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CN112452363B - Micro-fluidic chip for simulating soil-underground water heterogeneous system - Google Patents

Micro-fluidic chip for simulating soil-underground water heterogeneous system Download PDF

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CN112452363B
CN112452363B CN202011212867.5A CN202011212867A CN112452363B CN 112452363 B CN112452363 B CN 112452363B CN 202011212867 A CN202011212867 A CN 202011212867A CN 112452363 B CN112452363 B CN 112452363B
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王晓璞
王旭
李成华
李严
任玲玲
周泽
侯莲捷
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China University of Petroleum East China
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Abstract

The invention provides a micro-fluidic chip for simulating a soil-underground water heterogeneous system, wherein a micro-fluidic chip main body is formed by bonding two pieces of glass and comprises a uniform flow area and a non-uniform flow area, two ends of the non-uniform flow area are respectively connected with a liquid inlet uniform flow area and a liquid outlet uniform flow area of the uniform flow area, the liquid inlet uniform flow area is connected with a liquid inlet through a liquid inlet channel, and the liquid outlet uniform flow area is connected with a liquid outlet through a liquid outlet channel; the non-uniform flow area consists of a high-permeability area and a low-permeability area, the high-permeability area is sandwiched between the two low-permeability areas and is communicated with the low-permeability areas, a plurality of cylinders are arranged in the uniform flow area and the non-uniform flow area, and gaps among the cylinders are fluid flow channels. The invention also provides a method for simulating the formation and repair of the non-aqueous phase pollutants in the soil-underground water heterogeneous system, solves the problem of poor repair effect caused by difficulty in determining the underground distribution condition of the non-aqueous phase pollutants, and lays a foundation for making an economic and efficient non-aqueous phase pollutant repair scheme.

Description

一种用于模拟土壤-地下水非均质系统的微流控芯片A microfluidic chip for simulating soil-groundwater heterogeneous systems

技术领域technical field

本发明涉及土壤有机污染形成与修复技术领域,具体涉及一种用于模拟土壤-地下水非均质系统的微流控芯片。The invention relates to the technical field of soil organic pollution formation and restoration, in particular to a microfluidic chip for simulating a soil-groundwater heterogeneity system.

背景技术Background technique

近年来,原油泄漏事故频发,导致大量有毒物质进入土壤中,使得土壤石油污染成为全球性的问题。原油作为典型的非水相污染物(Non-Aqueous Phase Liquid,简称NAPL)对人体健康危害极大,且其在水中的溶解度低、化学活性弱,具有很高的辛醇/水分配系数(Kow),与土壤有机质结合能力强,抗脱附能力强,因此原油可以在土壤中长期存在。针对土壤-地下水NAPL污染,一些原位(in-situ)修复技术(如地下水循环井技术,表面活性剂强化含水层修复技术)也被相应提出,但在污染形成后,由于土壤-地下水系统的埋藏性和非均质性,人们往往不能掌握非水相污染物在地下的分布情况,致使修复效果欠佳。因此,了解非水相污染物的污染层在土壤-地下水中的形成机理对于提出经济高效修复方案至关重要,微流控模型能够精确刻蚀如土壤的多孔介质中的微观孔隙结构,实时监测多孔介质中的多相流体流动与分布情况,从而可以被广泛应用于非均质多孔介质研究中。In recent years, oil spill accidents have occurred frequently, leading to a large amount of toxic substances entering the soil, making soil oil pollution a global problem. As a typical Non-Aqueous Phase Liquid (NAPL), crude oil is extremely harmful to human health, and its solubility in water is low, its chemical activity is weak, and it has a high octanol/water partition coefficient (Kow). ), has strong binding ability with soil organic matter and strong anti-desorption ability, so crude oil can exist in soil for a long time. For soil-groundwater NAPL pollution, some in-situ (in-situ) remediation technologies (such as groundwater circulation well technology, surfactant-enhanced aquifer remediation technology) have also been proposed accordingly. Burial and heterogeneity, people often cannot grasp the distribution of non-aqueous pollutants in the ground, resulting in poor repair effect. Therefore, understanding the formation mechanism of the contamination layer of non-aqueous pollutants in soil-groundwater is crucial for proposing cost-effective remediation schemes. The flow and distribution of multiphase fluids in porous media can be widely used in the study of heterogeneous porous media.

发明内容SUMMARY OF THE INVENTION

针对现有技术难以掌握非水相污染物的地下分布情况,导致修复效果欠佳的问题,本发明提供了一种用于模拟土壤-地下水非均质系统的微流控芯片。Aiming at the problem that it is difficult to grasp the underground distribution of non-aqueous pollutants in the prior art, resulting in poor remediation effect, the present invention provides a microfluidic chip for simulating a soil-groundwater heterogeneous system.

为实现上述目的,本发明采用如下技术方案:To achieve the above object, the present invention adopts the following technical solutions:

一种用于模拟土壤-地下水非均质系统的微流控芯片,所述微流控芯片主体由两块等厚的玻璃键合而成,包括匀流区与非匀流区,匀流区包括入液匀流区3与出液匀流区6,非匀流区一端与入液匀流区3相连接,另一端与出液匀流区6相连接,入液匀流区3通过进液通道2与进液口1相连接,出液匀流区6通过出液通道7与出液口8相连接;A microfluidic chip for simulating a soil-groundwater heterogeneous system, the main body of the microfluidic chip is formed by bonding two pieces of glass of equal thickness, including a uniform flow area and a non-uniform flow area, and a uniform flow area Including the liquid inlet uniform flow area 3 and the liquid outlet uniform flow area 6, one end of the non-uniform flow area is connected with the liquid inlet uniform flow area 3, and the other end is connected with the liquid outlet uniform flow area 6. The liquid inlet uniform flow area 3 passes through the inlet. The liquid channel 2 is connected with the liquid inlet 1, and the liquid outlet uniform flow area 6 is connected with the liquid outlet 8 through the liquid outlet channel 7;

所述非匀流区由高渗区5和低渗区4组成,呈三层结构,高渗区5夹于两层低渗区4中间并与低渗区4相连通;所述入液匀流区3与出液匀流区6均呈梯形结构;The non-uniform flow area is composed of a high-permeability area 5 and a low-permeability area 4, and is in a three-layer structure. Both the flow area 3 and the effluent uniform flow area 6 are trapezoidal structures;

所述高渗区5、低渗区4、入液匀流区3与出液匀流区6内均设置有多个圆柱体,各圆柱体间的空隙为流体流通通道。The high-permeability zone 5 , the low-permeability zone 4 , the liquid inlet uniform flow zone 3 and the liquid outlet uniform flow zone 6 are all provided with a plurality of cylinders, and the gaps between the cylinders are fluid circulation channels.

优选地,所述玻璃厚度为1mm。Preferably, the thickness of the glass is 1 mm.

优选地,所述匀流区、非匀流区、进液通道2和出液通道7均通过湿法刻蚀于微流控芯片主体的顶层玻璃。Preferably, the uniform flow area, the non-uniform flow area, the liquid inlet channel 2 and the liquid outlet channel 7 are all wet-etched on the top glass of the main body of the microfluidic chip.

优选地,所述高渗区5、低渗区4和匀流区内的圆柱体均呈等边三角形矩阵排列,其中,高渗区5内圆柱体的直径为1.0575mm,高度为15μm,各圆柱体间的间距为0.3mm;低渗区4内圆柱体的直径为0.2mm,高度为15μm,各圆柱体间的间距为0.005mm;匀流区内圆柱体的直径为1mm,高度为15μm,各圆柱体间的间距为0.2115mm。Preferably, the cylinders in the high-permeability zone 5, the low-permeability zone 4 and the uniform flow zone are all arranged in an equilateral triangular matrix, wherein the cylinders in the high-permeability zone 5 have a diameter of 1.0575 mm and a height of 15 μm. The distance between the cylinders is 0.3mm; the diameter of the cylinders in the low permeability zone 4 is 0.2mm, the height is 15μm, and the distance between the cylinders is 0.005mm; the diameter of the cylinders in the uniform flow zone is 1mm and the height is 15μm , the spacing between the cylinders is 0.2115mm.

优选地,所述进液口1与出液口8均设置为直径1mm、高度1mm的圆柱体。Preferably, the liquid inlet 1 and the liquid outlet 8 are both configured as cylinders with a diameter of 1 mm and a height of 1 mm.

优选地,所述进液通道2与出液通道7均设置为长度4.3439mm、宽度0.95mm、高度15μm的长方体。Preferably, the liquid inlet channel 2 and the liquid outlet channel 7 are both set as rectangular parallelepipeds with a length of 4.3439 mm, a width of 0.95 mm and a height of 15 μm.

一种模拟土壤-地下水非均质系统中非水相污染物的形成方法,采用如上所述的一种用于模拟土壤-地下水非均质系统的微流控芯片,具体包括以下步骤:A method for simulating the formation of non-aqueous pollutants in a heterogeneous soil-groundwater system, using the above-mentioned microfluidic chip for simulating a heterogeneous soil-groundwater system, specifically comprising the following steps:

步骤1,利用PEEK接头将微流控芯片的进液口1与外部管线相连接;Step 1, using PEEK connector to connect the liquid inlet 1 of the microfluidic chip with the external pipeline;

步骤2,向进液口1中注入乙醇溶液,排出微流控芯片内的气体,直至微流控芯片中的流体流通通道内饱和乙醇溶液;Step 2, inject the ethanol solution into the liquid inlet 1, and discharge the gas in the microfluidic chip until the ethanol solution is saturated in the fluid circulation channel in the microfluidic chip;

步骤3,向进液口1中注入去离子水,排出微流控芯片内的乙醇溶液,直至微流控芯片中的流体流通通道内饱和去离子水;Step 3, inject deionized water into the liquid inlet 1, and discharge the ethanol solution in the microfluidic chip until the fluid flow channel in the microfluidic chip is saturated with deionized water;

步骤4,向进液口1中注入经Oil Red O染色的矿物油,排出微流控芯片内的去离子水,直至微流控芯片中的流体流通通道内饱和矿物油;Step 4, inject the mineral oil dyed with Oil Red O into the liquid inlet 1, and discharge the deionized water in the microfluidic chip until the mineral oil is saturated in the fluid flow channel in the microfluidic chip;

步骤5,设置多种流速,分别按照不同流速向进液口1中注入去离子水,利用ImageJ图像处理软件处理,获得不同流速条件下微流控芯片内非水相污染物的形成情况。Step 5, set multiple flow rates, inject deionized water into the liquid inlet 1 according to different flow rates respectively, and use ImageJ image processing software to process to obtain the formation of non-aqueous pollutants in the microfluidic chip under different flow rate conditions.

一种模拟土壤-地下水非均质系统中非水相污染物的修复方法,采用如上所述的一种用于模拟土壤-地下水非均质系统的微流控芯片,具体包括以下步骤:A method for remediating non-aqueous pollutants in a simulated soil-groundwater heterogeneous system, using the above-mentioned microfluidic chip for simulating a soil-groundwater heterogeneous system, specifically comprising the following steps:

步骤1,利用PEEK接头将微流控芯片的进液口1与外部管线相连接;Step 1, using PEEK connector to connect the liquid inlet 1 of the microfluidic chip with the external pipeline;

步骤2,向进液口1中注入乙醇溶液,排出微流控芯片内的气体,直至微流控芯片中的流体流通通道内饱和乙醇溶液;Step 2, inject the ethanol solution into the liquid inlet 1, and discharge the gas in the microfluidic chip until the ethanol solution is saturated in the fluid circulation channel in the microfluidic chip;

步骤3,向进液口1中注入去离子水,排出微流控芯片内的乙醇溶液,直至微流控芯片中的流体流通通道内饱和去离子水;Step 3, inject deionized water into the liquid inlet 1, and discharge the ethanol solution in the microfluidic chip until the fluid flow channel in the microfluidic chip is saturated with deionized water;

步骤4,向进液口1中注入经Oil Red O染色的矿物油,排出微流控芯片内的去离子水,直至微流控芯片中的流体流通通道内饱和矿物油;Step 4, inject the mineral oil dyed with Oil Red O into the liquid inlet 1, and discharge the deionized water in the microfluidic chip until the mineral oil is saturated in the fluid flow channel in the microfluidic chip;

步骤5,设置多种流速,分别按照不同流速向进液口1中注入去离子水,利用ImageJ图像处理软件处理,获得不同流速条件下微流控芯片内非水相污染物的形成情况;Step 5, set multiple flow rates, inject deionized water into the liquid inlet 1 according to different flow rates respectively, and use ImageJ image processing software to process to obtain the formation of non-aqueous pollutants in the microfluidic chip under different flow rate conditions;

步骤6,分别按照步骤5中设置的流速向进液口1中注入吐温80溶液,利用ImageJ图像处理软件处理,获得不同流速条件下微流控芯片内非水相污染物的去除情况及残留情况。Step 6, respectively inject Tween 80 solution into the liquid inlet 1 according to the flow rate set in step 5, and use ImageJ image processing software to process, to obtain the removal situation and residual of non-aqueous phase pollutants in the microfluidic chip under different flow rate conditions Happening.

优选地,所述吐温80溶液浓度为1g/L。Preferably, the concentration of the Tween 80 solution is 1 g/L.

本发明所带来的有益技术效果:Beneficial technical effects brought by the present invention:

本发明提出了一种用于模拟土壤-地下水非均质系统的微流控芯片,微流控芯片中各区域之间通过微通道相互连接,形成一个完整的系统,同时,本发明还利用该微流控芯片实现了土壤-地下水非均质系统中非水相污染层的形成与修复过程的实时模拟,解决了现有技术困难以确定非水相污染物的地下分布情况导致的修复效果欠佳的问题,为提出经济高效的非水相污染物修复方案奠定了基础。The present invention proposes a microfluidic chip for simulating a soil-groundwater heterogeneous system. The regions in the microfluidic chip are connected to each other through microchannels to form a complete system. At the same time, the present invention also utilizes the microfluidic chip. The microfluidic chip realizes the real-time simulation of the formation and remediation process of the non-aqueous contamination layer in the soil-groundwater heterogeneous system, and solves the difficulty of the existing technology to determine the subsurface distribution of the non-aqueous contaminants. Therefore, it has laid a foundation for proposing a cost-effective non-aqueous pollutant remediation scheme.

附图说明Description of drawings

图1为本发明一种用于模拟土壤-地下水非均质系统的微流控芯片的结构示意图。FIG. 1 is a schematic structural diagram of a microfluidic chip for simulating a soil-groundwater heterogeneous system according to the present invention.

图中:1-进液口,2-进液通道,3-入液匀流区,4-低渗区,5-高渗区,6-出液匀流区,7-出液通道,8-出液口。In the figure: 1- liquid inlet, 2- liquid inlet channel, 3- liquid inlet uniform flow area, 4- low osmotic zone, 5- high osmotic zone, 6- liquid uniform flow area, 7- liquid outlet channel, 8 - Liquid outlet.

具体实施方式Detailed ways

下面结合附图与实施例对本发明作进一步详细描述。The present invention will be described in further detail below with reference to the accompanying drawings and embodiments.

一种用于模拟土壤-地下水非均质系统的微流控芯片,如图1所示,所述微流控芯片主体由两块厚度为1mm的玻璃键合而成,微流控芯片主体包括匀流区与非匀流区,匀流区包括入液匀流区3与出液匀流区6,非匀流区一端与入液匀流区3相连接,另一端与出液匀流区6相连接,入液匀流区3通过进液通道2与进液口1相连接,出液匀流区6通过出液通道7与出液口8相连接。A microfluidic chip for simulating a soil-groundwater heterogeneous system, as shown in Figure 1, the main body of the microfluidic chip is formed by bonding two pieces of glass with a thickness of 1 mm, and the main body of the microfluidic chip includes Uniform flow area and non-uniform flow area. The uniform flow area includes the liquid inlet uniform flow area 3 and the liquid outlet uniform flow area 6. One end of the non-uniform flow area is connected with the liquid inlet uniform flow area 3, and the other end is connected with the liquid uniform flow area. 6 is connected, the liquid inlet uniform flow area 3 is connected with the liquid inlet 1 through the liquid inlet channel 2, and the liquid outlet uniform flow area 6 is connected with the liquid outlet 8 through the liquid outlet channel 7.

所述非匀流区由高渗区5和低渗区4组成,呈三层结构,高渗区5夹于两层低渗区4中间并与低渗区4相连通;所述入液匀流区3与出液匀流区6均呈梯形结构,梯形结构的上底为0.95mm、下底为14.1471mm、高为5.8456mm。The non-uniform flow area is composed of a high-permeability area 5 and a low-permeability area 4, and is in a three-layer structure. Both the flow area 3 and the outflow uniform flow area 6 are trapezoidal structures, and the upper bottom of the trapezoidal structure is 0.95 mm, the lower bottom is 14.1471 mm, and the height is 5.8456 mm.

所述高渗区5、低渗区4、入液匀流区3、出液匀流区6、进液通道2和出液通道7均通过湿法刻蚀于微流控芯片主体的顶层玻璃;高渗区5、低渗区4、入液匀流区3与出液匀流区6内均设置有多个圆柱体,各圆柱体均夹于两块玻璃之间,其中,高渗区5内圆柱体的直径为1.0575mm,高度为15μm,各圆柱体间的间距为0.3mm;低渗区4内圆柱体的直径为0.2mm,高度为15μm,各圆柱体间的间距为0.005mm;入液匀流区和出液均流区内圆柱体的直径为1mm,高度为15μm,各圆柱体间的间距为0.2115mm;各圆柱体间的空隙为流体流通通道,流体流通通道的高度与圆柱体高度相同,即流体流通通道的高度为15μm,流体流通通道宽度为相邻两个圆柱体间的间距。The high permeability zone 5, the low permeability zone 4, the liquid inlet uniform flow zone 3, the liquid outlet uniform flow zone 6, the liquid inlet channel 2 and the liquid outlet channel 7 are all wet-etched on the top glass of the main body of the microfluidic chip. ; A plurality of cylinders are arranged in the high-permeability zone 5, the low-permeability zone 4, the liquid inlet uniform flow zone 3 and the liquid outlet uniform flow zone 6, and each cylinder is sandwiched between two pieces of glass. Among them, the high-permeability zone 5 The diameter of the inner cylinder is 1.0575mm, the height is 15μm, and the spacing between the cylinders is 0.3mm; the diameter of the cylinder in the low-permeability zone 4 is 0.2mm, the height is 15μm, and the spacing between the cylinders is 0.005mm ; The diameter of the cylinders in the inflow and outflow equalization areas is 1mm, the height is 15μm, and the distance between the cylinders is 0.2115mm; the space between the cylinders is the fluid circulation channel, and the height of the fluid circulation channel The height of the fluid circulation channel is the same as that of the cylinder, that is, the height of the fluid circulation channel is 15 μm, and the width of the fluid circulation channel is the distance between two adjacent cylinders.

所述进液口1与出液口8均设置为直径1mm、高度1mm的圆柱体;进液通道2与出液通道7均设置为长度4.3439mm、宽度0.95mm、高度15μm的长方体。The liquid inlet 1 and the liquid outlet 8 are both configured as cylinders with a diameter of 1 mm and a height of 1 mm; the liquid inlet channel 2 and the liquid outlet channel 7 are both configured as rectangular parallelepipeds with a length of 4.3439 mm, a width of 0.95 mm and a height of 15 μm.

实施例1Example 1

一种模拟土壤-地下水非均质系统中非水相污染物的形成方法,采用如上所述的一种用于模拟土壤-地下水非均质系统的微流控芯片,具体包括以下步骤:A method for simulating the formation of non-aqueous pollutants in a heterogeneous soil-groundwater system, using the above-mentioned microfluidic chip for simulating a heterogeneous soil-groundwater system, specifically comprising the following steps:

步骤1,利用PEEK接头将微流控芯片的进液口1与外部管线相连接。Step 1, use a PEEK connector to connect the liquid inlet 1 of the microfluidic chip with an external pipeline.

步骤2,向进液口1中注入乙醇溶液,排出微流控芯片内的气体,直至微流控芯片中的流体流通通道内饱和乙醇溶液。Step 2, inject ethanol solution into the liquid inlet 1, and discharge the gas in the microfluidic chip until the ethanol solution is saturated in the fluid flow channel in the microfluidic chip.

步骤3,向进液口1中注入去离子水,排出微流控芯片内的乙醇溶液,直至微流控芯片中的流体流通通道内饱和去离子水。Step 3, inject deionized water into the liquid inlet 1, and discharge the ethanol solution in the microfluidic chip until the deionized water is saturated in the fluid flow channel in the microfluidic chip.

步骤4,向进液口1中注入经Oil Red O染色的矿物油,排出微流控芯片内的去离子水,直至微流控芯片中的流体流通通道内饱和矿物油。Step 4, inject the mineral oil dyed with Oil Red O into the liquid inlet 1, and discharge the deionized water in the microfluidic chip until the mineral oil is saturated in the fluid flow channel in the microfluidic chip.

步骤5,设置注入去离子水的流速为10μL/h、20μL/h和40μL/h,分别按照10μL/h、20μL/h和40μL/h的流速向微流控芯片进液口1中注入去离子水,利用ImageJ图像处理软件分析校正背景噪点的光强度,如式(1)所示,通过校正背景噪点光强度,修正显微镜系统中弧光灯光源强度的微小波动,从而获得不同流速条件下微流控芯片内非水相污染物的形成情况;Step 5: Set the flow rate of injected deionized water to 10 μL/h, 20 μL/h, and 40 μL/h, and inject the water into the microfluidic chip inlet 1 at the flow rates of 10 μL/h, 20 μL/h, and 40 μL/h, respectively. Ionized water, using ImageJ image processing software to analyze and correct the light intensity of the background noise, as shown in formula (1), by correcting the light intensity of the background noise, the slight fluctuation of the intensity of the arc light source in the microscope system is corrected, so as to obtain the light intensity under different flow rate conditions. The formation of non-aqueous pollutants in the fluidic chip;

背景噪点光强度校正公式如下所示;The background noise light intensity correction formula is as follows;

Figure GDA0003542304540000041
Figure GDA0003542304540000041

式中,

Figure GDA0003542304540000042
表示实际测量背景噪点光强度的校正值;Ij表示实际测量背景噪点的光强度;I0表示背景噪点值;IF表示充满非水相污染物时微流控芯片的光强。In the formula,
Figure GDA0003542304540000042
Represents the correction value of the light intensity of the actual measured background noise; I j represents the light intensity of the actual measured background noise; I 0 represents the value of the background noise; IF represents the light intensity of the microfluidic chip when it is filled with non-aqueous pollutants.

实施例2Example 2

一种模拟土壤-地下水非均质系统中非水相污染物的修复方法,采用如上所述的一种用于模拟土壤-地下水非均质系统的微流控芯片,具体包括以下步骤:A method for remediating non-aqueous pollutants in a simulated soil-groundwater heterogeneous system, using the above-mentioned microfluidic chip for simulating a soil-groundwater heterogeneous system, specifically comprising the following steps:

步骤1,利用PEEK接头将微流控芯片的进液口1与外部管线相连接。Step 1, use a PEEK connector to connect the liquid inlet 1 of the microfluidic chip with an external pipeline.

步骤2,向进液口1中注入乙醇溶液,排出微流控芯片内的气体,直至微流控芯片中的流体流通通道内饱和乙醇溶液。Step 2, inject ethanol solution into the liquid inlet 1, and discharge the gas in the microfluidic chip until the ethanol solution is saturated in the fluid flow channel in the microfluidic chip.

步骤3,向进液口1中注入去离子水,排出微流控芯片内的乙醇溶液,直至微流控芯片中的流体流通通道内饱和去离子水。Step 3, inject deionized water into the liquid inlet 1, and discharge the ethanol solution in the microfluidic chip until the deionized water is saturated in the fluid flow channel in the microfluidic chip.

步骤4,向进液口1中注入经Oil Red O染色的矿物油,排出微流控芯片内的去离子水,直至微流控芯片中的流体流通通道内饱和矿物油。Step 4, inject the mineral oil dyed with Oil Red O into the liquid inlet 1, and discharge the deionized water in the microfluidic chip until the mineral oil is saturated in the fluid flow channel in the microfluidic chip.

步骤5,分别按照10μL/h、20μL/h和40μL/h的流速向微流控芯片的进液口1中注入去离子水,利用ImageJ图像处理软件进行处理,获得不同流速条件下微流控芯片内非水相污染物的形成情况。Step 5, inject deionized water into the liquid inlet 1 of the microfluidic chip according to the flow rates of 10 μL/h, 20 μL/h and 40 μL/h respectively, and use ImageJ image processing software to process to obtain the microfluidic control under different flow rate conditions. Formation of non-aqueous contaminants within the chip.

步骤6,再分别按照10μL/h、20μL/h和40μL/h的流速向微流控芯片进液口1中注入浓度为1g/L的吐温80溶液,利用ImageJ图像处理软件对实验图像进行处理,获得不同流速条件下微流控芯片内非水相污染物的去除情况及残留情况。In step 6, Tween 80 solution with a concentration of 1 g/L was injected into the microfluidic chip inlet 1 at the flow rates of 10 μL/h, 20 μL/h and 40 μL/h respectively, and the experimental images were processed by ImageJ image processing software. Treatment was performed to obtain the removal and residual conditions of non-aqueous pollutants in the microfluidic chip under different flow rate conditions.

当然,上述说明并非是对本发明的限制,本发明也并不仅限于上述举例,本技术领域的技术人员在本发明的实质范围内所做出的变化、改型、添加或替换,也应属于本发明的保护范围。Of course, the above description is not intended to limit the present invention, and the present invention is not limited to the above examples. Changes, modifications, additions or substitutions made by those skilled in the art within the essential scope of the present invention should also belong to the present invention. the scope of protection of the invention.

Claims (8)

1. A micro-fluidic chip for simulating a soil-underground water heterogeneous system is characterized in that a micro-fluidic chip main body is formed by bonding two pieces of glass with equal thickness and comprises a uniform flow area and a non-uniform flow area, wherein the uniform flow area comprises a liquid inlet uniform flow area (3) and a liquid outlet uniform flow area (6), one end of the non-uniform flow area is connected with the liquid inlet uniform flow area (3), the other end of the non-uniform flow area is connected with the liquid outlet uniform flow area (6), the liquid inlet uniform flow area (3) is connected with a liquid inlet (1) through a liquid inlet channel (2), and the liquid outlet uniform flow area (6) is connected with a liquid outlet (8) through a liquid outlet channel (7);
the non-uniform flow area consists of a high-permeability area (5) and a low-permeability area (4) and is of a three-layer structure, and the high-permeability area (5) is sandwiched between the two low-permeability areas (4) and is communicated with the low-permeability areas (4); the liquid inlet uniform flow area (3) and the liquid outlet uniform flow area (6) are both in a trapezoidal structure;
a plurality of cylinders are arranged in the high-permeability area (5), the low-permeability area (4), the liquid inlet uniform flow area (3) and the liquid outlet uniform flow area (6), and gaps among the cylinders are fluid circulation channels;
the cylinders in the high-permeability area (5), the low-permeability area (4) and the uniform flow area are all arranged in an equilateral triangle matrix, wherein the diameter of the cylinder in the high-permeability area (5) is 1.0575mm, the height of the cylinder is 15 mu m, and the distance between the cylinders is 0.3 mm; the diameter of the cylinder in the hypotonic region (4) is 0.2mm, the height is 15 mu m, and the distance between the cylinders is 0.005 mm; the diameter of the inner cylinder of the uniform flow area is 1mm, the height is 15 μm, and the distance between the cylinders is 0.2115 mm.
2. The microfluidic chip for simulating a soil-groundwater heterogeneous system according to claim 1, wherein the glass thickness is 1 mm.
3. The microfluidic chip for simulating the soil-groundwater heterogeneous system according to claim 1, wherein the uniform flow region, the non-uniform flow region, the liquid inlet channel (2) and the liquid outlet channel (7) are etched on the top glass of the microfluidic chip body by a wet method.
4. A microfluidic chip for simulating a soil-groundwater heterogeneous system according to claim 1, wherein the liquid inlet (1) and the liquid outlet (8) are both arranged as cylinders with a diameter of 1mm and a height of 1 mm.
5. A microfluidic chip for simulating a soil-groundwater heterogeneous system according to claim 1, wherein the liquid inlet channel (2) and the liquid outlet channel (7) are both provided in a cuboid shape with a length of 4.3439mm, a width of 0.95mm and a height of 15 μm.
6. A method for simulating the formation of non-aqueous phase pollutants in a soil-groundwater heterogeneous system is characterized in that the microfluidic chip for simulating the soil-groundwater heterogeneous system disclosed in claim 1 is adopted, and the method comprises the following steps:
step 1, connecting a liquid inlet (1) of a microfluidic chip with an external pipeline by using a PEEK joint;
step 2, injecting an ethanol solution into the liquid inlet (1), and discharging gas in the microfluidic chip until the fluid circulation channel in the microfluidic chip is saturated with the ethanol solution;
step 3, injecting deionized water into the liquid inlet (1), and discharging an ethanol solution in the microfluidic chip until the fluid circulation channel in the microfluidic chip is saturated with deionized water;
step 4, injecting Oil Red O dyed mineral Oil into the liquid inlet (1), and discharging deionized water in the microfluidic chip until mineral Oil is saturated in a fluid circulation channel in the microfluidic chip;
and step 5, setting multiple flow rates, injecting deionized water into the liquid inlet (1) according to different flow rates, and processing by using ImageJ image processing software to obtain the formation condition of the non-aqueous phase pollutants in the microfluidic chip under different flow rate conditions.
7. The method for repairing non-aqueous phase pollutants in a soil-groundwater heterogeneous system is characterized in that the microfluidic chip for simulating the soil-groundwater heterogeneous system in claim 1 is adopted, and the method specifically comprises the following steps:
step 1, connecting a liquid inlet (1) of a microfluidic chip with an external pipeline by using a PEEK joint;
step 2, injecting an ethanol solution into the liquid inlet (1), and discharging gas in the microfluidic chip until the fluid circulation channel in the microfluidic chip is saturated with the ethanol solution;
step 3, injecting deionized water into the liquid inlet (1), and discharging an ethanol solution in the microfluidic chip until the fluid circulation channel in the microfluidic chip is saturated with deionized water;
step 4, injecting Oil Red O dyed mineral Oil into the liquid inlet (1), and discharging deionized water in the microfluidic chip until mineral Oil is saturated in a fluid circulation channel in the microfluidic chip;
step 5, setting multiple flow rates, respectively injecting deionized water into the liquid inlet (1) according to different flow rates, and processing by ImageJ image processing software to obtain the formation condition of non-aqueous phase pollutants in the microfluidic chip under different flow rate conditions;
and 6, injecting a Tween 80 solution into the liquid inlet (1) according to the flow rate set in the step 5, and processing by using ImageJ image processing software to obtain the removal condition and the residual condition of the non-aqueous phase pollutants in the microfluidic chip under different flow rate conditions.
8. The method for remediating non-aqueous phase contaminants in a soil-groundwater heterogeneous system as claimed in claim 7, wherein the concentration of the tween 80 solution is 1 g/L.
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