Spatiotemporal simulation display system based on two-dimensional water quality simulation method
Through a space-time simulation display system based on two-dimensional water quality simulation method, the problem of difficulty in displaying space-time changes and failure to consider the impact of sewage discharge operations on water quality is solved, and efficient space-time display and management of water quality areas is achieved.
Patent Information
- Application Number
- CN202410259650.1
- Authority / Receiving Office
- CN · China
- Patent Type
- Patents(China)
- Current Assignee / Owner
- Filing Date
- 2024-03-07
- Publication Date
- 2025-04-15
- Estimated Expiration
- 2044-03-07
AI Technical Summary
Traditional water quality simulation methods are difficult to provide intuitive display of time and space changes, and fail to effectively consider the impact of sewage discharge operations of sewage discharge pipes in water areas on water quality, resulting in inefficient water quality management.
Develop a space-time simulation display system based on two-dimensional water quality simulation method. The system includes a data collection module, a water quality monitoring module, a classification module, a comprehensive analysis module, a space-time simulation module, an evaluation module and a display module. Through grid division, data collection and analysis, space-time display and early warning of water quality areas are achieved.
The system can more intuitively display the time and space changes of the water quality area, timely discover and deal with water quality problems, and improve the efficiency and effectiveness of water quality management.
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Figure CN118153135B_ABST
Abstract
Description
Technical Field
[0001] The present invention relates to the technical field of water quality management, and more specifically, to a spatiotemporal simulation display system based on a two-dimensional water quality simulation method. Background Art
[0002] With the development of industrialization and urbanization, water pollution is becoming increasingly serious. In order to effectively manage and control water quality, it is necessary to monitor pollutants in water in real time. Traditional water quality simulation methods are difficult to provide intuitive spatiotemporal changes, and often rely on complex mathematical models and a large amount of computing resources in the process of analyzing the water quality of water bodies. In addition, traditional water quality simulation methods only simulate water quality without considering the impact of sewage discharge operations in sewage pipes in water areas on water quality. Therefore, the development of a simple and efficient spatiotemporal simulation display system based on two-dimensional water quality simulation methods is of great significance for water quality management.
[0003] Invention Project
[0004] To achieve the above object, the present invention provides the following technical solutions:
[0005] A spatiotemporal simulation display system based on a two-dimensional water quality simulation method, including a data collection module, a water quality monitoring module, a classification module, a comprehensive analysis module, a spatiotemporal simulation module, an evaluation module, and a display module;
[0006] The space-time simulation module is used to grid the target water quality area, obtain the grid division results and transmit them to the data collection module and the water quality monitoring module;
[0007] The data collection module is used to collect emission data for each grid in the grid division result, and then summarize all the collected emission data to obtain the emission data set and transmit it to the evaluation module;
[0008] The water quality monitoring module is used to collect water quality data for each grid in the grid division result, and then summarizes all the collected water quality data to obtain a water quality data set and transmit it to the classification module;
[0009] The classification module is used to classify the data types in the water quality data set according to the preset classification standard to obtain water quality classification set 1, water quality classification set 2 and water quality classification set 3, and then summarize the water quality classification set 1, water quality classification set 2 and water quality classification set 3 together to obtain the classified data set and transmit it to the comprehensive analysis module;
[0010] The comprehensive analysis module is used to analyze the water quality of the target grid obtained after division according to the classification data set, obtain the analysis value, and then obtain different types of analysis results according to the analysis value, and then summarize all the analysis values into an analysis value set and transmit it to the display module;
[0011] The evaluation module is used to calculate the emission value based on the emission data set, and then evaluate the emission value with the standard emission threshold to obtain the evaluation value, summarize the evaluation results into an evaluation set and transmit it to the display module;
[0012] The display module is used to display the target water quality area in time and space according to the analysis values and evaluation sets in the comprehensive analysis module and the preset display strategy.
[0013] In a preferred embodiment, the spatiotemporal simulation display system based on the two-dimensional water quality simulation method further includes an early warning module.
[0014] The comprehensive analysis module is used to analyze the water quality of the target grid obtained after division according to the classification data set, obtain the analysis value, and then obtain different types of analysis results according to the analysis value, and then summarize all the analysis results into an analysis type set and transmit it to the early warning module;
[0015] The evaluation results in the evaluation module are summarized into evaluation sets and then transmitted to the display module and the early warning module;
[0016] The early warning module is used to decide whether to issue or not issue early warning signals of different levels based on the analysis type set and evaluation set.
[0017] In a preferred embodiment, the grid division result refers to gridding the target water quality area according to a preset division standard to obtain multiple separate grids after division, and then numbering the multiple separate grids after division in the space-time simulation module to obtain multiple consecutively numbered grids, namely the grid division result.
[0018] In a preferred embodiment, the data collection module is used to collect emission data for each grid in the grid division result, which means: the emission data in each grid in the grid division result is collected according to a preset time window, and the emission data includes data corresponding to m emission indicators. The emission data is marked as PFm according to the classification of the emission indicators, where m = 1, 2, 3, 4, ..., a, and a is a positive integer.
[0019] In a preferred embodiment, the water quality monitoring module is used to collect water quality data for each grid in the grid division result, and then summarizes all the collected water quality data to obtain a water quality data set and transmits it to the classification module.
[0020] Step A1, collecting corresponding data according to the water resource index for each grid in the grid division result according to the preset time window, and obtaining a water resource index data subset;
[0021] Step A2, collecting corresponding data according to the water environment index for each grid in the grid division result according to the preset time window, and obtaining a water environment index data subset;
[0022] Step A3, collecting corresponding data according to the water ecological index for each grid in the grid division result according to the preset time window, and obtaining a water ecological index data subset;
[0023] Step A4, summarizing the water resource index data subset, water environment index data subset, and water ecology index data subset in each grid to obtain a water quality index data subset;
[0024] Step A5: Aggregate all the water quality index data subsets in step A4 to obtain a water quality data set and transmit it to the classification module.
[0025] In a preferred embodiment, the classification module is used to classify the data types in the water quality data set according to a preset classification standard, and the water quality classification set 1, water quality classification set 2 and water quality classification set 3 refer to:
[0026] The data types in the water quality data set are classified according to the preset classification standards to obtain Class I data, Class II data, and Class III data. Then all Class I data are summarized to obtain water quality classification set one, all Class II data are summarized to obtain water quality classification set two, and all Class III data are summarized to obtain water quality classification set three.
[0027] In a preferred embodiment, the comprehensive analysis module is used to perform water quality analysis on the target grid obtained after division according to the classified data set to obtain analysis values, and then obtain different types of analysis results according to the analysis values, which refers to:
[0028] Step 1: Mark each data in water quality classification set 1 as FL1i, and then substitute it into calculation formula 1 to obtain impact value 1: YX1 is the influence value one, fi is the influence coefficient corresponding to each data FL1i in the water quality classification set one and fi is not zero, BL1i is the standard data value of a class corresponding to each data FL1i in the water quality classification set one;
[0029] Step 2: Mark each data in the water quality classification set 2 as FL2i, and then substitute it into the calculation formula 2 to obtain the impact value 2: YX2 = ∑ (qi*FL2i) 2 , YX2 is the impact value 2, qi is the impact coefficient corresponding to each data FL2i in the water quality classification set 2, and qi is not zero;
[0030] Step 3: Mark each data in water quality classification set 3 as FL2i, and then substitute it into calculation formula 3 to obtain impact value 3: YX3 is the influence value three, pi is the influence coefficient corresponding to each data FL3i in the water quality classification set three and pi is not zero;
[0031] Step 4: Substitute the influence value 1 YX1, influence value 2 YX2, and influence value 3 YX3 into the analysis value calculation formula: y1, y2, y3 are all preset proportional values, and y1, y2, y3 are all greater than zero and the sum of y1, y2, y3 is one, X1, X2, X3 are analysis thresholds corresponding to influence value one YX1, influence value two YX2, influence value three YX3 respectively, FX is the analysis value;
[0032] Step 5: Compare the analysis value FX with the preset standard analysis value. When the analysis value FX is greater than or equal to the preset standard analysis value, the result of analysis type 1 is obtained. When the analysis value FX is less than the preset standard analysis value, the result of analysis type 2 is obtained.
[0033] In a preferred embodiment, the evaluation module is used to calculate the emission value according to the emission data set, and then evaluate the emission value with the standard emission threshold value, and the evaluation value obtained refers to:
[0034] First calculate the emission value: FZ is the emission value, hm is the proportional coefficient corresponding to the emission data PFm, and then the ratio of the emission value FZ to the standard emission threshold is calculated, and the sewage outlets in the target grid are sorted according to the size of the ratio. Each serial number corresponds to a pre-set evaluation value.
[0035] In a preferred embodiment, the warning module is used to decide whether to issue or not issue warning signals of different levels based on the analysis type set and the evaluation set, which means that when the target grid in the analysis type set is the result of analysis type one, no warning signal is issued; otherwise, according to the preset evaluation value-warning signal level form, the warning signal level corresponding to the evaluation value of each sewage outlet in the target grid is found and a warning signal of the corresponding level is issued.
[0036] Technical effects and advantages of the present invention:
[0037] The spatiotemporal simulation module provided in the present invention divides the target water quality area to obtain a plurality of separate grids, ensuring that the water conditions of each grid are approximately the same, so as to enable better comparison and analysis; after the grid division is completed, the data collection module collects the discharge data of each grid; the water quality monitoring module collects the water quality data of each grid, such as temperature, turbidity, pH value, etc.; the classification module classifies the collected water quality data; the comprehensive analysis module uses the classified data to perform a detailed water quality analysis on each grid; the evaluation module calculates the discharge value using the discharge data set, and compares it with the standard discharge threshold value to obtain the evaluation value; the display module displays the target water quality area in spatiotemporal according to the preset strategy based on the results of the comprehensive analysis module and the evaluation module, so as to facilitate the user to have a real-time understanding of the water quality of the target water quality area and a more intuitive display.
[0038] The early warning module in the present invention decides whether to issue an early warning signal based on the analysis type set and the evaluation set. The level of the early warning signal will be determined based on the evaluation value. In conjunction with the data collection module, water quality monitoring module, classification module, comprehensive analysis module, space-time simulation module, evaluation module, and display module in the space-time simulation display system based on the two-dimensional water quality simulation method, it can effectively monitor and manage water quality, promptly discover and deal with problems, and protect water resources and the environment. BRIEF DESCRIPTION OF THE DRAWINGS
[0039] In order to facilitate understanding by those skilled in the art, the present invention is further described below in conjunction with the accompanying drawings;
[0040] Figure 1 It is a schematic diagram of the spatiotemporal simulation display system based on the two-dimensional water quality simulation method in the present invention. DETAILED DESCRIPTION
[0041] The following will be combined with the drawings in the embodiments of the present invention to clearly and completely describe the technical solutions in the embodiments of the present invention. Obviously, the described embodiments are only part of the embodiments of the present invention, not all of the embodiments. Based on the embodiments of the present invention, all other embodiments obtained by ordinary technicians in this field without creative work are within the scope of protection of the present invention.
[0042] Example 1
[0043] The spatiotemporal simulation display system based on the two-dimensional water quality simulation method includes a data collection module, a water quality monitoring module, a classification module, a comprehensive analysis module, a spatiotemporal simulation module, an evaluation module, and a display module; the data collection module, the water quality monitoring module, the classification module, the comprehensive analysis module, the spatiotemporal simulation module, the evaluation module, and the display module are communicatively connected.
[0044] The selection of water body models is based on the following considerations: 1. Spatial complexity: The two-dimensional model can simultaneously consider the changes in the length and width of the water body, which is crucial for studying grids with complex geometric shapes such as curved rivers, lakes, and near-shore waters. It allows the simulation of water flow and pollutant transport in the lateral and longitudinal directions, and more accurately reflects the actual flow conditions; 2. Hydrodynamic simulation: One-dimensional models usually assume that water flows only along the axis of the river or the main flow direction, ignoring lateral flow and mixing, while two-dimensional models can simulate the flow velocity distribution perpendicular to the main flow direction, as well as the complex flow field caused by changes in the river's banks and bottom terrain; 3. Diffusion of pollutants: In real water bodies, pollutants not only diffuse along the direction of the water flow, but also diffuse and mix on the cross-section perpendicular to the flow direction. The two-dimensional model can better describe this cross-section pollutant distribution and diffusion process; 4. Boundary condition processing: 2 The two-dimensional model can define and process various boundary conditions in more detail, such as inflow / outflow boundaries, water level fluctuations, rainfall infiltration, terrain changes, etc., so that the simulation results are more in line with the actual situation; 5. Environmental management decision-making: For environmental management and planning, it is very important to understand the specific concentrations of pollutants in different locations. The high-resolution data provided by the two-dimensional model can help decision makers formulate more reasonable water quality management plans and emergency response strategies; 6. Scientific research and education: In the field of scientific research and education, the two-dimensional model provides more details and the possibility of in-depth understanding, which helps to reveal the inherent mechanism of pollutant transport and transformation and enhance the understanding of the water environment system; and under reasonable simplification, the two-dimensional model can obtain the required results faster than the three-dimensional model, and greatly save computing resources, which makes the two-dimensional model have higher efficiency and practicality in practical applications. Therefore, the two-dimensional model is adopted in the present invention.
[0045] The space-time simulation module is used to grid the target water quality area, obtain the grid division results and transmit them to the data collection module and the water quality monitoring module; the target water quality area is divided according to the preset standards to obtain multiple separate grids, each grid will be assigned a number, and all numbers are continuous to facilitate subsequent data collection and analysis. The purpose of this division is to ensure that the water conditions of each grid are approximately consistent as much as possible. The standards and methods of division can refer to the two-dimensional water quality simulation method in the prior art, which is the prior art and will not be elaborated on here.
[0046] The data collection module is used to collect emission data for each grid in the grid division result, and then summarize all the collected emission data to obtain an emission data set and transmit it to the evaluation module; the specific implementation method is: the emission data in each grid in the grid division result is collected according to the preset time window, and the emission data contains data corresponding to m emission indicators. According to the classification of emission indicators, the emission data is marked as PFm, m = 1, 2, 3, 4, ..., a, a is a positive integer, and an example is given as: from a mechanical point of view, some substances mixed into the water body can significantly affect the density of the water, thereby affecting the mechanical properties of the water body; while some substances will not, therefore, the former is called dynamically active substances and the latter is called dynamically inert substances. Dynamically inert substances are pollutants with a density equivalent to that of the ambient water. Their mixing does not affect the original dynamic characteristics of the ambient water. It is not necessary to separate them from the ambient water when taking particles for mechanical analysis. Dynamically active substances will change their dynamic characteristics after intervening in the ambient water, such as cooling water discharge or the invasion of density flow. From a physical and biochemical perspective, some substances mixed into the ambient water will cause biochemical reactions or biodegradation, generate new substances, and change their original concentrations, but some will not. The former are called non-conservative substances and the latter are conservative substances. Therefore, when collecting emission data for each grid in the grid division result, the data corresponding to the m emission indicators contained in the emission data refer to the m conservative dynamically inert emission substances.
[0047] The water quality monitoring module is used to collect water quality data for each grid in the grid division result, and then summarize all the collected water quality data to obtain the water quality data set and transmit it to the classification module; referring to water quality indicators and standards, the quality of water can be judged by certain indicators, which mainly include: physical indicators such as temperature, chromaticity, turbidity, solid content, conductivity, etc.; chemical indicators such as pH value, hardness, dissolved oxygen concentration, chloride content, etc.; microbial indicators such as total bacteria count, total E. coli count, etc.; specifically refers to:
[0048] Step A1, according to the preset time window, collect corresponding data according to the water resource index for each grid in the grid division result, and obtain a water resource index data subset; such as temperature, chromaticity, turbidity and solid content, etc. In many cases, the lower the better for these indicators, for example, higher turbidity usually means more suspended matter in the water, which may affect the transparency and sensory quality of the water;
[0049] Step A2, according to the preset time window, collect the corresponding data of each grid in the grid division result according to the water environment index, and obtain the water environment index data subset; including pH value, hardness, dissolved oxygen concentration and chloride content, among which, pH value generally has a moderate range, and the pH value data type is classified into water quality classification set 2 in the following text, too high or too low is not ideal; too high hardness may cause scale deposition; and the higher the dissolved oxygen concentration, the better, because it indicates that there is enough oxygen in the water for biological use, and it is classified into water quality classification set 1; water with too high chloride content may not be suitable for drinking, and it is classified into water quality classification set 3;
[0050] Step A3: Collect corresponding data according to water ecological indicators for each grid in the grid division result according to the preset time window to obtain a subset of water ecological indicator data; such as total bacteria count and total E. coli count, the lower the better. High levels of bacteria or E. coli counts indicate that the water may be contaminated by feces, increasing the risk of disease transmission;
[0051] Step A4, summarizing the water resource index data subset, water environment index data subset, and water ecology index data subset in each grid to obtain a water quality index data subset;
[0052] Step A5: Aggregate all the water quality index data subsets in step A4 to obtain a water quality data set and transmit it to the classification module.
[0053] The classification module is used to classify the data types in the water quality data set according to the preset classification standards to obtain water quality classification set one, water quality classification set two and water quality classification set three, and then summarize the water quality classification set one, water quality classification set two and water quality classification set three to obtain a classified data set and transmit it to the comprehensive analysis module; specifically: the data types in the water quality data set are classified according to the preset classification standards to obtain Class I data, Class II data, and Class III data, Class I data indicates that the higher the data is, the better, Class II data indicates that the data is too high or too low, which is not ideal, and Class III data indicates that the lower the data is, the better; then all Class I data are summarized to obtain water quality classification set one, all Class II data are summarized to obtain water quality classification set two, and all Class III data are summarized to obtain water quality classification set three.
[0054] The comprehensive analysis module is used to analyze the water quality of the target grid obtained after division according to the classification data set, obtain the analysis value, and then obtain different types of analysis results according to the analysis value, and then summarize all the analysis values into an analysis value set and transmit it to the display module; the specific logic is as follows:
[0055] Step 1: Mark each data in water quality classification set 1 as FL1i, and then substitute it into calculation formula 1 to obtain impact value 1: YX1 is the impact value 1, fi is the impact coefficient corresponding to each data FL1i in the water quality classification set 1 and fi is not zero, BL1i is the standard data value of a class corresponding to each data FL1i in the water quality classification set 1; the impact value 1 YX1 indicates the overall impact of all indicators on water quality, the higher the data, the better it is;
[0056] Step 2: Mark each data in the water quality classification set 2 as FL2i, and then substitute it into the calculation formula 2 to obtain the impact value 2: YX2 = ∑ (qi*FL2i) 2 , YX2 is the impact value 2, qi is the impact coefficient corresponding to each data FL2i in the water quality classification set 2, and qi is not zero; the impact value 2 YX2 represents the overall impact of all indicators on water quality that are too high or too low;
[0057] Step 3: Mark each data in water quality classification set 3 as FL2i, and then substitute it into calculation formula 3 to obtain impact value 3: YX3 is the third impact value, pi is the impact coefficient corresponding to each data FL3i in the third water quality classification set, and pi is not zero; the third impact value YX3 indicates the overall impact of all indicators on water quality, the lower the data, the better;
[0058] Step 4: Substitute the influence value 1 YX1, influence value 2 YX2, and influence value 3 YX3 into the analysis value calculation formula: y1, y2, y3 are all preset proportional values, and y1, y2, y3 are all greater than zero and the sum of y1, y2, y3 is one. y1, y2, y3 correspond to the influence value 1 YX1, influence value 2 YX2, influence value 3 YX3 on the water quality of the individual grid, i.e., the target grid obtained after division. X1, X2, X3 are the analysis thresholds corresponding to the influence value 1 YX1, influence value 2 YX2, influence value 3 YX3, respectively. FX is the analysis value.
[0059] Step 5. Compare the analysis value FX with the preset standard analysis value. When the analysis value FX is greater than or equal to the preset standard analysis value, the result of analysis type one is obtained. When the analysis value FX is less than the preset standard analysis value, the result of analysis type two is obtained. The larger the analysis value FX, the better the water quality. The smaller the analysis value FX, the worse the water quality. The analysis value FX can be used to show whether the water quality of the individual grid meets the requirements.
[0060] The evaluation module is used to calculate the emission value based on the emission data set, and then evaluate the emission value with the standard emission threshold to obtain the evaluation value. The evaluation results are summarized into an evaluation set and transmitted to the display module; specifically: first calculate the emission value: FZ is the emission value, hm is the proportionality coefficient corresponding to the emission data PFm, and then the ratio of the emission value FZ to the standard emission threshold is calculated. The standard emission threshold is established in the following way: for the sewage outlets within the target grid obtained after division, the sewage discharge permit of the enterprise corresponding to the sewage outlet is obtained. The sewage discharge permit stipulates the various environmental protection requirements that the sewage discharge unit must comply with when discharging sewage. These requirements include the location and number of sewage outlets, the discharge method, the discharge destination, the type of pollutants discharged, the emission concentration and emission amount, and the emission standards that must be implemented. Then, professionals determine the proportionality coefficient hm based on the degree of impact of the emission data PFm on the water quality, and determine the standard emission threshold of the target grid obtained after the division. Moreover, the sewage discharge permit of the enterprise is generally updated once a year. Therefore, when the sewage discharge permit of the enterprise is updated, the standard emission thresholds of the corresponding target grids obtained after division also need to be adjusted annually.
[0061] The sewage outlets in the target grid are sorted according to the size of the ratio. Each serial number corresponds to a preset evaluation value. For example, if there are n sewage outlets in the target grid, the emission values of these n sewage outlets are calculated first, and then the ratio of the emission value FZ to the standard emission threshold is calculated. The sewage outlets in the target grid are sorted according to the size of the ratio. For example, after descending order, the preset evaluation value corresponding to the first sewage outlet is 100, and the evaluation value is reduced by 10 for each decrease in position. The preset evaluation value corresponding to the second sewage outlet is 90.
[0062] The display module is used to display the target water quality area in time and space according to the analysis value and evaluation set in the comprehensive analysis module and the preset display strategy; specifically: the water quality of the target water quality area at different times is displayed in chronological order, and a three-dimensional model of the target water quality area is established at the same time, and then the corresponding number is assigned to the individual grids after division according to the grid division result, and the corresponding position of the sewage outlet in the individual grid, that is, the target grid obtained after division, is displayed. The sewage outlet can also be numbered. When the analysis value FX is greater than or equal to the preset standard analysis value and the result of analysis type one is obtained, the water body of the individual grid is clear. When the analysis value FX is less than the preset standard analysis value and the result of analysis type two is obtained, the water body of the individual grid is turbid. , and when the water in the individual grid is turbid, the internal sewage outlets will display different colors in the graphics corresponding to the sewage outlets according to the level of the early warning signal. The more obvious the color is, the greater the impact of the sewage outlet on the water quality of the individual grid is, and a sewage investigation is needed. The relevant departments can conduct sewage outlet investigation operations; it can also be that the corresponding number assigned to the individual grid is used as the horizontal axis, its analysis value FX is used as the vertical axis, and the preset standard analysis value is used as the standard line, which can display in real time whether the individual grids in the target water quality area have water quality problems, or it can be that time is used as the horizontal axis, the analysis value FX of a specific individual grid is used as the vertical axis, and the preset standard analysis value is used as the standard line, which can display in real time whether the specific individual grid has water quality problems.
[0063] The grid division result refers to the grid division of the target water quality area according to the preset division standard to obtain multiple separate grids after division, and then the multiple separate grids after division are numbered in the space-time simulation module to obtain multiple continuously numbered grids, namely the grid division result. The purpose of division is to ensure that the water conditions of each grid are approximately consistent as much as possible, and the purpose of lot numbering is to better display the target water quality area in space and time in the display module. The following is a detailed description and example, and no further elaboration is required here.
[0064] Example 2
[0065] A spatiotemporal simulation and display system based on a two-dimensional water quality simulation method includes a data collection module, a water quality monitoring module, a classification module, a comprehensive analysis module, a spatiotemporal simulation module, an evaluation module, and a display module; the spatiotemporal simulation module is used to grid the target water quality area, obtain the grid division results and transmit them to the data collection module and the water quality monitoring module; the data collection module is used to collect emission data for each grid in the grid division results, and then summarize all the collected emission data to obtain an emission data set and transmit it to the evaluation module; the water quality monitoring module is used to collect water quality data for each grid in the grid division results, and then summarize all the collected water quality data to obtain a water quality data set and transmit it to the classification module; the classification module is used to classify the data types in the water quality data set according to preset classification standards. Classification is performed to obtain water quality classification set one, water quality classification set two and water quality classification set three, and then the water quality classification set one, water quality classification set two and water quality classification set three are summarized together to obtain a classification data set and transmitted to the comprehensive analysis module; the comprehensive analysis module is used to perform water quality analysis on the target grid obtained after division according to the classification data set to obtain analysis values, and then obtain different types of analysis results according to the analysis values, and then summarize all the analysis values into analysis value sets and transmit them to the display module; the evaluation module is used to calculate the emission value according to the emission data set, and then evaluate the emission value with the standard emission threshold to obtain an evaluation value, summarize the evaluation results into an evaluation set and transmit it to the display module; the display module is used to perform spatiotemporal display of the target water quality area according to the analysis values and evaluation sets in the comprehensive analysis module and according to a preset display strategy.
[0066] The spatiotemporal simulation display system based on the two-dimensional water quality simulation method also includes an early warning module.
[0067] The comprehensive analysis module is used to analyze the water quality of the target grid obtained after division according to the classification data set, obtain the analysis value, and then obtain different types of analysis results according to the analysis value, and then summarize all the analysis results into an analysis type set and transmit it to the early warning module;
[0068] The evaluation results in the evaluation module are summarized into evaluation sets and then transmitted to the display module and the early warning module;
[0069] The warning module is used to decide whether to issue or not issue warning signals of different levels according to the analysis type set and the evaluation set. Specifically, when the target grid in the analysis type set is the result of analysis type one, no warning signal is issued. Otherwise, according to the preset evaluation value-warning signal level form, the warning signal level corresponding to the evaluation value of each sewage outlet in the target grid is found and a warning signal of the corresponding level is issued. For example, if the evaluation value of one of the sewage outlets in the target grid is 70 and the corresponding warning signal level is level seven, a level seven warning signal is issued. The level of the warning signal can be expressed in the following forms: the flashing speed of the warning light, the volume of the warning buzzer, and the color vividness of the graphic corresponding to the sewage outlet when it is displayed on the display module.
[0070] The spatiotemporal simulation and display system based on the two-dimensional water quality simulation method also includes a recording module, which is used to record the entire operation process of the spatiotemporal simulation and display system based on the two-dimensional water quality simulation method. The recording module, early warning module, data collection module, water quality monitoring module, classification module, comprehensive analysis module, spatiotemporal simulation module, evaluation module, and display module are communicatively connected.
[0071] The above formulas are all dimensionless and numerical calculations. The formula is a formula for the most recent real situation obtained by collecting a large amount of data and performing software simulation. The preset parameters in the formula are set by technicians in this field according to actual conditions.
[0072] It should be understood that in the various embodiments of the present application, the size of the serial numbers of the above-mentioned processes does not mean the order of execution. The execution order of each process should be determined by its function and internal logic, and should not constitute any limitation on the implementation process of the embodiments of the present application.
[0073] In addition, each functional unit in each embodiment of the present application may be integrated into one processing unit, or each unit may exist physically separately, or two or more units may be integrated into one unit.
[0074] Those of ordinary skill in the art will appreciate that the units and algorithm steps of each example described in conjunction with the embodiments disclosed herein can be implemented in electronic hardware, or a combination of computer software and electronic hardware. Whether these functions are performed in hardware or software depends on the specific application and design constraints of the technical solution. Professional and technical personnel can use different methods to implement the described functions for each specific application, but such implementation should not be considered to be beyond the scope of this application.
[0075] Those skilled in the art can clearly understand that, for the convenience and brevity of description, the specific working processes of the systems, devices and units described above can refer to the corresponding processes in the aforementioned method embodiments and will not be repeated here.
[0076] The above is only a specific implementation of the present application, but the protection scope of the present application is not limited thereto. Any person skilled in the art who is familiar with the present technical field can easily think of changes or substitutions within the technical scope disclosed in the present application, which should be included in the protection scope of the present application. Therefore, the protection scope of the present application should be based on the protection scope of the claims.
Claims
1. A spatiotemporal simulation display system based on a two-dimensional water quality simulation method, characterized in that: It includes data collection module, water quality monitoring module, classification module, comprehensive analysis module, space-time simulation module, evaluation module and display module; The space-time simulation module is used to grid the target water quality area, obtain the grid division results and transmit them to the data collection module and water quality monitoring module; The grid division result refers to the grid division of the target water quality area according to the preset division standard to obtain multiple divided individual grids, and then the multiple divided individual grids are numbered in the space-time simulation module to obtain multiple consecutively numbered grids, i.e., the grid division result; The data collection module is used to collect emission data for each grid in the grid division result, and then summarize all the collected emission data to obtain the emission data set and transmit it to the evaluation module; The water quality monitoring module is used to collect water quality data for each grid in the grid division result, and then summarizes all the collected water quality data to obtain a water quality data set and transmit it to the classification module; The classification module is used to classify the data types in the water quality data set according to the preset classification standard to obtain water quality classification set 1, water quality classification set 2 and water quality classification set 3, and then summarize the water quality classification set 1, water quality classification set 2 and water quality classification set 3 together to obtain the classified data set and transmit it to the comprehensive analysis module; The comprehensive analysis module is used to analyze the water quality of the target grid obtained after division according to the classification data set, obtain the analysis value, and then obtain different types of analysis results according to the analysis value, and then summarize all the analysis values into an analysis value set and transmit it to the display module; The evaluation module is used to calculate the emission value based on the emission data set, and then evaluate the emission value with the standard emission threshold to obtain the evaluation value, summarize the evaluation results into an evaluation set and transmit it to the display module; The display module is used to display the target water quality area in time and space according to the analysis values and evaluation sets in the comprehensive analysis module and the preset display strategy; The classification module is used to classify the data types in the water quality data set according to the preset classification standards, and the water quality classification set 1, water quality classification set 2 and water quality classification set 3 refer to: The data types in the water quality data set are classified according to the preset classification standard to obtain Class I data, Class II data, and Class III data. Then all Class I data are summarized to obtain water quality classification set 1, all Class II data are summarized to obtain water quality classification set 2, and all Class III data are summarized to obtain water quality classification set 3; The comprehensive analysis module is used to analyze the water quality of the target grid obtained after division according to the classified data set, obtain the analysis value, and then obtain different types of analysis results according to the analysis value: Step 1: Mark each data in water quality classification set 1 as FL1i, and then substitute it into calculation formula 1 to obtain impact value 1: , YX1 is the influence value one, fi is the influence coefficient corresponding to each data FL1i in the water quality classification set one and fi is not zero, BL1i is a type of standard data value corresponding to each data FL1i in the water quality classification set one; Step 2: Mark each data in water quality classification set 2 as FL2i, and then substitute it into calculation formula 2 to obtain impact value 2: , YX2 is the impact value 2, qi is the impact coefficient corresponding to each data FL2i in the water quality classification set 2, and qi is not zero; Step 3: Mark each data in water quality classification set 3 as FL3i, and then substitute it into calculation formula 3 to obtain impact value 3: , YX3 is the influence value three, pi is the influence coefficient corresponding to each data FL3i in the water quality classification set three, and pi is not zero; Step 4: Substitute the influence value 1 YX1, influence value 2 YX2, and influence value 3 YX3 into the analysis value calculation formula: , y1, y2, y3 are all preset proportional values, and y1, y2, y3 are all greater than zero and the sum of y1, y2, y3 is one, X1, X2, X3 are analysis thresholds corresponding to influence value one YX1, influence value two YX2, influence value three YX3 respectively, FX is the analysis value; Step 5: Compare the analysis value FX with the preset standard analysis value. When the analysis value FX is greater than or equal to the preset standard analysis value, the result of analysis type 1 is obtained. When the analysis value FX is less than the preset standard analysis value, the result of analysis type 2 is obtained. The evaluation module is used to calculate the emission value based on the emission data set, and then evaluate the emission value with the standard emission threshold. The evaluation value is: First calculate the emission value: , FZ is the emission value, hm is the proportional coefficient corresponding to the emission data PFm, and then the ratio of the emission value FZ to the standard emission threshold is calculated, and the sewage outlets in the target grid are sorted according to the size of the ratio. Each serial number corresponds to a preset evaluation value.
2. The spatiotemporal simulation display system based on the two-dimensional water quality simulation method according to claim 1, characterized in that: The spatiotemporal simulation display system based on the two-dimensional water quality simulation method also includes an early warning module. The comprehensive analysis module is used to analyze the water quality of the target grid obtained after division according to the classification data set, obtain the analysis value, and then obtain different types of analysis results according to the analysis value, and then summarize all the analysis results into an analysis type set and transmit it to the early warning module; The evaluation results in the evaluation module are summarized into evaluation sets and then transmitted to the display module and the early warning module; The early warning module is used to decide whether to issue or not issue early warning signals of different levels based on the analysis type set and evaluation set.
3. The spatiotemporal simulation display system based on the two-dimensional water quality simulation method according to claim 2 is characterized in that: The data collection module is used to collect emission data for each grid in the grid division result, which means: the emission data in each grid in the grid division result is collected according to the preset time window. The emission data contains data corresponding to m emission indicators. According to the classification of emission indicators, the emission data is marked as PFm, m=1, 2, 3, 4, ..., a, and a is a positive integer.
4. The spatiotemporal simulation display system based on the two-dimensional water quality simulation method according to claim 3 is characterized in that: The water quality monitoring module is used to collect water quality data for each grid in the grid division result, and then summarizes all the collected water quality data to obtain a water quality data set and transmit it to the classification module. Step A1, collecting corresponding data according to the water resource index for each grid in the grid division result according to the preset time window, and obtaining a water resource index data subset; Step A2, collecting corresponding data according to the water environment index for each grid in the grid division result according to the preset time window, and obtaining a water environment index data subset; Step A3, collecting corresponding data according to the water ecological index for each grid in the grid division result according to the preset time window, and obtaining a water ecological index data subset; Step A4, summarizing the water resource index data subset, water environment index data subset, and water ecology index data subset in each grid to obtain a water quality index data subset; Step A5: Aggregate all the water quality index data subsets in step A4 to obtain a water quality data set and transmit it to the classification module.
5. The spatiotemporal simulation display system based on the two-dimensional water quality simulation method according to claim 4 is characterized in that: The warning module is used to decide whether to issue or not issue warning signals of different levels according to the analysis type set and the evaluation set. This means that when the target grid in the analysis type set is the result of analysis type one, no warning signal is issued. Otherwise, according to the preset evaluation value-warning signal level form, the warning signal level corresponding to the evaluation value of each sewage outlet in the target grid is found and a warning signal of the corresponding level is issued.
Citation Information
Patent Citations
Water environment pre-warning and comprehensive management platform
CN107609742A