CN1793881A - Automatic determination device of soil moisture solute moving parameter - Google Patents

Automatic determination device of soil moisture solute moving parameter Download PDF

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CN1793881A
CN1793881A CN 200510124583 CN200510124583A CN1793881A CN 1793881 A CN1793881 A CN 1793881A CN 200510124583 CN200510124583 CN 200510124583 CN 200510124583 A CN200510124583 A CN 200510124583A CN 1793881 A CN1793881 A CN 1793881A
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solute
soil
water
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parameters
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CN100405048C (en
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王全九
樊军
赵军
郑纪勇
邵明安
张兴昌
李世清
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Institute Of Soil And Water Conservation Ministry Of Water Resources Chinese Academy Of Sciences
Xian University of Technology
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Xian University of Technology
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Abstract

本发明公开了一种土壤水分、溶质运移参数自动测定装置,包括水和溶质供给器、三通电磁阀、压力传感器、土壤水平柱、探针、自动采集器和计算机控制单元;计算机控制单元通过连接线分别与压力传感器、三通电磁阀、探针和溶液收集器连接,控制水和溶质供给器的水、溶质的自动切换,并对溶液收集器中的液体信号自动采集,得到不同土壤水平柱内不同位置的土壤样品的电导率和入渗量,并自动根据采集到的数据计算土壤湿润锋、溶质锋面位置和入渗量随时间变化过程。该装置利用同一土壤样本自动测定土壤水力参数和溶质迁移参数,测定数据求得的参数与实际情况相符。

Figure 200510124583

The invention discloses an automatic measuring device for soil moisture and solute migration parameters, comprising a water and solute supplier, a three-way solenoid valve, a pressure sensor, a soil level column, a probe, an automatic collector and a computer control unit; the computer control unit Connect the pressure sensor, three-way solenoid valve, probe and solution collector through the connection line to control the automatic switching of water and solute in the water and solute supplier, and automatically collect the liquid signal in the solution collector to obtain different soils. Conductivity and infiltration of soil samples at different positions in the horizontal column, and automatically calculate the soil wetting front, solute front position and infiltration over time based on the collected data. The device uses the same soil sample to automatically measure soil hydraulic parameters and solute migration parameters, and the parameters obtained from the measured data are consistent with the actual situation.

Figure 200510124583

Description

土壤水分、溶质运移参数自动测定装置Automatic measuring device for soil moisture and solute transport parameters

                         技术领域Technical field

本发明属于水土保持研究领域,涉及一种测量装置,特别涉及一种土壤水分、溶质运移参数自动测定的装置。The invention belongs to the field of soil and water conservation research, and relates to a measuring device, in particular to a device for automatically measuring soil moisture and solute migration parameters.

                         背景技术 Background technique

对于干旱半干旱地区水资源短缺是制约工农业发展和社会全面进步的重要因素。高效利用有限水资源成为缓减水资源短缺、实现工农业可持续发展,以及生态恢复的重要手段。土壤作为作物生长所需各种能量的供给和存储场所,预测预报和适时调控土壤中物质循环过程是实施农业高效用水与生态环境建设的重要内容。土壤水分不仅是作物各种营养元素的溶剂和载体,也是作物生长必需的营养元素之一,它对于合理调控土壤中物质循环过程起这关键性作用,因此揭示土壤水分运动特征和合理调控土壤水分状况是生态环境建设的基础。The shortage of water resources in arid and semi-arid areas is an important factor restricting the development of industry and agriculture and the overall progress of society. Efficient use of limited water resources has become an important means to alleviate water shortages, achieve sustainable industrial and agricultural development, and ecological restoration. Soil is the supply and storage place of various energy required for crop growth. Prediction and forecasting and timely regulation of the material cycle process in soil are important contents for the implementation of efficient agricultural water use and ecological environment construction. Soil moisture is not only the solvent and carrier of various nutrient elements of crops, but also one of the nutrient elements necessary for crop growth. It plays a key role in rationally regulating the material cycle process in the soil, so it reveals the characteristics of soil moisture movement and reasonably regulates soil moisture. Conditions are the foundation of ecological environment construction.

国内外学者已就土壤水分和溶质测定技术、土壤水分运动与溶质运移理论进行了大量的研究工作,并逐步由简单的试验研究发展为利用数学模型来预测土壤水分和溶质运移过程。就数学模拟而言,目前常用Richards方程来描述土壤水分运动特征,利用对流弥散理论描述土壤溶质迁移过程,模拟计算的准确性直接取决于所涉及水力参数和土壤溶质迁移参数的可靠性和精度。涉及的主要水力参数是土壤水分特征曲线、非饱和导水率、扩散率,溶质迁移参数包括水动力弥散系数和滞留因子。目前确定参数方法有直接测定法和间接推求法。测定水力参数的直接测定法主要利用张力计、压力膜、离心机测定土壤水分特征曲线,利用降雨入渗、蒸发和积水入渗法来测定非饱和导水率。这些方法概念明确,但耗时、实验费用昂贵、参数的不确定性、土壤空间变异性往往限制这些方法在田间的应用。同时测定水分特征曲线的样本与进行土壤水分运动研究的样本不相一致,产生样本误差。如果土壤存在层状结构和优先流路径,这些方法的应用存在严重问题。近几十年来,人们为了克服直接测定法中存在的缺点,寻求利用简单方法来估计土壤水分运动参数,如利用土壤颗粒组成来估计土壤水分特征曲线(Arya et al.,1999),并利用已建立的土壤水分特征曲线与非饱和导水率关系预测非饱和导水率,但由于土壤水力特征受到土壤容重和土壤结构的影响,因此利用颗粒组成确定土壤水分特征曲线仍处于理论探索阶段。另外人们可以利用土壤水分运动方程与相应的实验资料,通过数学模型进行参数的反推,但大量研究表明这种方法所造成的参数的不唯一性和方法收敛性限制着这一方法的发展与应用。邵明安(1998)发展了一个积分方法来确定土壤水分运动参数(van Genuchten模型,1980)。王全九(2002)发展了利用水平一维入渗试验来推求Brooks-Corey(1964)模型参数的方法,这一方法仅需测定入渗量和湿润锋随时间变化过程,为确定土壤水力参数提供了有效的理论。Scholars at home and abroad have done a lot of research work on soil moisture and solute measurement technology, soil moisture movement and solute transport theory, and gradually developed from simple experimental research to using mathematical models to predict soil moisture and solute transport processes. As far as mathematical simulation is concerned, the Richards equation is commonly used to describe the characteristics of soil water movement, and the convection-dispersion theory is used to describe the migration process of soil solutes. The accuracy of simulation calculations directly depends on the reliability and accuracy of the hydraulic parameters and soil solute migration parameters involved. The main hydraulic parameters involved are soil moisture characteristic curve, unsaturated hydraulic conductivity, diffusivity, and solute transport parameters include hydrodynamic diffusion coefficient and retention factor. At present, there are two methods for determining parameters: direct measurement method and indirect derivation method. The direct measurement method for measuring hydraulic parameters mainly uses tensiometer, pressure membrane, and centrifuge to measure soil moisture characteristic curve, and uses rainfall infiltration, evaporation and ponding water infiltration methods to measure unsaturated hydraulic conductivity. These methods have clear concepts, but time-consuming, expensive experiments, parameter uncertainties, and soil spatial variability often limit the application of these methods in the field. At the same time, the sample for measuring the moisture characteristic curve is not consistent with the sample for soil moisture movement research, resulting in sample error. There are serious problems with the application of these methods if the soil has a layered structure and preferential flow paths. In recent decades, in order to overcome the shortcomings of direct measurement methods, people have sought to use simple methods to estimate soil water movement parameters, such as using soil particle composition to estimate soil water characteristic curves (Arya et al., 1999), and using the existing The relationship between the established soil moisture characteristic curve and unsaturated hydraulic conductivity is used to predict the unsaturated hydraulic conductivity. However, since the hydraulic characteristics of soil are affected by soil bulk density and soil structure, the use of particle composition to determine the soil moisture characteristic curve is still in the theoretical exploration stage. In addition, people can use the soil moisture motion equation and the corresponding experimental data to invert the parameters through the mathematical model, but a large number of studies have shown that the non-uniqueness of the parameters and the convergence of the method caused by this method limit the development and development of this method. application. Ming'an Shao (1998) developed an integral method to determine soil moisture movement parameters (van Genuchten model, 1980). Wang Quanjiu (2002) developed a method for deriving the parameters of the Brooks-Corey (1964) model using horizontal one-dimensional infiltration tests. This method only needs to measure the time-varying process of infiltration and wetting front, which provides a basis for determining soil hydraulic parameters. valid theory.

目前测定水力参数的直接测定法主要利用张力计、压力膜、离心机测定土壤水分特征曲线,利用降雨入渗、蒸发和积水入渗法来测定非饱和导水率。这些方法概念明确,但耗时、实验费用昂贵、参数的不确定性、土壤空间变异性往往限制这些方法在田间的应用。同时测定水分特征曲线的样本与进行土壤水分运动研究的样本不相一致,产生样本误差。如果土壤存在层状结构和优先流路径,这些方法的应用存在严重问题。At present, the direct measurement method of measuring hydraulic parameters mainly uses tensiometer, pressure membrane and centrifuge to measure soil moisture characteristic curve, and uses rainfall infiltration, evaporation and ponding water infiltration method to measure unsaturated hydraulic conductivity. These methods have clear concepts, but time-consuming, expensive experiments, parameter uncertainties, and soil spatial variability often limit the application of these methods in the field. At the same time, the sample for measuring the moisture characteristic curve is not consistent with the sample for soil moisture movement research, resulting in sample error. There are serious problems with the application of these methods if the soil has a layered structure and preferential flow paths.

土壤溶质迁移参数测定常采用穿透曲线来进行确定,这种方法费时、费力。邵明安提出的边界层理论为确定溶质迁移参数提供了有效理论。但目前由于实验系统和研究方法的限制,在测定水力参数和溶质运移所采用的土壤样本不一致,产生了样本误差,因此需要开发利用同一土壤样本测定水力参数和溶质运移参数装置。The determination of soil solute transport parameters is often determined by breakthrough curves, which is time-consuming and laborious. The boundary layer theory proposed by Shao Ming'an provides an effective theory for determining solute transport parameters. However, due to the limitations of the experimental system and research methods, the soil samples used in the determination of hydraulic parameters and solute transport are inconsistent, resulting in sample errors. Therefore, it is necessary to develop a device that uses the same soil sample to measure hydraulic parameters and solute transport parameters.

                         发明内容Contents of invention

本发明的目的在于,提供一种土壤水分、溶质运移参数自动测定装置。The object of the present invention is to provide an automatic measuring device for soil moisture and solute transport parameters.

为了实现上述任务,本发明采取的技术解决方案是:一种土壤水分、溶质运移参数自动测定装置,其特征在于,该装置包括:In order to achieve the above tasks, the technical solution adopted by the present invention is: an automatic measuring device for soil moisture and solute transport parameters, characterized in that the device includes:

一水和溶质供给器,用于给土柱提供水和溶液,该供给器由两个装有水和溶质的有机玻璃管组成,通过马氏瓶原理可以维持恒定的水头。每个有机玻璃管连接到控制水或溶质流出的转换开关,并通过管路与三通电磁阀连接;在每个有机玻璃管液体出口处,分别有用于监测水或溶质的流出量的压力传感器;A water and solute feeder is used to provide water and solution to the soil column. The feeder consists of two plexiglass tubes filled with water and solute, and a constant water head can be maintained by the principle of the Martens bottle. Each plexiglass tube is connected to a switch that controls the outflow of water or solute, and is connected to a three-way solenoid valve through a pipeline; at the liquid outlet of each plexiglass tube, there are pressure sensors for monitoring the outflow of water or solute ;

一土壤水平柱,用于放置被测土壤样品,该土壤水平柱上均匀分布有测定电导率的探针,土壤水平柱一端通过三通电磁阀和管路与溶质供给器连通,另一端的下方有一个出流液体的溶液收集器;A soil level column, which is used to place the soil sample to be tested. The probes for measuring conductivity are evenly distributed on the soil level column. One end of the soil level column is connected with the solute supplier through a three-way solenoid valve and a pipeline, and the bottom of the other end is There is a solution collector for the effluent;

一计算机控制单元,计算机控制单元通过连接线分别与压力传感器、三通电磁阀、探针和溶液收集器连接,用于控制水和溶质供给器的水、溶质的自动切换,并对溶液收集器内的液体信号自动采集,得到不同土壤水平柱内不同位置的土壤样品的电导率和入渗量,并自动根据采集到的数据计算土壤湿润锋、溶质锋面位置和入渗量随时间变化过程。A computer control unit, the computer control unit is respectively connected with the pressure sensor, the three-way solenoid valve, the probe and the solution collector through the connection line, and is used to control the automatic switching of water and solute of the water and solute supplier, and to control the solution collector. The liquid signal in the soil is automatically collected to obtain the electrical conductivity and infiltration of soil samples at different positions in different soil horizontal columns, and automatically calculate the soil wetting front, solute front position and infiltration over time based on the collected data.

本发明的装置具备以下功能:The device of the present invention has the following functions:

(1)利用同一土壤样本自动测定土壤水力参数和溶质迁移参数;(1) Using the same soil sample to automatically measure soil hydraulic parameters and solute migration parameters;

(2)采用计算机自动控制,实现人机对话;(2) Adopt computer automatic control to realize man-machine dialogue;

(3)根据测定的有关变量,计算机自动计算相关参数。(3) According to the relevant variables measured, the computer automatically calculates the relevant parameters.

                         附图说明Description of drawings

图1是本发明的装置结构示意图;Fig. 1 is a schematic view of the device structure of the present invention;

图2是两种质地土壤湿润锋随时间的变化过程;其中图(a)是黄绵土润湿峰随时间的变化图;图(b)是塿土峰随时间的变化图。Fig. 2 is the change process of the soil wetting front of two kinds of textures with time; among them, picture (a) is the change map of loess soil wetting peak with time; picture (b) is the change map of loess soil peak with time.

图3是不同质地土壤溶质穿透曲线,其中图(a)是黑垆土,图(b)是砂土,图(c)是壤土,图(d)是黄绵土。Figure 3 is the solute penetration curves of soils with different textures, in which picture (a) is black loam, picture (b) is sandy soil, picture (c) is loam soil, and picture (d) is yellow cotton soil.

以下结合附图和装置的工作原理和过程对本发明作进一步的详细描述。The present invention will be further described in detail below in conjunction with the accompanying drawings and the working principle and process of the device.

                       具体实施方式 Detailed ways

参见图1,本发明的土壤水分、溶质运移参数自动测定装置,由三部分组成:Referring to Fig. 1, soil moisture of the present invention, solute transport parameter automatic measuring device, are made up of three parts:

(1)水和溶质供应器,本部分采用马氏瓶原理给土壤水平柱提供水和溶液,由两个有机玻璃管组成,并有控制水或者溶质的流出的转换开关,并通过管路与三通电磁阀连接,在每个有机玻璃管液体出口处,分别有用于监测水或溶质的渗入量的压力传感器。(1) Water and solute supplier. This part adopts the principle of Martens bottle to provide water and solution to the soil horizontal column. It is composed of two plexiglass tubes, and has a switch to control the outflow of water or solute, and through the pipeline and The three-way solenoid valve is connected, and there are pressure sensors for monitoring the infiltration of water or solute at the liquid outlet of each plexiglass tube.

(2)土壤水平柱,该土壤水平柱是长60cm内径5cm的有机玻璃管,在其上面间隔8cm插入探针进行电导率的测定,其一端为水或溶液的入口,另一端为出流口,在出流口的下方,有出流液体的溶液自动收集器。(2) Soil level column, which is a plexiglass tube with a length of 60 cm and an inner diameter of 5 cm, on which a probe is inserted at an interval of 8 cm to measure the conductivity. One end is the inlet of water or solution, and the other end is the outlet. , below the outflow port, there is an automatic solution collector for the outflow liquid.

探针以5个为一组固定在探头上,长3.5cm、直径1mm,四个探针以间距1cm呈正方形四周分布,中心处一个。The probes are fixed on the probe in groups of 5, with a length of 3.5 cm and a diameter of 1 mm. The four probes are distributed around a square with a distance of 1 cm, and one is in the center.

(3)计算机控制单元,计算机控制单元通过连接线分别与压力传感器、三通电磁阀、探针和溶液收集器连接,用于控制水和溶质供给器的水、溶质的自动切换,并对溶液收集器内的液体信号自动采集,得到不同土壤水平柱内不同位置的土壤样品的电导率和渗入量,并自动根据采集到的数据计算土壤湿润锋、溶质锋面位置和渗入量随时间变化过程。(3) Computer control unit, the computer control unit is respectively connected with the pressure sensor, the three-way solenoid valve, the probe and the solution collector through the connection line, and is used to control the automatic switching of the water and the solute of the water and solute supplier, and the solution The liquid signal in the collector is automatically collected to obtain the conductivity and infiltration of soil samples at different positions in different soil horizontal columns, and automatically calculate the soil wetting front, solute front position and infiltration over time based on the collected data.

溶液收集器选择上海青浦沪西仪器厂的BS-100A型号,该溶液收集器采用单片机芯片控制,六位数码管显示,能进行1秒-9小时59分59秒倒、顺定时控制。试验流程如图4所示:The solution collector chooses the BS-100A model of Shanghai Qingpu Huxi Instrument Factory. The solution collector is controlled by a single-chip microcomputer chip and displayed by a six-digit digital tube. It can perform timing control from 1 second to 9 hours, 59 minutes and 59 seconds. The test process is shown in Figure 4:

试验过程为:首先按照一定的容重在土壤水平柱中装入被测土壤样品,土壤样品经过风干和过2mm筛,将电导率探头插入土壤水平柱中,并和计算机控制单元连接。在水和溶质供应器中分别装入蒸馏水和溶质。The test process is as follows: firstly, according to a certain bulk density, the soil sample to be tested is loaded into the soil horizontal column, the soil sample is air-dried and passed through a 2mm sieve, the conductivity probe is inserted into the soil horizontal column, and connected to the computer control unit. Fill the water and solute supplies with distilled water and solute, respectively.

开启计算机控制单元的控制程序(SWSP),水和溶质供应器首先开始供水,控制程序会自动打开三通控制阀的水给土壤水平柱供水,压力传感器开始自动采样记录流入土壤水平柱的渗入量,土壤水平柱上不同位置的探针自动记录电导率的变化过程,以确定湿润峰的位置。直到水渗入到土壤水平柱最后的探针后,土壤水平柱的出流口有溶液流出,被溶液收集器收集,计算机控制单元的溶液自动采集系统开始运行,采集土壤水平柱的出流液体(即流入溶液收集器的液体)。当最后一个探针的电导率稳定后,说明此时土壤水平柱已经完全饱和,根据溶液收集器中的溶液体积和时间可以得到饱和导水率。这时控制程序停止供水,切换转换开关,水和溶质供应器开始供溶液。计算机控制单元同样以上述程序进行采集溶质的流入土壤水平柱的渗入量,溶质峰数据,采集到的出流溶液可以分析以对比确定仪器自动计算参数的准确性。Turn on the control program (SWSP) of the computer control unit, the water and solute supplier first starts to supply water, the control program will automatically open the three-way control valve to supply water to the soil level column, and the pressure sensor starts to automatically sample and record the infiltration into the soil level column , Probes at different positions on the soil level column automatically record the change process of conductivity to determine the position of the wetting peak. After the water penetrates into the last probe of the soil level column, the outflow of the soil level column has a solution flowing out, which is collected by the solution collector, and the automatic solution collection system of the computer control unit starts to run, and collects the outflow liquid of the soil level column ( That is, the liquid flowing into the solution collector). When the conductivity of the last probe is stable, it means that the soil level column is completely saturated at this time, and the saturated hydraulic conductivity can be obtained according to the solution volume and time in the solution collector. At this time, the control program stops the water supply, switches the switch, and the water and solute supplier starts to supply the solution. The computer control unit also collects the infiltration amount of the solute flowing into the horizontal column of the soil and the solute peak data with the above procedure, and the collected outflow solution can be analyzed to compare and determine the accuracy of the automatic calculation parameters of the instrument.

试验验证:Test verification:

使用本发明的装置进行湿润峰测量,当水分未到达最后一个探针的探测点之前,装置的读数很小,此时干土壤的相对电导值在3-6个读数之间。当湿润峰到达监测点后,装置读数突然增加,读数突然增加的时间就是湿润峰到达监测点的时间。将装置的测定时间与湿润峰位置绘制曲线和人工监测所得到的曲线相比较,二者曲线几乎重合,说明用该装置测定湿润峰和时间的关系十分准确(参见图2)。Using the device of the present invention to measure the wet peak, when the moisture has not reached the detection point of the last probe, the reading of the device is very small, and the relative conductivity value of the dry soil is between 3 and 6 readings. When the humidity peak reaches the monitoring point, the reading of the device increases suddenly, and the time when the reading increases suddenly is the time when the humidity peak reaches the monitoring point. Comparing the measured time of the device with the curve drawn by the position of the wet peak and the curve obtained by manual monitoring, the two curves almost overlap, indicating that the device is used to determine the relationship between the wet peak and time is very accurate (see Figure 2).

待土壤水平柱中的土壤样品饱和并溶液流出稳定时,换成KCl溶液进行Cl-的迁移研究。溶质峰面没到达探测点时,装置显示的相对电导值基本为一恒定值,当溶质峰面到达后,显示数值开始逐渐上升,反映到土壤盐分上就是土壤溶液浓度开始增加,所绘曲线类似穿透曲线的变化,这种规律的变化说明用该装置探测溶质峰面的可行性。表1为各探测点的探针位置及溶质峰到达的时间。When the soil sample in the soil horizontal column was saturated and the solution outflow was stable, it was replaced with KCl solution for Cl - migration research. When the solute peak surface does not reach the detection point, the relative conductance value displayed by the device is basically a constant value. When the solute peak surface arrives, the displayed value begins to rise gradually, which is reflected in the soil salinity, that is, the concentration of the soil solution begins to increase, and the drawn curve is similar to The change of the breakthrough curve shows the feasibility of using the device to detect the solute peak surface. Table 1 shows the position of the probe at each detection point and the arrival time of the solute peak.

                                             表1  测量数据 探测点          塿土        黄绵土        黑垆土         砂土   d(t)   t   d(t)   t   d(t)   t   d(t)   t   1   3   5.33   3   0.60   3   2.75   3   0.53   2   7   16.20   7   1.42   7   9.92   7   1.73   3   11   29.20   11   2.58   11   16.58   11   2.53   4   15   39.00   15   3.42   15   22.08   17   3.90 Table 1 Measurement data detection point Soil Loess soil black clay sand d(t) t d(t) t d(t) t d(t) t 1 3 5.33 3 0.60 3 2.75 3 0.53 2 7 16.20 7 1.42 7 9.92 7 1.73 3 11 29.20 11 2.58 11 16.58 11 2.53 4 15 39.00 15 3.42 15 22.08 17 3.90

下面表2中的测量数据是按照边界层理论的三次表达式进行处理,并进行二次多项式拟合,可以得出溶质峰在几种土壤中的数学表达式:The measurement data in Table 2 below are processed according to the cubic expression of the boundary layer theory, and the quadratic polynomial fitting is performed to obtain the mathematical expression of the solute peak in several soils:

                      表2   土样   拟合数学表达式   R2   塿土(杨凌)   y=1.4042x2-0.4583x   0.9942   砂土(渭河)   y=0.1896x2-0.7674x   0.9176   黑垆土   y=0.5731x2-0.2911x   0.9866   黄绵土   y=0.2618x2-1.0579x   0.6658 Table 2 soil sample Fit Mathematical Expression R 2 Yantu (Yangling) y=1.4042x 2 -0.4583x 0.9942 Sand (Wei River) y= 0.1896x2-0.7674x 0.9176 black clay y=0.5731x 2 -0.2911x 0.9866 Loess soil y=0.2618x 2 -1.0579x 0.6658

由于溶质为非反应性Cl-,首先认定R=1,所求D值如表3所示:Since the solute is non-reactive Cl - , first assume that R = 1, and the obtained D value is shown in Table 3:

                                               表3 参数          塿土          砂土         黑垆土         黄绵土   BTC   边界层   BTC   边界层   BTC   边界层   BTC   边界层   D   0.07   0.06   0.29   0.44   0.14   0.15   0.29   0.32 table 3 parameter Soil sand black clay Loess soil BTC boundary layer BTC boundary layer BTC boundary layer BTC boundary layer D. 0.07 0.06 0.29 0.44 0.14 0.15 0.29 0.32

可见,除砂土外,表3中通过边界层得出的D值与土壤溶质穿透曲线所得值十分接近。利用边界层方法得出的参数带入CXTFIT程序中推求土壤溶质穿透曲线和传统方法(滴定出流液浓度变化)得到的土壤溶质穿透曲线同时绘于图中,见图3。从图中可知,用该装置测定数据求得的参数与实际情况相符。It can be seen that, except for sandy soil, the D value obtained through the boundary layer in Table 3 is very close to the value obtained from the soil solute breakthrough curve. The parameters obtained by using the boundary layer method were brought into the CXTFIT program to calculate the soil solute breakthrough curve and the soil solute breakthrough curve obtained by the traditional method (titration of the effluent concentration change) was drawn simultaneously in the figure, as shown in Figure 3. It can be seen from the figure that the parameters obtained from the measured data of the device are consistent with the actual situation.

Claims (2)

1. a soil moisture, solute transfer parameter apparatus for automatically measuring is characterized in that this device comprises:
One water and solute feeder are used for providing water and solution to earth pillar, and this feeder is made up of two plexi-glass tubulars that water and solute are housed, and each plexi-glass tubular is connected with the switch of control water or solute outflow, and are connected with three-way solenoid valve by pipeline; At each plexi-glass tubular liquid outlet, be useful on the pressure transducer of the infiltration capacity of monitoring water or solute respectively;
One horizontal soil column, be used to place tested pedotheque, be evenly distributed with the probe of measuring conductivity on this horizontal soil column, horizontal soil column one end is communicated with the solute feeder by three-way solenoid valve and pipeline, and there is a solution catcher that the flow liquid body below of the other end;
One computer control unit, computer control unit is connected with pressure transducer, three-way solenoid valve, probe and solution catcher respectively by connecting line, be used to control the water of water and solute feeder, the automatic switchover of solute, and the liquid signal in the solution catcher gathered automatically, obtain the conductivity and the infiltration capacity of the pedotheque of diverse location in the different soils horizontal columns, and automatically according to the data computation soil wetting front, solute front position and the infiltration capacity that collect change procedure in time.
2. device as claimed in claim 1 is characterized in that, the long 3.5cm of the probe of described mensuration conductivity, and diameter 1mm is one group with per 5 and is fixed on the probe that 4 probes wherein are square profile with spacing 1cm, foursquare center is placed 1.
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