CN111872095B - Flexible bushing and method for monitoring contaminated sites combined with flexible bushing - Google Patents
Flexible bushing and method for monitoring contaminated sites combined with flexible bushing Download PDFInfo
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- 238000012544 monitoring process Methods 0.000 title claims abstract description 31
- 238000000034 method Methods 0.000 title claims abstract description 27
- 230000004888 barrier function Effects 0.000 claims abstract description 31
- 239000003344 environmental pollutant Substances 0.000 claims abstract description 27
- 231100000719 pollutant Toxicity 0.000 claims abstract description 27
- 238000005516 engineering process Methods 0.000 claims abstract description 24
- 230000035699 permeability Effects 0.000 claims abstract description 22
- 239000002689 soil Substances 0.000 claims abstract description 22
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- XLYOFNOQVPJJNP-UHFFFAOYSA-N water Substances O XLYOFNOQVPJJNP-UHFFFAOYSA-N 0.000 claims description 11
- 238000003860 storage Methods 0.000 claims description 10
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- 238000009826 distribution Methods 0.000 claims description 6
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- 239000008346 aqueous phase Substances 0.000 claims 1
- 230000000694 effects Effects 0.000 abstract description 8
- 238000005553 drilling Methods 0.000 abstract description 5
- 238000011109 contamination Methods 0.000 abstract 1
- 239000003673 groundwater Substances 0.000 description 11
- 230000008569 process Effects 0.000 description 10
- 238000004458 analytical method Methods 0.000 description 7
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- PXHVJJICTQNCMI-UHFFFAOYSA-N Nickel Chemical compound [Ni] PXHVJJICTQNCMI-UHFFFAOYSA-N 0.000 description 2
- 229910000278 bentonite Inorganic materials 0.000 description 2
- 239000000440 bentonite Substances 0.000 description 2
- SVPXDRXYRYOSEX-UHFFFAOYSA-N bentoquatam Chemical compound O.O=[Si]=O.O=[Al]O[Al]=O SVPXDRXYRYOSEX-UHFFFAOYSA-N 0.000 description 2
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- 238000011065 in-situ storage Methods 0.000 description 2
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- VYZAMTAEIAYCRO-UHFFFAOYSA-N Chromium Chemical compound [Cr] VYZAMTAEIAYCRO-UHFFFAOYSA-N 0.000 description 1
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- 238000012271 agricultural production Methods 0.000 description 1
- 230000009286 beneficial effect Effects 0.000 description 1
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- 150000008280 chlorinated hydrocarbons Chemical class 0.000 description 1
- 229910052804 chromium Inorganic materials 0.000 description 1
- 239000011651 chromium Substances 0.000 description 1
- 230000001808 coupling effect Effects 0.000 description 1
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- B09C1/00—Reclamation of contaminated soil
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Abstract
本发明提供一种柔性衬套以及结合柔性衬套的污染场地监测方法,监测井布设柔性衬套即通过在钻空中布设不透水的圆柱形套筒对钻孔进行密封,对污染场地土体的渗透系数、污染物特征进行监测;根据监测所得的结果选择相应类型的竖向屏障,在污染场地采用竖向阻隔技术进行处理;处理期间继续利用柔性衬套技术监测污染场地及其周围土体的修复和阻截效果,并根据实际需要注入药液进行修补。本发明可以通过柔性衬套技术有效监测污染场地的污染物特征,并且能够实时观察场地周围土体中污染物浓度和渗透系数的变化,提高污染场地的修复效果。
The invention provides a flexible bushing and a polluted site monitoring method combined with the flexible bushing. The deployment of the flexible bushing in the monitoring well is to seal the borehole by arranging an impermeable cylindrical sleeve in the drilling space, so as to prevent the contamination of soil in the polluted site. Monitor the permeability coefficient and pollutant characteristics; select the corresponding type of vertical barrier according to the monitoring results, and use vertical barrier technology to treat the polluted site; continue to use the flexible bushing technology to monitor the pollution of the polluted site and its surrounding soil during the treatment period. Repair and block effects, and inject liquid medicine to repair according to actual needs. The invention can effectively monitor the pollutant characteristics of the polluted site through the flexible bushing technology, and can observe the changes of the pollutant concentration and permeability coefficient in the soil around the site in real time, thereby improving the restoration effect of the polluted site.
Description
技术领域technical field
本发明属于污染场地控制与治理技术领域,涉及一种柔性衬套以及结合柔性衬套的污染场地监测方法。The invention belongs to the technical field of control and treatment of polluted sites, and relates to a flexible bush and a polluted site monitoring method combined with the flexible bush.
背景技术Background technique
随着社会和经济的进步,工业和农业不断发展,同时因此产生的土体污染问题也越来越严重。工业生产过程中产生的废物废气经降雨后遗留在土体中的铬、镍等重金属污染,农业生产过程中由于农药的使用在土体中留下的多环芳烃、氯代烃等有毒有害物质,都是当前存在的不可避免的土体问题。污染物在土体中的扩散和运移是较为复杂的过程,包括扩散作用、对流作用、吸附作用等,且易收到化学场、温度场的多场耦合作用。因此土体污染在空间上的影响范围较大,各类问题往往出现连锁反应,造成地下水、大气等其他生态环境的破坏,故对其进行治理是必不可少的。With the progress of society and economy, industry and agriculture continue to develop, and at the same time, the problem of soil pollution is becoming more and more serious. Heavy metal pollution such as chromium and nickel left in the soil by the waste and exhaust gas produced in the industrial production process after rainfall, and toxic and harmful substances such as polycyclic aromatic hydrocarbons and chlorinated hydrocarbons left in the soil due to the use of pesticides in the agricultural production process , are the inevitable soil problems that currently exist. The diffusion and migration of pollutants in the soil is a relatively complex process, including diffusion, convection, adsorption, etc., and is prone to multi-field coupling effects of chemical and temperature fields. Therefore, soil pollution has a wide range of influence in space, and various problems often have a chain reaction, causing damage to groundwater, the atmosphere and other ecological environments, so it is essential to control them.
对各类污染场地的治理中,原位修复是其中的主要手段。而针对原位修复周期长,彻底修复难度大的特点,竖向隔离技术作为一种风险管控与修复手段被提出。在竖向屏障施工过程中,由于各深度土层中水的交叉流动,在污染场地内很容易交叉污染,造成污染程度加剧的问题。为了进行密封,前期监测中一般采用膨润土密封的办法处理钻孔,但实际上膨润土会对待修复场地造成一定污染。In the treatment of various contaminated sites, in-situ remediation is the main means. In view of the long period of in-situ repair and the difficulty of complete repair, vertical isolation technology was proposed as a means of risk control and repair. During the construction of the vertical barrier, due to the cross flow of water in the soil layers at various depths, it is easy to cross-contaminate in the polluted site, causing the problem of aggravated pollution. In order to seal, bentonite is generally used to seal the boreholes in the early monitoring, but in fact, bentonite will cause some pollution to the repair site.
发明内容Contents of the invention
本发明旨在提供一种柔性衬套以及结合柔性衬套的污染场地监测方法,该方法将竖向屏障与柔性衬套技术相结合,避免了交叉污染,测定了场地水文特征和污染物特征,同时确保污染场地修复过程中不发生微量污染物泄露,从而提高污染场地的修复效果。The present invention aims to provide a flexible bushing and a polluted site monitoring method combined with the flexible bushing. The method combines the vertical barrier with the flexible bushing technology, avoids cross-contamination, and measures the hydrological characteristics and pollutant characteristics of the site. At the same time, ensure that no trace pollutants leak during the restoration of the contaminated site, thereby improving the restoration effect of the contaminated site.
具体的技术方案;specific technical solutions;
柔性衬套,包括不透水的柔性材料制成的圆柱形套筒,圆柱形套筒布置在钻空中,在钻空内形成严密的密封层;在圆柱形套筒外壁上每隔一段距离设置外侧透水且内侧密封的环状的隔段,隔段通过软管与圆柱形套筒底部的暂存区连接;圆柱形套筒内通过导气管与空气动力装置连通;暂存区内设有取样管,对暂存区取样。Flexible bushing, including a cylindrical sleeve made of impermeable flexible material, the cylindrical sleeve is arranged in the drilling space, forming a tight sealing layer in the drilling space; the outer wall of the cylindrical sleeve is set at intervals A water-permeable and inner-sealed ring-shaped partition, which is connected to the temporary storage area at the bottom of the cylindrical sleeve through a hose; the cylindrical sleeve is connected to the aerodynamic device through an air guide tube; a sampling tube is provided in the temporary storage area , to sample the staging area.
本发明将一种新的地下水采样技术——柔性衬套技术,应用在竖向屏障的施工过程中。采用柔性衬套技术可以有效地查清污染场地土体的渗透系数和污染物特征,并防止交叉污染和微量污染物泄露。在圆柱形套筒中每隔一段距离设置外侧透水且内侧密封的环状隔段,取样时待测污染场地中的地下水流入隔段,通过隔段中的软管进入圆柱形套筒底部的暂存区,暂存区内有两根导管即导气管和取样管,通过气压原理和向下的止回阀,将地下水样品导入地面的取样瓶当中。在进行污染场地监测时,根据前期的场地信息在周围布置好柔性衬套,较为准确地测出场地土体的渗透系数与污染物特征。根据所得监测结果制定竖向屏障、活性PRB反应墙和曝气法相结合的具体施工方案,同时在外侧继续布置柔性衬套。在施工过程中监测周围土地的污染物浓度,判断是否发生污染物泄露或竖向屏障的击穿。利用柔性衬套技术所测得的数据作为施工前的依据以及施工时的实时监测结果。The invention applies a new groundwater sampling technology—flexible bushing technology to the construction process of the vertical barrier. The use of flexible bushing technology can effectively find out the permeability coefficient and pollutant characteristics of the polluted site soil, and prevent cross-contamination and leakage of trace pollutants. In the cylindrical sleeve, ring-shaped partitions that are permeable on the outside and sealed on the inside are set at intervals. When sampling, the groundwater in the polluted site to be tested flows into the partition and enters the temporary tube at the bottom of the cylindrical sleeve through the hose in the partition. In the storage area, there are two conduits in the temporary storage area, namely the air guide tube and the sampling tube. Through the principle of air pressure and the downward check valve, the groundwater samples are introduced into the sampling bottles on the ground. During the monitoring of contaminated sites, flexible bushings are arranged around the site according to the previous site information, and the permeability coefficient and pollutant characteristics of the site soil can be measured more accurately. According to the monitoring results obtained, a specific construction plan combining vertical barriers, active PRB reaction walls and aeration method is formulated, and flexible linings are continued to be arranged on the outside. During the construction process, monitor the concentration of pollutants in the surrounding land to judge whether there is a leakage of pollutants or a breakdown of the vertical barrier. The data measured by the flexible bushing technology are used as the basis before construction and the real-time monitoring results during construction.
为此,提出结合柔性衬套技术的污染场地监测方法。在施工中采用柔性衬套技术不仅可以对钻孔进行暂时性的密封,也可以通过监测向下扩张的衬套从孔洞中的下落速度,利用得到的衬套降速数据和压力表读数计算出污染场地土层的渗透系数(岩层为透水系数,土层为水力传导性系数)。另外对柔性衬套技术取样得到的地下水进行分析可以得到相应的污染物特征,根据这些结果可以确定出适合目标场地的竖向屏障类型,达到更好的修复效果。具体技术方案为:For this reason, a method of monitoring contaminated sites combined with flexible bushing technology is proposed. The use of flexible bushing technology in construction can not only temporarily seal the borehole, but also can be calculated by monitoring the falling speed of the downwardly expanding bush from the hole, using the obtained bushing deceleration data and pressure gauge readings. The permeability coefficient of the soil layer of the polluted site (the rock layer is the hydraulic conductivity coefficient, and the soil layer is the hydraulic conductivity coefficient). In addition, the analysis of the groundwater sampled by the flexible bushing technology can obtain the corresponding pollutant characteristics. According to these results, the vertical barrier type suitable for the target site can be determined to achieve a better restoration effect. The specific technical solutions are:
一种结合柔性衬套技术的污染场地监测方法,包括以下步骤:A method for monitoring contaminated sites combined with flexible bushing technology, comprising the following steps:
第一步:在污染场地外围根据污染源分布情况、地下水水流方向,监测井内布设柔性衬套;利用柔性衬套的监测数据计算得到污染场地渗水区的渗透系数K值,岩层为透水系数,土层为水力传导性系数;取样收集NAPL即非水相液体相样本,并分析污染场地的污染物种类;The first step: According to the distribution of pollution sources and the direction of groundwater flow, a flexible bushing is arranged in the monitoring well around the polluted site; the K value of the permeability coefficient of the seepage area of the polluted site is calculated by using the monitoring data of the flexible bushing. The rock layer is the permeability coefficient, and the soil layer is the hydraulic conductivity coefficient; sampling collects NAPL, that is, non-aqueous liquid phase samples, and analyzes the types of pollutants in the polluted site;
第二步:根据第一步监测所得的结果,由渗透系数K值、污染物种类和分布确定相应的竖向屏障类型;Step 2: According to the results obtained in the first step of monitoring, the corresponding vertical barrier type is determined from the K value of the permeability coefficient, the type and distribution of pollutants;
第三步:进行竖向屏障施工的同时继续利用柔性衬套进行监测,分析污染场地周围土体的渗透系数变化、其所含污染物浓度和种类是否发生变化;并根据实际需要利用柔性衬套注入相应的药液进行修复,直至竖向屏障施工结束。Step 3: While carrying out the construction of the vertical barrier, continue to use the flexible bushing to monitor, analyze the changes in the permeability coefficient of the soil around the polluted site, and whether the concentration and type of pollutants contained in it have changed; and use the flexible bushing according to actual needs Inject the corresponding liquid medicine for repair until the completion of the vertical barrier construction.
施工期间在原设计监测点中布置柔性衬套,在柔性衬套中放置监测仪器和传感器,实时监测污染场地周围土体状况,分析竖向阻隔运行状况,判断是否发生阻隔局部击穿,若发现污染物则通过套筒注入药剂进行修补。During the construction period, arrange flexible bushings in the original design monitoring points, place monitoring instruments and sensors in the flexible bushings, monitor the soil conditions around the polluted site in real time, analyze the operation status of the vertical barrier, and judge whether there is a partial breakdown of the barrier. Objects are repaired by injecting agents through the sleeve.
进一步的,根据柔性衬套下降速率及压力表读数,计算得到渗透系数K值。Further, according to the descending rate of the flexible bushing and the reading of the pressure gauge, the permeability coefficient K value is calculated.
在污染场地的治理过程中,为了达到更好的治理效果,常常将竖向屏障技术与活性PRB反应墙、曝气法等技术联合使用。在多种修复技术联合使用的过程中,如何进行布局与设计是其中的关键之处。本发明利用柔性衬套技术测出的水力传导系数可以识别优先水流区域,与阻隔器的水力测量结果相互配合,可以得到污染区域的水文地质特征。同时,取样得到的污染区域地下水样品分析可以得到污染物特征。结合所得信息可以对污染场地的施工手段进行更为合理的设计布局,达到更好的治理效果。另外,在施工过程中通过在柔性衬套中的监测设备和相应传感器进行监测,观察是否发生污染物微量泄露或隔离墙击穿,必要时可以通过套筒向土层输送药品,对有缺陷的屏障进行修补。In the treatment process of polluted sites, in order to achieve better treatment effects, vertical barrier technology is often used in combination with active PRB reaction wall, aeration and other technologies. In the process of combining multiple restoration techniques, how to carry out layout and design is the key point. The invention uses the hydraulic conductivity measured by the flexible bushing technology to identify the preferential water flow area, and cooperates with the hydraulic measurement results of the barrier to obtain the hydrogeological characteristics of the polluted area. At the same time, the analysis of groundwater samples in polluted areas obtained by sampling can obtain the characteristics of pollutants. Combined with the obtained information, the construction methods of the polluted site can be more reasonably designed and laid out to achieve better treatment effects. In addition, during the construction process, the monitoring equipment and corresponding sensors in the flexible bushing are used to monitor whether there is a slight leakage of pollutants or a breakdown of the separation wall. The barrier is repaired.
相对于单独使用竖向屏障、曝气法、活性PRB反应墙,修复过程中结合柔性衬套技术的污染场地监测方法,可以有效地观察到地下水、污染物特征,同时可以了解地下的裂隙分布状况。竖向屏障施工时,这些因素可能会导致污染物处理效果的降低。另外,了解地下的裂隙以及地下水分布情况,也有利于选择合适的施工工程机械。总之,在竖向屏障修复污染场地的过程中,结合柔性衬套技术对污染场地进行监测,相对于一般的竖向屏障施工方法,有其独特的优势和创新点,是提高污染场地修复效果的一种可靠的方法。Compared with using vertical barriers, aeration method, and active PRB reaction wall alone, the contaminated site monitoring method combined with flexible bushing technology during the restoration process can effectively observe the characteristics of groundwater and pollutants, and at the same time understand the distribution of underground cracks . These factors may lead to a reduction in the effectiveness of pollutant treatment when vertical barriers are constructed. In addition, understanding the cracks in the ground and the distribution of groundwater is also conducive to choosing the appropriate construction machinery. In short, in the process of vertical barrier repairing contaminated sites, combined with flexible bushing technology to monitor contaminated sites, compared with general vertical barrier construction methods, it has its unique advantages and innovations, and is the key to improving the effect of contaminated site restoration. A reliable method.
综上所述,本发明具有的有益效果:柔性衬套是实现钻孔快速密封的可行技术,本发明将竖向屏障施工与柔性衬套技术相结合,有效的防止施工过程中的交叉污染,并可以提供污染场地土体的渗透系数和污染物特征,且防止了施工过程中产生的二次污染。To sum up, the present invention has beneficial effects: the flexible bushing is a feasible technology for fast sealing of boreholes, and the present invention combines vertical barrier construction with flexible bushing technology to effectively prevent cross-contamination during construction, It can also provide the permeability coefficient and pollutant characteristics of the polluted site soil, and prevent secondary pollution during the construction process.
附图说明Description of drawings
图1为本发明的柔性衬套结构示意图;Fig. 1 is the structural schematic diagram of flexible bushing of the present invention;
图2为实施例污染场地监测点位布置图;Fig. 2 is the arrangement diagram of the monitoring points of the polluted site of the embodiment;
图3为实施例检测水层分析剖析系统组件图;Fig. 3 is a component diagram of the embodiment detection water layer analysis analysis system;
图4为实施例假想衬套降速曲线图;Fig. 4 is the hypothetical liner deceleration curve figure of embodiment;
图5为实施例施工示意图。Fig. 5 is the schematic diagram of embodiment construction.
具体实施方式Detailed ways
结合实施例说明本发明的具体技术方案。The specific technical solutions of the present invention are described in conjunction with the examples.
如图1所示,柔性衬套,包括不透水的柔性材料制成的圆柱形套筒5,圆柱形套筒5布置在钻空中,在钻空内形成严密的密封层;在圆柱形套筒5外壁上每隔一段距离设置外侧透水且内侧密封的环状的隔段,隔段通过软管与圆柱形套筒5底部的暂存区3连接;圆柱形套筒5内通过导气管1与空气动力装置4连通;暂存区3内设有取样管2,对暂存区3取样。As shown in Figure 1, the flexible bushing includes a cylindrical sleeve 5 made of impermeable flexible material, the cylindrical sleeve 5 is arranged in the drilling space, and a tight sealing layer is formed in the drilling space; in the cylindrical sleeve 5. On the outer wall, ring-shaped partitions that are permeable on the outside and sealed on the inside are arranged at intervals. The partitions are connected to the temporary storage area 3 at the bottom of the cylindrical sleeve 5 through flexible pipes; The
根据污染场地的前期勘察资料确定柔性衬套的布置位置,在污染较为严重的地区增加柔性衬套的布设密度,如图2所示,图中污染地块7周围布置多个柔性衬套技术监测点位6。根据柔性衬套技术的原理进行地下水采样与分析。According to the preliminary investigation data of the polluted site, the arrangement position of the flexible bushing is determined, and the deployment density of the flexible bushing is increased in the seriously polluted area, as shown in Figure 2, where multiple flexible bushings are arranged around the polluted plot 7 for
利用柔性衬套中测速装置测量衬套在孔洞中的下落速度,如图3所示的检测水层分析剖析系统组件图。测速装置包括测速器8、注水管9、压力计10、传感器11,通过内翻衬套绞盘12将装置放下。Use the speed measuring device in the flexible bush to measure the falling speed of the bush in the hole, as shown in Figure 3, the component diagram of the detection water layer analysis and analysis system. The speed measuring device comprises a
根据衬套降速数据,即如图4假想衬套降速曲线图和压力计读数P,计算渗水区的渗透系数K值(岩层为透水系数,土层为水力传导性系数)。According to the liner deceleration data, that is, the imaginary liner deceleration curve shown in Figure 4 and the reading P of the pressure gauge, the permeability coefficient K value of the seepage area is calculated (the rock layer is the water permeability coefficient, and the soil layer is the hydraulic conductivity coefficient).
式中:K为渗透系数,m/s;k为渗透率,D,1D=1m2;ρ为流体密度,N·s2/m4;g为重力加速度,m/s2;μ为动力粘度,N·s/m2;η为运动粘度, In the formula: K is the permeability coefficient, m/s; k is the permeability, D, 1D=1m 2 ; ρ is the fluid density, N·s 2 /m 4 ; g is the gravity acceleration, m/s 2 ; μ is the power Viscosity, N·s/m 2 ; η is kinematic viscosity,
式中,Q为渗流量,m3/s;k为渗透率,D,1D=1m2;A为孔洞的横截面积,m2;△P为压差,即压力表读数,Pa;μ为流体动力粘度,Pa·s,即N·s/m2;△L为渗流长度,m。In the formula, Q is the seepage rate, m 3 /s; k is the permeability, D, 1D=1m 2 ; A is the cross-sectional area of the hole, m 2 ; △P is the pressure difference, that is, the pressure gauge reading, Pa; μ is fluid dynamic viscosity, Pa·s, namely N·s/m 2 ; △L is seepage length, m.
ΔL=L-L1 (3)ΔL=LL 1 (3)
式中,△L为渗流长度,m;L为钻孔总长度,m;L1为已下放套管长度,m。In the formula, △L is the seepage length, m; L is the total length of the borehole, m; L1 is the length of the lowered casing, m.
Q=v·A (4)Q=v·A (4)
式中,Q为渗流量,m3/s;v为衬管下放速度,即测速器读数,m/s;A为孔洞的横截面积,m2。In the formula, Q is the seepage rate, m 3 /s; v is the liner lowering speed, that is, the velocimeter reading, m/s; A is the cross-sectional area of the hole, m 2 .
根据计算所得透水区渗透系数K值得到污染场地的水文地质特征,分析地下水样品得到待处理区域的污染物15的特征。结合所得信息确定竖向屏障14的具体施工方案,确定是否结合活性PRB反应墙13等技术进行施工,并在污染场地边缘设置柔性衬套,如图5。The hydrogeological characteristics of the polluted site are obtained according to the calculated permeability coefficient K value of the permeable area, and the characteristics of the
在竖向屏障的施工过程中,由于人为或自然因素,有可能造成一小部分屏障产生缺陷,导致微量污染物出现泄漏现象,应在施工的同时继续在柔性衬套中布设监测设备或传感器监测周围土体中的污染物浓度,判断是否发生泄漏。During the construction of the vertical barrier, due to human or natural factors, a small part of the barrier may be defective, resulting in the leakage of trace pollutants. Monitoring equipment or sensors should be continuously deployed in the flexible bushing during construction. Concentration of pollutants in the surrounding soil to determine whether a leak occurs.
将柔性衬套技术应用到竖向屏障的施工中,可以使施工方法更为合理,提高污染场地的修复效果。Applying the flexible bushing technology to the construction of the vertical barrier can make the construction method more reasonable and improve the restoration effect of the polluted site.
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| CN115508263B (en) * | 2022-08-17 | 2023-07-21 | 中国地质大学(北京) | Method, device, equipment, and medium for measuring permeability coefficient of aquifer in polluted site |
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Citations (7)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| CN102330435A (en) * | 2011-07-05 | 2012-01-25 | 东南大学 | Separation wall for carrying out in situ separation repair on pollution site and construction method thereof |
| CN104324938A (en) * | 2014-11-18 | 2015-02-04 | 青岛新天地环境保护有限责任公司 | Horizontal permeable reaction layer for soil remediation and soil remediating method |
| CN105973759A (en) * | 2016-06-23 | 2016-09-28 | 北京建工环境修复股份有限公司 | Method for determining in situ injection repair diffusion radiuses of contaminated soil and underground water |
| CN106517407A (en) * | 2016-12-06 | 2017-03-22 | 成都理工大学 | Method for remedying polluted groundwater in refuse landfill with PRB (permeable reactive barrier) technology |
| CN106799395A (en) * | 2017-02-08 | 2017-06-06 | 东南大学 | The construction method of contaminated site is repaired in a kind of environmentally friendly medicament injection in situ |
| CN208270263U (en) * | 2018-06-27 | 2018-12-21 | 长江水利委员会长江科学院 | A kind of soil and water-bearing layer in-situ monitoring and solution sampling apparatus |
| CN110108517A (en) * | 2019-05-30 | 2019-08-09 | 中国地质科学院水文地质环境地质研究所 | A kind of in-situ acquisition filter device and its application method based on phreatic water |
Family Cites Families (1)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| US20030035691A1 (en) * | 2001-07-26 | 2003-02-20 | Sivavec Timothy M. | Permeable-reactive barrier monitoring method and system |
-
2020
- 2020-06-19 CN CN202010565316.0A patent/CN111872095B/en active Active
Patent Citations (7)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| CN102330435A (en) * | 2011-07-05 | 2012-01-25 | 东南大学 | Separation wall for carrying out in situ separation repair on pollution site and construction method thereof |
| CN104324938A (en) * | 2014-11-18 | 2015-02-04 | 青岛新天地环境保护有限责任公司 | Horizontal permeable reaction layer for soil remediation and soil remediating method |
| CN105973759A (en) * | 2016-06-23 | 2016-09-28 | 北京建工环境修复股份有限公司 | Method for determining in situ injection repair diffusion radiuses of contaminated soil and underground water |
| CN106517407A (en) * | 2016-12-06 | 2017-03-22 | 成都理工大学 | Method for remedying polluted groundwater in refuse landfill with PRB (permeable reactive barrier) technology |
| CN106799395A (en) * | 2017-02-08 | 2017-06-06 | 东南大学 | The construction method of contaminated site is repaired in a kind of environmentally friendly medicament injection in situ |
| CN208270263U (en) * | 2018-06-27 | 2018-12-21 | 长江水利委员会长江科学院 | A kind of soil and water-bearing layer in-situ monitoring and solution sampling apparatus |
| CN110108517A (en) * | 2019-05-30 | 2019-08-09 | 中国地质科学院水文地质环境地质研究所 | A kind of in-situ acquisition filter device and its application method based on phreatic water |
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