WO2017071104A1 - Combined soil washing desorption method and device - Google Patents
Combined soil washing desorption method and device Download PDFInfo
- Publication number
- WO2017071104A1 WO2017071104A1 PCT/CN2016/000013 CN2016000013W WO2017071104A1 WO 2017071104 A1 WO2017071104 A1 WO 2017071104A1 CN 2016000013 W CN2016000013 W CN 2016000013W WO 2017071104 A1 WO2017071104 A1 WO 2017071104A1
- Authority
- WO
- WIPO (PCT)
- Prior art keywords
- washing
- tank
- soil
- solid
- liquid
- Prior art date
Links
Images
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
-
- 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
Definitions
- the invention relates to a method and a device for swirling, ultrasonic and detergent combined soil washing and desorption, belonging to the field of ectopic repair of contaminated soil.
- Soil is an important part of the ecological environment and the basis for people's survival.
- the deterioration of the soil environment is caused by many reasons, such as: the use of a large number of chemical fertilizers and pesticides in agriculture; the discharge of industrial waste water in the industry, the landfill of solid waste; and the landfill of daily garbage.
- the contaminated soil will form a secondary pollution to water resources, and will be enriched into the human body through the soil-plant system or the soil-plant-animal system food chain, which directly endangers human health.
- Soil pollution has the characteristics of concealment, irreversibility and long-term, and the severity of the impact. Therefore, the solution of soil pollution has always been an international difficult and hot issue.
- soil remediation methods at home and abroad mainly include physical repair methods, chemical repair methods and bioremediation methods, but there are disadvantages such as high cost, incompleteness, long cycle, and large environmental conditions.
- Soil leaching repair technology is a fast and efficient chemical leaching technology, and one of the EPA recommended soil remediation methods at the end of the 20th century.
- the amount of pollutants is closely related to the particle size distribution of the soil. Whether it is organic matter adsorbed to the soil or heavy metals that are in contact with the surface functional groups of the soil, the pollutants are mainly attached or adsorbed to the particle size.
- the washing effect is poor and needs to be treated in other ways. Therefore, the washing and sieving of the soil and the improvement of the washing separation efficiency of the small-sized soil particles are crucial for improving the soil washing efficiency and reducing the processing cost.
- the separation of heavy metal fine soil particles is generally carried out by mechanical screening, hydraulic sorting, gravity sorting, flotation, magnetic separation, etc.
- the cyclone separation technology relies on its own simple structure, large processing capacity and low operating cost. The advantages have been more and more widely used in soil washing and restoration.
- the cyclone soil leaching and remediation technology adopts cyclone fractionation and leaching solution to remove pollutants from the soil, so that the soil environmental quality standard meets the corresponding planning land requirements.
- the ectopic soil washing method has a wide application range, and has the advantages of short repair cycle, high removal efficiency, and simple operation. However, it is necessary to develop one A method and apparatus for cyclonic separation grading suitable for soil washing.
- the domestic soil washing technology is still in the laboratory research stage.
- the focus of research is usually to select the eluent, rinsing mechanism and rinsing conditions suitable for a certain heavy metal element, and the core equipment in the soil washing and repairing system.
- the patent authorization publication number is CN202192081U, and the name is an experimental device for removing pollutants. These devices are only suitable for laboratory ideal conditions and cannot be directly scaled up for use in soil remediation projects.
- the patent application publication number is CN103990644A, and the name is an in-situ fully automatic contaminated soil repairing device.
- the equipment has weak processing capacity and many chemical residues. Therefore, it is necessary to develop a combined rinsing and repairing method and device which is suitable for the characteristics of soil properties in China and which is compact and efficient, and consumes less washing liquid.
- the present invention provides a method and apparatus for soil washing and desorption using a combination of swirling, ultrasonic, and detergent techniques, using a vibrating sieve to sort out large particle size impurities, eluent during agitation and ultrasonication.
- a combined soil washing and desorption method comprises the following steps:
- the mixer is transported and mixed, and then desorbed and classified by swirl washing in the first cyclone.
- the function of the first cyclone is particle classification, the classification accuracy is set to 100-200 ⁇ m; the first stage cyclone overflow
- the solid washing liquid discharged from the outlet is deeply separated by a second cyclone equipped with a micro-swirl sequencer at the front end, and the function of the second cyclone is a separation function with a separation precision of 3 ⁇ m to ensure return of the washing liquid storage tank.
- the solid content of the washing liquid is less than 0.03%;
- step (4) The soil separated in step (4) enters the washing tank, is washed and desorbed, and then enters the fourth cyclone equipped with a micro-swirl sequencer for concentration, and the function of the fourth cyclone is set to enrichment.
- the liquid solid content is increased from 3-10% to 40-60%, and then dehydrated by a centrifuge.
- the removed water enters the tap water tank for reuse, and the dehydrated soil is backfilled.
- the storage tank for washing and desorbing the detergent is provided with an inlet and outlet pipeline, the fresh detergent is replenished through the inlet pipeline, and the detergent is discharged from the outlet pipeline to the regeneration system or the desorption system after a certain number of cycles; the detergent outlet pipeline is provided with a precision filter, The goal is to entangle the soil particles without entrainment into the regeneration system.
- the washing liquid entering the regeneration system can be reused again, so as not to directly efflux and not pollute the environment.
- the washing and desorption treatment is ultrasonic, stirring, and eluent mixing washing and desorption.
- the washing method of the washing tank is stirring and washing with water.
- the solid-liquid mixture in the solid-liquid mixer rotates, and the linear velocity of the liquid is controlled to be 2-5 m/s, which ensures the conveying function and has the particle reaction washing and desorption function.
- a combined swirling soil washing and desorption device comprises the following units connected in sequence: wet multistage vibrating screen 3, mud water storage tank 4, first washing tank 5-1, first solid liquid mixer 8-1 a first hydrocyclone 10-1, a second hydrocyclone 10-2 of the first micro-swirl sequencer 9-1;
- the outlets of the first hydrocyclone 10-1 and the second hydrocyclone 10-2 are both connected to the second rinse tank 5-2;
- the second hydrocyclone 10-2, the detergent tank 15, and the first precision filter 12-1 are sequentially connected;
- the detergent tank 15 is connected to the dosing tank 14 and the second precision filter 12-2, respectively;
- the second rinsing tank 5-2, the second solid-liquid mixer 8-2, the third hydrocyclone 10-3, the second precision filter 12-2, the washing tank 6, and the second micro-swirl sorting The fourth hydrocyclone 10-4 and the centrifuge 13 of the device 9-2 are connected in sequence;
- the shower device 2 is disposed above the wet multi-stage vibrating screen 3.
- the above device also has a water tank 16 which is respectively associated with a shower device 2 and a water washing tank 6.
- the centrifuge 13 is connected.
- the first rinse tank 5-1 and the second rinse tank 5-2 have an ultrasound system 11-1 and an ultrasound system 11-2, respectively.
- a mud pump 7-1 is disposed between the first rinse tank 5-1 and the first solid-liquid mixer 8-1; the second rinse tank 5-2 is mixed with the second solid liquid
- a mud pump 7-2 is disposed between the tanks 8-2;
- a mud pump 7-3 is disposed between the water washing tank 6 and the second micro-swirl sequencer 9-2.
- a double impeller mixer is installed on the upper ends of the first rinse tank 5-1, the second rinse tank 5-2 and the water wash tank 6; and the first rinse tank 5-1 and the second rinse tank 5-2 are respectively provided with ultrasonic vibration plates.
- the first micro-swirl sequencer 9-1 is a spin sequencer connected in a spiral manner with the first hydrocyclone 10-1; the second micro-swirl sequencer 9-2 is a reverse rotation The sequencer is connected in reverse rotation with the fourth hydrocyclone 10-4.
- the first solid-liquid mixer 8-1 and the second solid-liquid mixer 8-2 are axial flow mixers, every 8-12D (D refers to the nominal diameter of the pipe, that is, 8-12 times the nominal diameter of the pipe) Install one, two forward and reverse according to the flow direction.
- the first solid-liquid mixer 8-1 and the second solid-liquid mixer 8-2 are K-type pipe mixers, every 8-12D (D refers to the nominal diameter of the pipe, that is, 8-12 times the nominal diameter of the pipe) ) Install one.
- the detergent tank 15 is continuously replenished with fresh detergent by the dosing tank 14, and the waste liquid containing the detergent in the second precision filter 12-2 is discharged to the detergent tank 15.
- the spraying device 2 has a plurality of nozzles; the wet multi-stage vibrating screen 3 is divided into two stages, the first stage screen removes stones larger than 20 mm, and the second stage screens out 3-20 mm coarse sand.
- the first hydrocyclone 10-1 and the second hydrocyclone 10-2 can separate a small portion of fine particle contaminants of less than about 3 ⁇ m from the soil, enter the detergent tank 15, and enter the first rinse again.
- the tank 5-1 and the second rinse tank 5-2 are rinsed.
- the above device can expand the processing capability by means of a parallel hydrocyclone.
- the second precision filter 12-2 can be replaced with a centrifuge according to actual processing conditions.
- the centrifuge 13 can be replaced with a filter press according to actual processing conditions.
- the soil is multi-classified by wet multi-stage vibrating screen and hydrocyclone, and the treatment is different, which reduces the total amount of soil washing; while stirring and ultrasonic are installed in the washing tank, the washing time is greatly shortened. Improve processing efficiency; at the end of the use of precision backwash filters to achieve deep separation of wastewater and soil particles, And achieve the purpose of recycling waste water and detergent;
- the method and device have the characteristics of high degree of automation, high controllability, wide application range, compact and high efficiency, and low consumption of washing liquid.
- FIG. 1 is a schematic structural view of a device of Embodiment 1;
- FIG. 2 is a schematic diagram of a combination of a microswirl sequencer and a hydrocyclone; wherein (a) is a schematic diagram of a connection mode of a spin sequencer and a hydrocyclone, and (b) is a reverse sequencer and a hydrocyclone. Schematic diagram of the connection method of the device;
- Figure 3 is a schematic diagram of the outer three views and the internal spiral structure of the reverse sequencer, as shown in (a), (b), (c), (d), respectively;
- Figure 4 is a schematic diagram of the outer three views and internal spiral structure of the spin sequencer, as shown in (a), (b), (c), (d), respectively.
- the inventors of the present application have found through extensive and intensive research that the most effective and inexpensive method for the treatment of contaminated soils is that the treatment is large and the treatment is difficult, and the most effective and inexpensive method is to use cyclone washing and desorption.
- the initial position of the particles at the inlet section of the cyclone has an important influence on the separation performance.
- the particles are chaotic, and the design is based on the new type of cyclone.
- the swirler arranged in the reverse spiral arrangement of the particles has a particle size ranging from small to large, and the concentration is from high to low, which can improve the separation efficiency; and the sequential arrangement can improve the classification efficiency.
- Fig. 1 it mainly comprises: wet multistage vibrating screen 3, mud water storage tank 4, first washing tank 5-1, second washing tank 5-2, washing tank 6, mud pump 7-1 to 7-3, the first solid-liquid mixer 8-1, the second solid-liquid mixer 8-2, the first micro-swirl sequencer 9-1, the second micro-swirl sequencer 9-2, the first to the first
- the micro-swirl sequencer 9-1 is a spin sorter
- the micro-swirl sorter 9-2 is a reverse-sequence sorter.
- the contaminated soil is continuously conveyed by the conveyor belt 1 to the upper side of the vibrating screen while being sprayed and sieved.
- the wet multi-stage vibrating screen 3 has a two-stage screen.
- the primary screen has a pore size of 20 mm for removing large stones.
- the secondary screen has a pore size of 3 mm for removing 3-20 mm of coarse sand, but the screen The pores can be selected according to the actual situation.
- the fine soil particle suspension flowing into the mud water storage tank 4 flows into the first washing tank 5-1 by gravity, is stirred and ultrasonically mixed, and is continuously added with the eluent; the mud pump 7-1 pumps the mixed liquid into the first solid in series.
- the overflow port of the upper end of the cyclone 10-2 is discharged into the detergent tank 15, and the detergent tank 15 is connected with the first rinse tank 5-1 and the second rinse tank 5-2 to promote the multiple circulation of the detergent.
- the outlet pipeline enters the regeneration system, and the indirect precision filter ensures that the soil particles are not entrained into the regeneration system and the plugging condition occurs, and the detergent tank 15 is connected to the dosing tank 14 to realize the supplement of the fresh detergent.
- the mixture of the lower end of the first hydrocyclone 10-1 and the second hydrocyclone 10-2 flows into the second rinse tank 5-2, and the mixing is continued by stirring and ultrasonication while continuously adding the eluent.
- Mud pump 7-2 will mix
- the second solid-liquid mixer 8-2 and the third hydrocyclone 10-3 which are sequentially connected are pumped, and the fine soil particle suspension is discharged into the second shower by the upper overflow port of the third hydrocyclone 10-3.
- the washing tank 5-2 is rinsed again, and the mixture of the lower end of the third hydrocyclone 10-3 flows into the second precision filter 12-2, so that the detergent enters the detergent tank to realize reuse, and realizes as little washing liquid as possible.
- the soil is entrained into the wash tank 6.
- the washing tank 6 is continuously mixed by stirring while continuously adding clean tap water.
- the washed mixture is passed through the mud pump 7-3 into the sequentially connected second micro-swirl sequencer 9-2 and the fourth hydrocyclone 10-4, and separated again, and the overflow mixture is discharged into the washing tank 6 again.
- the water is washed, the lower part is suspended into a centrifuge for dehydration, the lower part is obtained by directly backfilling the soil, and the water obtained in the upper part is returned to the tap water tank 16 for reuse.
- the operation of the entire set of equipment can be controlled by an automatic control cabinet.
- (a) is a schematic diagram of a connection mode of a spin sequencer and a hydrocyclone
- (b) is a schematic diagram of a connection mode of a reverse sequencer and a hydrocyclone.
- Figure 3 is a schematic diagram of the outer three views and the internal spiral structure of the reverse sequencer, as shown in (a), (b), (c), (d), respectively;
- Figure 4 is a schematic diagram of the outer three views and internal spiral structure of the spin sequencer, as shown in (a), (b), (c), (d), respectively.
Landscapes
- Life Sciences & Earth Sciences (AREA)
- Soil Sciences (AREA)
- Engineering & Computer Science (AREA)
- Environmental & Geological Engineering (AREA)
- Separation Of Solids By Using Liquids Or Pneumatic Power (AREA)
- Processing Of Solid Wastes (AREA)
Abstract
Provided are a combined soil washing desorption method and device. The method is as follows: polluted soil is sprayed and sieved with a wet multistage vibrating sieve (3) to remove large particles of stones or coarse sand that can be directly backfilled; washing desorption treatment is carried out on a fine soil particle suspension, and same is subjected to cyclones (10-1,10-2,10-3) connected in series and respectively equipped with solid-liquid mixers (8-1,8-2) and a micro rotational flow sequencer (9-1) in order to achieve the separation of clay pollutants of small particle size; washing desorption treatment and cyclone separation are carried out on the remaining sandy soil of intermediate particle size, wherein the recycling of a washing liquid is achieved by a precision filter (12-1); and washing treatment using clear water and cyclone separation are carried out on the soil after filtration, and finally, after dehydration through a centrifugal machine (13), the deep separation of waste water and soil particles is finally achieved, thus achieving the purposes of backfilling soil, recycling tap water and recycling a washing agent. The device parameters can be adjusted and optimized according to actual conditions, thereby effectively removing pollutants containing heavy metals, pesticides, etc., and overcoming the deficiency that current soil washing cannot be industrialized.
Description
本发明涉及一种旋流、超声、洗涤剂组合式土壤洗涤脱附的方法和装置,属于污染土壤异位修复领域。The invention relates to a method and a device for swirling, ultrasonic and detergent combined soil washing and desorption, belonging to the field of ectopic repair of contaminated soil.
土壤是生态环境的重要组成部分,是人们赖以生存的基础。土壤环境的日益恶化是由多方面的原因造成的,比如:农业上大量化肥、农药的使用;工业上大量工业废水的排放、固体废弃物的填埋;日常生活垃圾的填埋等。被污染的土壤会通过对水资源形成二次污染,经过土壤-植物系统或土壤-植物-动物系统食物链富集进入人体,直接危及到人体健康。土壤污染具有隐蔽性、不可逆性和长期性、影响的严重性等特点,因此土壤污染的解决一直是国际上的难点和热点问题。Soil is an important part of the ecological environment and the basis for people's survival. The deterioration of the soil environment is caused by many reasons, such as: the use of a large number of chemical fertilizers and pesticides in agriculture; the discharge of industrial waste water in the industry, the landfill of solid waste; and the landfill of daily garbage. The contaminated soil will form a secondary pollution to water resources, and will be enriched into the human body through the soil-plant system or the soil-plant-animal system food chain, which directly endangers human health. Soil pollution has the characteristics of concealment, irreversibility and long-term, and the severity of the impact. Therefore, the solution of soil pollution has always been an international difficult and hot issue.
目前,国内外土壤修复方法主要有物理修复法、化学修复法和生物修复法等,但存在着成本高、不彻底、周期长、环境条件影响大等不足。土壤淋洗修复技术是一种快速高效的化学淋洗技术,也是二十世纪末美国EPA推荐的土壤修复方法之一。At present, soil remediation methods at home and abroad mainly include physical repair methods, chemical repair methods and bioremediation methods, but there are disadvantages such as high cost, incompleteness, long cycle, and large environmental conditions. Soil leaching repair technology is a fast and efficient chemical leaching technology, and one of the EPA recommended soil remediation methods at the end of the 20th century.
随着技术的应用和研究的深入,发现污染物的量与土壤粒径分布息息相关,不论是吸附于土壤的有机质或与土壤表面官能基错合的重金属,污染物主要附着或吸附于粒径较小的土壤,大粒径范围2~4mm污染程度较低,介于2~0.076mm中间粒径土壤颗粒最多,属于沙质土,污染浓度较高,适合清洗,小于0.076mm的粘土污染浓度高但洗涤效果差,需采用其它方式处理。因此土壤的洗涤筛分以及提高对小粒径土壤颗粒的洗涤分离效率对于提高土壤洗涤效率降低处理成本有着至关重要的作用。国外实地修复中对重金属细土壤颗粒的分选一般采用机械筛选、水力分选、重力分选、浮选、磁力分离等方法,旋流分离技术依靠自身结构简单、处理量大、操作成本低的优势在土壤洗涤修复中得到了越来越广泛的应用。旋流土壤淋洗修复技术是采用旋流分级分离、淋洗液清洗去除土壤中污染物,使土壤环境质量标准达到相应的规划用地要求。这种异位土壤洗涤方法适用范围非常广,同时具有修复周期短、去除效率高、操作简便等优点。然而需要开发一
套适用于土壤洗涤的旋流分离分级的方法和装置。With the application of technology and research, it is found that the amount of pollutants is closely related to the particle size distribution of the soil. Whether it is organic matter adsorbed to the soil or heavy metals that are in contact with the surface functional groups of the soil, the pollutants are mainly attached or adsorbed to the particle size. Small soil, large particle size range of 2 ~ 4mm, low pollution degree, between 2 ~ 0.076mm intermediate particle size soil particles most, belonging to sandy soil, high pollution concentration, suitable for cleaning, high concentration of clay pollution less than 0.076mm However, the washing effect is poor and needs to be treated in other ways. Therefore, the washing and sieving of the soil and the improvement of the washing separation efficiency of the small-sized soil particles are crucial for improving the soil washing efficiency and reducing the processing cost. In the field repair in foreign countries, the separation of heavy metal fine soil particles is generally carried out by mechanical screening, hydraulic sorting, gravity sorting, flotation, magnetic separation, etc. The cyclone separation technology relies on its own simple structure, large processing capacity and low operating cost. The advantages have been more and more widely used in soil washing and restoration. The cyclone soil leaching and remediation technology adopts cyclone fractionation and leaching solution to remove pollutants from the soil, so that the soil environmental quality standard meets the corresponding planning land requirements. The ectopic soil washing method has a wide application range, and has the advantages of short repair cycle, high removal efficiency, and simple operation. However, it is necessary to develop one
A method and apparatus for cyclonic separation grading suitable for soil washing.
目前,国内的土壤洗涤技术还处在实验室研究阶段,研究的重点通常是筛选适合于某种重金属元素的淋洗剂、淋洗机理及淋洗条件,而对于土壤洗涤修复系统中的核心设备,如旋流分离技术在土壤洗涤应用的研究未见到相关报道。如专利授权公开号为CN202192081U,名称为一种去除污染物的实验装置。这些设备只适合实验室理想条件下进行,无法直接放大应用于土壤修复工程中。如专利申请公开号为CN103990644A,名称为一种原位全自动污染土壤修复装置。该设备处理能力弱,化学残余多。因此,需开发一种适合于我国土壤性质特点的紧凑高效、洗涤液耗量少的组合式淋洗修复方法和装置。At present, the domestic soil washing technology is still in the laboratory research stage. The focus of research is usually to select the eluent, rinsing mechanism and rinsing conditions suitable for a certain heavy metal element, and the core equipment in the soil washing and repairing system. There are no reports on the application of cyclone separation technology in soil washing applications. For example, the patent authorization publication number is CN202192081U, and the name is an experimental device for removing pollutants. These devices are only suitable for laboratory ideal conditions and cannot be directly scaled up for use in soil remediation projects. For example, the patent application publication number is CN103990644A, and the name is an in-situ fully automatic contaminated soil repairing device. The equipment has weak processing capacity and many chemical residues. Therefore, it is necessary to develop a combined rinsing and repairing method and device which is suitable for the characteristics of soil properties in China and which is compact and efficient, and consumes less washing liquid.
发明内容Summary of the invention
鉴于以上问题,本发明提供了一种利用旋流、超声、洗涤剂组合技术进行土壤洗涤脱附的方法和装置,采用振动筛分选出大粒径的杂物、淋洗剂在搅拌和超声条件下洗涤脱附,并充分利用旋流分离结构简单、成本低、可靠性高的优点,主要经过一级旋流分级,二级旋流洗涤脱附及预分离,三级提浓和精细分离,最终实现废水与土壤颗粒的深度分离,达到土壤回填、自来水回用、洗涤剂再生利用的目的,保证系统洗涤剂、自来水消耗低、紧凑高效、经济性好、不造成再次污染。In view of the above problems, the present invention provides a method and apparatus for soil washing and desorption using a combination of swirling, ultrasonic, and detergent techniques, using a vibrating sieve to sort out large particle size impurities, eluent during agitation and ultrasonication. Washing and desorption under conditions, and taking full advantage of the advantages of simple cyclone separation structure, low cost and high reliability, mainly through one-stage cyclone classification, two-stage cyclone washing desorption and pre-separation, three-stage enrichment and fine separation Finally, the deep separation of wastewater and soil particles is achieved, and the purpose of soil backfilling, tap water reuse, and detergent recycling is achieved, ensuring low consumption of system detergent and tap water, compact and efficient, good economy, and no re-contamination.
具体的技术方案如下:The specific technical solutions are as follows:
一种组合式土壤洗涤脱附的方法,包括如下步骤:A combined soil washing and desorption method comprises the following steps:
(1)喷淋污染土壤后用湿式多级振动筛进行筛分,以去除粒径大于3mm的可直接回填的石块和粗砂,保证进入洗涤脱附系统的粒径为50μm-3mm的颗粒质量浓度为70%以上;(1) After spraying the contaminated soil, it is sieved with a wet multi-stage vibrating sieve to remove the directly backfilled stones and coarse sand with a particle diameter of more than 3 mm to ensure the particles having a particle size of 50 μm - 3 mm entering the washing and desorption system. The mass concentration is 70% or more;
(2)对步骤(1)得到的筛下细土壤颗粒悬浮液进行洗涤脱附处理,控制流速为2-5m/s,固液混合液的体积浓度为5~40%;通过第一固液混合器进行输送和混合,然后在第一旋流器中旋流洗涤脱附并分级,第一旋流器的功能为颗粒分级,分级精度设置为100-200μm;第一级旋流器溢流出口出来的含固洗涤液通过前端装有微旋流排序器的第二旋流器进行深度分离,第二旋流器的功能为分离功能,分离精度为3μm,以保证返回洗涤液储罐的洗涤液含固量小于0.03%;(2) washing and desorbing the fine soil particle suspension obtained in the step (1), controlling the flow rate to be 2-5 m/s, and the volume concentration of the solid-liquid mixture is 5 to 40%; The mixer is transported and mixed, and then desorbed and classified by swirl washing in the first cyclone. The function of the first cyclone is particle classification, the classification accuracy is set to 100-200 μm; the first stage cyclone overflow The solid washing liquid discharged from the outlet is deeply separated by a second cyclone equipped with a micro-swirl sequencer at the front end, and the function of the second cyclone is a separation function with a separation precision of 3 μm to ensure return of the washing liquid storage tank. The solid content of the washing liquid is less than 0.03%;
(3)用淋洗剂淋洗步骤(2)分离出的剩余中间粒径10μm-3mm的沙质土
并通过第二固液混合器进行混合和洗涤脱附,然后通过第三旋流器进行旋流脱附并提浓,第三旋流器的功能设置为含固液体增浓及土壤颗粒中污染物的深度脱附功能,达到预分离的目的;(3) The remaining sandy soil with a median diameter of 10 μm to 3 mm separated by the eluent rinsing step (2)
And mixing and washing desorption by the second solid-liquid mixer, followed by cyclone desorption and concentration by the third cyclone, and the function of the third cyclone is set to contain solid liquid enrichment and soil particle contamination Deep desorption function of the object to achieve the purpose of pre-separation;
(4)对预分离后的悬浮液进行精细分离,保证洗涤液尽量少的随土壤夹带到后续水洗过程且能达到洗涤液回用的目的;(4) Finely separating the pre-separated suspension to ensure that the washing liquid is entrained to the subsequent washing process as little as possible and can achieve the purpose of washing liquid reuse;
(5)步骤(4)分离得到的土壤进入水洗罐洗涤脱附后进入前端装有微旋流排序器的第四旋流器进行提浓,第四旋流器的功能设置为增浓作用,使液体含固量从3-10%提高到40-60%,之后通过离心机进行脱水,脱除的水进入自来水罐进行回用,脱水后的土壤回填。(5) The soil separated in step (4) enters the washing tank, is washed and desorbed, and then enters the fourth cyclone equipped with a micro-swirl sequencer for concentration, and the function of the fourth cyclone is set to enrichment. The liquid solid content is increased from 3-10% to 40-60%, and then dehydrated by a centrifuge. The removed water enters the tap water tank for reuse, and the dehydrated soil is backfilled.
洗涤脱附所用洗涤剂的储罐设置有进出口管线,新鲜洗涤剂通过进口管线补充,洗涤剂循环一定次数后从出口管线流出进入再生系统或脱附系统;洗涤剂出口管线设置精密过滤器,目的是将土壤颗粒不夹带到再生系统而导致堵塞。进入再生系统的洗涤液可再次回用,达到不直接外排、不污染环境的作用。The storage tank for washing and desorbing the detergent is provided with an inlet and outlet pipeline, the fresh detergent is replenished through the inlet pipeline, and the detergent is discharged from the outlet pipeline to the regeneration system or the desorption system after a certain number of cycles; the detergent outlet pipeline is provided with a precision filter, The goal is to entangle the soil particles without entrainment into the regeneration system. The washing liquid entering the regeneration system can be reused again, so as not to directly efflux and not pollute the environment.
所述洗涤脱附处理为超声、搅拌、淋洗液混合洗涤脱附。The washing and desorption treatment is ultrasonic, stirring, and eluent mixing washing and desorption.
所述水洗罐洗涤方式为搅拌、清水混合洗涤。The washing method of the washing tank is stirring and washing with water.
所述固液混合器内固液混合物旋转流动,液体的线速度控制为2-5m/s,保证输送功能的同时又具有颗粒反应洗涤脱附功能。The solid-liquid mixture in the solid-liquid mixer rotates, and the linear velocity of the liquid is controlled to be 2-5 m/s, which ensures the conveying function and has the particle reaction washing and desorption function.
一种组合式旋流土壤洗涤脱附的装置,包括依次连接的以下单元:湿式多级振动筛3、泥水储罐4、第一淋洗罐5-1、第一固液混合器8-1、第一水力旋流器10-1、第一微旋流排序器9-1的第二水力旋流器10-2;A combined swirling soil washing and desorption device comprises the following units connected in sequence: wet multistage vibrating screen 3, mud water storage tank 4, first washing tank 5-1, first solid liquid mixer 8-1 a first hydrocyclone 10-1, a second hydrocyclone 10-2 of the first micro-swirl sequencer 9-1;
所述第一水力旋流器10-1和第二水力旋流器10-2的出口均与第二淋洗罐5-2连接;The outlets of the first hydrocyclone 10-1 and the second hydrocyclone 10-2 are both connected to the second rinse tank 5-2;
所述第二水力旋流器10-2、洗涤剂罐15、第一精密过滤器12-1依次连接;The second hydrocyclone 10-2, the detergent tank 15, and the first precision filter 12-1 are sequentially connected;
所述洗涤剂罐15分别与加药罐14和第二精密过滤器12-2相连;The detergent tank 15 is connected to the dosing tank 14 and the second precision filter 12-2, respectively;
所述第二淋洗罐5-2、第二固液混合器8-2、第三水力旋流器10-3、第二精密过滤器12-2、水洗罐6、第二微旋流排序器9-2的第四水力旋流器10-4、离心机13依次连接;The second rinsing tank 5-2, the second solid-liquid mixer 8-2, the third hydrocyclone 10-3, the second precision filter 12-2, the washing tank 6, and the second micro-swirl sorting The fourth hydrocyclone 10-4 and the centrifuge 13 of the device 9-2 are connected in sequence;
所述湿式多级振动筛3的上方配置喷淋设备2。The shower device 2 is disposed above the wet multi-stage vibrating screen 3.
上述装置还具有自来水罐16,所述自来水罐16分别与喷淋设备2、水洗罐
6、离心机13连接。The above device also has a water tank 16 which is respectively associated with a shower device 2 and a water washing tank
6. The centrifuge 13 is connected.
所述第一淋洗罐5-1、第二淋洗罐5-2分别具有超声仪11-1和超声仪11-2。The first rinse tank 5-1 and the second rinse tank 5-2 have an ultrasound system 11-1 and an ultrasound system 11-2, respectively.
所述第一淋洗罐5-1与所述第一固液混合器8-1之间设有泥浆泵7-1;所述第二淋洗罐5-2与所述第二固液混合器8-2之间设有泥浆泵7-2;所述水洗罐6与所述第二微旋流排序器9-2之间设有泥浆泵7-3。a mud pump 7-1 is disposed between the first rinse tank 5-1 and the first solid-liquid mixer 8-1; the second rinse tank 5-2 is mixed with the second solid liquid A mud pump 7-2 is disposed between the tanks 8-2; a mud pump 7-3 is disposed between the water washing tank 6 and the second micro-swirl sequencer 9-2.
所述第一淋洗罐5-1、第二淋洗罐5-2和水洗罐6的上端均安装有双叶轮搅拌机;并且,所述第一淋洗罐5-1、第二淋洗罐5-2分别设有超声振动板。a double impeller mixer is installed on the upper ends of the first rinse tank 5-1, the second rinse tank 5-2 and the water wash tank 6; and the first rinse tank 5-1 and the second rinse tank 5-2 are respectively provided with ultrasonic vibration plates.
所述第一微旋流排序器9-1是顺旋排序器,与所述第一水力旋流器10-1按顺旋连接;所述第二微旋流排序器9-2是逆旋排序器,与所述第四水力旋流器10-4按逆旋连接。The first micro-swirl sequencer 9-1 is a spin sequencer connected in a spiral manner with the first hydrocyclone 10-1; the second micro-swirl sequencer 9-2 is a reverse rotation The sequencer is connected in reverse rotation with the fourth hydrocyclone 10-4.
所述第一固液混合器8-1、第二固液混合器8-2为轴流式混合器,每隔8-12D(D指管道的公称直径,即8-12倍的管道公称直径)安装一个,按照流动方向相邻两个分别为正转和反转。The first solid-liquid mixer 8-1 and the second solid-liquid mixer 8-2 are axial flow mixers, every 8-12D (D refers to the nominal diameter of the pipe, that is, 8-12 times the nominal diameter of the pipe) Install one, two forward and reverse according to the flow direction.
所述第一固液混合器8-1、第二固液混合器8-2为K型管道混合器,每隔8-12D(D指管道的公称直径,即8-12倍的管道公称直径)安装一个。The first solid-liquid mixer 8-1 and the second solid-liquid mixer 8-2 are K-type pipe mixers, every 8-12D (D refers to the nominal diameter of the pipe, that is, 8-12 times the nominal diameter of the pipe) ) Install one.
所述洗涤剂罐15由加药罐14不断补充新鲜的洗涤剂,第二精密过滤器12-2中含有洗涤剂的废液排出至洗涤剂罐15。The detergent tank 15 is continuously replenished with fresh detergent by the dosing tank 14, and the waste liquid containing the detergent in the second precision filter 12-2 is discharged to the detergent tank 15.
喷淋设备2具有多个喷头;湿式多级振动筛3分为两级,一级筛除大于20mm的石块,二级筛除3-20mm的粗砂。The spraying device 2 has a plurality of nozzles; the wet multi-stage vibrating screen 3 is divided into two stages, the first stage screen removes stones larger than 20 mm, and the second stage screens out 3-20 mm coarse sand.
第一水力旋流器10-1和第二水力旋流器10-2可以从土壤中分离出小于3μm左右的少部分细粒径污染物,进入洗涤剂罐15,并再次进入第一淋洗罐5-1和第二淋洗罐5-2进行淋洗。The first hydrocyclone 10-1 and the second hydrocyclone 10-2 can separate a small portion of fine particle contaminants of less than about 3 μm from the soil, enter the detergent tank 15, and enter the first rinse again. The tank 5-1 and the second rinse tank 5-2 are rinsed.
上述装置可以采用并联水力旋流器的方法扩大处理能力。The above device can expand the processing capability by means of a parallel hydrocyclone.
所述第二精密过滤器12-2可以根据实际处理条件替换为离心机。The second precision filter 12-2 can be replaced with a centrifuge according to actual processing conditions.
所述离心机13可以根据实际处理条件替换为压滤机。The centrifuge 13 can be replaced with a filter press according to actual processing conditions.
本发明的有益效果在于:The beneficial effects of the invention are:
(1)采用湿式多级振动筛和水力旋流器对土壤进行多次分级,区别处理,降低了土壤洗涤的总量;在淋洗罐中同时安装搅拌和超声,大大缩短了淋洗时间,提高处理效率;在最后采用精密反冲洗过滤器,达到废水与土壤颗粒的深度分离,
并且达到废水、洗涤剂回用的目的;(1) The soil is multi-classified by wet multi-stage vibrating screen and hydrocyclone, and the treatment is different, which reduces the total amount of soil washing; while stirring and ultrasonic are installed in the washing tank, the washing time is greatly shortened. Improve processing efficiency; at the end of the use of precision backwash filters to achieve deep separation of wastewater and soil particles,
And achieve the purpose of recycling waste water and detergent;
(2)采用固液混合器将普通管道的流体输送功能改为既有输送功能,又有颗粒反应洗涤脱附功能;(2) Using a solid-liquid mixer to change the fluid transport function of the ordinary pipeline to the existing transport function and the particle reaction washing and desorption function;
(3)采用微旋流排序器及对应的逆旋进口和顺旋进口型旋流器,基于旋流场中微粒排序理论,通过使旋流分离器入口截面上微粒分布由均匀混合态转变为有序排列态,从而逆旋提高了微粒分离效率、顺旋提高了微粒分级效率;(3) Using the micro-swirl sequencer and the corresponding counter-rotating inlet and the cyclo-injection type cyclone, based on the particle sorting theory in the swirling flow field, by changing the particle distribution on the inlet section of the cyclone separator from a homogeneous mixed state to Arranging states, thereby reversing the particle separation efficiency and smoothing the particle classification efficiency;
(4)通过串联的两个旋流器降低了废液中粒径大小,减少了废液的量,从而提高了回填率、促进了洗涤剂的减量化;(4) The particle size in the waste liquid is reduced by the two cyclones connected in series, and the amount of waste liquid is reduced, thereby improving the backfill rate and promoting the reduction of the detergent;
(5)针对污染土壤修复,该方法和装置具有自动化程度高、可控性高、适用范围广、紧凑高效、洗涤液耗量少等特点。(5) For the repair of contaminated soil, the method and device have the characteristics of high degree of automation, high controllability, wide application range, compact and high efficiency, and low consumption of washing liquid.
图1是实施例1的装置结构示意图;1 is a schematic structural view of a device of Embodiment 1;
图2是微旋流排序器和水力旋流器的组合方式示意图;其中,(a)是顺旋排序器和水力旋流器的连接方式示意图,(b)是逆旋排序器和水力旋流器的连接方式示意图;2 is a schematic diagram of a combination of a microswirl sequencer and a hydrocyclone; wherein (a) is a schematic diagram of a connection mode of a spin sequencer and a hydrocyclone, and (b) is a reverse sequencer and a hydrocyclone. Schematic diagram of the connection method of the device;
图3是逆旋排序器的外部三视图和内部螺旋结构示意图,分别如(a)、(b)、(c)、(d)所示;Figure 3 is a schematic diagram of the outer three views and the internal spiral structure of the reverse sequencer, as shown in (a), (b), (c), (d), respectively;
图4是顺旋排序器的外部三视图和内部螺旋结构示意图,分别如(a)、(b)、(c)、(d)所示。Figure 4 is a schematic diagram of the outer three views and internal spiral structure of the spin sequencer, as shown in (a), (b), (c), (d), respectively.
符号说明:Symbol Description:
1 传送带;2 喷淋设备;3 湿式多级振动筛;4 泥水储罐;1 conveyor belt; 2 spray equipment; 3 wet multi-stage vibrating screen; 4 mud water storage tank;
5-1 第一淋洗罐;5-2 第二淋洗罐;6 水洗罐;7-1、7-2、7-3 泥浆泵;5-1 first washing tank; 5-2 second washing tank; 6 washing tank; 7-1, 7-2, 7-3 mud pump;
8-1 第一固液混合器;8-2 第二固液混合器;9-1第一微旋流排序器;9-2第二微旋流排序器;10-1 第一水力旋流器;10-2 第二水力旋流器;10-3第三水力旋流器;10-4 第四水力旋流器;11-1、11-2 超声仪;12-1、12-2为精密过滤器;13 离心机;14 加药罐;15 洗涤剂罐;16 自来水罐。8-1 first solid-liquid mixer; 8-2 second solid-liquid mixer; 9-1 first micro-swirl sequencer; 9-2 second micro-swirl sequencer; 10-1 first hydrocyclone 10-2 second hydrocyclone; 10-3 third hydrocyclone; 10-4 fourth hydrocyclone; 11-1, 11-2 ultrasound; 12-1, 12-2 Precision filter; 13 centrifuge; 14 dosing tank; 15 detergent tank; 16 tap water tank.
下面,通过实施例对本发明进行具体描述。有必要在此指出的是,以下实施例只用于对本发明作进一步说明,不能理解为对本发明保护范围的限制,该领域
的专业技术人员根据本发明的内容作出的一些非本质的改进和调整,仍属于本发明的保护范围。Hereinafter, the present invention will be specifically described by way of examples. It is to be noted that the following examples are merely illustrative of the invention and are not to be construed as limiting the scope of the invention.
Some non-essential improvements and modifications made by those skilled in the art in light of the present invention are still within the scope of the present invention.
实施例1Example 1
本申请的发明人经过广泛而深入的研究后发现,对于污染土壤洗涤这种处理量大、处理难度大的固液体系,最有效、廉价的方法是采用旋流洗涤脱附。基于研究,旋流器入口截面处微粒的初始位置对分离性能有着重要的影响,而对于常规旋流器入口截面处颗粒属于混乱分布,设计基于进口微粒排序调控的新型旋流器。微粒逆旋排列的旋流器,其进口外边壁到内边壁粒径由小到大排列、浓度自高到低排序,可以提高分离效率;而顺旋排列可以提高分级效率。基于以上发现,本发明得以完成。The inventors of the present application have found through extensive and intensive research that the most effective and inexpensive method for the treatment of contaminated soils is that the treatment is large and the treatment is difficult, and the most effective and inexpensive method is to use cyclone washing and desorption. Based on the research, the initial position of the particles at the inlet section of the cyclone has an important influence on the separation performance. For the conventional cyclone inlet section, the particles are chaotic, and the design is based on the new type of cyclone. The swirler arranged in the reverse spiral arrangement of the particles has a particle size ranging from small to large, and the concentration is from high to low, which can improve the separation efficiency; and the sequential arrangement can improve the classification efficiency. Based on the above findings, the present invention has been completed.
如图1所示,其主要包括:湿式多级振动筛3、泥水储罐4、第一淋洗罐5-1、第二淋洗罐5-2、水洗罐6、泥浆泵7-1至7-3、第一固液混合器8-1、第二固液混合器8-2、第一微旋流排序器9-1、第二微旋流排序器9-2、第一至第四水力旋流器10-1~10-4、超声仪11-1和11-2、第一精密过滤器12-1、第二精密过滤器12-2、离心机13、加药罐14、洗涤剂罐15、自来水罐16等。其中,微旋流排序器9-1是顺旋排序器;微旋流排序器9-2是逆旋排序器。As shown in Fig. 1, it mainly comprises: wet multistage vibrating screen 3, mud water storage tank 4, first washing tank 5-1, second washing tank 5-2, washing tank 6, mud pump 7-1 to 7-3, the first solid-liquid mixer 8-1, the second solid-liquid mixer 8-2, the first micro-swirl sequencer 9-1, the second micro-swirl sequencer 9-2, the first to the first The four hydrocyclones 10-1 to 10-4, the ultrasound systems 11-1 and 11-2, the first precision filter 12-1, the second precision filter 12-2, the centrifuge 13, the dosing tank 14, Detergent tank 15, tap water tank 16, and the like. Among them, the micro-swirl sequencer 9-1 is a spin sorter; the micro-swirl sorter 9-2 is a reverse-sequence sorter.
污染土壤通过传送带1连续不断的输送至振动筛上方一边喷淋一边筛分。湿式多级振动筛3具有两级筛网,一级筛网孔隙为20mm,用于去除较大的石块;二级筛网孔隙为3mm,用于去除3-20mm的粗砂,但筛网的的孔隙可根据实际情况需要选择。流入泥水储罐4的细土壤颗粒悬浮液依靠重力流入第一淋洗罐5-1,搅拌、超声混合,同时不断加入淋洗剂;泥浆泵7-1将混合液泵入串联的第一固液混合器8-1、第一水力旋流器10-1、第一微旋流排序器9-1、第二水力旋流器10-2,小于3μm的细土壤颗粒悬浮液由第二水力旋流器10-2上端溢流口排入洗涤剂罐15,洗涤剂罐15与第一淋洗罐5-1、第二淋洗罐5-2联通,促进洗涤剂多次循环,另有出口管线进再生系统,中间接精密过滤器保证土壤颗粒不夹带进再生系统而发生堵塞工况,洗涤剂罐15接加药罐14,实现新鲜洗涤剂的补充。第一水力旋流器10-1和第二水力旋流器10-2的下端混合液流入第二淋洗罐5-2,通过搅拌、超声继续混合,同时不断加入淋洗剂。泥浆泵7-2将混合液
泵入顺序连接的第二固液混合器8-2和第三水力旋流器10-3,细土壤颗粒悬浮液由第三水力旋流器10-3的上端溢流口排入第二淋洗罐5-2再次淋洗,第三水力旋流器10-3下端混合液流入第二精密过滤器12-2,使洗涤剂进入洗涤剂罐实现回用,并实现尽量少的洗涤液随土壤夹带进入水洗罐6。水洗罐6通过搅拌继续混合,同时不断加入洁净的自来水。水洗后的混合液经泥浆泵7-3进入顺序连接的第二微旋流排序器9-2和第四水力旋流器10-4,再次分离,溢流口混合液再次排入水洗罐6进行水洗,下部得到悬浮液进入离心机进行脱水,下部得到可以直接回填的土壤,上部得到的水进入自来水罐16回用。整套设备的运行可经过自动控制柜控制。The contaminated soil is continuously conveyed by the conveyor belt 1 to the upper side of the vibrating screen while being sprayed and sieved. The wet multi-stage vibrating screen 3 has a two-stage screen. The primary screen has a pore size of 20 mm for removing large stones. The secondary screen has a pore size of 3 mm for removing 3-20 mm of coarse sand, but the screen The pores can be selected according to the actual situation. The fine soil particle suspension flowing into the mud water storage tank 4 flows into the first washing tank 5-1 by gravity, is stirred and ultrasonically mixed, and is continuously added with the eluent; the mud pump 7-1 pumps the mixed liquid into the first solid in series. The liquid mixer 8-1, the first hydrocyclone 10-1, the first micro-swirl sequencer 9-1, the second hydrocyclone 10-2, the fine soil particle suspension of less than 3 μm by the second hydraulic force The overflow port of the upper end of the cyclone 10-2 is discharged into the detergent tank 15, and the detergent tank 15 is connected with the first rinse tank 5-1 and the second rinse tank 5-2 to promote the multiple circulation of the detergent. The outlet pipeline enters the regeneration system, and the indirect precision filter ensures that the soil particles are not entrained into the regeneration system and the plugging condition occurs, and the detergent tank 15 is connected to the dosing tank 14 to realize the supplement of the fresh detergent. The mixture of the lower end of the first hydrocyclone 10-1 and the second hydrocyclone 10-2 flows into the second rinse tank 5-2, and the mixing is continued by stirring and ultrasonication while continuously adding the eluent. Mud pump 7-2 will mix
The second solid-liquid mixer 8-2 and the third hydrocyclone 10-3 which are sequentially connected are pumped, and the fine soil particle suspension is discharged into the second shower by the upper overflow port of the third hydrocyclone 10-3. The washing tank 5-2 is rinsed again, and the mixture of the lower end of the third hydrocyclone 10-3 flows into the second precision filter 12-2, so that the detergent enters the detergent tank to realize reuse, and realizes as little washing liquid as possible. The soil is entrained into the wash tank 6. The washing tank 6 is continuously mixed by stirring while continuously adding clean tap water. The washed mixture is passed through the mud pump 7-3 into the sequentially connected second micro-swirl sequencer 9-2 and the fourth hydrocyclone 10-4, and separated again, and the overflow mixture is discharged into the washing tank 6 again. The water is washed, the lower part is suspended into a centrifuge for dehydration, the lower part is obtained by directly backfilling the soil, and the water obtained in the upper part is returned to the tap water tank 16 for reuse. The operation of the entire set of equipment can be controlled by an automatic control cabinet.
如图2所示,其中,(a)是顺旋排序器和水力旋流器的连接方式示意图,(b)是逆旋排序器和水力旋流器的连接方式示意图。As shown in FIG. 2, (a) is a schematic diagram of a connection mode of a spin sequencer and a hydrocyclone, and (b) is a schematic diagram of a connection mode of a reverse sequencer and a hydrocyclone.
图3是逆旋排序器的外部三视图和内部螺旋结构示意图,分别如(a)、(b)、(c)、(d)所示;Figure 3 is a schematic diagram of the outer three views and the internal spiral structure of the reverse sequencer, as shown in (a), (b), (c), (d), respectively;
图4是顺旋排序器的外部三视图和内部螺旋结构示意图,分别如(a)、(b)、(c)、(d)所示。
Figure 4 is a schematic diagram of the outer three views and internal spiral structure of the spin sequencer, as shown in (a), (b), (c), (d), respectively.
Claims (12)
- 一种组合式土壤洗涤脱附的方法,其特征在于,包括如下步骤:A combined soil washing and desorption method, comprising the steps of:(1)喷淋污染土壤后用湿式多级振动筛进行筛分,以去除粒径大于3mm的可直接回填的石块和粗砂,保证进入洗涤脱附系统的粒径为50μm~3mm的颗粒质量浓度为70%以上;(1) After spraying the contaminated soil, it is sieved with a wet multi-stage vibrating screen to remove the directly backfillable stones and coarse sand with a particle diameter of more than 3 mm to ensure the particles having a particle size of 50 μm to 3 mm entering the washing and desorption system. The mass concentration is 70% or more;(2)对步骤(1)得到的筛下细土壤颗粒悬浮液进行洗涤脱附处理,控制流速为2~5m/s,固液混合液的体积浓度为5~40%;通过第一固液混合器进行输送和混合,然后在第一旋流器中旋流洗涤脱附并分级,第一旋流器的主要功能为颗粒分级,分级精度为100~200μm;第一级旋流器溢流出口出来的含固洗涤液通过前端装有微旋流排序器的第二旋流器进行深度分离,第二旋流器的功能为分离功能,分离精度为3μm,以保证返回洗涤液储罐的洗涤液含固量小于0.03%;(2) washing and desorbing the fine soil particle suspension obtained in the step (1), controlling the flow rate to be 2 to 5 m/s, and the volume concentration of the solid-liquid mixture is 5 to 40%; The mixer is transported and mixed, and then desorbed and classified by swirl washing in the first cyclone. The main function of the first cyclone is particle classification, the classification accuracy is 100-200 μm; the first-stage cyclone overflow The solid washing liquid discharged from the outlet is deeply separated by a second cyclone equipped with a micro-swirl sequencer at the front end, and the function of the second cyclone is a separation function with a separation precision of 3 μm to ensure return of the washing liquid storage tank. The solid content of the washing liquid is less than 0.03%;(3)用淋洗剂淋洗步骤(2)分离出的剩余中间粒径为10μm~3mm的沙质土并通过第二固液混合器进行混合和洗涤脱附,然后通过第三旋流器进行旋流洗涤脱附并提浓,第三旋流器的功能设置为含固液体增浓及土壤颗粒中污染物的深度脱附功能,达到预分离的目的;(3) using the eluent rinsing step (2) to remove the remaining sandy soil having an intermediate particle diameter of 10 μm to 3 mm and mixing and washing the desorption by the second solid-liquid mixer, and then passing through the third cyclone The cyclone washing is desorbed and concentrated, and the function of the third cyclone is set to deepen the desorption function of the solid liquid and the contaminants in the soil particles to achieve the purpose of pre-separation;(4)对预分离后的悬浮液进行精细分离;(4) fine separation of the pre-separated suspension;(5)步骤(4)分离得到的土壤进入水洗罐洗涤脱附后进入前端装有微旋流排序器的第四旋流器进行提浓,第四旋流器的功能设置为增浓作用,使液体含固量从3~10%提高到40~60%,之后通过离心机进行脱水,脱除的水进入自来水罐进行回用,脱水后的土壤回填。(5) The soil separated in step (4) enters the washing tank, is washed and desorbed, and then enters the fourth cyclone equipped with a micro-swirl sequencer for concentration, and the function of the fourth cyclone is set to enrichment. The liquid solid content is increased from 3 to 10% to 40 to 60%, and then dehydrated by a centrifuge, and the removed water is returned to the tap water tank for reuse, and the dehydrated soil is backfilled.
- 根据权利要求1所述的方法,其特征在于,所述洗涤脱附处理为超声、搅拌、淋洗液混合洗涤脱附。The method of claim 1 wherein said washing and desorbing treatment is ultrasonic, agitating, eluent, mixed washing and desorption.
- 根据权利要求1所述的方法,其特征在于,所述水洗罐洗涤方式为搅拌、清水混合洗涤脱附。The method according to claim 1, wherein the washing tank washing mode is stirring, water mixing washing and desorption.
- 根据权利要求1所述的方法,其特征在于,所述固液混合器内固液混合物旋转流动,液体的线速度控制为2~5m/s。The method according to claim 1, wherein the solid-liquid mixture in the solid-liquid mixer is rotated, and the linear velocity of the liquid is controlled to 2 to 5 m/s.
- 一种组合式旋流土壤洗涤脱附的装置,其特征在于,包括依次连接的以下单元: A combined swirling soil washing and desorption device, comprising the following units connected in sequence:湿式多级振动筛(3)、泥水储罐(4)、第一淋洗罐(5-1)、第一固液混合器(8-1)、第一水力旋流器(10-1)、第一微旋流排序器(9-1)的第二水力旋流器(10-2);Wet multi-stage vibrating screen (3), mud water storage tank (4), first elution tank (5-1), first solid-liquid mixer (8-1), first hydrocyclone (10-1) a second hydrocyclone (10-2) of the first micro-swirl sequencer (9-1);所述第一水力旋流器(10-1)和第二水力旋流器(10-2)的出口均与第二淋洗罐(5-2)连接;The outlets of the first hydrocyclone (10-1) and the second hydrocyclone (10-2) are both connected to the second rinse tank (5-2);所述第二水力旋流器(10-2)、洗涤剂罐(15)、第一精密过滤器(12-1)依次连接;The second hydrocyclone (10-2), the detergent tank (15), and the first precision filter (12-1) are sequentially connected;所述洗涤剂罐(15)分别与加药罐(14)和第二精密过滤器(12-2)相连;The detergent tank (15) is respectively connected to the dosing tank (14) and the second precision filter (12-2);所述第二淋洗罐(5-2)、第二固液混合器(8-2)、第三水力旋流器(10-3)、第二精密过滤器(12-2)、水洗罐(6)、第二微旋流排序器(9-2)的第四水力旋流器(10-4)、离心机(13)依次连接;The second rinsing tank (5-2), the second solid-liquid mixer (8-2), the third hydrocyclone (10-3), the second precision filter (12-2), and the washing tank (6) The fourth hydrocyclone (10-4) and the centrifuge (13) of the second micro-swirl sequencer (9-2) are sequentially connected;所述湿式多级振动筛(3)的上方配置喷淋设备(2)。A spraying device (2) is disposed above the wet multi-stage vibrating screen (3).
- 根据权利要求5所述的装置,其特征在于,还具有自来水罐(16),所述自来水罐(16)分别与喷淋设备(2)、水洗罐(6)、离心机(13)连接。The apparatus according to claim 5, further comprising a tap water tank (16), the tap water tank (16) being connected to the shower device (2), the water washing tank (6), and the centrifuge (13), respectively.
- 根据权利要求5所述的装置,其特征在于,所述第一淋洗罐(5-1)、第二淋洗罐(5-2)分别具有超声仪(11-1)和超声仪(11-2)。The apparatus according to claim 5, wherein said first rinse tank (5-1) and said second rinse tank (5-2) have an ultrasound system (11-1) and an ultrasound system (11, respectively) -2).
- 根据权利要求5所述的装置,其特征在于,所述第一淋洗罐(5-1)与所述第一固液混合器(8-1)之间设有泥浆泵(7-1);所述第二淋洗罐(5-2)与所述第二固液混合器(8-2)之间设有泥浆泵(7-2);所述水洗罐(6)与所述微旋流排序器(9-2)之间设有泥浆泵(7-3)。The apparatus according to claim 5, characterized in that a mud pump (7-1) is provided between the first rinse tank (5-1) and the first solid-liquid mixer (8-1) a mud pump (7-2) is disposed between the second rinse tank (5-2) and the second solid-liquid mixer (8-2); the water wash tank (6) and the micro A mud pump (7-3) is provided between the swirl sorters (9-2).
- 根据权利要求5所述的装置,其特征在于,所述第一淋洗罐(5-1)、第二淋洗罐(5-2)和水洗罐(6)的上端均安装有双叶轮搅拌机;并且,所述第一淋洗罐(5-1)、第二淋洗罐(5-2)分别设有超声振动板。The apparatus according to claim 5, characterized in that the upper ends of the first rinse tank (5-1), the second rinse tank (5-2) and the water wash tank (6) are equipped with a double impeller mixer And, the first rinsing tank (5-1) and the second rinsing tank (5-2) are respectively provided with ultrasonic vibration plates.
- 根据权利要求5所述的装置,其特征在于,所述第一微旋流排序器(9-1)是顺旋排序器,与所述第一水力旋流器(10-1)按顺旋连接;所述第二微旋流排序器(9-2)是逆旋排序器,与所述第四水力旋流器(10-4)按逆旋连接。The apparatus according to claim 5, wherein said first micro-swirl sequencer (9-1) is a spin sequencer, and said first hydrocyclone (10-1) is rotated in sequence The second micro-swirl sequencer (9-2) is a reverse-sequencer that is connected in reverse to the fourth hydrocyclone (10-4).
- 根据权利要求5所述的装置,其特征在于,所述第一固液混合器(8-1)、第二固液混合器(8-2)为轴流式混合器,每隔8~12D;安装一个,按照流动方向相邻两个分别为正转和反转; The apparatus according to claim 5, wherein said first solid-liquid mixer (8-1) and said second solid-liquid mixer (8-2) are axial flow mixers, every 8 to 12D Install one, two forward and reverse according to the flow direction;D指管道的公称直径,即8-12倍的管道公称直径。D refers to the nominal diameter of the pipe, which is 8-12 times the nominal diameter of the pipe.
- 根据权利要求5所述的装置,其特征在于,所述第一固液混合器(8-1)、第二固液混合器(8-2)为K型管道混合器,每隔8~12D安装一个;The apparatus according to claim 5, wherein said first solid-liquid mixer (8-1) and said second solid-liquid mixer (8-2) are K-type pipe mixers every 8 to 12D. Install one;D指管道的公称直径,即8-12倍的管道公称直径。 D refers to the nominal diameter of the pipe, which is 8-12 times the nominal diameter of the pipe.
Applications Claiming Priority (2)
Application Number | Priority Date | Filing Date | Title |
---|---|---|---|
CN201510705751.8A CN105170630B (en) | 2015-10-27 | 2015-10-27 | A kind of method and apparatus of combined type soil washing desorption |
CN201510705751.8 | 2015-10-27 |
Publications (1)
Publication Number | Publication Date |
---|---|
WO2017071104A1 true WO2017071104A1 (en) | 2017-05-04 |
Family
ID=54893318
Family Applications (1)
Application Number | Title | Priority Date | Filing Date |
---|---|---|---|
PCT/CN2016/000013 WO2017071104A1 (en) | 2015-10-27 | 2016-01-11 | Combined soil washing desorption method and device |
Country Status (2)
Country | Link |
---|---|
CN (1) | CN105170630B (en) |
WO (1) | WO2017071104A1 (en) |
Cited By (7)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
CN107185953A (en) * | 2017-06-20 | 2017-09-22 | 陕西科技大学 | A kind of prosthetic device and method for extracting heavy metal in soil |
CN109433811A (en) * | 2018-11-28 | 2019-03-08 | 中国科学院地理科学与资源研究所 | Contaminated soil remediation device |
CN112692045A (en) * | 2020-11-30 | 2021-04-23 | 四川长虹格润环保科技股份有限公司 | Leaching process for repairing high-load metal polluted soil |
CN113774238A (en) * | 2021-09-15 | 2021-12-10 | 江西离子型稀土工程技术研究有限公司 | Process for cascade leaching of ammonia nitrogen in ionic rare earth tailings |
CN115026120A (en) * | 2022-05-23 | 2022-09-09 | 中国人民解放军63653部队 | Polluted sandy soil ex-situ chemical leaching system and plutonium polluted sandy soil ex-situ leaching method |
CN115401063A (en) * | 2021-05-27 | 2022-11-29 | 郑州德森环境科技有限公司 | Automatic soil leaching system |
CN117415150A (en) * | 2023-12-05 | 2024-01-19 | 中国科学院地理科学与资源研究所 | Emergency disposal method and system suitable for polluted soil |
Families Citing this family (10)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
CN105170630B (en) * | 2015-10-27 | 2018-05-18 | 华东理工大学 | A kind of method and apparatus of combined type soil washing desorption |
CN105772497B (en) * | 2016-04-12 | 2019-07-30 | 上海格林曼环境技术有限公司 | A kind of soil heterotopic elution reparation complete set of equipments |
CN105935684A (en) * | 2016-06-23 | 2016-09-14 | 大连德联投资控股有限公司 | Integrated soil reusing and repairing system of waste landfill site and working method thereof |
CN106040729A (en) * | 2016-06-30 | 2016-10-26 | 华东理工大学 | Method for reinforcing pollutant desorption in fine soil particles |
CN106077062A (en) * | 2016-06-30 | 2016-11-09 | 华东理工大学 | The method that a kind of soil slurry wash desorption and enrichment process |
CN106583438A (en) * | 2017-01-25 | 2017-04-26 | 江苏三联安全评价咨询有限公司 | Remediation system and method for poisonous and harmful soil |
CN108405588B (en) * | 2018-03-21 | 2020-07-31 | Jiu株式会社 | Flotation equipment for ex-situ leaching remediation of contaminated soil |
CN112222173B (en) * | 2020-09-01 | 2023-09-22 | 山西大学 | Boiling type micro-foam multifunctional soil pollutant desorption device |
CN112845553A (en) * | 2020-12-28 | 2021-05-28 | 华东理工大学 | Method and device for restoring heavy metal contaminated soil |
CN113000586A (en) * | 2021-02-05 | 2021-06-22 | 广州市第一市政工程有限公司 | Be used for prosthetic drip washing device of soil |
Citations (6)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
CN1660515A (en) * | 2004-02-27 | 2005-08-31 | 阿斯特古股份有限公司 | Purification method of polluted soil |
JP2006116397A (en) * | 2004-10-20 | 2006-05-11 | Shimizu Corp | Washing method and washing apparatus of contaminated soil |
KR101167479B1 (en) * | 2011-11-10 | 2012-07-27 | 현대건설주식회사 | System and method for remediating contaminated soil of highly contaminant-concentrated fine soil using multiple micro hydrocyclone |
CN103286122A (en) * | 2013-04-12 | 2013-09-11 | 浙江桃花源环保科技有限公司 | Leaching restoration engineered apparatus for persistent organic pollutant-contaminated site |
CN104889149A (en) * | 2015-06-10 | 2015-09-09 | 中国科学院地理科学与资源研究所 | Ectopic classification leaching repair complete process of arsenic and heavy metal contaminated soil |
CN105170630A (en) * | 2015-10-27 | 2015-12-23 | 华东理工大学 | Combined type soil washing and desorption method and device |
Family Cites Families (6)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
CN1513891A (en) * | 2003-01-29 | 2004-07-21 | 田玉忠 | Biodegradable water absorprion agent and its microorganism composite preparation method |
JP5796152B2 (en) * | 2010-05-07 | 2015-10-21 | パナソニックIpマネジメント株式会社 | Pretreatment method for PCB contaminated soil |
CN103240266A (en) * | 2012-04-27 | 2013-08-14 | 罗春晖 | Mobile soil washing apparatus and method thereof |
KR101227173B1 (en) * | 2012-06-07 | 2013-02-05 | 주식회사 대일이앤씨 | Explosives-contaminated soil purification method using basic hydrolysing agent |
CN104607454B (en) * | 2015-01-23 | 2018-04-06 | 苏州同和环保工程有限公司 | The heat treatment restorative procedure and system of a kind of contaminated soil |
CN204448809U (en) * | 2015-01-23 | 2015-07-08 | 苏州同和环保工程有限公司 | A kind of for the system in the heat treatment restorative procedure of contaminated soil |
-
2015
- 2015-10-27 CN CN201510705751.8A patent/CN105170630B/en active Active
-
2016
- 2016-01-11 WO PCT/CN2016/000013 patent/WO2017071104A1/en active Application Filing
Patent Citations (6)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
CN1660515A (en) * | 2004-02-27 | 2005-08-31 | 阿斯特古股份有限公司 | Purification method of polluted soil |
JP2006116397A (en) * | 2004-10-20 | 2006-05-11 | Shimizu Corp | Washing method and washing apparatus of contaminated soil |
KR101167479B1 (en) * | 2011-11-10 | 2012-07-27 | 현대건설주식회사 | System and method for remediating contaminated soil of highly contaminant-concentrated fine soil using multiple micro hydrocyclone |
CN103286122A (en) * | 2013-04-12 | 2013-09-11 | 浙江桃花源环保科技有限公司 | Leaching restoration engineered apparatus for persistent organic pollutant-contaminated site |
CN104889149A (en) * | 2015-06-10 | 2015-09-09 | 中国科学院地理科学与资源研究所 | Ectopic classification leaching repair complete process of arsenic and heavy metal contaminated soil |
CN105170630A (en) * | 2015-10-27 | 2015-12-23 | 华东理工大学 | Combined type soil washing and desorption method and device |
Cited By (9)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
CN107185953A (en) * | 2017-06-20 | 2017-09-22 | 陕西科技大学 | A kind of prosthetic device and method for extracting heavy metal in soil |
CN107185953B (en) * | 2017-06-20 | 2023-05-26 | 陕西科技大学 | Repairing device and method for extracting heavy metals in soil |
CN109433811A (en) * | 2018-11-28 | 2019-03-08 | 中国科学院地理科学与资源研究所 | Contaminated soil remediation device |
CN112692045A (en) * | 2020-11-30 | 2021-04-23 | 四川长虹格润环保科技股份有限公司 | Leaching process for repairing high-load metal polluted soil |
CN112692045B (en) * | 2020-11-30 | 2022-03-08 | 四川长虹格润环保科技股份有限公司 | Leaching process for repairing high-load metal polluted soil |
CN115401063A (en) * | 2021-05-27 | 2022-11-29 | 郑州德森环境科技有限公司 | Automatic soil leaching system |
CN113774238A (en) * | 2021-09-15 | 2021-12-10 | 江西离子型稀土工程技术研究有限公司 | Process for cascade leaching of ammonia nitrogen in ionic rare earth tailings |
CN115026120A (en) * | 2022-05-23 | 2022-09-09 | 中国人民解放军63653部队 | Polluted sandy soil ex-situ chemical leaching system and plutonium polluted sandy soil ex-situ leaching method |
CN117415150A (en) * | 2023-12-05 | 2024-01-19 | 中国科学院地理科学与资源研究所 | Emergency disposal method and system suitable for polluted soil |
Also Published As
Publication number | Publication date |
---|---|
CN105170630A (en) | 2015-12-23 |
CN105170630B (en) | 2018-05-18 |
Similar Documents
Publication | Publication Date | Title |
---|---|---|
WO2017071104A1 (en) | Combined soil washing desorption method and device | |
CN104399689B (en) | A kind of cleaning equipment of concrete-agitating axle of circulation type | |
KR100952752B1 (en) | Apparatus for washing soils polluted with oil and heavy metal and method thereof | |
WO2022105698A1 (en) | Processing system and method for offshore gas field complex production fluid | |
KR100534067B1 (en) | Soil washing method and facility for physical separation and remediation of polluted soil | |
CN101580322A (en) | Sewage processing method and sewage processing device | |
JP2004321839A (en) | Filter device and filtering method using the same | |
CN110104852A (en) | It is a kind of can be by the car wash water water supply device of wastewater from car washer cycling and reutilization | |
CN209052494U (en) | Mine waste discharge water treatment facilities | |
WO2017071103A1 (en) | Movable combined method and movable combined device for washing oil sand | |
CN201799196U (en) | Steel structure dust removing device | |
CN106040729A (en) | Method for reinforcing pollutant desorption in fine soil particles | |
CN105344682A (en) | Cleaning device for oil tank | |
CN203577382U (en) | Flowing liquid wall-washing recoilless filter | |
CN105618281B (en) | A kind of method for separating and device of different-grain diameter contaminated soil particle | |
CN205803170U (en) | A kind of Waste Water Treatment in coal | |
CN106745902A (en) | The processing system and method for cleaning fluid in Coating Pretreatment | |
CN108744708B (en) | A kind of environment-friendly type intelligent car carwash waste water segment processing pond | |
KR101270065B1 (en) | Chemistry washing method | |
CN207287732U (en) | A kind of stock grading recovery system of Soil leaching | |
CN215365170U (en) | Car washing sewage recycling system | |
CN102976507A (en) | Wastewater rotational flow treatment device | |
CN204307857U (en) | A kind of cleaning equipment of concrete-agitating axle of circulation type | |
JP2012041590A (en) | Foreign matter-removing system in treatment tank | |
CN107537262A (en) | Spiral-flow type air cleaning system |
Legal Events
Date | Code | Title | Description |
---|---|---|---|
121 | Ep: the epo has been informed by wipo that ep was designated in this application |
Ref document number: 16858555 Country of ref document: EP Kind code of ref document: A1 |
|
NENP | Non-entry into the national phase |
Ref country code: DE |
|
122 | Ep: pct application non-entry in european phase |
Ref document number: 16858555 Country of ref document: EP Kind code of ref document: A1 |