CN103969419A - Indoor simulation system applied to pollutant migration process researches under artificial rainfall - Google Patents
Indoor simulation system applied to pollutant migration process researches under artificial rainfall Download PDFInfo
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Abstract
Description
技术领域technical field
本发明涉及用以研究污染物界面迁移与物理过程的实验室模拟设备,特别是一种应用于土壤和水界面过程中污染物迁移与转化研究的室内模拟控制系统,属于地学及环境科学领域。The invention relates to laboratory simulation equipment for studying pollutant interface migration and physical process, in particular to an indoor simulation control system applied to the research of pollutant migration and transformation in soil and water interface process, which belongs to the field of geology and environmental science.
背景技术Background technique
在进行土壤污染物迁移过程试验、土壤入渗试验以及其他需要模拟降雨的科学实验时,为了避免自然因素的影响,需要在既定时间内迅速获得试验所需数据,顺利完成计划试验。通常利用人工模拟降雨装置进行人工模拟降雨,目前的人工模拟降雨通常分为喷嘴式和针管式2种类型,喷嘴式人工模拟降雨机是从喷嘴或喷孔中把水喷射至空中,受空气阻力作用的影响,水流破碎形成不同大小的雨滴,降落至地表形成降雨,通过改变喷嘴的摆动次数可以得到3-10个固定的降雨强度(以下简称雨强)。目前的这种喷嘴式的人工模拟降雨器,雨滴与天然降雨比较接近,但是降雨的均匀性还不是很好,造价也比较昂贵。When carrying out soil pollutant migration process tests, soil infiltration tests, and other scientific experiments that require simulated rainfall, in order to avoid the influence of natural factors, it is necessary to quickly obtain the data required for the test within a predetermined time and successfully complete the planned test. Usually, artificial simulated rainfall devices are used to artificially simulate rainfall. The current artificial simulated rainfall is usually divided into two types: nozzle type and needle tube type. Influenced by the effect, the water flow is broken to form raindrops of different sizes, which fall to the surface to form rainfall. By changing the number of swings of the nozzle, 3-10 fixed rainfall intensities (hereinafter referred to as rain intensities) can be obtained. In the current nozzle-type artificial simulated rainfall device, the raindrops are closer to natural rainfall, but the uniformity of rainfall is not very good, and the cost is also relatively expensive.
目前,实验室内进行的污染物迁移过程及土水界面研究在对实验条件,如降雨、剖面样品动态监测与收集、界面环境梯度控制等方面兼顾难以齐全,其主要原因还在于实验设备的不完善和未加以整合。理想的模拟装置所产生的人工降雨,应与自然降雨相似,主要的降雨指标包括降雨强度、降雨均匀性、雨滴直径分布,雨滴降落终点速度等。对于降雨径流的模拟实验,只要具备降雨均匀性和降雨强度的相似性,即能满足实验要求;对于降雨侵蚀的模拟实验,只要具备满足降雨均匀性、雨滴中数直径、终点速度和雨滴谱的相似性条件,同样满足实验要求。At present, it is difficult to fully consider the experimental conditions, such as rainfall, dynamic monitoring and collection of profile samples, and interface environmental gradient control, in the research of pollutant migration process and soil-water interface in the laboratory. The main reason lies in the lack of experimental equipment. Perfect and unintegrated. The artificial rainfall produced by an ideal simulation device should be similar to natural rainfall. The main rainfall indicators include rainfall intensity, rainfall uniformity, raindrop diameter distribution, and raindrop terminal velocity. For the simulation experiment of rainfall runoff, as long as it has the similarity of rainfall uniformity and rainfall intensity, it can meet the experimental requirements; for the simulation experiment of rainfall erosion, as long as it has the requirements of rainfall uniformity, raindrop median diameter, terminal velocity and raindrop spectrum The similarity condition also meets the experimental requirements.
由于自然降雨周期长,季节分布性较强,年度分部极不均匀,导致基于自然降雨的野外和试验小区观测周期长,获得数据速度慢。在农田土壤-降雨界面和土壤(沉积物)-水界面的化学、物理以及生物过程是最为活跃的,而这些过程在实际过程中,由于受到野外实验条件、风浪、船只以及底栖动物的影响,而难以捕捉。因此,有必要研制人工模拟降雨装置尽可能代替自然降雨,加速土壤侵蚀、降雨产流及入渗等实验进度,避免自然因素的影响,在既定时间内迅速获得试验所需数据。Due to the long period of natural rainfall, strong seasonal distribution, and extremely uneven annual division, the observation period of field and experimental plots based on natural rainfall is long and the speed of data acquisition is slow. The chemical, physical, and biological processes at the soil-rainfall interface and soil (sediment)-water interface are the most active in farmland, and these processes are affected by field experimental conditions, wind waves, ships, and benthic animals in actual processes. , and difficult to capture. Therefore, it is necessary to develop an artificial rainfall simulation device to replace natural rainfall as much as possible, to accelerate the progress of experiments such as soil erosion, rainfall runoff, and infiltration, to avoid the influence of natural factors, and to quickly obtain the data required for the experiment within a given time.
发明内容Contents of the invention
1、发明目的1. Purpose of the invention
本发明的目的在于针对现有技术中存在的实际问题,考虑到实际过程中影响污染物迁移转化的主要因素是降雨,为特定土壤-降雨界面和土壤(沉积物)-水界面的污染物迁移研究提供便利,提供一种应用于人工降雨条件下污染物迁移过程研究的室内模拟系统,能够满足降雨均匀性、雨滴中数直径、终点速度和雨滴谱的相似性条件,直接用于人工降雨条件下土壤(沉积物)-水界面污染物的迁移过程研究与模拟。The purpose of the present invention is to be aimed at the practical problem existing in the prior art, considering that the main factor that influences pollutant migration transformation in the actual process is rainfall, is the pollutant migration of specific soil-rainfall interface and soil (sediment)-water interface The research provides convenience, and provides an indoor simulation system applied to the research of pollutant migration process under artificial rainfall conditions, which can meet the similarity conditions of rainfall uniformity, raindrop median diameter, terminal velocity and raindrop spectrum, and can be directly used in artificial rainfall conditions Research and simulation of the migration process of pollutants at the soil (sediment)-water interface.
2、技术解决方案2. Technical solutions
本发明的上述目的是这样实现的:一种应用于人工降雨条件下土壤/沉积物-水界面过程研究的室内模拟装置,其特征是由降雨控制系统,污染物垂向运移模拟系统,样品收集系统三部分构成;降雨控制系统主要由供水器、降雨器、供水管和阀门组成。其特征是供水器选用较大直径的容器以保证在一定供水强度的情况下短时间内供水器内水位不会明显变化,通过水位升降控制器调节供水器与降雨器之间的水头差。降雨器选用16mm电缆线外管钻孔外接8号医用注射针头制作而成,通过使用不同数量的针头和调节降雨器水位来满足模拟不同降雨量的需要。降雨器一端通过带有控制阀门的供水管与供水器相连,另一端用橡皮塞封闭作为降雨器排气开关;污染物垂向运移模拟系统,其特征是土柱柜主要由有机玻璃柱组成。土柱侧面玻璃柱板标有刻度线,以方便观察记录土柱内的渗流过程。环土柱侧壁不同深度布有采样圆孔,孔的直径为4cm,以监测模拟系统内土壤/沉积物不同深度的污染物浓度变化过程,也可以用盖子进行密封,盖子内侧有密封橡胶圈;盖子外有进出水口,进出水口中有螺纹,可以由密封螺丝封住;样品收集系统,其特征是通过橡皮管和玻璃管的组合,实现下渗土壤水溶液的定时采集与更换,可以方便的实现水样的收集。The above-mentioned purpose of the present invention is achieved in that a kind of indoor simulation device applied to soil/sediment-water interface process research under artificial rainfall conditions is characterized by a rainfall control system, a pollutant vertical migration simulation system, a sample The collection system consists of three parts; the rainfall control system is mainly composed of water supply, rain, water supply pipes and valves. The characteristic is that the water supply device uses a larger diameter container to ensure that the water level in the water supply device will not change significantly in a short period of time under the condition of a certain water supply intensity, and the water head difference between the water supply device and the rainfall device is adjusted by the water level controller. The rainfall device is made of a 16mm cable outer tube drilled and connected with a No. 8 medical injection needle. By using different numbers of needles and adjusting the water level of the rainfall device, it can meet the needs of simulating different rainfall. One end of the rainfall device is connected to the water supply device through a water supply pipe with a control valve, and the other end is closed with a rubber plug as the discharge switch of the rainfall device; the vertical migration simulation system of pollutants is characterized in that the soil column cabinet is mainly composed of plexiglass columns . The glass column plate on the side of the soil column is marked with scale lines to facilitate the observation and recording of the seepage process in the soil column. Sampling round holes are arranged at different depths on the side wall of the surrounding soil column. The diameter of the hole is 4cm to monitor the change process of pollutant concentration in the soil/sediment at different depths in the simulation system. It can also be sealed with a cover, and there is a sealing rubber ring inside the cover. There are water inlets and outlets outside the cover, and there are threads in the water inlet and outlets, which can be sealed by sealing screws; the sample collection system is characterized in that it can realize the regular collection and replacement of infiltrating soil aqueous solution through the combination of rubber tubes and glass tubes, which can be conveniently To realize the collection of water samples.
3、技术效果3. Technical effects
本发明的优点及效果:Advantage and effect of the present invention:
(1)该装置的降雨均匀性系数大于85%,具有较高的降雨稳定性,可重复性好。生成的雨滴特性与天然降雨雨滴特性具有较高的相似性。(1) The rainfall uniformity coefficient of the device is greater than 85%, which has high rainfall stability and good repeatability. The characteristics of the generated raindrops have a high similarity to those of natural rainfall.
(2)该装置由孔径大小不同的,独立的喷头组成,每个模拟降雨单元装置由16个喷头组成,可以根据需要任意扩展。经过装置的轻量化改进后,可以从一个地点移动到另一个地点;(2) The device is composed of independent nozzles with different aperture sizes, and each simulated rainfall unit device is composed of 16 nozzles, which can be expanded arbitrarily as required. After the lightweight improvement of the device, it can be moved from one location to another;
(3)可以模拟不同降雨强度控制下土壤和水界面过程中污染物迁移转化特征,模拟的土壤土质特征可以按照实际条件进行;(3) It can simulate the migration and transformation characteristics of pollutants in the process of soil and water interface under the control of different rainfall intensities, and the simulated soil and soil characteristics can be carried out according to actual conditions;
(4)4、该装置在运行过程中,只要供电正常,水质清洁,可以保证试验研究的持续进行,具有较高的可靠性。日常维护主要是清洁水池、防止喷头堵塞;(4) 4. During the operation of the device, as long as the power supply is normal and the water quality is clean, it can ensure the continuous progress of the experimental research and has high reliability. Routine maintenance is mainly to clean the pool and prevent nozzle clogging;
(5)该装置造价较低,便于与正在建设的比尺模型降雨装置协调和协同试验,使试验数据有可比性。(5) The cost of the device is low, which is convenient for coordination and collaborative testing with the scale model rainfall device under construction, so that the test data can be compared.
附图及附图的简单说明Brief Description of Drawings and Drawings
图1降雨模拟装置侧面图Fig.1 Side view of rainfall simulation device
图2降雨模拟装置俯视图Figure 2 Top view of rainfall simulation device
图3土柱侧面图Figure 3 Side view of soil column
图4模拟装置立体图Figure 4 Stereoscopic view of the simulation device
图中:1,滑轮;2,水位升降控制器;3,吊绳;4,供水器;5,水位;6,水位控制龙头;7,降雨模拟器;8,针眼降雨器;9,传感器;10,匀质土壤;11,有机玻璃柱;12,透水膜;13,软导管;14,地表径流孔;15,径流收集瓶;16,取样/缓冲瓶;17,石英砂层。In the figure: 1, pulley; 2, water level lifting controller; 3, hanging rope; 4, water supply device; 5, water level; 6, water level control faucet; 7, rainfall simulator; 8, pinhole rainfall device; 9, sensor; 10, homogeneous soil; 11, plexiglass column; 12, permeable membrane; 13, soft conduit; 14, surface runoff hole; 15, runoff collection bottle; 16, sampling/buffer bottle; 17, quartz sand layer.
具体实施方式Detailed ways
(1)按照图2,进行降雨器的安装;(1) According to Fig. 2, carry out the installation of rainfall device;
(2)按照图1,进行不同液面(5)条件下降雨强度的预实验,获取不同深度的降雨强度值,并在图1的降雨控制系统的柱面上进行标注;(2) According to Fig. 1, carry out the pre-experiment of rainfall intensity under different liquid level (5) conditions, obtain the rainfall intensity values of different depths, and mark on the cylinder surface of the rainfall control system in Fig. 1;
(3)采集需要实验的土壤介质,按照层次土质情况进行填充,相同层次的土质在填充之前混合均匀,根据实验要求和目的进行分层填装到图3的污染物垂向运移模拟系统中;(3) Collect the soil medium that needs to be tested, fill it according to the soil quality of the layer, mix the soil quality of the same layer evenly before filling, and fill it layer by layer into the pollutant vertical migration simulation system in Figure 3 according to the experimental requirements and purposes ;
(4)在污染物垂向运移模拟系统中不同深度安装传感器和设置采样孔,将橡皮塞对采样孔进行封闭;(4) Install sensors and sampling holes at different depths in the pollutant vertical migration simulation system, and seal the sampling holes with rubber stoppers;
(5)按照示意图4,将降雨控制系统图1和污染物垂向运移模拟系统图3进行固定,保证实验过程中装置的稳定与加固;(5) Fix the rainfall control system Figure 1 and the pollutant vertical migration simulation system Figure 3 according to the schematic diagram 4 to ensure the stability and reinforcement of the device during the experiment;
(6)按照图3,进行地表径流装置(15)和地下渗流装置(16)样品收集系统的安装与固定;(6) according to Fig. 3, carry out the installation and fixing of surface runoff device (15) and underground seepage device (16) sample collection system;
(7)对每个采样装置和进水装置进行检查,直至所有管子和装置均接好;(7) Check each sampling device and water inlet device until all pipes and devices are connected;
(8)启动降雨装置,调频电机,调节至预设降雨强度;(8) Start the rainfall device, adjust the frequency motor, and adjust to the preset rainfall intensity;
(9)(根据实验目的)计算时间,进行例行采样;直至采集完所有样品;根据实验要求分析水样的物理,化学及生物性质等;(9) (according to the purpose of the experiment) calculate the time and carry out routine sampling; until all samples are collected; analyze the physical, chemical and biological properties of the water samples according to the experimental requirements;
(10)观测传感器的读数变化过程,(根据实验目的)设置监测时间频率,同时进行土壤不同深度溶液的收集和分析;(10) Observe the reading change process of the sensor, set the monitoring time frequency (according to the experimental purpose), and simultaneously collect and analyze the solutions at different depths of the soil;
(11)(根据实验目的)在取出装有沉积物的采样管后,对沉积物进行分层取样或者只取表层样,然后分析沉积物样品的物理,化学以及生物性质等;(11) (according to the purpose of the experiment) after taking out the sampling tube containing the sediment, carry out layered sampling of the sediment or only take the surface sample, and then analyze the physical, chemical and biological properties of the sediment sample;
(12)清点仪器配件,实验结束。(12) Check the accessories of the instrument, and the experiment is over.
实施案例一:对不同降雨强度下云南抚仙湖典型农业区土壤中氮素的迁移规律和淋失通量进行研究。云南抚仙湖北岸集水区集中了大量农田,由于农田中化肥的施用对水体造成的氮、磷污染已越来越引起关注,农业非点源污染目前已上升为抚仙湖水污染的重要因素。抚仙湖北岸地下水位埋深较浅,约为60cm,受降雨入渗影响,该区的地下水可能已受到农田土壤农药化肥的污染,并且北岸平原区以平均坡度6.4‰由北(平原区)向南(湖泊)倾斜,地下水总的流向由北向南,入渗湖泊,因此浅层地下水已成为向湖泊输送营养物质的主要载体之一。由于目前监测手段的落后,加之降雨过程的随机性,使得观测自然降雨条件下营养盐在土体中的垂向迁移过程和规律在很大程度上存在周期长、工作量大、数据不够准确等困难和缺憾。欲对降雨-入渗-径流-渗流规律以及氮素动态迁移过程进行准确、快速、全面的了解,采用人工模拟降雨的方法,进行室内土柱模拟试验是一种行之有效的方法。实验过程中先选取具有代表性的抚仙湖集水区梁王河流域一蔬菜地进行土壤样品的采集。采用分层采样,按容重进行填充的方法获得供试土柱。实验根据对抚仙湖区域多年来的短时降雨强度进行概率频度分布分析,以此为依据,确定了四种不同的降雨强度,这四种强度代表了当地常见的短时降雨过程的强度,实验一到实验四的降雨强度分别为0.59、0.47、0.38、0.24mm min-1。实验共进行四组,每组设计了两种不同的初始营养盐含量,其中实验组一、实验组二中土壤的初始营养盐含量相同,取自同一时间和同一地点的供试土壤;实验组三、实验组四中土壤的初始营养盐含量相同,为同一批次土壤。利用人工降雨条件下污染物迁移过程研究的室内模拟系统装置开展室内模拟实验,每组实验的降雨强度均不同,实验过程中还对土壤基本物理性质、初始营养盐含量以及渗漏液的营养盐浓度进行分析。实验过程通过带刻度和溢流口的PVC圆柱体管来实现对降雨强度的控制,水通过橡皮管注入PVC圆柱体后,一部分通过PVC管体底部所安装的32个均匀分布的针孔渗出而作用于土壤表层,而多余的水则通过侧向溢流口排出,这样就可以使圆柱体的水压始终处于恒定状态,降雨强度也就处于恒定状态,通过调节不同的水压来获得不同降雨强度的恒定降雨量,降雨强度通过可以通过计算单位时间内的水量下渗来获得。在土壤表层铺装一层软质砂布和滤纸,让水流缓缓渗入土层,以防止股状流和优先流的产生。渗漏液经石英砂过滤层后采用量杯进行人工收集,以供分析测定之用。模拟实验土柱由有机玻璃管柱设计而成,高度50cm,直径18cm,在土柱底部加一层石英砂过滤层以防止堵塞入渗口,渗漏液通过渗漏瓶进行定时收集。在土柱侧面有一个直径为4cm侧向孔,当入径流量大于土壤入渗能力时,能满足地表径流从侧向孔中流出。测定结果为四组实验的渗漏液占入渗总量的百分比的计算结果变化于0.40-0.47,平均值为0.44。对同一初始营养盐含量的土柱实验来看,渗漏液中总氮随降雨强度的增加呈现增大的趋势,但降雨强度的变化对渗漏液中总磷的影响不呈现出明显的规律性;随着降雨强度的增加,渗漏液中铵态氮的出流浓度呈现降低的趋势,渗漏液中硝态氮的出流浓度则与之相反,出流浓度随着降雨强度的增加而相应增大;硝态氮的入渗能力和迁移速度明显强于铵态氮,降雨强度对硝态氮的影响大于铵态氮。该装置可以用于研究人工降雨条件下土壤/沉积物污染物迁移转化研究,同时装置设置的高度也能满足实验的需要。通过HydruslD软件对室内降雨试验进行数值模拟,数值模拟和实测结果基本一致,进一步验证了试验的可行性和准确性,此试验为人工降雨条件下污染物迁移过程研究提供了新途径。Implementation case 1: Research on the migration law and leaching flux of nitrogen in the soil of a typical agricultural area of Fuxian Lake in Yunnan under different rainfall intensities. A large amount of farmland is concentrated in the catchment area on the north bank of Fuxian Lake in Yunnan. The nitrogen and phosphorus pollution caused by the application of chemical fertilizers in farmland has attracted more and more attention. Agricultural non-point source pollution has now become an important factor in the water pollution of Fuxian Lake. . The groundwater level in the north bank of Fuxian Lake is relatively shallow, about 60cm. Due to the impact of rainfall infiltration, the groundwater in this area may have been polluted by farmland soil, pesticides and fertilizers, and the north bank plain area has an average slope of 6.4‰ from the north (plain area) Tilting to the south (the lake), the general flow direction of groundwater is from north to south, infiltrating into the lake. Therefore, shallow groundwater has become one of the main carriers for transporting nutrients to the lake. Due to the backwardness of the current monitoring methods and the randomness of the rainfall process, the observation of the vertical migration process and law of nutrients in the soil under natural rainfall conditions has a long cycle, a large workload, and inaccurate data to a large extent. Difficulties and shortcomings. In order to have an accurate, rapid and comprehensive understanding of the rainfall-infiltration-runoff-seepage law and the nitrogen dynamic migration process, it is an effective method to use the method of artificially simulating rainfall and conduct indoor soil column simulation experiments. During the experiment, a representative vegetable field in the Liangwang River Basin in the catchment area of Fuxian Lake was first selected to collect soil samples. The soil column for testing was obtained by layered sampling and filling method according to bulk density. The experiment is based on the probability frequency distribution analysis of the short-term rainfall intensity in the Fuxian Lake area over the years. Based on this, four different rainfall intensities are determined. These four intensities represent the intensity of the common short-term rainfall process in the local area. , the rainfall intensities of Experiment 1 to Experiment 4 were 0.59, 0.47, 0.38, 0.24mm min -1 . Four groups of experiments were carried out, and two different initial nutrient salt contents were designed for each group. Among them, the initial nutrient salt contents of the soil in experimental group 1 and experimental group 2 were the same, and they were taken from the test soil at the same time and at the same place; the experimental group 3. The initial nutrient content of the soil in the experimental group 4 is the same, which is the same batch of soil. Indoor simulation experiments were carried out using the indoor simulation system device for the study of pollutant migration process under artificial rainfall. The rainfall intensity of each group of experiments was different. During the experiment, the basic physical properties of the soil, the initial nutrient content and the nutrient salt of the seepage concentration was analyzed. During the experiment, the rainfall intensity is controlled by a PVC cylinder pipe with scale and overflow port. After the water is injected into the PVC cylinder through the rubber pipe, part of it seeps out through 32 evenly distributed pinholes installed at the bottom of the PVC pipe body. It acts on the soil surface, and the excess water is discharged through the lateral overflow port, so that the water pressure of the cylinder is always in a constant state, and the rainfall intensity is also in a constant state. By adjusting different water pressures, different water pressures can be obtained. The constant rainfall of rainfall intensity, the rainfall intensity can be obtained by calculating the water infiltration per unit time. Spread a layer of soft emery cloth and filter paper on the soil surface to allow water to slowly infiltrate into the soil layer to prevent strand flow and preferential flow. The seepage liquid is manually collected with a measuring cup after passing through the quartz sand filter layer for analysis and determination. The simulated experiment soil column is designed by a plexiglass column, with a height of 50cm and a diameter of 18cm. A layer of quartz sand filter layer is added at the bottom of the soil column to prevent the clogging of the infiltration port, and the seepage is collected regularly through the seepage bottle. There is a lateral hole with a diameter of 4cm on the side of the soil column. When the runoff flow is greater than the soil infiltration capacity, it can satisfy the surface runoff to flow out of the lateral hole. As a result of the measurement, the calculation results of the percentage of seepage in the total infiltration of four groups of experiments varied from 0.40 to 0.47, and the average value was 0.44. From the soil column experiment with the same initial nutrient content, the total nitrogen in the seepage liquid shows an increasing trend with the increase of the rainfall intensity, but the influence of the change of rainfall intensity on the total phosphorus in the seepage liquid does not show an obvious rule With the increase of rainfall intensity, the outflow concentration of ammonium nitrogen in the seepage fluid showed a decreasing trend, while the outflow concentration of nitrate nitrogen in the seepage fluid was the opposite. The infiltration capacity and migration speed of nitrate nitrogen are obviously stronger than that of ammonium nitrogen, and the impact of rainfall intensity on nitrate nitrogen is greater than that of ammonium nitrogen. The device can be used to study the migration and transformation of soil/sediment pollutants under artificial rainfall conditions, and the height of the device setting can also meet the needs of the experiment. The numerical simulation of the indoor rainfall test was carried out by HydrusID software. The numerical simulation and the measured results are basically consistent, which further verifies the feasibility and accuracy of the test. This test provides a new way for the study of pollutant migration process under artificial rainfall conditions.
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