CN114840616A - Dynamic atmospheric natural environment modeling method based on space-time interpolation - Google Patents
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Abstract
Description
技术领域technical field
本发明提供一种基于时空插值的动态大气自然环境建模方法。它是一种基于典型大气环境数据收集、大气环境数据时空插值建模、环境数据综合统计分析的动态大气自然环境建模方法。它针对典型的大气环境因素和时空位置,综合考虑时间和地理位置的影响,通过时空插值的方法,建立地理位置精度达到0.5度的时空动态变化模型,提供大气自然环境动态变化数据,对环境因素进行综合分析,形成动态大气自然环境建模方法。本专利适用于自然环境建模相关技术领域。The invention provides a dynamic atmospheric natural environment modeling method based on space-time interpolation. It is a dynamic atmospheric natural environment modeling method based on the collection of typical atmospheric environmental data, spatial-temporal interpolation modeling of atmospheric environmental data, and comprehensive statistical analysis of environmental data. Based on typical atmospheric environmental factors and temporal and spatial positions, it comprehensively considers the influence of time and geographic location, and establishes a temporal and spatial dynamic change model with a geographic location accuracy of 0.5 degrees by means of temporal and spatial interpolation. Comprehensive analysis is carried out to form a dynamic atmospheric natural environment modeling method. This patent applies to the technical field related to natural environment modeling.
背景技术Background technique
在大气自然环境条件下,产品所处的自然环境条件不仅在时间尺度上存在连续的变化,在空间尺度上同样存在不同的变化规律,带来的环境效应也不相同,由于受环境因素差异性的影响,建立符合大气自然环境因素时空变化规律的模型具有重要意义。为了获取观测站点外区域的自然环境数据,通常将统计学方法与地理信息系统相结合,基于已有观测站点的观测值进行估算,即自然环境数据空间插值,空间插值方法分为两类:一类是确定性方法,另一类是地质统计学方法。确定性插值方法是基于信息点之间的相似程度或者整个曲面的光滑性来创建一个拟合曲面,比如反距离加权平均插值法、趋势面法、样条函数法等;地质统计学插值方法是利用样本点的统计规律,使样本点之间的空间自相关性定量化,从而在待预测的点周围构建样本点的空间结构模型,比如克里金插值法。确定性插值方法的特点是在样本点处的插值结果和原样本点实际值基本一致,若是利用非确定性插值方法的话,在样本处的插值结果与样本实测值就不一定一致了,有的相差甚远。无论是哪种插值方法,都存在着距离衰减效应,即空间位置上越靠近的点,越可能具有相似的观察值;而距离越远的点,其特征值相似的可能性越小。大气自然环境中,相距较远的点之间相互影响效应较小,可以进行忽略处理,通过在待测环境区域中根据连通性划分区块,将复杂的整体分解成一系列局部单元,有利于减少误差,提高插值和预测的精度。因此,要准确地对产品所经历的实际环境条件进行准确的描述,需要同时对其时间和空间上的变化规律进行描述,进行动态大气自然环境建模。基于此,本发明提出一种基于时空插值的动态大气自然环境建模方法。Under the atmospheric natural environment conditions, the natural environment conditions in which the products are located not only continuously change on the time scale, but also have different changing laws on the spatial scale, resulting in different environmental effects. Due to differences in environmental factors It is of great significance to establish a model that conforms to the temporal and spatial variation of atmospheric natural environment factors. In order to obtain the natural environment data outside the observation site, the statistical method is usually combined with the geographic information system, and the estimation is based on the observation value of the existing observation site, that is, the spatial interpolation of the natural environment data. One class is deterministic methods and the other is geostatistical methods. Deterministic interpolation methods are based on the similarity between information points or the smoothness of the entire surface to create a fitting surface, such as inverse distance weighted average interpolation method, trend surface method, spline function method, etc. Geostatistical interpolation methods are Using the statistical law of sample points, the spatial autocorrelation between sample points is quantified, so as to build a spatial structure model of sample points around the point to be predicted, such as kriging interpolation. The characteristic of the deterministic interpolation method is that the interpolation result at the sample point is basically consistent with the actual value of the original sample point. If the non-deterministic interpolation method is used, the interpolation result at the sample point and the measured value of the sample may not be consistent. Far from it. No matter which interpolation method is used, there is a distance attenuation effect, that is, the closer the points in space are, the more likely they have similar observed values; while the farther the points are, the less likely their eigenvalues are similar. In the atmospheric natural environment, the mutual influence effect between points far apart is small and can be ignored. By dividing the block according to the connectivity in the environmental area to be measured, the complex whole is decomposed into a series of local units, which is conducive to reducing error, improving the accuracy of interpolation and prediction. Therefore, in order to accurately describe the actual environmental conditions experienced by the product, it is necessary to describe its time and space variation laws at the same time, and to model the dynamic atmospheric natural environment. Based on this, the present invention proposes a dynamic atmospheric natural environment modeling method based on spatiotemporal interpolation.
发明内容SUMMARY OF THE INVENTION
(1)本发明的目的:(1) purpose of the present invention:
本发明的目的是提供一种基于时空插值的动态大气自然环境建模方法,它是针对大气自然环境数据收集困难、查询困难、分析困难等一系列问题,提供动态大气自然环境建模方法,它是一种包含典型大气环境数据收集、大气环境数据时空插值建模、环境数据综合统计分析的动态大气自然环境建模方法。通过考虑到不同区域的环境因素差异性,收集不同时空位置的典型大气环境因素,通过对环境因素的综合统计分析,考虑时间和地理位置的影响,采用克里金插值法建立地理位置精度达到0.5度的时空动态变化模型,进行动态大气自然环境建模,最终给出基于时空插值的动态大气自然环境建模方法。The purpose of the present invention is to provide a dynamic atmospheric natural environment modeling method based on space-time interpolation, which is aimed at a series of problems such as difficulty in collecting, querying, and analyzing atmospheric natural environment data, and provides a dynamic atmospheric natural environment modeling method. It is a dynamic atmospheric natural environment modeling method that includes typical atmospheric environment data collection, spatial-temporal interpolation modeling of atmospheric environment data, and comprehensive statistical analysis of environmental data. By taking into account the differences of environmental factors in different regions, typical atmospheric environmental factors in different time and space locations are collected, and through comprehensive statistical analysis of environmental factors, considering the influence of time and geographical location, the Kriging interpolation method is used to establish a geographical location accuracy of 0.5 The spatial and temporal dynamic change model of degree is used to model the dynamic atmospheric natural environment, and finally the dynamic atmospheric natural environment modeling method based on spatio-temporal interpolation is given.
(2)技术方案:基于上述理论和思路,本发明提供一种基于时空插值的动态大气自然环境建模方法,其具体的实施步骤如下:(2) Technical solution: Based on the above theories and ideas, the present invention provides a dynamic atmospheric natural environment modeling method based on space-time interpolation, and its specific implementation steps are as follows:
步骤一:典型大气环境数据收集;Step 1: Collection of typical atmospheric environment data;
大气环境因素主要包含温度、湿度、太阳辐射、降雨、污染物等;本发明针对大气环境中工作的产品,拟考虑的环境参数包括温度和相对湿度;温度是影响材料腐蚀失效的一个重要因素,会对水汽的凝聚及水膜中的气体和盐类的溶解度造成影响,平均气温高的地方,大气腐蚀速率较大;如果大气环境中存在污染物情况,如氯离子,其沉积或溶解在材料表面液膜中时,能够在材料表面形成腐蚀微电池或氧浓差电池,导致材料表面发生腐蚀失效;大气中相对湿度越大,金属表面越容易结露,表面上的电解液膜存在的时间也就越长,腐蚀失效的速度也会增加,对产品的工作性能也会产生影响;因此,针对上述典型环境数据,为满足最终的差值模型地理位置精度达0.5度经纬度的要求,需要对数据收集来源的环境观测站进行筛选:The atmospheric environmental factors mainly include temperature, humidity, solar radiation, rainfall, pollutants, etc.; the present invention is aimed at products working in the atmospheric environment, and the environmental parameters to be considered include temperature and relative humidity; temperature is an important factor affecting the corrosion failure of materials, It will affect the condensation of water vapor and the solubility of gases and salts in the water film. Where the average temperature is high, the atmospheric corrosion rate is larger; if there are pollutants in the atmospheric environment, such as chloride ions, they are deposited or dissolved in the material. When the surface liquid film is in, corrosion micro-battery or oxygen concentration cell can be formed on the surface of the material, resulting in corrosion failure on the surface of the material; the higher the relative humidity in the atmosphere, the easier the metal surface is to condense, and the time the electrolyte film on the surface exists. The longer it is, the faster the corrosion failure will increase, and the working performance of the product will also be affected; therefore, for the above typical environmental data, in order to meet the requirements of the final difference model geographic location accuracy of 0.5 degrees of latitude and longitude, it is necessary to Data collection sources are screened by environmental observatories:
①根据不同环境因素数据来源进行环境数据筛选收集(观测站、文献、数据网);① Screening and collecting environmental data according to different sources of environmental factor data (observation stations, literature, data networks);
②编写程序对科学格式文件数据进行处理和整理;② Write programs to process and organize scientific format file data;
步骤二:大气环境数据时空插值建模;Step 2: Spatial-temporal interpolation modeling of atmospheric environment data;
由于已收集整理完成的环境因素数据存在不完整和缺失的情况,想要覆盖获得目标地区位置的整体环境因素信息,需要通过对已有地理位置的环境数据进行大气环境数据时空插值建模,得到目标地区的整体环境因素数据;Since the collected and sorted environmental factor data is incomplete and missing, in order to cover and obtain the overall environmental factor information of the target area, it is necessary to perform spatial-temporal interpolation modeling of atmospheric environmental data on the environmental data of the existing geographical location to obtain Overall environmental factor data for the target area;
克里金插值法被广泛应用于地质统计的插值计算方法,具有线性、无偏、估计方差最小的特点;克里金插值法的思路是给予空间已知样本点的观测数据以相应的权重值,用以估计未知点的相应数据;由于大气环境的连续性,可以假设温度,相对湿度这些环境变量均满足二阶平稳假设和本征假设,因此可用普通克里金插值法进行计算;假设某一环境因素变量为Z(x),它在各处已知地理位置的观测值分别为:Z(x1),Z(x2),Z(x3),…,Z(xn);Kriging interpolation method is widely used in the interpolation calculation method of geostatistics, which has the characteristics of linearity, unbiasedness and minimum estimation variance; the idea of kriging interpolation method is to give the observation data of known sample points in space with corresponding weight values , used to estimate the corresponding data of the unknown point; due to the continuity of the atmospheric environment, it can be assumed that the environmental variables such as temperature and relative humidity satisfy the second-order stationary assumption and the eigen assumption, so the ordinary kriging interpolation method can be used for calculation; An environmental factor variable is Z(x), and its observed values at known geographic locations are: Z(x 1 ), Z(x 2 ), Z(x 3 ), …, Z(x n );
则在x0处该变量估计值由如下公式求得:Then the estimated value of the variable at x 0 is obtained by the following formula:
式中:Z*(x0)代表x0处该变量的估计值,Z(xi)代表观测值(i=1,…,n),λi为权重系数,可以表示为各个位置的观测值对于估计值的贡献程度;因此问题转变为λi的确定,由于表达式已经满足了线性的要求,因此可以利用剩余的两个限定条件求解:无偏性和估计方差最小;因此,输出的求解方程组为:In the formula: Z * (x 0 ) represents the estimated value of the variable at x 0 , Z(x i ) represents the observed value (i=1,...,n), λ i is the weight coefficient, which can be expressed as the observation at each position The contribution of the value to the estimated value; therefore, the problem turns into the determination of λ i . Since the expression already satisfies the linearity requirements, it can be solved by using the remaining two constraints: unbiasedness and minimum estimated variance; therefore, the output of Solving the system of equations is:
式中:μ为拉格朗日常数,c(xi,xj)是xi和xj的协方差函数;由于变异函数γ(·)与协方差函数c(·)之间的关系近似于此消彼长,可以用变异函数来代入方程组求解,以代替协方差函数,通过变异函数模型表示空间中随距离变化的函数,常见的变异函数模型有:高斯模型,指数模型,球面模型等;In the formula: μ is the Lagrangian number, c(x i , x j ) is the covariance function of x i and x j ; since the relationship between the variogram γ(·) and the covariance function c(·) approximates This trade-off can be solved by substituting the variogram into the equation system instead of the covariance function. The variogram model is used to represent the function that changes with distance in the space. Common variogram models are: Gaussian model, exponential model, spherical model Wait;
所述的:“高斯模型”,是指Said: "Gaussian model", means
所述的:“指数模型”,是指Said: "Exponential Model", means
所述的:“球面模型”,是指Said: "spherical model", means
其中,Δx为xj-xi,j>i;e为指数;a为变程,代表参数均匀具有的空间相关性范围,反应参数空间变化的速度大小,a越大,空间相关性范围越大,说明参数的空间变化速度越小;C0为块金常数,是由于参数误差和微结构所造成的,代表参数随机性变化的部分;C0+C为基台值,反映参数在数值大小上的最大变化幅度;C为拱高,代表参数结构性变化的部分;Among them, Δx is x j -x i , j>i; e is the index; a is the variation range, representing the uniform spatial correlation range of the parameters, the speed of the spatial variation of the response parameters, the larger the a, the greater the spatial correlation range. Larger, indicating that the spatial change speed of the parameter is smaller; C 0 is the nugget constant, which is caused by the parameter error and microstructure, and represents the part of the random change of the parameter; C 0 +C is the base value, reflecting the parameter in the numerical value The maximum change in size; C is the arch height, which represents the structural change of the parameter;
步骤三:环境数据综合统计分析;Step 3: Comprehensive statistical analysis of environmental data;
对于不同地区而言,环境因素的变化存在一定差异,例如在不同区域温差较大,气温的剧烈变化也影响着产品的工作情况,若产品在工作过程中遇到温度降低后,使得材料表面的温度低于周围大气温度,大气中的水蒸气结露凝结在材料表面,就会加速腐蚀;同时,同一地点不同时间的环境因素具有一定差异性,例如某些地区夏季的高温干旱与冬季的低温潮湿,会导致产品的工作环境发生显著变化,直接影响到产品的工作性能;因此,针对不同区域的环境因素特点,对环境进行时间和空间上的分类,以精确到小时的时间维度对环境因素在不同经纬度进行分类筛选,然后通过对环境数据的综合统计分析,形成基于时空插值的动态大气自然环境建模方法;For different regions, there are certain differences in the changes of environmental factors. For example, the temperature difference in different regions is large, and the drastic changes in temperature also affect the working conditions of the product. If the product encounters a temperature drop during the working process, the surface of the material will be When the temperature is lower than the surrounding atmospheric temperature, the condensation of water vapor in the atmosphere will condense on the surface of the material, which will accelerate corrosion; at the same time, the environmental factors at the same location at different times have certain differences, such as high temperature and drought in summer in some areas and low temperature in winter. Humidity will lead to significant changes in the working environment of the product, which will directly affect the working performance of the product; therefore, according to the characteristics of environmental factors in different regions, the environment is classified in time and space, and the time dimension accurate to the hour is used. Classification and screening at different latitudes and longitudes, and then through comprehensive statistical analysis of environmental data, a dynamic atmospheric natural environment modeling method based on spatiotemporal interpolation is formed;
通过以上步骤,达到了通过经纬度等空间信息来准确估计某地区给定时间信息的特定环境因素的效果,解决了环境因素统计、建模、和预测困难的实际问题。Through the above steps, the effect of accurately estimating specific environmental factors of a given time information in a certain area through spatial information such as latitude and longitude is achieved, and the practical problems of environmental factor statistics, modeling, and prediction difficulties are solved.
(3)优点和功效:(3) Advantages and efficacy:
本发明是一种基于时空插值的动态大气自然环境建模方法,其优点为:The present invention is a dynamic atmospheric natural environment modeling method based on space-time interpolation, and has the following advantages:
①本发明针对典型的大气环境因素和时空位置,对环境因素进行分析,综合考虑时间和地理位置的影响,通过克里金插值的方法,建立地理位置精度达到0.5度的时空动态变化模型,提供大气自然环境动态变化数据,并在时间维度对大气自然环境数据进行统计分析,形成基于时空插值的动态大气自然环境建模方法。① The present invention analyzes the environmental factors according to typical atmospheric environmental factors and space-time positions, comprehensively considers the influence of time and geographical position, and establishes a space-time dynamic change model with a geographical position accuracy of 0.5 degrees by means of Kriging interpolation, providing Atmospheric natural environment dynamic change data, and statistical analysis of atmospheric natural environment data in the time dimension, forming a dynamic atmospheric natural environment modeling method based on spatiotemporal interpolation.
②本发明提出的方法计算简便,容易实现,且更加符合工程实际,方便工程技术人员掌握使用,方法科学,工艺性好,便于应用推广。② The method proposed by the present invention is simple to calculate, easy to implement, more in line with engineering practice, convenient for engineering and technical personnel to master and use, scientific method, good manufacturability, and convenient for application and popularization.
附图说明Description of drawings
图1是本发明所述方法的流程图。Figure 1 is a flow chart of the method of the present invention.
图2是太平洋海域-东南亚区域地图。Figure 2 is a map of the Pacific Ocean-Southeast Asia region.
图3是太平洋海域大气温度数据的插值计算结果。Figure 3 shows the interpolation calculation results of the atmospheric temperature data in the Pacific Ocean.
图4是南海海域年温度和相对湿度变化图。Figure 4 shows the annual temperature and relative humidity changes in the South China Sea.
图5是海南地区月温度概率密度分布图。Figure 5 is the distribution map of monthly temperature probability density in Hainan.
具体实施方式Detailed ways
下面以某海域大气自然环境数据中的部分数据为例,结合附图1,对本发明作进一步详细说明。本发明提出一种基于时空插值的动态大气自然环境建模方法,见图1所示,其具体的实施步骤如下:The present invention will be further described in detail below by taking part of the data in the atmospheric natural environment data of a certain sea area as an example and in conjunction with FIG. 1 . The present invention proposes a dynamic atmospheric natural environment modeling method based on space-time interpolation, as shown in Figure 1, and its specific implementation steps are as follows:
步骤一:典型大气环境数据收集Step 1: Collection of typical atmospheric environment data
选取太平洋海域-东南亚区域作为目标海域进行分析,如图2所示,具体经纬度如下所示:Select the Pacific Ocean-Southeast Asia region as the target sea area for analysis, as shown in Figure 2. The specific latitude and longitude are as follows:
表1海域经纬度Table 1 Longitude and latitude of sea area
为满足最终的插值模型地理位置精度达0.5度经纬度的要求,需要对数据收集来源的环境观测站进行筛选。不同环境因素数据的来源如下表所示:In order to meet the requirement that the geographic location accuracy of the final interpolation model reaches 0.5 degrees of latitude and longitude, it is necessary to screen the environmental observation stations from which the data is collected. The sources of data on different environmental factors are shown in the table below:
表2环境因素收集数据来源Table 2 Data sources for environmental factors collection
收集的数据为NetCDF科学格式,无法直接读取,经编写程序转换后,整理为EXCEL可处理格式,并对需要的环境因素进行筛选;The collected data is in the NetCDF scientific format, which cannot be read directly. After being converted by the programming program, it is organized into an EXCEL processable format, and the required environmental factors are screened;
所述的:“NetCDF”,是指网络通用数据格式(network Common Data Form),是由美国大学大气研究协会(University Corporation for Atmospheric Research)的科学家针对科学数据的特点开发的,是一种面向数组型并适于网络共享的数据的描述和编码标准;其广泛应用于大气科学、水文、海洋学、环境模拟、地球物理等诸多领域。用户可以借助多种方式方便地管理和操作该数据集;Said: "NetCDF", refers to the network common data format (Network Common Data Form), which was developed by scientists of the University Corporation for Atmospheric Research (University Corporation for Atmospheric Research) for the characteristics of scientific data, is an array-oriented data format. It is a description and coding standard of data that is suitable for network sharing; it is widely used in atmospheric science, hydrology, oceanography, environmental simulation, geophysics and many other fields. Users can easily manage and manipulate this dataset in a variety of ways;
步骤二:大气环境数据时空插值建模Step 2: Spatial-temporal interpolation modeling of atmospheric environment data
根据整理完成的环境因素数据,在空间上以0.5度为单位对经纬度进行网格化处理,在时间上精确到小时的时间维度对环境因素进行处理,基于以上数据,开展插值计算与自然环境建模,通过移除趋势项,计算自相关系数,求解克里金方程组,误差分析等步骤,进行大气自然环境时空动态建模;具体的,在进行克里金插值计算及建模时,首先需要从原始数据中移除趋势项,这是由于这种周期变化显著影响了变量分布的平稳性,同时造成时间变异函数拟合时出现明显的孔穴效应,不利于时空变异函数的建模,因此在插值实验时,应首先将季节因素去掉,待插值之后再将对应的季节项加上;然后计算序列的自相关系数随延迟时期数的衰减规律,用自相关图检法判断去趋势项数据的平稳性;进而分别对去趋势项后的数据构建时空变差函数,并进行拟合,求解克里金方程组并插值计算环境因素的时空分布数据;以太平洋海域2007年1月1日和8月1日的大气温度环境数据为例,环境剖面计算结果如图3所示,单位均为摄氏度;图中可以看出1月份的气温较低,而8月份气温整体高于1月份;According to the completed environmental factor data, the latitude and longitude are gridded in units of 0.5 degrees in space, and the environmental factors are processed in the time dimension accurate to the hour. Based on the above data, interpolation calculation and natural environment construction are carried out. By removing the trend term, calculating the autocorrelation coefficient, solving the Kriging equations, and analyzing the errors, the spatial and temporal dynamic modeling of the atmospheric natural environment is carried out. Specifically, when performing kriging interpolation calculation and modeling, first The trend term needs to be removed from the original data, because this periodic change significantly affects the stationarity of the variable distribution, and at the same time causes an obvious hole effect in the fitting of the time variogram, which is not conducive to the modeling of the spatiotemporal variogram. Therefore, In the interpolation experiment, the seasonal factor should be removed first, and the corresponding seasonal item should be added after the interpolation; then the decay law of the autocorrelation coefficient of the sequence with the number of delay periods should be calculated, and the detrended item data should be judged by the autocorrelation graph inspection method. Then, the time-space variation function is constructed for the data after detrending, and fitting is performed to solve the Kriging equations and interpolate to calculate the spatio-temporal distribution data of environmental factors; Taking the atmospheric temperature and environmental data on August 1 as an example, the calculation results of the environmental profile are shown in Figure 3, and the units are in degrees Celsius; it can be seen from the figure that the temperature in January is lower, and the temperature in August is generally higher than that in January;
步骤三:环境数据综合统计分析Step 3: Comprehensive statistical analysis of environmental data
通过时空插值建模计算结果给出的环境因素大数据,根据经纬度信息将环境因素的地理位置进行空间分类,同时根据不同时间信息将环境因素的变化进行时间分类,对环境数据进行综合统计分析;Based on the big data of environmental factors given by the calculation results of spatio-temporal interpolation, the geographical location of environmental factors is classified spatially according to the latitude and longitude information, and the changes of environmental factors are classified in time according to different time information, and comprehensive statistical analysis of environmental data is carried out;
由于太平洋海域覆盖范围大,包含不同气候类型,在此范围内环境因素的统计性质变化较大,因此可以选择将目标海域缩小至南海海域(105°E~118°E,4°N~21°N);根据大气温度环境数据,计算给出近14年南海海域的年温度和相对湿度的变化如图4所示,可以看到年平均温度的一直维持在比较稳定的阶段,逐年变化较小,变化范围仅在1℃之间;同时,年平均相对湿度与平均温度有呈现相反升降趋势的情况,原因在于相对湿度的增加可能会导致温度降低,与实际情况一致;Since the Pacific Ocean covers a large area and includes different climate types, the statistical properties of environmental factors within this range vary greatly, so you can choose to narrow the target area to the South China Sea (105°E~118°E, 4°N~21° N); According to the atmospheric temperature and environmental data, the changes in the annual temperature and relative humidity in the South China Sea in the past 14 years are calculated and shown in Figure 4. It can be seen that the annual average temperature has been maintained at a relatively stable stage, and the annual change is small. , the variation range is only between 1 °C; at the same time, the annual average relative humidity and the average temperature have an opposite trend of rising and falling, because the increase in relative humidity may lead to a decrease in temperature, which is consistent with the actual situation;
对于环境因素分布的研究,考虑将目标区域进一步缩小至海南省(108°E~111°E,18°N~20°N),根据大气温度环境数据,计算给出海南省的月温度概率密度分布如图5所示,可以看出1月-12月均呈现比较典型的正态分布,同时温度也是由1月份开始逐渐升温,达到8月份最高后,逐渐呈现降低趋势;For the study of the distribution of environmental factors, consider further reducing the target area to Hainan Province (108°E~111°E, 18°N~20°N), and calculate the monthly temperature probability density of Hainan Province according to the atmospheric temperature environment data The distribution is shown in Figure 5. It can be seen that the months from January to December show a typical normal distribution. At the same time, the temperature gradually increases from January to the highest in August, and then gradually shows a downward trend;
通过以上步骤,形成基于时空插值的动态大气自然环境建模方法;Through the above steps, a dynamic atmospheric natural environment modeling method based on spatiotemporal interpolation is formed;
综上所述,本发明设计一种考虑典型大气环境数据收集、大气环境数据时空插值建模、环境数据综合统计分析的动态大气自然环境建模方法;它针对典型的大气环境因素和时空位置,对环境因素进行筛选,综合考虑时间和地理位置的影响,采用克里金插值法建立地理位置精度达到0.5度的时空动态变化模型,提供大气自然环境动态变化数据,通过时间维度对大气自然环境数据进行统计分析,形成基于时空插值的动态大气自然环境建模方法。To sum up, the present invention designs a dynamic atmospheric natural environment modeling method that considers the collection of typical atmospheric environment data, the spatial-temporal interpolation modeling of atmospheric environment data, and the comprehensive statistical analysis of environmental data; Screening of environmental factors, comprehensively considering the influence of time and geographical location, Kriging interpolation method is used to establish a time-space dynamic change model with a geographical location accuracy of 0.5 degrees, providing dynamic change data of the atmospheric natural environment, and analyzing the atmospheric natural environment data through the time dimension. Statistical analysis is carried out to form a dynamic atmospheric natural environment modeling method based on spatiotemporal interpolation.
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Cited By (5)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
CN116680518A (en) * | 2023-08-04 | 2023-09-01 | 北京市智慧水务发展研究院 | Space-time situation analysis method for surface water environment |
CN116701371A (en) * | 2023-06-09 | 2023-09-05 | 中国科学院地理科学与资源研究所 | Interpolation method and interpolation device for missing values of atmospheric temperature data under covariance analysis |
CN117313307A (en) * | 2023-06-26 | 2023-12-29 | 北京航空航天大学 | Climate model simulation temperature data correction method integrating space-time environment information |
CN117992760A (en) * | 2024-04-07 | 2024-05-07 | 中国电子科技集团公司第十研究所 | Electromagnetic environment monitoring task planning method based on cognitive map |
CN119201925A (en) * | 2024-11-07 | 2024-12-27 | 崂山国家实验室 | Geological investigation whole-flow data gathering system for ancient ocean environment evolution |
Citations (3)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
CN110766191A (en) * | 2019-08-27 | 2020-02-07 | 东华理工大学 | Newly-added PM2.5 fixed monitoring station site selection method based on space-time kriging interpolation |
CN111625993A (en) * | 2020-05-25 | 2020-09-04 | 中国水利水电科学研究院 | Small watershed surface rainfall interpolation method based on mountainous terrain and rainfall characteristic prediction |
CN113159141A (en) * | 2021-04-02 | 2021-07-23 | 北京首创大气环境科技股份有限公司 | Remote sensing estimation method for high-resolution near-real-time PM2.5 concentration |
-
2021
- 2021-12-28 CN CN202111622550.3A patent/CN114840616A/en active Pending
Patent Citations (3)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
CN110766191A (en) * | 2019-08-27 | 2020-02-07 | 东华理工大学 | Newly-added PM2.5 fixed monitoring station site selection method based on space-time kriging interpolation |
CN111625993A (en) * | 2020-05-25 | 2020-09-04 | 中国水利水电科学研究院 | Small watershed surface rainfall interpolation method based on mountainous terrain and rainfall characteristic prediction |
CN113159141A (en) * | 2021-04-02 | 2021-07-23 | 北京首创大气环境科技股份有限公司 | Remote sensing estimation method for high-resolution near-real-time PM2.5 concentration |
Non-Patent Citations (5)
Title |
---|
周体鹏: "基于克里金插值法的昆明市PM2.5预测", 《中国优秀硕士学位论文全文数据库》, no. 2, 15 February 2017 (2017-02-15), pages 6 - 15 * |
徐爱萍;胡力;舒红;: "空间克里金插值的时空扩展与实现", 计算机应用, no. 01, 1 January 2011 (2011-01-01) * |
李如仁 等: "京津冀气溶胶数据普通克里金插值研究", 《沈阳建筑大学学报》, vol. 36, no. 1, 31 January 2020 (2020-01-31), pages 180 - 181 * |
李莎;舒红;徐正全;: "东北三省月降水量的时空克里金插值研究", 水文, no. 03, 25 June 2011 (2011-06-25) * |
谢铖: "深圳市城市热岛与高温热浪日变化特征及人口暴露度研究", 《中国优秀硕士学位论文全文数据库》, no. 7, 15 July 2021 (2021-07-15), pages 14 * |
Cited By (7)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
CN116701371A (en) * | 2023-06-09 | 2023-09-05 | 中国科学院地理科学与资源研究所 | Interpolation method and interpolation device for missing values of atmospheric temperature data under covariance analysis |
CN116701371B (en) * | 2023-06-09 | 2024-03-22 | 中国科学院地理科学与资源研究所 | Interpolation method and device for missing values of atmospheric temperature data under covariance analysis |
CN117313307A (en) * | 2023-06-26 | 2023-12-29 | 北京航空航天大学 | Climate model simulation temperature data correction method integrating space-time environment information |
CN116680518A (en) * | 2023-08-04 | 2023-09-01 | 北京市智慧水务发展研究院 | Space-time situation analysis method for surface water environment |
CN116680518B (en) * | 2023-08-04 | 2023-10-20 | 北京市智慧水务发展研究院 | Space-time situation analysis method for surface water environment |
CN117992760A (en) * | 2024-04-07 | 2024-05-07 | 中国电子科技集团公司第十研究所 | Electromagnetic environment monitoring task planning method based on cognitive map |
CN119201925A (en) * | 2024-11-07 | 2024-12-27 | 崂山国家实验室 | Geological investigation whole-flow data gathering system for ancient ocean environment evolution |
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