repair system in situ and restorative procedure in situ
CN107971331A (en) * 2017-12-28 2018-05-01 江苏盖亚环境科技股份有限公司 A kind of dystopy gas heating extracts integral type thermal desorption device
CN107983759A (en) * 2017-11-29 2018-05-04 武汉都市环保工程技术股份有限公司 Organic polluted soil original position thermal desorption prosthetic device
CN108114970A (en) * 2017-12-21 2018-06-05 永清环保股份有限公司 A kind of contaminated soil original position thermal desorption repair system and method
CN108311535A (en) * 2017-12-18 2018-07-24 北京市环境保护科学研究院 The system and administering method of electrical heating renovation of organic pollution soil in situ
CN108772413A (en) * 2018-07-14 2018-11-09 中节能大地(杭州)环境修复有限公司 A kind of organic material contaminated soil batch heating disposal plant and method of disposal
CN109013685A (en) * 2018-07-06 2018-12-18 北京石油化工学院 A kind of hydrocarbon contamination soil repair system based on thermal desorption in situ
CN109500072A (en) * 2018-12-28 2019-03-22 叶淑源 A kind of organic polluted soil original position thermal desorption prosthetic device
CN109821874A (en) * 2019-04-17 2019-05-31 北京建工环境修复股份有限公司 Sealing stops vapour structure and the method with the structure assisted in situ thermal desorption soil remediation
CN110270589A (en) * 2018-03-14 2019-09-24 北京中毅工程科技有限公司 Soil repair system and method
CN111014269A (en) * 2019-12-31 2020-04-17 中科鼎实环境工程有限公司 Contaminated soil electric heat conduction in-situ thermal desorption repair system
CN111013310A (en) * 2019-12-24 2020-04-17 北京建工环境修复股份有限公司 Tail water and tail gas treatment system and method in-situ heat conduction repair process
CN111069264A (en) * 2019-12-31 2020-04-28 北京建工环境修复股份有限公司 In-situ thermal desorption repair system and repair method for polluted site
CN111299311A (en) * 2020-03-26 2020-06-19 杰瑞环保科技有限公司 Multiphase extraction coupling recharge processing system
WO2020192177A1 (en) * 2019-03-26 2020-10-01 清华大学 Soil and groundwater linkage processing device and processing method therefor
CN112570437A (en) * 2020-11-26 2021-03-30 北京建工环境修复股份有限公司 System and method for restoring organic polluted site by in-situ heat conduction coupling electroosmosis well point dewatering
CN113319111A (en) * 2021-04-08 2021-08-31 江苏港峰环境科技有限公司 Laminated soil in-situ thermal desorption device
CN115178577A (en) * 2022-07-07 2022-10-14 江苏华东地质建设集团有限公司 Soil and underground water pollution prevention and control system and use method thereof

Citations (11)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
US5190405A (en) * 1990-12-14 1993-03-02 Shell Oil Company Vacuum method for removing soil contaminants utilizing thermal conduction heating
WO2000035608A1 (en) * 1998-12-17 2000-06-22 Edison International Ground water decontamination using lower-side thermal barrier
CN1441709A (en) * 2000-04-14 2003-09-10 国际壳牌研究有限公司 Heater element for use in situ thermal desorption soil remediation system
CN102513347A (en) * 2011-12-22 2012-06-27 天津生态城环保有限公司 Method for treating contaminated soil by combining in-situ heat strengthening and soil vapor extraction technology
CN202638859U (en) * 2012-06-11 2013-01-02 上海市环境科学研究院 Vapor phase extraction heat conduction strengthening advanced oxidization in situ repairing facility for contaminated soil
CN103008335A (en) * 2012-12-12 2013-04-03 华北电力大学 In-situ heating combined double-phase vacuum drawing soil restoration device and method
CN103624072A (en) * 2013-05-24 2014-03-12 上海市环境科学研究院 Radio-frequency heating vapor-extraction advanced-oxidation in-situ restoration apparatus suitable for high-viscosity contaminated soil and restoration method thereof
CN205289226U (en) * 2015-12-30 2016-06-08 北京高能时代环境技术股份有限公司 A normal position thermal desorption system for handling VOCSVOC pollutes soil
CN105689382A (en) * 2016-01-26 2016-06-22 清华大学 In-situ remediation system for organic contaminated soil
CN105834205A (en) * 2016-06-03 2016-08-10 上海格林曼环境技术有限公司 In-situ electric heating desorption restoration technology and device for contaminated site
CN106216381A (en) * 2016-08-05 2016-12-14 上海漕河泾桃浦科技智慧城经济发展有限公司 Freezing isolation and in-situ heat desorbing integral system and the processing method of contaminated soil

Patent Citations (11)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
US5190405A (en) * 1990-12-14 1993-03-02 Shell Oil Company Vacuum method for removing soil contaminants utilizing thermal conduction heating
WO2000035608A1 (en) * 1998-12-17 2000-06-22 Edison International Ground water decontamination using lower-side thermal barrier
CN1441709A (en) * 2000-04-14 2003-09-10 国际壳牌研究有限公司 Heater element for use in situ thermal desorption soil remediation system
CN102513347A (en) * 2011-12-22 2012-06-27 天津生态城环保有限公司 Method for treating contaminated soil by combining in-situ heat strengthening and soil vapor extraction technology
CN202638859U (en) * 2012-06-11 2013-01-02 上海市环境科学研究院 Vapor phase extraction heat conduction strengthening advanced oxidization in situ repairing facility for contaminated soil
CN103008335A (en) * 2012-12-12 2013-04-03 华北电力大学 In-situ heating combined double-phase vacuum drawing soil restoration device and method
CN103624072A (en) * 2013-05-24 2014-03-12 上海市环境科学研究院 Radio-frequency heating vapor-extraction advanced-oxidation in-situ restoration apparatus suitable for high-viscosity contaminated soil and restoration method thereof
CN205289226U (en) * 2015-12-30 2016-06-08 北京高能时代环境技术股份有限公司 A normal position thermal desorption system for handling VOCSVOC pollutes soil
CN105689382A (en) * 2016-01-26 2016-06-22 清华大学 In-situ remediation system for organic contaminated soil
CN105834205A (en) * 2016-06-03 2016-08-10 上海格林曼环境技术有限公司 In-situ electric heating desorption restoration technology and device for contaminated site
CN106216381A (en) * 2016-08-05 2016-12-14 上海漕河泾桃浦科技智慧城经济发展有限公司 Freezing isolation and in-situ heat desorbing integral system and the processing method of contaminated soil

Cited By (28)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN107552554A (en) * 2017-09-26 2018-01-09 上海格林曼环境技术有限公司 Extracting condensation and Separate System of Water-jet for the thermal desorption reparation of contaminated site original position
CN107626730A (en) * 2017-09-26 2018-01-26 上海格林曼环境技术有限公司 A kind of extracting gang of wells for contaminated site in-situ immobilization engineering
CN107685073A (en) * 2017-09-26 2018-02-13 上海格林曼环境技术有限公司 A kind of concentrated combustion formula original position thermal desorption prosthetic device for contaminated site
CN107685072A (en) * 2017-09-26 2018-02-13 上海格林曼环境技术有限公司 A kind of method of concentrated combustion formula original position thermal desorption reparation for contaminated site
CN107520246A (en) * 2017-09-26 2017-12-29 上海格林曼环境技术有限公司 Burning heat transfer and residual neat recovering system for the thermal desorption reparation of contaminated site original position
CN107952789B (en) * 2017-11-14 2020-07-31 中国环境科学研究院 In-situ thermal desorption system, in-situ thermal desorption-oxidation repair system and repair method
CN107952789A (en) * 2017-11-14 2018-04-24 中国环境科学研究院 Thermal desorption system, thermal desorption-oxidation repair system in situ and restorative procedure in situ
CN107671116A (en) * 2017-11-16 2018-02-09 北京高能时代环境技术股份有限公司 A kind of improved organic material contaminated soil or underground water In-situ resistance heating hot repair complex system and hot restorative procedure
CN107983759A (en) * 2017-11-29 2018-05-04 武汉都市环保工程技术股份有限公司 Organic polluted soil original position thermal desorption prosthetic device
CN108311535A (en) * 2017-12-18 2018-07-24 北京市环境保护科学研究院 The system and administering method of electrical heating renovation of organic pollution soil in situ
CN108311535B (en) * 2017-12-18 2021-10-01 北京市环境保护科学研究院 System for repairing organic contaminated soil through in-situ electric heating and treatment method
CN108114970A (en) * 2017-12-21 2018-06-05 永清环保股份有限公司 A kind of contaminated soil original position thermal desorption repair system and method
CN107971331A (en) * 2017-12-28 2018-05-01 江苏盖亚环境科技股份有限公司 A kind of dystopy gas heating extracts integral type thermal desorption device
CN110270589A (en) * 2018-03-14 2019-09-24 北京中毅工程科技有限公司 Soil repair system and method
CN109013685A (en) * 2018-07-06 2018-12-18 北京石油化工学院 A kind of hydrocarbon contamination soil repair system based on thermal desorption in situ
CN108772413A (en) * 2018-07-14 2018-11-09 中节能大地(杭州)环境修复有限公司 A kind of organic material contaminated soil batch heating disposal plant and method of disposal
CN109500072A (en) * 2018-12-28 2019-03-22 叶淑源 A kind of organic polluted soil original position thermal desorption prosthetic device
WO2020192177A1 (en) * 2019-03-26 2020-10-01 清华大学 Soil and groundwater linkage processing device and processing method therefor
CN109821874A (en) * 2019-04-17 2019-05-31 北京建工环境修复股份有限公司 Sealing stops vapour structure and the method with the structure assisted in situ thermal desorption soil remediation
CN109821874B (en) * 2019-04-17 2023-09-29 北京建工环境修复股份有限公司 Water and steam stopping structure and method for repairing in-situ thermal desorption soil by using structure
CN111013310A (en) * 2019-12-24 2020-04-17 北京建工环境修复股份有限公司 Tail water and tail gas treatment system and method in-situ heat conduction repair process
CN111069264A (en) * 2019-12-31 2020-04-28 北京建工环境修复股份有限公司 In-situ thermal desorption repair system and repair method for polluted site
CN111014269A (en) * 2019-12-31 2020-04-17 中科鼎实环境工程有限公司 Contaminated soil electric heat conduction in-situ thermal desorption repair system
CN111299311A (en) * 2020-03-26 2020-06-19 杰瑞环保科技有限公司 Multiphase extraction coupling recharge processing system
CN112570437A (en) * 2020-11-26 2021-03-30 北京建工环境修复股份有限公司 System and method for restoring organic polluted site by in-situ heat conduction coupling electroosmosis well point dewatering
CN113319111A (en) * 2021-04-08 2021-08-31 江苏港峰环境科技有限公司 Laminated soil in-situ thermal desorption device
CN113319111B (en) * 2021-04-08 2022-05-03 江苏港峰环境科技有限公司 Laminated soil in-situ thermal desorption device
CN115178577A (en) * 2022-07-07 2022-10-14 江苏华东地质建设集团有限公司 Soil and underground water pollution prevention and control system and use method thereof

Similar Documents

Publication Publication Date Title
CN106734153A (en) For thermal desorption processing system in situ and method that contaminated soil is carried out with heat exchange pattern
CN202490819U (en) In-situ remediation device for organic contaminated soil
CN108114970A (en) A kind of contaminated soil original position thermal desorption repair system and method
CN105834205A (en) In-situ electric heating desorption restoration technology and device for contaminated site
CN107685072B (en) Centralized combustion type in-situ thermal desorption restoration method for polluted site
CN203343163U (en) Polluted soil in-situ combined desorption restoration system
CN106734167A (en) Strengthen repair system and technique in a kind of organic contamination place
CN208050568U (en) A kind of contaminated soil original position thermal desorption repair system
CN111069264A (en) In-situ thermal desorption repair system and repair method for polluted site
CN206382324U (en) Strengthen repair system in a kind of organic contamination place
CN107685073A (en) A kind of concentrated combustion formula original position thermal desorption prosthetic device for contaminated site
CN102580993A (en) In-situ remediation technology for organic polluted soil
CN112958612A (en) In-situ thermal desorption method for repairing organic contaminated soil
CN102513347A (en) Method for treating contaminated soil by combining in-situ heat strengthening and soil vapor extraction technology
CN105234166B (en) A kind of system of solar energy home position strengthening gas phase extracting rehabilitating soil organic pollution
CN112570437A (en) System and method for restoring organic polluted site by in-situ heat conduction coupling electroosmosis well point dewatering
CN108906869A (en) A kind of contaminated soil in-situ heat repair system and method using distributed energy
CN110614266A (en) Heap thermal desorption treatment system for repairing organic contaminated soil
CN109396168A (en) Contaminated soil in-situ heat reparation combination exchanger and Soil Thermal repair system
CN202591210U (en) Device for treating contaminated soil by using in-situ thermal reinforced combined soil vapor extraction technology
CN212216583U (en) Heterotopic soil vapor extraction system is reinforceed to dystopy thermal desorption high temperature tail gas
CN106006771B (en) Multichannel for polluting water and soil reparation is connected to gang of wells and takes out filling circulating water treatment method
CN210497636U (en) Heating well system for in-situ soil thermal desorption
CN112958613A (en) In-situ thermal desorption system for repairing organic contaminated soil
CN112588809A (en) Electroosmosis-enhanced precipitation and in-situ thermal desorption soil remediation system and 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
RJ01 Rejection of invention patent application after publication

Application publication date: 20170531

RJ01 Rejection of invention patent application after publication