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CN103286120A - Microwave electric soil in-situ restoration device and restoration method - Google Patents

Microwave electric soil in-situ restoration device and restoration method Download PDF

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CN103286120A
CN103286120A CN2013102271198A CN201310227119A CN103286120A CN 103286120 A CN103286120 A CN 103286120A CN 2013102271198 A CN2013102271198 A CN 2013102271198A CN 201310227119 A CN201310227119 A CN 201310227119A CN 103286120 A CN103286120 A CN 103286120A
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CN103286120B (en
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何理
李晶
董焕焕
潘海洋
卢宏玮
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North China Electric Power University
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Abstract

The invention discloses a microwave electric soil in-situ restoration device and a restoration method, and belongs to the technical field of in-situ restoration for soil pollutions. The device consists of an electrode system, a microwave heating system and an underground water circulation system and comprises a negative electrode well (1) and the like, wherein a negative electrode (3) is arranged in the negative electrode well (1). A microwave absorption material is buried into the soil; a closed gas collection shed is constructed; a pH monitoring device and a temperature sensor are arranged in the closed gas collection shed; part of organic pollutants and heavy metals in the soil are treated; underground water is pumped out and then injected into the soil to increase the migration speed of live particles and accelerate the soil heating process; volatile organic compounds are recycled; distilled water is injected into the underground water; non-volatile and non-degradable organic pollutants and residual heavy metals are treated by a high-temperature microwave soil thermal restoration technology. The technical equipment is compact in structure, easy to operate and high in reliability and has high popularization potential home and abroad and in particular has a wide application prospect to composite soil pollutions with the heavy metals and the organic compounds.

Description

一种微波电动土壤原位修复装置及修复方法A microwave electrodynamic soil in-situ restoration device and restoration method

技术领域technical field

本发明涉及一种微波电动土壤原位修复装置及修复方法,属于土壤污染的原位修复技术领域。The invention relates to a microwave electric soil in-situ repair device and a repair method, belonging to the technical field of in-situ repair of soil pollution.

背景技术Background technique

随着我国工业化、城市化及现代农业化的进程,土壤污染日益严重,并逐步表现为多种污染物的复合污染。尤以重金属污染和高毒性、持久性有机物污染最为突出,它们主要来自废厂矿区、污灌区、生活垃圾、工业三废以及农药、化肥的大量使用。调查研究显示,我国受镉、砷、铅等重金属污染造成的经济损失巨大。另一方面,有机污染以其持久性、高毒性、积聚性、流动性的特征,协同重金属污染的隐蔽性、长期性、不可逆性特点,成为当前的研究热点。总之,重金属、有机污染物不仅改变土壤的理化特征,导致土壤的退化、农作物产量和品质的降低,而且通过径流和淋洗作用污染地表水和地下水,恶化水文环境,并可能通过直接接触、食物链等途径危及人类的生命和健康。因此,解决这类复合型污染土壤的修复问题,迫在眉睫。With the process of industrialization, urbanization and modern agriculturalization in our country, soil pollution is becoming more and more serious, and it gradually manifests as compound pollution of various pollutants. In particular, heavy metal pollution and highly toxic and persistent organic pollution are the most prominent. They mainly come from abandoned factories and mines, sewage irrigation areas, domestic garbage, industrial waste, and the extensive use of pesticides and fertilizers. Investigations and studies have shown that heavy metal pollution such as cadmium, arsenic, and lead in my country has caused huge economic losses. On the other hand, organic pollution has become a current research hotspot due to its persistent, highly toxic, accumulative, and fluid characteristics, combined with the concealment, long-term, and irreversible characteristics of heavy metal pollution. In short, heavy metals and organic pollutants not only change the physical and chemical characteristics of the soil, leading to soil degradation, crop yield and quality reduction, but also pollute surface water and groundwater through runoff and leaching, deteriorating the hydrological environment, and may cause pollution through direct contact, food chain and other ways to endanger human life and health. Therefore, it is imminent to solve the remediation problem of this kind of compound polluted soil.

当前,污染土壤修复技术主要包括物理工程修复、蒸汽萃取和生物修复等。其中蒸汽萃取虽能有效地处理气相污染物,但对液相、残留相的污染物只能采取其他方法处理,导致处理系统复杂、处理成本高昂。植物修复法就是利用植物直接或间接的吸收、同化、降解作用,修复受污染的土壤,但其处理周期较长,短时间内达不到明显的效果。而微生物降解法虽然操作比较简单、且无污染,但是特定的微生物只降解特定类型的化学物质。此外,微生物活性还受温度和其它环境条件变化的影响较大,这就极大的限制了微生物降解法的应用范围。由此可见,每种方法都有其修复对象的针对性和优缺点,事实上也正是由于这种修复的针对性或单一性,在处理复合污染时便不具备应用价值。为克服这一局限性,一种联合修复技术应用而生。Currently, contaminated soil remediation technologies mainly include physical engineering remediation, steam extraction and bioremediation. Among them, although steam extraction can effectively treat gas-phase pollutants, other methods can only be used to treat liquid-phase and residual-phase pollutants, resulting in complex treatment systems and high treatment costs. Phytoremediation is the use of direct or indirect absorption, assimilation, and degradation of plants to restore contaminated soil, but the treatment cycle is long and no obvious effect can be achieved in a short time. Although the microbial degradation method is relatively simple to operate and has no pollution, specific microorganisms only degrade specific types of chemical substances. In addition, microbial activity is also greatly affected by changes in temperature and other environmental conditions, which greatly limits the scope of application of microbial degradation methods. It can be seen that each method has its pertinence, advantages and disadvantages of the remediation object. In fact, it is precisely because of the pertinence or singleness of this remediation that it has no application value when dealing with complex pollution. To overcome this limitation, a combined repair technique was developed.

电动力学技术是一种新兴的土壤原位修复技术。该技术可以有效的去除土壤的有机和无机污染物,尤其是重金属,具有可控性强和处理效果好、容易安装和操作、耗费人力少、接触毒害物质少、经济效益高且不破坏原有自然环境等优点,从而能够在进行环境修复的同时,最大限度地保护原有的生态环境。近几年国内外已有较多的小试研究报道,也有少量中试和工程应用实例。鉴于该方法对有机物处理效率不高,进而我们引进修复效率较高的热处理法作为该项联合修复技术的另一核心内容,考虑到联合修复系统的可操作性、简易性、经济性、前瞻性以及不对已有电动修复产生干扰影响,微波加热法是一个合理的选择。近年来微波技术作为一项新的污染土壤修复技术,开始引起广泛关注。微波用于土壤修复,不仅能处理挥发性、半挥发性的有机物,如卤代烃、多环芳烃、多氯联苯等,还能处理重金属等非挥发性物质。微波加热可对被加热物质里外一起加热,加热极快,并且热损耗小、热效率高。在热修复污染土壤时具有高效、快捷,操作灵活,对环境影响小,适用范围广且具有选择性加热的特点,可分离回收某些有用的组分。目前已有人做过微波修复土壤中有机溶剂、多环芳烃、多氯联苯和重金属等的研究,处理效果较好。但大部分研究都集中在微波对污染土壤的异位修复,重点进行了污染土壤修复效果和机理的实验研究,没有对修复技术的系统性及工业化进行探讨。因此,鉴于以上两种方法都能处理重金属和有机污染物,且其处理对象的侧重点又优势互补,可相得益彰应用于土壤原位联合修复。Electrokinetic technology is an emerging soil in-situ remediation technology. This technology can effectively remove organic and inorganic pollutants in soil, especially heavy metals. It has strong controllability, good treatment effect, easy installation and operation, less manpower consumption, less exposure to toxic substances, high economic benefits and no damage to the original Natural environment and other advantages, so as to protect the original ecological environment to the greatest extent while carrying out environmental restoration. In recent years, there have been many small test research reports at home and abroad, and there are also a small number of pilot test and engineering application examples. In view of the low efficiency of this method for the treatment of organic matter, we introduced the heat treatment method with high restoration efficiency as another core content of this joint restoration technology. Considering the operability, simplicity, economy, and forward-looking of the joint restoration system And without disturbing the existing electric restoration, the microwave heating method is a reasonable choice. In recent years, microwave technology, as a new contaminated soil remediation technology, has attracted widespread attention. Microwave is used for soil remediation, not only can deal with volatile and semi-volatile organic compounds, such as halogenated hydrocarbons, polycyclic aromatic hydrocarbons, polychlorinated biphenyls, etc., but also non-volatile substances such as heavy metals. Microwave heating can heat the inside and outside of the heated substance together, the heating is extremely fast, and the heat loss is small and the thermal efficiency is high. It has high efficiency, quickness, flexible operation, small impact on the environment, wide application range and selective heating when thermally remediating polluted soil, and can separate and recover some useful components. At present, some people have done research on microwave remediation of organic solvents, polycyclic aromatic hydrocarbons, polychlorinated biphenyls and heavy metals in soil, and the treatment effect is good. However, most of the research focuses on the ex-situ remediation of contaminated soil by microwave, focusing on the experimental research on the effect and mechanism of remediation of contaminated soil, without discussing the systematic and industrialization of remediation technology. Therefore, in view of the fact that the above two methods can deal with heavy metals and organic pollutants, and the focus of their treatment objects is complementary, they can complement each other and be applied to soil in-situ joint restoration.

发明内容Contents of the invention

本发明的目的在于针对现有电动力修复和土壤热修复技术的不足,将二者结合并强化,提出一种微波电动土壤原位处理技术,处理前期采用电动力修复和微波加热联合修复技术处理土壤中部分有机污染物和重金属,后期采用高温微波土壤热修复技术处理难挥发、难降解的有机污染物和残余重金属。具有修复时间短,修复效果好,能处理重金属以及有机物复合型污染的土壤,流程简单易操作等优点。The purpose of the present invention is to address the deficiencies of the existing electrodynamic restoration and soil thermal restoration technologies, combine and strengthen the two, and propose a microwave electrodynamic soil in-situ treatment technology, which uses electrodynamic restoration and microwave heating combined restoration technology in the early stage For some organic pollutants and heavy metals in the soil, high-temperature microwave soil thermal remediation technology is used in the later stage to deal with organic pollutants and residual heavy metals that are difficult to volatilize and degrade. It has the advantages of short repair time, good repair effect, can deal with heavy metal and organic compound-contaminated soil, and the process is simple and easy to operate.

一种微波电动土壤原位修复装置,该修复装置由电极系统、微波加热系统、地下水循环系统三部分组成。A microwave electric soil in-situ restoration device is composed of three parts: an electrode system, a microwave heating system, and a groundwater circulation system.

1、电极系统由分布在所处理土壤区域两端的石墨组成的阳极和阴极电极井组成,在电极中装有电解液。1. The electrode system consists of anode and cathode electrode wells composed of graphite distributed at both ends of the treated soil area, and the electrodes are filled with electrolyte.

2、微波加热系统包括安装在所处理土壤区域上方的集气棚、微波辐射器以及埋在土壤中的微波吸收材料组成。2. The microwave heating system consists of a gas-gathering shed installed above the treated soil area, a microwave radiator, and microwave-absorbing materials buried in the soil.

3、地下水循环处理系统由分布在所处理土壤区域外围的抽水井、注水井以及真空抽吸泵组成。3. The groundwater circulation treatment system consists of pumping wells, water injection wells and vacuum pumps distributed around the treated soil area.

一种微波电动土壤原位修复方法,该方法步骤为:A microwave electrokinetic soil repair method in situ, the method steps are:

1)启动离心泵将适量的地下水抽出缓缓地注入所处理土壤的土层之中,是土壤中保持一定的水分。1) Start the centrifugal pump to pump out an appropriate amount of groundwater and slowly inject it into the soil layer of the treated soil to maintain a certain amount of water in the soil.

2)启动供电系统,开启电动力修复系统。存在于土壤中的带正电荷的离子(尤其是重金属离子)会向阴极移动,使其富集到阴极附近的区域;带负电荷的离子会向阳极移动,使其富集到阳极附近的区域,达到去除土壤中污染物的目的。同时打开安装在电极井中的pH监测系统,监测电极液的pH变化,以便向电极液中加入酸或碱来调节pH。2) Start the power supply system and turn on the electric power repair system. Positively charged ions (especially heavy metal ions) present in the soil move towards the cathode, enriching the area near the cathode; negatively charged ions move towards the anode, enriching the area near the anode , to achieve the purpose of removing pollutants in the soil. At the same time, the pH monitoring system installed in the electrode well is turned on to monitor the pH change of the electrode solution, so as to add acid or alkali to the electrode solution to adjust the pH.

3)同时打开土壤上方的微波辐射器,使微波辐射到土壤深处,土壤被慢慢加热到一定温度。此时,微波加热和电动力修复同时进行。由于存在事先埋在土壤中的微波吸收材料,并且土壤中还含有从地下水中注入的一定的水分,所以使得微波被吸收的更快更好,使得土壤受热均匀迅速。同时打开埋在土壤中的温度监控装置,监测土壤的升温状况。3) At the same time, turn on the microwave radiator above the soil to radiate the microwave into the depth of the soil, and the soil is slowly heated to a certain temperature. At this time, microwave heating and electrodynamic restoration are carried out simultaneously. Because there are microwave absorbing materials buried in the soil in advance, and the soil also contains a certain amount of water injected from the groundwater, the microwave is absorbed faster and better, and the soil is heated evenly and rapidly. At the same time, the temperature monitoring device buried in the soil is turned on to monitor the temperature rise of the soil.

4)当土壤温度在100℃左右时,土壤中易挥发性有机物和半挥发性有机物开始混合着水蒸气被挥发出土壤,混合气体向上移动从安装在集气棚中的集气口以及连接管道进入多级蒸馏装置。有机物经过多级蒸馏被回收利用,分馏出来的水分用过连接管道回注到地下水中以保持地下水的水力平衡。4) When the soil temperature is around 100°C, the volatile organic compounds and semi-volatile organic compounds in the soil begin to mix with water vapor and be volatilized out of the soil, and the mixed gas moves upwards and enters from the gas collection port installed in the gas collection shed and the connecting pipes Multistage distillation unit. The organic matter is recycled through multi-stage distillation, and the fractionated water is reinjected into the groundwater through connecting pipes to maintain the hydraulic balance of the groundwater.

5)当土壤中的温度高于200℃的时候,停止电动力修复系统,继续对土壤进行微波辐射,使土壤继续升温。污染物特别是有机物及重金属离子进入土壤黏土矿物晶格层间而被固定,并进一步被玻璃化的土壤包裹,最终固定于土壤。5) When the temperature in the soil is higher than 200°C, stop the electrodynamic repair system and continue to irradiate the soil with microwaves to make the soil continue to heat up. Pollutants, especially organic matter and heavy metal ions, entered the interlayer of soil clay mineral lattice and were fixed, and were further wrapped by vitrified soil, and finally fixed in the soil.

步骤2)中的pH自动监控系统,由数字工业酸度计和单通道蠕动泵组成。蠕动泵的开关通过酸度计上设定的临界值来控制。在电动力修复过程中,一旦酸度计测得的pH值超过了设定的临界值,连接的蠕动泵便开始工作,释放出酸或碱的溶液来中和电解产生的OH-和H+,直到酸度计测得的pH值回到设定的范围内,蠕动泵才停止动作。The pH automatic monitoring system in step 2) consists of a digital industrial pH meter and a single-channel peristaltic pump. The switch of the peristaltic pump is controlled by the threshold value set on the pH meter. In the process of electrodynamic restoration, once the pH value measured by the pH meter exceeds the set critical value, the connected peristaltic pump starts to work, releasing acid or alkali solution to neutralize the OH- and H+ produced by electrolysis, until The peristaltic pump stops when the pH value measured by the acidity meter returns to the set range.

步骤3)中埋在土壤中的微波吸收材料为炭颗粒、碳棒、石墨或者磁性纳米颗粒等。由于本发明使用电动力修复技术,因此不考虑在土壤中埋入金属棒这一类微波吸收材料,以免影响电动力修复中电场分布和污染物的移动方向。The microwave absorbing material buried in the soil in step 3) is carbon particles, carbon rods, graphite or magnetic nanoparticles. Since the present invention uses electrodynamic restoration technology, it is not considered to embed microwave absorbing materials such as metal rods in the soil, so as not to affect the electric field distribution and the moving direction of pollutants in electrodynamic restoration.

步骤3)中安装在土壤中的温度监控装置由温度传感器和报警器组成,当土壤中温度超过200℃的时候会发出报警信号,这时会电动力修复装置将会被停止工作。The temperature monitoring device installed in the soil in step 3) is composed of a temperature sensor and an alarm. When the temperature in the soil exceeds 200°C, an alarm signal will be issued, and the electric restoration device will stop working.

步骤4)中收集气体的集气棚搭建在整个所处理土壤的四周和上方,构成一个密闭的空间,以便挥发出来的有机物通过集气口进入多级蒸馏装置进一步处理。The gas collection shed for collecting gas in step 4) is built around and above the entire treated soil to form a closed space, so that the volatilized organic matter enters the multi-stage distillation device for further processing through the gas collection port.

本发明的优点在于:The advantages of the present invention are:

1)本技术引入地下水循环装置,将处理区域内地下水抽出注入到污染土壤中,促进电动力修复中带电粒子在土壤中的移动。不仅如此,水快速吸收微波成为热源,使土壤微波受热更迅速更均匀。随着挥发性有机物被蒸发的水分通过多级蒸馏回注入地下水中,保持了地下水的水力平衡。1) This technology introduces a groundwater circulation device to pump out the groundwater in the treatment area and inject it into the contaminated soil, so as to promote the movement of charged particles in the soil during electrodynamic restoration. Not only that, the water quickly absorbs microwaves and becomes a heat source, which makes the soil heated by microwaves more quickly and evenly. As the volatile organic compounds are evaporated, the water is injected back into the groundwater through multi-stage distillation, maintaining the hydraulic balance of the groundwater.

2)所处理区域上部空间安装集气棚,在污染土壤上方构成一个密闭的空间,使污染土壤与外部环境隔绝,减少了外部环境受污染的风险。并且利用集气棚收集挥发出来的有机物并提纯回收利用,节省资源,不造成浪费。2) Install the air-gathering shed in the upper space of the treated area to form a closed space above the polluted soil, which isolates the polluted soil from the external environment and reduces the risk of contamination of the external environment. And use the gas collection shed to collect the volatilized organic matter and purify and recycle it, saving resources and not causing waste.

3)微波辐射使土壤温度升高,土壤温度升高又促进了电动力修复中带电粒子在电场中的迁移速度,加快电动力的修复过程。3) Microwave radiation increases the soil temperature, and the increase in soil temperature promotes the migration speed of charged particles in the electric field during electrokinetic restoration, speeding up the electrokinetic restoration process.

4)电动力修复和微波辐射的联合强化修复技术跟以往的技术相比,修复周期大大缩短,修复效果极为出色。有机物的去除率达到了98%,重金属的去除率也在90%以上,具有很高的环境效益和时间效益。4) Compared with the previous technology, the joint enhanced repair technology of electrodynamic repair and microwave radiation has greatly shortened the repair period and has excellent repair effect. The removal rate of organic matter has reached 98%, and the removal rate of heavy metals is also above 90%, which has high environmental and time benefits.

5)本技术设备结构紧凑,操作简单,可靠性高,在国内外具有良好的推广潜力,尤其是针对重金属和有机物的复合型土壤污染拥有广阔的应用前景。5) The technical equipment has compact structure, simple operation and high reliability, and has good promotion potential at home and abroad, especially for the compound soil pollution of heavy metals and organic matter, which has broad application prospects.

附图说明Description of drawings

图1为微波电动土壤原位修复装置结构示意图。其中,1-阴极井、2-阳极井、3-阴极、4-阳极、5-工业数字PH计、6-蠕动泵、7-酸碱槽、8-直流电源、9-微波发生器、10-波导、11-辐射器、12-微波吸收材料、13-抽水井、14-注水井、15-离心泵、16-温度感应器、17-集气棚、18-集气口、19-多级蒸馏装置、20-有机物收集装置、21-输水管道、22-导线、23-地下水、24-集气管道。Figure 1 is a schematic diagram of the structure of a microwave electrokinetic soil in-situ remediation device. Among them, 1-cathode well, 2-anode well, 3-cathode, 4-anode, 5-industrial digital pH meter, 6-peristaltic pump, 7-acid-base tank, 8-DC power supply, 9-microwave generator, 10 -Waveguide, 11-radiator, 12-microwave absorbing material, 13-pumping well, 14-injection well, 15-centrifugal pump, 16-temperature sensor, 17-gathering shed, 18-gathering port, 19-multistage Distillation device, 20-organic matter collection device, 21-water pipeline, 22-conductor, 23-underground water, 24-gas collection pipeline.

图2为微波电动土壤原位修复方法流程图。Fig. 2 is a flow chart of the microwave electrokinetic soil in-situ remediation method.

具体实施方式Detailed ways

下面结合附图和具体实例对本发明做进一步说明。The present invention will be further described below in conjunction with the accompanying drawings and specific examples.

图1是本发明装置示意图,如图1所示,一种微波电动土壤原位修复装置,该装置包括电极系统、微波加热系统、地下水循环系统,具体部件如下:1-阴极井、2-阳极井、3-阴极、4-阳极、5-工业数字PH计、6-蠕动泵、7-酸碱槽、8-直流电源、9-微波发生器、10-波导、11-辐射器、12-微波吸收材料、13-抽水井、14-注水井、15-离心泵、16-温度感应器、17-集气棚、18-集气口、19-多级蒸馏装置、20-有机物收集装置、21-输水管道、22-导线、23-地下水、24-集气管道。在电极系统中,阴极井1与阴极井2分别垂直放置于土壤中,阴极3置于阴极井1中,阳极4置于阳极井2中,直流电源8的正极与阳极4通过导线22连接,负极与阴极3相连,阴极井1与阳极井2都通过蠕动泵6和酸碱槽7连接,在阴极井1与阳极井2内分别放置工业数字PH计5。所述地下水循环系统,包括抽水井13与注水井14,抽水井13通过离心泵15连通输水管道21从地下水23中抽出被污染的水。所述微波加热系统,微波发生器9连接到集气棚17上,辐射器11通过波导10与9相连,土壤中埋设微波吸收材料12和温度感应器16,在集气棚17上设有集气口18,它通过集气管道24与多级蒸馏装置19连接,多级蒸馏装置的一端连接有机物收集装置20,另一端通过输水管道21连接到注水井14中进而进入地下水23。Fig. 1 is a schematic diagram of the device of the present invention, as shown in Fig. 1, a kind of microwave electric soil repairing device in situ, this device comprises electrode system, microwave heating system, underground water circulation system, and concrete parts are as follows: 1-cathode well, 2-anode Well, 3-cathode, 4-anode, 5-industrial digital PH meter, 6-peristaltic pump, 7-acid-base tank, 8-DC power supply, 9-microwave generator, 10-waveguide, 11-radiator, 12- Microwave absorbing material, 13-pumping well, 14-water injection well, 15-centrifugal pump, 16-temperature sensor, 17-gas collection shed, 18-gas collection port, 19-multistage distillation device, 20-organic matter collection device, 21 -Water pipeline, 22-wire, 23-underground water, 24-gas collection pipeline. In the electrode system, the cathode well 1 and the cathode well 2 are placed vertically in the soil respectively, the cathode 3 is placed in the cathode well 1, the anode 4 is placed in the anode well 2, the positive pole of the DC power supply 8 is connected to the anode 4 through a wire 22, The negative pole is connected to the cathode 3, the cathode well 1 and the anode well 2 are connected through a peristaltic pump 6 and an acid-base tank 7, and an industrial digital pH meter 5 is placed in the cathode well 1 and the anode well 2 respectively. The groundwater circulation system includes a pumping well 13 and a water injection well 14 , and the pumping well 13 is connected to a water delivery pipeline 21 through a centrifugal pump 15 to extract polluted water from the groundwater 23 . In the microwave heating system, the microwave generator 9 is connected to the gas collection shed 17, the radiator 11 is connected to the 9 through the waveguide 10, the microwave absorbing material 12 and the temperature sensor 16 are buried in the soil, and the gas collection shed 17 is provided with a collection The gas port 18 is connected to the multi-stage distillation device 19 through the gas collection pipe 24, one end of the multi-stage distillation device is connected to the organic matter collection device 20, and the other end is connected to the water injection well 14 through the water delivery pipe 21 and then enters the groundwater 23.

一种微波电动土壤原位修复装置及修复方法,如图2所示,该方法,A microwave electrodynamic soil repairing device and repairing method in situ, as shown in Figure 2, the method,

前期处理:Pre-processing:

在所处理土壤区域范围内搭建集气棚17,上部安装有集气口18,构成一个密闭的空间。翻松土壤,将微波吸收材料12均匀埋入土壤中。在所处理土壤区域范围两端安装阴极3和阳极4,并注入电解液,安装pH自动监控装置5-7。在所处理土壤外围两端打两口井联通地下水,一口为抽水井13,另一个作为注水井14与多级蒸馏装置19相连,以便地下水循环,保持水力平衡。A gas-collecting shed 17 is built within the area of the treated soil, and a gas-collecting port 18 is installed on the top to form a closed space. Loosen the soil, and bury the microwave absorbing material 12 evenly in the soil. Install cathode 3 and anode 4 at both ends of the treated soil area, inject electrolyte, and install pH automatic monitoring device 5-7. Two wells are drilled at both ends of the treated soil to communicate with groundwater, one is a pumping well 13, and the other is connected to a multi-stage distillation device 19 as a water injection well 14, so that the groundwater circulates and maintains hydraulic balance.

在土壤空间正上方均匀地布置微波发射装置9-11,使微波能够完全覆盖所处理的污染土壤范围。在土壤中插入温度感应器16,监控土壤温度变化。The microwave emitting devices 9-11 are uniformly arranged directly above the soil space, so that the microwave can completely cover the treated contaminated soil. A temperature sensor 16 is inserted into the soil to monitor soil temperature changes.

该方法步骤为:The method steps are:

1、启动离心泵15将适量的地下水从抽水井13抽出缓缓地注入所处理土壤的土层之中,使土壤中保持一定的水分。1. Start the centrifugal pump 15 to pump out an appropriate amount of groundwater from the pumping well 13 and slowly inject it into the soil layer of the treated soil to keep a certain amount of moisture in the soil.

2、开启电动力修复装置1-4,8,22以及pH自动监控装置5-7。存在于土壤中的带正电荷的离子(尤其是重金属离子)会向阴极移动,使其富集到阴极附近的区域;带负电荷的离子会向阳极移动,使其富集到阳极附近的区域,达到去除土壤中污染物的目的。电极井1-2中的工业数字pH计5监测电极液的pH变化。当pH计监测到电解液的pH超出设定的临界值时,便启动单通道蠕动泵6的开关,使酸碱槽中的酸或碱流向电极液中来调节pH,直到pH回到设定范围内水平,单通道蠕动泵停止工作。2. Turn on the electrodynamic restoration devices 1-4, 8, 22 and the pH automatic monitoring devices 5-7. Positively charged ions (especially heavy metal ions) present in the soil move towards the cathode, enriching the area near the cathode; negatively charged ions move towards the anode, enriching the area near the anode , to achieve the purpose of removing pollutants in the soil. The industrial digital pH meter 5 in the electrode well 1-2 monitors the pH change of the electrode solution. When the pH meter detects that the pH of the electrolyte exceeds the set critical value, the switch of the single-channel peristaltic pump 6 is activated to allow the acid or alkali in the acid-base tank to flow into the electrode solution to adjust the pH until the pH returns to the set value. Level within the range, the single channel peristaltic pump stops working.

3、同时打开土壤上方的微波辐射器9-11,使微波辐射到土壤深处,土壤被慢慢加热到一定温度。此时,微波加热和电动力修复同时进行。由于存在事先埋在土壤中的微波吸收材料12,并且土壤中还含有从地下水中注入的一定的水分,所以使得微波被吸收的更快更好,使得土壤受热均匀迅速。同时打开埋在土壤中的温度感应器16,监测土壤的升温状况。3. Simultaneously open the microwave radiators 9-11 above the soil to radiate microwaves deep into the soil, and the soil is slowly heated to a certain temperature. At this time, microwave heating and electrodynamic restoration are carried out simultaneously. Because there is the microwave absorbing material 12 buried in the soil in advance, and the soil also contains a certain amount of water injected from the groundwater, the microwave is absorbed faster and better, and the soil is heated evenly and rapidly. Simultaneously, the temperature sensor 16 buried in the soil is opened to monitor the temperature rise of the soil.

4、当土壤温度在100℃左右时,土壤中易挥发性有机物和半挥发性有机物开始混合着水蒸气被挥发出土壤,混合气体向上移动从安装在集气棚17中的集气口18以及连接管道24进入多级蒸馏装置19。有机物经过多级蒸馏被回收进入有机物收集装置20,分馏出来的水分用连接管道进入注水井14回注到地下水中以保持地下水的水力平衡。4. When the soil temperature is around 100°C, the volatile organic compounds and semi-volatile organic compounds in the soil begin to mix with water vapor and be volatilized out of the soil, and the mixed gas moves upwards from the gas collection port 18 installed in the gas collection shed 17 and the connection Line 24 enters multistage distillation unit 19 . The organic matter is recycled into the organic matter collection device 20 through multi-stage distillation, and the fractionated water enters the water injection well 14 through a connecting pipe and is reinjected into the groundwater to maintain the hydraulic balance of the groundwater.

5、当土壤中的温度高于200℃的时候,停止电动力修复系统,继续对土壤进行微波辐射,使土壤继续升温。污染物特别是有机物及重金属离子进入土壤黏土矿物晶格层间而被固定,并进一步被玻璃化的土壤包裹,最终固定于土壤。5. When the temperature in the soil is higher than 200°C, stop the electrodynamic repair system and continue to irradiate the soil with microwaves to make the soil continue to heat up. Pollutants, especially organic matter and heavy metal ions, entered the interlayer of soil clay mineral lattice and were fixed, and were further wrapped by vitrified soil, and finally fixed in the soil.

实例1:Example 1:

在电镀厂周围含Cd Zn Cu和苯、丙酮的污染土壤中选取5m*5m范围进行处理,土壤污染深度大约有1.5m,将微波吸收材料均匀的埋入该区域中,在污染区域上方设置一个5.3*5.3*2.3的集气棚,采用PbO2/Ti电极为阳极,石墨为阴极;电解缓冲液采用0.5mol/L、PH值为3的醋酸—醋酸钠缓冲溶液;恒电压15V,相应的电场强度为1.5V/cm,处理时间设定为30h,。在集气棚上安装微波发射装置,在污染区域放置温度感应器,开始处理。电动力修复装置开启之后,存在土壤中的带正电荷的离子会向阴极移动,富集到阴极附近的区域,带有负电荷的离子会富集到阳极区域。当pH超出设定的临界值时,利用酸碱槽中的酸或碱调节pH;在微波加热时,土壤中易挥发性有机物和半挥发性有机物及水蒸气会挥发出土壤,通过集气棚进入蒸馏装置。当土壤的温度超过200℃时,将电动力修复装置的电源关闭,继续微波加热。实验结束后,采用原子吸收仪测量土壤中Cd Zn Cu离子的浓度,结果表明这三种离子的平均去除率都达到85%以上,采用萃取法测定有机物的含量,结果表明苯和丙酮平均去除率达90%以上,处理耗能为8Kwh/m3Select a range of 5m*5m in the polluted soil containing Cd Zn Cu, benzene and acetone around the electroplating factory for treatment. The soil pollution depth is about 1.5m. The microwave absorbing material is evenly buried in this area, and a 5.3*5.3*2.3 gas-collecting shed, using PbO 2 /Ti electrode as the anode, graphite as the cathode; electrolysis buffer using 0.5mol/L acetic acid-sodium acetate buffer solution with a pH value of 3; constant voltage 15V, the corresponding The electric field strength is 1.5V/cm, and the treatment time is set to 30h. Install a microwave emission device on the gas collection shed, place a temperature sensor in the contaminated area, and start processing. After the electrodynamic repair device is turned on, the positively charged ions in the soil will move to the cathode and concentrate in the area near the cathode, and the negatively charged ions will enrich in the anode area. When the pH exceeds the set critical value, use the acid or alkali in the acid-base tank to adjust the pH; when microwave heating, the volatile organic compounds, semi-volatile organic compounds and water vapor in the soil will volatilize the soil and pass through the air collection shed Enter the distillation unit. When the temperature of the soil exceeds 200° C., turn off the power supply of the electric restoration device and continue microwave heating. After the experiment, the atomic absorption instrument was used to measure the concentration of Cd Zn Cu ions in the soil. The results showed that the average removal rates of these three ions were above 85%. The extraction method was used to measure the content of organic matter. The results showed that the average removal rates of benzene and acetone Up to 90%, and the processing energy consumption is 8Kwh/m 3 .

实例2Example 2

在化工厂周围含Ag、Cd和正己烷、二甲苯的污染土壤中选取2.5m*3m范围进行处理,土壤污染深度大约为1.2m,将微波吸收材料均匀的埋入该区域中,在污染区域上方设置一个2.8*3.8*2.3的集气棚,阴阳极均采用石墨板为电极;电解缓冲液采用PH值为6的柠檬酸—柠檬酸钠缓冲溶液;恒电压2V,相应的电场强度为0.2V/cm,处理时间为60h。在集气棚上安装微波发射装置,在污染区域放置温度感应器,开始处理。电动力修复装置开启之后,存在土壤中的带正电荷的离子会向阴极移动,富集到阴极附近的区域,带有负电荷的离子会向阳极移动,富集到阳极附近的区域。当pH超出设定的临界值时,利用酸碱槽中的酸或碱调节pH;在微波加热时,土壤中易挥发性有机物和半挥发性有机物及水蒸气会挥发出土壤,通过集气棚进入蒸馏装置。当土壤的温度超过200℃时,将电动力修复装置的电源关闭,继续微波加热。实验结束后,采用原子吸收仪测量土壤中Ag、Cd离子的浓度,结果表明这两种种离子的平均去除率都达到88.3%以上,采用萃取法测定有机物的含量,结果表明正己烷和二甲苯平均去除率达89%以上,处理耗能为6Kwh/m3Select a range of 2.5m*3m in the polluted soil containing Ag, Cd, n-hexane, and xylene around the chemical plant for treatment. The soil pollution depth is about 1.2m, and the microwave absorbing material is evenly embedded in this area. A 2.8*3.8*2.3 gas-collecting shed is set above, and graphite plates are used as electrodes for the anode and cathode; citric acid-sodium citrate buffer solution with a pH value of 6 is used as the electrolytic buffer solution; the constant voltage is 2V, and the corresponding electric field strength is 0.2 V/cm, the treatment time is 60h. Install a microwave emission device on the gas collection shed, place a temperature sensor in the contaminated area, and start processing. After the electrodynamic repair device is turned on, the positively charged ions in the soil will move to the cathode and be enriched in the area near the cathode, and the negatively charged ions will move to the anode and be enriched in the area near the anode. When the pH exceeds the set critical value, use the acid or alkali in the acid-base tank to adjust the pH; when microwave heating, the volatile organic compounds, semi-volatile organic compounds and water vapor in the soil will volatilize the soil and pass through the air collection shed Enter the distillation unit. When the temperature of the soil exceeds 200° C., turn off the power supply of the electric restoration device and continue microwave heating. After the experiment, the atomic absorption instrument was used to measure the concentration of Ag and Cd ions in the soil. The results showed that the average removal rate of these two kinds of ions reached more than 88.3%. The removal rate is over 89%, and the treatment energy consumption is 6Kwh/m 3 .

实例3Example 3

在蓄电池厂周围含Pb、Cd和酚类、醛类、有机胺的污染土壤中选取2m*2m范围进行处理,土壤污染深度大约为1.0m,对该区域目标污染物含量做一个基本测量,然后将微波吸收材料均匀的埋入该区域中,在污染区域上方设置一个2.5*2.5*1.5的集气棚,阴阳极均采用石墨板为电极;电解缓冲液采用0.5mol/L、PH值为3的醋酸—醋酸钠缓冲溶液;恒电压12V,相应的电场强度为1.2V/cm,处理时间设定为24h,。在集气棚上安装微波发射装置,在污染区域放置温度感应器,开始处理。电动力修复装置开启之后,存在土壤中的带正电荷的离子会向阴极移动,富集到阴极附近的区域,带有负电荷的离子会富集到阳极区域。当pH超出设定的临界值时,利用酸碱槽中的酸或碱调节pH;在微波加热时,土壤中易挥发性有机物和半挥发性有机物及水蒸气会挥发出土壤,通过集气棚进入蒸馏装置。当土壤的温度超过200℃时,将电动力修复装置的电源关闭,继续微波加热。实验结束后,采用原子吸收仪测量土壤中Pb、Cd离子的浓度,结果表明这三种离子的平均去除率都达到80%以上,采用萃取法测定有机物的含量,结果表明酚类、醛类和有机胺平均去除率达85%以上,处理耗能为7.2Kwh/m3Select a range of 2m*2m in the polluted soil containing Pb, Cd, phenols, aldehydes, and organic amines around the battery factory for treatment. The soil pollution depth is about 1.0m. Make a basic measurement of the target pollutant content in this area, and then Evenly embed microwave absorbing materials in this area, set up a 2.5*2.5*1.5 gas collection shed above the polluted area, use graphite plates as electrodes for both cathode and anode; use 0.5mol/L electrolytic buffer solution with a pH value of 3 The acetic acid-sodium acetate buffer solution; the constant voltage is 12V, the corresponding electric field strength is 1.2V/cm, and the treatment time is set to 24h. Install a microwave emission device on the gas collection shed, place a temperature sensor in the contaminated area, and start processing. After the electrodynamic repair device is turned on, the positively charged ions in the soil will move to the cathode and concentrate in the area near the cathode, and the negatively charged ions will enrich in the anode area. When the pH exceeds the set critical value, use the acid or alkali in the acid-base tank to adjust the pH; when microwave heating, the volatile organic compounds, semi-volatile organic compounds and water vapor in the soil will volatilize the soil and pass through the air collection shed Enter the distillation unit. When the temperature of the soil exceeds 200° C., turn off the power supply of the electric restoration device and continue microwave heating. After the experiment, the atomic absorption instrument was used to measure the concentration of Pb and Cd ions in the soil. The results showed that the average removal rate of these three ions reached more than 80%. The average removal rate of organic amines is over 85%, and the treatment energy consumption is 7.2Kwh/m 3 .

本发明引入地下水循环装置,将处理区域内地下水抽出注入到污染土壤中,促进电动力修复中带电粒子在土壤中的移动。不仅如此,水快速吸收微波成为热源,使土壤微波受热更迅速更均匀。随着挥发性有机物被蒸发的水分通过多级蒸馏回注入地下水中,保持了地下水的水力平衡。所处理区域上部空间安装集气棚,在污染土壤上方构成一个密闭的空间,使污染土壤与外部环境隔绝,减少了外部环境受污染的风险。并且利用集气棚收集挥发出来的有机物并提纯回收利用,节省资源,不造成浪费。微波辐射使土壤温度升高,土壤温度升高又促进了电动力修复中带电粒子在电场中的迁移速度,加快电动力的修复过程。电动力修复和微波辐射的联合强化修复技术跟以往的技术相比,修复周期大大缩短,修复效果极为出色。机物的去除率达到了98%,重金属的去除率也在90%以上,具有很高的环境效益和时间效益。本发明设备结构紧凑,操作简单,可靠性高,在国内外具有良好的推广潜力,尤其是针对重金属和有机物的复合型土壤污染拥有广阔的应用前景。The invention introduces an underground water circulation device, pumps out the ground water in the treatment area and injects it into the polluted soil, and promotes the movement of charged particles in the soil during electrodynamic restoration. Not only that, the water quickly absorbs microwaves and becomes a heat source, which makes the soil heated by microwaves more quickly and evenly. As the volatile organic compounds are evaporated, the water is injected back into the groundwater through multi-stage distillation, maintaining the hydraulic balance of the groundwater. The air-gathering shed is installed in the upper space of the treated area to form a closed space above the polluted soil, which isolates the polluted soil from the external environment and reduces the risk of contamination of the external environment. And use the gas collection shed to collect the volatilized organic matter and purify and recycle it, saving resources and not causing waste. Microwave radiation increases the soil temperature, and the increase in soil temperature promotes the migration speed of charged particles in the electric field during electrokinetic restoration, speeding up the electrokinetic restoration process. Compared with the previous technology, the joint enhanced repair technology of electrodynamic repair and microwave radiation has greatly shortened the repair period and has excellent repair effect. The removal rate of organic matter has reached 98%, and the removal rate of heavy metals is also above 90%, which has high environmental and time benefits. The device of the invention has the advantages of compact structure, simple operation and high reliability, and has good popularization potential both at home and abroad, especially for compound soil pollution of heavy metals and organic matter, which has broad application prospects.

Claims (6)

1.一种微波电动土壤原位修复装置,其特征在于,该装置包括电极系统、微波加热系统、地下水循环系统三部分;  1. A microwave electric soil repairing device in situ is characterized in that the device comprises three parts: an electrode system, a microwave heating system, and a groundwater circulation system; 电极系统包括分布在所处理土壤区域两端的石墨组成的阳极和阴极电极井,在电极中装有电解液;  The electrode system consists of anodic and cathodic electrode wells composed of graphite distributed at both ends of the soil area to be treated, containing an electrolyte in the electrodes; 微波加热系统包括安装在所处理土壤区域上方的集气棚、微波辐射器以及埋在土壤中的微波吸收材料;  The microwave heating system includes a gas collection shed installed above the treated soil area, microwave radiators and microwave absorbing materials buried in the soil; 地下水循环处理系统由分布在所处理土壤区域外围的抽水井、注水井以及真空抽吸泵组成。  The groundwater circulation treatment system consists of pumping wells, water injection wells and vacuum pumps distributed around the treated soil area. the 2.根据权利要求1所述的一种微波电动土壤原位修复装置,其特征在于,该装置包括阴极井(1)、阳极井(2)、阴极(3)、阳极(4)、工业数字PH计(5)、蠕动泵(6)、酸碱槽(7)、直流电源(8)、微波发生器(9)、波导(10)、辐射器(11)、微波吸收材料(12)、抽水井(13)、注水井(14)、离心泵(15)、温度感应器(16)、集气棚(17)、集气口(18)、多级蒸馏装置(19)、有机物收集装置(20)、输水管道(21)、导线(22)、地下水(23)、集气管道(24);  2. A microwave electric soil in-situ remediation device according to claim 1, characterized in that the device includes a cathode well (1), an anode well (2), a cathode (3), an anode (4), an industrial digital PH meter (5), peristaltic pump (6), acid-base tank (7), DC power supply (8), microwave generator (9), waveguide (10), radiator (11), microwave absorbing material (12), Pumping well (13), water injection well (14), centrifugal pump (15), temperature sensor (16), gas collection shed (17), gas collection port (18), multi-stage distillation device (19), organic matter collection device ( 20), water pipeline (21), wire (22), groundwater (23), gas collection pipeline (24); 在所需要处理土壤区域范围内搭建集气棚(17),集气棚(17)上部安装有集气口(18),构成一个密闭的空间;  Build a gas-gathering shed (17) within the area where the soil needs to be treated, and a gas-gathering port (18) is installed on the upper part of the gas-gathering shed (17), forming a closed space; 阴极井(1)与阴极井(2)分别垂直放置于土壤中,阴极(3)置于阴极井(1)中,阳极(4)置于阳极井(2)中,直流电源(8)的正极与阳极(4)通过导线(22)连接,直流电源(8)的负极与阴极(3)相连,阴极井(1)与阳极井(2)都通过蠕动泵(6)和酸碱槽(7)连接,在阴极井(1)与阳极井(2)内分别放置工业数字PH计(5);  The cathode well (1) and the cathode well (2) are placed vertically in the soil respectively, the cathode (3) is placed in the cathode well (1), the anode (4) is placed in the anode well (2), and the DC power supply (8) The positive pole is connected to the anode (4) through a wire (22), the negative pole of the DC power supply (8) is connected to the cathode (3), and both the cathode well (1) and the anode well (2) pass through the peristaltic pump (6) and the acid-base tank ( 7) Connect, place industrial digital pH meter (5) in cathode well (1) and anode well (2) respectively; 所述抽水井(13)通过离心泵(15)连通输水管道(21)从地下水(23)中抽出被污染的水;  Described pumping well (13) is connected with water pipeline (21) by centrifugal pump (15) and extracts polluted water from groundwater (23); 微波发生器(9)连接到集气棚(17)上,辐射器(11)通过波导(10)与微波发生器(9)相连,土壤中埋设微波吸收材料(12)和温度感应器(16),集气棚(17)上的集气口(18)通过集气管道(24)与多级蒸馏装置(19)连接,多级蒸馏装置(19)的一端连接有机物收集装置(20),另一端通过输水管道(21)连接到注水井(14)中进而进入地下水(23)。  The microwave generator (9) is connected to the gas collection shed (17), the radiator (11) is connected to the microwave generator (9) through the waveguide (10), and the microwave absorbing material (12) and the temperature sensor (16) are buried in the soil ), the gas collection port (18) on the gas collection shed (17) is connected to the multi-stage distillation device (19) through the gas collection pipe (24), one end of the multi-stage distillation device (19) is connected to the organic matter collection device (20), and the other One end is connected to the water injection well (14) through the water pipeline (21) and then enters the groundwater (23). the 3.利用如权利要求2所述的一种微波电动土壤原位修复装置的一种微波电动土壤原位修复方法,其特征在于,该方法步骤为:  3. Utilize a kind of microwave electrokinetic soil in-situ remediation method of a kind of microwave electrokinetic soil in-situ remediation device as claimed in claim 2, it is characterized in that, the method step is: 1)启动离心泵(15)将地下水从抽水井(13)抽出缓缓地注入所处理土壤的土层 之中,使土壤中保持水分;  1) Start the centrifugal pump (15) to extract groundwater from the pumping well (13) and slowly inject it into the soil layer of the treated soil to keep moisture in the soil; 2)开启阴极井(1)、阳极井(2)、阴极(3)、阳极(4)、工业数字PH计(5)、蠕动泵(6)、酸碱槽(7)、直流电源(8)。存在于土壤中的带正电荷的离子,尤其是重金属离子,会向阴极移动,富集到阴极附近的区域;带负电荷的离子会向阳极移动,富集到阳极附近的区域,达到去除土壤中污染物的目的;阴极井(1)、阳极井(2)中的工业数字PH计(5)监测电极液的pH变化,当工业数字PH计(5)监测到电解液的pH超出设定的临界值时,启动单通道蠕动泵(6)的开关,使酸碱槽中的酸或碱流向电极液中来调节pH,直到pH回到设定范围内,单通道蠕动泵停止工作;  2) Turn on the cathode well (1), anode well (2), cathode (3), anode (4), industrial digital pH meter (5), peristaltic pump (6), acid-base tank (7), DC power supply (8 ). Positively charged ions present in the soil, especially heavy metal ions, will move to the cathode and be enriched to the area near the cathode; negatively charged ions will move to the anode and be enriched to the area near the anode to remove the soil The purpose of pollutants in the medium; the industrial digital pH meter (5) in the cathode well (1) and the anode well (2) monitors the pH change of the electrode solution, when the industrial digital pH meter (5) detects that the pH of the electrolyte exceeds the setting When the critical value is reached, start the switch of the single-channel peristaltic pump (6), so that the acid or alkali in the acid-base tank flows into the electrode solution to adjust the pH, until the pH returns to the set range, the single-channel peristaltic pump stops working; 3)同时打开土壤上方的微波发生器(9)、波导(10)、辐射器(11),使微波辐射到土壤深处,土壤被慢慢加热到一定温度;此时,微波加热和电动力修复同时进行;由于存在事先埋在土壤中的微波吸收材料(12),并且土壤中还含有从地下水中注入的水分,所以使得微波被吸收的更快更好,使得土壤受热均匀迅速;同时打开埋在土壤中的温度感应器(16),监测土壤的升温状况;  3) Simultaneously turn on the microwave generator (9), waveguide (10) and radiator (11) above the soil to radiate microwaves deep into the soil, and the soil is slowly heated to a certain temperature; at this time, microwave heating and electric power Restoration is carried out at the same time; due to the microwave absorbing material (12) buried in the soil in advance, and the soil also contains water injected from the groundwater, the microwave is absorbed faster and better, so that the soil is heated evenly and rapidly; at the same time open A temperature sensor (16) buried in the soil monitors the temperature rise of the soil; 4)当土壤温度在100℃左右时,土壤中易挥发性有机物和半挥发性有机物开始混合着水蒸气被挥发出土壤,混合气体向上移动从安装在集气棚(17)中的集气口(18)以及连接管道(24)进入多级蒸馏装置(19);有机物经过多级蒸馏被回收进入有机物收集装置(20),分馏出来的水分用连接管道进入注水井(14)回注到地下水中以保持地下水的水力平衡;  4) When the soil temperature is around 100°C, the volatile organic compounds and semi-volatile organic compounds in the soil begin to mix with water vapor and be volatilized out of the soil, and the mixed gas moves upward from the gas collection port installed in the gas collection shed (17) ( 18) and the connecting pipeline (24) enters the multi-stage distillation device (19); the organic matter is recycled into the organic matter collection device (20) through multi-stage distillation, and the fractionated water enters the water injection well (14) through the connecting pipe and is reinjected into the groundwater To maintain the hydraulic balance of groundwater; 5)当土壤中的温度高于200℃的时候,停止电动力修复系统,继续对土壤进行微波辐射,使土壤继续升温;污染物特别是有机物及重金属离子进入土壤黏土矿物晶格层间而被固定,并进一步被玻璃化的土壤包裹,最终固定于土壤。  5) When the temperature in the soil is higher than 200°C, stop the electrodynamic restoration system and continue to irradiate the soil with microwaves to make the soil continue to heat up; pollutants, especially organic matter and heavy metal ions, enter the interlayer of the soil clay mineral lattice and are destroyed. Fixed, and further wrapped in vitrified soil, finally fixed in the soil. the 4.根据权利要求3所述的一种微波电动土壤原位修复方法,其特征在于,所述蠕动泵的开关通过工业数字PH计(5)上设定的临界值来控制,在修复过程中,一旦工业数字PH计(5)、测得的pH值超过了设定的临界值,连接的蠕动泵便开始工作,释放出酸或碱的溶液来中和电解产生的OH-和H+,直到酸度计测得的pH值回到设定的范围内,蠕动泵才停止动作。  4. A microwave electrokinetic in-situ repair method for soil according to claim 3, characterized in that the switch of the peristaltic pump is controlled by the critical value set on the industrial digital pH meter (5), during the repair process , once the industrial digital pH meter (5), the measured pH value exceeds the set critical value, the connected peristaltic pump will start to work, releasing acid or alkali solution to neutralize the OH- and H + produced by electrolysis, The peristaltic pump does not stop until the pH value measured by the acidity meter returns to the set range. 5.根据权利要求3所述的一种微波电动土壤原位修复方法,其特征在于,所述埋在土壤中的微波吸收材料为炭颗粒、碳棒、石墨或者磁性纳米颗粒。  5. A microwave electrokinetic soil in-situ remediation method according to claim 3, characterized in that the microwave absorbing material embedded in the soil is carbon particles, carbon rods, graphite or magnetic nanoparticles. the 6.根据权利要求3所述的一种微波电动土壤原位修复方法,其特征在于,所述安装在土壤中的温度监控装置由温度传感器和报警器组成,当土壤中温度超过200℃的时候会发出 报警信号,这时此修复装置将会停止工作。  6. A microwave electrodynamic soil in-situ restoration method according to claim 3, characterized in that the temperature monitoring device installed in the soil is composed of a temperature sensor and an alarm, and when the temperature in the soil exceeds 200°C An alarm signal will be sent, at this moment the repair device will stop working. the
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Citations (9)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
US5545804A (en) * 1995-02-28 1996-08-13 Exxon Research And Engineering Company Metal fixation in oily waste contaminated soil using microwave radiation acting on in-situ produced coupling agent
JP2000140819A (en) * 1998-11-02 2000-05-23 Maeda Corp Method for cleaning heavy metal-contaminated soil
JP2006346519A (en) * 2005-06-13 2006-12-28 Kubota Corp In-situ purification method of contaminated soil
CN101138767A (en) * 2007-09-29 2008-03-12 华中科技大学 A kind of remediation method of heavy metal polluted soil
CN101513643A (en) * 2009-03-20 2009-08-26 华中科技大学 In situ microwave repairing method and apparatus of contaminated soil
KR100964176B1 (en) * 2010-02-08 2010-06-25 한라건설주식회사 Method for remediation of arsenic and heavy metals contaminated soils using electrokinetic technology enhanced by metal reducing microorganisms
CN102125927A (en) * 2010-12-29 2011-07-20 上海市环境科学研究院 Method for repairing heavy metal polluted soil
CN102284474A (en) * 2011-05-16 2011-12-21 重庆大学 Method and device for restoring polluted soil and treating solid wastes by utilizing electric energy
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

Patent Citations (9)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
US5545804A (en) * 1995-02-28 1996-08-13 Exxon Research And Engineering Company Metal fixation in oily waste contaminated soil using microwave radiation acting on in-situ produced coupling agent
JP2000140819A (en) * 1998-11-02 2000-05-23 Maeda Corp Method for cleaning heavy metal-contaminated soil
JP2006346519A (en) * 2005-06-13 2006-12-28 Kubota Corp In-situ purification method of contaminated soil
CN101138767A (en) * 2007-09-29 2008-03-12 华中科技大学 A kind of remediation method of heavy metal polluted soil
CN101513643A (en) * 2009-03-20 2009-08-26 华中科技大学 In situ microwave repairing method and apparatus of contaminated soil
KR100964176B1 (en) * 2010-02-08 2010-06-25 한라건설주식회사 Method for remediation of arsenic and heavy metals contaminated soils using electrokinetic technology enhanced by metal reducing microorganisms
CN102125927A (en) * 2010-12-29 2011-07-20 上海市环境科学研究院 Method for repairing heavy metal polluted soil
CN102284474A (en) * 2011-05-16 2011-12-21 重庆大学 Method and device for restoring polluted soil and treating solid wastes by utilizing electric energy
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

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* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
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