Intelligent number type dynamic water conservancy management and control system and method

Abstract

The invention provides a smart number type dynamic water conservancy management and control system and method, and belongs to the field of flood monitoring and early warning, and the system comprises a digital twinborn module which carries out the construction of a digital ecological environment model in a region based on the obtained water conservancy information, and comprises a single digital water area unit and a digital ecological environment twinborn unit, each unit comprises a plurality of fluctuation points, the fluctuation points serve as input and are sent to the digital ecological environment model, the model outputs a single water area dynamic expectation graph, and the water area dynamic expectation graph comprises a water area change curve and an ecological simulation change graph; the early warning module is used for calculating the flood discharge buffer degree # imgabs0 # of the multiple ecological simulation monomers and the flood discharge kurtosis # imgabs1 # of the water area digital simulation body, flood discharge early warning response is carried out by combining the multiple water area dynamic expected maps, the flood discharge buffer degree is used for evaluating the influence of the environment on the water area, and the flood discharge kurtosis is used for evaluating the flood discharge trend.

Description

Technical Field

[0001] This specification relates to the field of water conservancy management, and particularly to an intelligent digital dynamic water conservancy control system and method. Background Art

[0002] The comprehensive management of water conservancy mainly includes flood control and prevention. When disasters such as floods, flash floods, etc. occur or water conservancy projects are in danger, efficient and rapid command and dispatch can minimize casualties and property losses to the greatest extent. According to the locations of local reservoirs, lakes and ponds, low-lying areas, and rainfall conditions, a perfect flash flood warning system is established.

[0003] In order to provide a more perfect digital flood control layout during the flood season, the existing technologies were understood. The existing digital water conservancy management systems, such as a flood control response release system named a digital management based on response rules in Chinese patents, with the publication number CN115994647A, manage the response level as the object, rather than just digitizing the specific response process. The response conditions, response actions, and content of the release procedures corresponding to the response level are classified and digitally managed, and the classification of response conditions is associated with the measuring stations in the basin, so as to realize the automatic extraction and collection of relevant content of response information, facilitate the efficient and semi-automatic initiation of flood control responses, and form response logs. The system includes: a response rule management module for maintaining response rule information corresponding to each response level; a response filling module for generating a response form according to the response information filled in by the user; a response process circulation module for releasing the response form according to the response information filled in by the user in the response filling module according to a preset process; a response form viewing module for displaying the current response and historical responses through a list and recording the response process.

[0004] The above response system can analyze and edit according to the acquired information, generate response information and release it. The above technology delves into information collection and release, formulates response modules and response strategies, but does not delve into information collection, especially the acquisition of water conservancy-related dynamics. And the key to flood control lies in the timely acquisition and processing of water conservancy information.

[0005] Therefore, there is a need to provide an intelligent digital dynamic water conservancy control system and method that can realize the digital management and response of water conservancy information. Summary of the Invention

[0006] One embodiment of this specification provides an intelligent digital dynamic water conservancy control system, which acquires the water area and the surrounding environment, constructs an overall digital virtual scene, and effectively improves the efficiency of flood control and flood fighting through digital water conservancy monitoring and flood discharge expectation simulation.

[0007] In some embodiments, an intelligent digital dynamic water conservancy control system includes The digital twin module constructs a digital ecological environment model within a region based on the obtained water conservancy information, including individual digital water units and digital ecological environment twin units. Each unit contains multiple fluctuation points, which are sent as inputs to the digital ecological environment model. The model outputs a single water area dynamic prediction map, which includes a water area change curve and an ecological simulation change map. The digital water unit is a single water area digital simulation body set within the region, and the digital ecological environment twin unit is an ecological simulation monomer set around the water area digital simulation body. The early warning module calculates the flood discharge buffer degree of multiple ecological simulation monomers and the flood discharge peak degree of the water area digital simulation body and combines multiple water area dynamic prediction maps to carry out flood discharge early warning response. Among them, the flood discharge buffer degree is used to evaluate the impact of the environment on the water area, and the flood discharge peak degree evaluates the flood discharge trend.

[0008] Through the above technical means, the water area and environment in reality can be simulated as an online digital scene. The water area and the environmental ecology are interrelated, realizing the overall linkage of the picture, being able to display the influence between flood discharge elements, improving the accuracy and efficiency of flood discharge prevention and providing convenience for later water conservancy maintenance.

[0009] Furthermore, the construction process of the digital ecological environment model includes S1: Perform parameter positioning extraction on the water conservancy information, first carry out digital simulation of the water area, and then carry out digital simulation of the ecology; S2: Set the flood discharge environment parameters as fluctuation points, obtain the historical flood discharge environment parameters and their flood discharge results, and train the digital ecological environment model; S3: Combine the digital pictures of the water area and the digital pictures of the ecology for the trained digital ecological environment model.

[0010] Through the above technical means, by analyzing and training historical ecological data and water area data, the types of fluctuation points are determined, providing convenience for later flood discharge strategies.

[0011] Furthermore, the water conservancy information includes the geographical information, ecological environment information, and artificial environment information of the water area. The flood discharge environment parameters include rainfall, wind speed, vegetation rate, runoff rate, soil moisture, air temperature, fire protection rate, water depth of the water area, and sediment volume at the bottom of the water.

[0012] Through the above technical means, the parameters related to the water area are obtained as multi-source heterogeneous data, which are used as both independent variables and dependent variables of the model, providing a new direction for digital flood discharge.

[0013] Furthermore, the calculation of the flood discharge buffer degree of the ecological simulation monomer is as follows , Peakness of flood discharge of the water area digital simulation body The calculation is as follows: , , , In the formula: is the vegetation rate of the environment; is the runoff rate of the water area; is the soil moisture of the environment; is the flood discharge velocity; is the cross-sectional area of flood discharge; is the water depth of the water area; is the water velocity of the water area; is the water cross-section at the flood discharge position; is the average value of flood discharge; is the fire protection rate.

[0014] Through the above technical means, through the calculation of a large amount of water conservancy data, it can be obtained that the two most important values affecting flood discharge, and through the association between the data, the flood discharge buffer degree and the peakness of flood discharge of the influencing factors of the function formula, to provide more accurate guidance for each step in flood discharge.

[0015] Furthermore, the runoff rate is the ratio of the water inflow at the beginning of the water area to the water outflow at the end of the water area, and the fire protection rate is the response efficiency of manual participation in flood discharge.

[0016] Through the above technical means, by obtaining the runoff rate calculate the flood discharge buffer degree .

[0017] Furthermore, the flood discharge early warning response includes multi-level responses in the corresponding area. When the responses triggered by the water areas adjacent to the area are different, digital simulation of the elevation difference between regions is carried out for multiple adjacent digital ecological environment models. Specifically, adjacent digital ecological environment units and digital ecological environment twin units in multiple adjacent digital ecological environment models are obtained respectively, a digital simulation unit of the environment after the levee breach is constructed, and the flood discharge environment parameters to be improved in the environment are calculated.

[0018] Through the above technical means, through the simulation between adjacent water areas, the changes between water areas before and after flood discharge are calculated, making the overall picture more coherent and vivid.

[0019] Furthermore, the water area is a single runoff under a specific length. The specific length is calculated according to the water conservancy information in the area. A runoff contains at least one water area, and an ecological simulation monomer contains a water area digital simulation body.

[0020] Through the above technical means, water conservancy is divided into multiple water areas, and digital ecological environment models for individual water areas are constructed and combined to identify the specific water area to be flood-discharged, and the environment of this water area is improved and maintained.

[0021] In some embodiments, a smart digital dynamic water conservancy control method further includes the following steps. ST1: Divide the water area and the surrounding environment, simulate the dynamic digital water area environment, and construct digital ecological environment models for multiple water areas within the region. ST2: Statistically analyze the flood-discharge environment parameters and calculate the flood-discharge buffer degree of the environment and the flood-discharge peak degree of the water area . When the flood-discharge peak degree is positive, execute step ST4. When the flood-discharge peak degree is negative, execute step ST3. ST3: Combine with the dynamic water area anticipation map. When the water area change curve decreases, initiate a secondary flood-discharge response. ST4: Combine with the dynamic water area anticipation map. When the water area change curve increases, initiate a primary flood-discharge response, increase the flood-discharge buffer degree , reduce the flood-discharge peak degree , until the flood-discharge peak degree is negative.

[0022] Through the above technical means, when the flood-discharge peak degree is positive, the water area plane increases, the environmental buffer degree is low, and the water area is in a high-risk state of flood-discharge. After calculating the flood-discharge peak degree in advance through the anticipation map, the environment is transformed to increase the environmental buffer degree and reduce the flood-discharge peak degree, stabilizing the water area state at low risk.

[0023] Further, in step ST1, the method for dividing the surrounding environment of the water area is to take the water area as the center, calculate the environmental boundary according to the volume of the water area, and obtain the spatio-temporal data, sensor data, and experimental observation data of the environmental ecology within the boundary.

[0024] Through the above technical means, water conservancy information is collected, obtained and saved in the above manner, improving the accuracy of subsequent digital simulation models.

[0025] The beneficial effects of the present invention are as follows: 1. Transforming the real water area ecology into a water area simulation with environmental display. Compared with traditional single runoff simulation, the present application can associate the environment affecting the runoff velocity with the simulation model, constructing a digital twin linkage between the environment and the water area. 2. Dividing the runoff into multiple water areas for management, separately analyzing the environmental impact of each water area, and then transforming the environment at specific locations to increase the flood-discharge buffer degree. BRIEF DESCRIPTION OF THE DRAWINGS

[0026] This specification will be further described by way of exemplary embodiments, which will be described in detail through the accompanying drawings. These embodiments are not restrictive. In these embodiments, the same numbers represent the same structures, where:

[0027] Figure 1 is a schematic diagram of the system principle shown in some embodiments of this specification; Figure 2 is the schematic diagram of the principle of optimizing the water area environment shown in some embodiments of this specification. DETAILED DESCRIPTION OF THE EMBODIMENTS

[0028] In order to more clearly illustrate the technical solutions of the embodiments of this specification, the accompanying drawings required for the description of the embodiments will be briefly introduced below. Obviously, the accompanying drawings in the following description are only some examples or embodiments of this specification. For those of ordinary skill in the art, without creative efforts, this specification can also be applied to other similar scenarios based on these drawings. Unless obvious from the language context or otherwise stated, the same reference numerals in the drawings represent the same structure or operation.

[0029] It should be understood that the "system", "device", "unit" and / or "module" used herein is a way to distinguish different components, elements, parts, portions or assemblies at different levels. However, if other words can achieve the same purpose, the said words can be replaced by other expressions.

[0030] As shown in this specification and the claims, unless the context clearly indicates an exceptional situation, words such as "a", "an", "one" and / or "the" are not specifically singular and may also include the plural. Generally speaking, the terms "comprising" and "including" only indicate the inclusion of the clearly identified steps and elements, and these steps and elements do not constitute an exclusive list. The method or device may also include other steps or elements.

[0031] Flowcharts are used in this specification to illustrate the operations performed by the system according to the embodiments of this specification. It should be understood that the operations before or after do not necessarily have to be executed precisely in sequence. On the contrary, the steps can be processed in reverse order or simultaneously. At the same time, other operations can also be added to these processes, or one or several steps can be removed from these processes.

[0032] Embodiment: Please refer to Figure 1 , this embodiment is based on a smart digital dynamic water control system, including, The digital twin module constructs a digital ecological environment model within a region based on the obtained water conservancy information, including individual digital water units and digital ecological environment twin units. Each unit contains multiple fluctuation points, which are sent as inputs to the digital ecological environment model. The model outputs a single water area dynamic prediction map, which includes a water area change curve and an ecological simulation change map. The digital water unit is a single water area digital simulation body set within the region, and the digital ecological environment twin unit is an ecological simulation monomer set around the water area digital simulation body. The early warning module calculates the flood discharge buffer degrees of multiple ecological simulation monomers and the flood discharge peak degrees of water area digital simulation bodies and conducts flood discharge early warning responses by combining multiple water area dynamic prediction maps. Among them, the flood discharge buffer degree is used to evaluate the impact of the environment on the water area, and the flood discharge peak degree evaluates the flood discharge trend.

[0033] It should be noted that digital twin means building a digital world parallel to the real physical world, mapping the virtual world and the real world to accurately reflect the changes in the real world. Landscape architecture uses digital twin technology to simulate and model the real world, integrating the knowledge and technologies of multiple disciplines. Based on the Internet of Things technology, it utilizes the functions of computer graphics technology and multi-sensor technology. Based on the big data collected from the landscape architecture in the physical world, it simulates and maps the operating state of the landscape architecture. The collection and transmission of data are the basis for constructing the twin space. The data in the twin space is truly multi-source heterogeneous data. In addition to the position and attribute data of the observed objects obtained from various platforms or sensors in the natural entity space, it also includes social media and web page data in the virtual space. Natural entity space data: 1. Spatiotemporal data (remote sensing data, UAV data, GPS trajectories, mobile phone data, etc.); 2. Sensor data (vehicle-mounted sensors, Internet of Things, pipeline sensors, etc.); 3. Experimental observation data (experimental observation data of surface system elements and processes, such as runoff, air temperature, and soil moisture).

[0034] Virtual space data: 1. Social media data (such as web searches), and then quickly determine the types of vegetation in the environment, the water content of the roots of the vegetation, the types of soil in the environment, the water storage capacity of the soil, the distance between the water surface and the soil plane, etc.

[0035] The construction process of the digital ecological environment model includes S1: Perform parameter positioning extraction on the water conservancy information, first conduct water area digital simulation, and then conduct ecological digital simulation; S2: Set the flood discharge environment parameters as fluctuation points, obtain the historical flood discharge environment parameters and their flood discharge results, and train the digital ecological environment model; S3: Combine the water area digital and ecological digital images of the trained digital ecological environment model.

[0036] The above training method is adopted.

[0037] It should be noted that by using the method of oblique photography, multi-angle aerial photography is carried out on the geographical environment and artificial environment of the water area. ContextCapture (Smart 3D) is used to conduct real-scene modeling on the photos obtained by oblique photography. The spatial model file in the.stl or.3ds three-dimensional format is imported into PHEONICS to determine the areas of the natural environment, artificial environment, and water area. The flood discharge environment parameters collected by the above sensors are input into the software parameters according to the data measured in time periods. The shapes and quantities of the digital simulation bodies of the water area and the ecological simulation monomers in the model are set. Usually, the number of digital simulation bodies of the water area is 1, and the ecological simulation monomers are multiple units with different types and various shapes. According to the type, the monomers can be vegetation - three-dimensional, soil - planar, cement body - planar, grass - planar, etc.

[0038] It should be noted that through cleaning the historical flood discharge environment parameters and their flood discharge results, multi-dimensional variables of spatial positions can be obtained. For example, at a certain time on a certain day, when the rainfall is XX ml, the runoff at xx section receives debris flows converging from both sides, resulting in the turbidity of the water surface color and an instantaneous rise of xx cm in the water surface. The flow velocity and the opening duration at the flood discharge outlet of the runoff are obtained. Through training with multiple groups of the above data, a digital dynamic twin model of the association between the water area and the surrounding environment is obtained.

[0039] It should be noted that the specific combination of the pictures of the above monomers is as follows. According to the position arrangement in the data, various combinations of three-dimensional and planar are obtained, making the pictures more vivid and appropriate. In the middle of the three-dimensional digital simulation body of the water area, planar, three-dimensional, and planar - three-dimensional combined simulation vegetation and soil are surrounded on both sides, and the tortuous three-dimensional water flow simulation panorama is coordinated with the uneven environmental monomers.

[0040] It should be noted that the water conservancy information includes the geographical information, ecological environment information, and artificial environment information of the water area. The flood discharge environment parameters include rainfall, wind speed, vegetation rate, runoff rate, soil humidity, air temperature, fire protection rate, water depth of the water area, and sediment volume at the bottom of the water.

[0041] It should be noted that the flood discharge buffer degree of the ecological simulation monomer is calculated as follows, , The flood discharge peak degree of the digital simulation body of the water area is calculated as follows, , , , In the formula, is the vegetation rate of the environment, is the runoff rate of the water area, is the soil humidity of the environment, is the flood discharge velocity, is the cross-sectional area of flood discharge, is the water depth of the water area, is the water velocity of the water area, is the water area cross-section at the flood discharge position, is the average value of flood discharge volume, is the fire protection rate.

[0042] It should be noted that the runoff rate is the ratio of the water inflow at the start of the water area to the water outflow at the end of the water area. The fire protection rate is the response efficiency of manual participation in flood discharge, specifically the reciprocal of the time difference from when the environmental parameters change to when the manual flood discharge feedback is made. The average value of flood discharge volume is the average value of the water surface height during all flood discharges within a year.

[0043] It should be noted that the flood discharge early warning response includes multi-level responses in the corresponding area. When the responses triggered by adjacent water areas are different, digital simulation of the elevation difference between regions is carried out for multiple adjacent digital ecological environment models. Specifically, adjacent digital ecological environment units and digital ecological environment twin units in multiple adjacent digital ecological environment models are respectively obtained, an environmental digital simulation unit after embankment breach is constructed, and the flood discharge environmental parameters to be improved in the environment are calculated.

[0044] Since this application conducts simulation for the water area under a unit length, in order to avoid simulation faults between adjacent digital water areas and affect the overall effect of the picture, especially the incoherence at the adjacent models after flood discharge, the environmental digital simulation unit after embankment breach is superimposed, the data of the elevation difference is automatically interpolated, and the average value of the maximum value and the minimum value is taken as the new data, which is substituted into the model to construct a new environmental monomer. When the result output by the model is flood discharge, the picture scene is defined as the flood discharge scene and associated with this new data. That is, through the above multiple operations, the accuracy of the water area model at the adjacent part is improved, and when the environmental input value of high-risk flood discharge is obtained, the adjacent part can quickly output and display the simulation scene after flood discharge.

[0045] The water area is a single runoff under a specific length, and the specific length is calculated according to the water conservancy information in the region. One runoff contains at least one water area, and the ecological simulation monomer contains a water area digital simulation body; Please refer to Figure 2 , and the embodiment further includes the following steps, ST1: Divide the water area and the surrounding environment of the water area, simulate the dynamic digital water area environment, and construct digital ecological environment models of multiple water areas within the region; ST2: Statistically analyze the flood discharge environmental parameters and calculate the flood discharge buffer degree of the environment and the flood discharge kurtosis of the water area . When the flood discharge kurtosis is positive, execute step ST4. When the flood discharge kurtosis is negative, execute step ST3; ST3: Combine with the dynamic expectation map of the water area. When the water area change curve decreases, initiate a secondary flood discharge response; ST4: Combine with the dynamic expectation map of the water area. When the water area change curve increases, initiate a primary flood discharge response, increase the flood discharge buffer degree , reduce the flood discharge kurtosis , until the flood discharge kurtosis is negative.

[0046] It should be noted that the secondary flood discharge response includes raising the dam size, increasing the protection length on both sides of the water area, modifying the vegetation type on both sides of the water area, modifying the water area width, modifying the sediment height in the water area. The primary flood discharge response includes evacuating the crowd, sending flood discharge warning text messages, maintaining a first-level alert for the flood discharge channels, and sending warning signals to the upstream and downstream flood discharge channels.

[0047] In summary, the water inflow and outflow of the water area are interrelated with the environment. When environmental factors such as increased rainfall, barren vegetation, and soil erosion cause the water level of the water area to rise, it is urgent to open the floodgates for flood discharge. It will also reduce the later water level rising speed and improve the flood discharge efficiency due to dam reinforcement, sediment removal from the river bottom, and soil reinforcement on both sides of the water area, etc. The environmental flood discharge buffer degree and the flood discharge kurtosis of the water area are twin-related and digitally presented panoramically, providing a reference for subsequent flood discharge drills, and also being able to calculate and simulate in advance the state of the water area and the surrounding environment during flood discharge. This application is particularly applicable to the monitoring of natural runoff and lakes.

[0048] Similarly, it should be noted that, in order to simplify the presentation disclosed in this specification and thus assist in the understanding of one or more embodiments of the invention, in the foregoing description of the embodiments of this specification, sometimes multiple features are combined into one embodiment, drawing, or description thereof. However, this disclosure method does not mean that the features required by the subject matter of this specification are more than those mentioned in the claims. In fact, the features of the embodiments are fewer than all the features of the individual embodiments disclosed above.

[0049] Finally, it should be understood that the embodiments described in this specification are only used to illustrate the principles of the embodiments of this specification. Other variations may also fall within the scope of this specification. Therefore, by way of example and not limitation, alternative configurations of the embodiments of this specification can be considered to be in accordance with the teachings of this specification. Accordingly, the embodiments of this specification are not limited to the embodiments explicitly introduced and described in this specification.

Claims

1. A smart digital dynamic water conservancy management and control system, characterized in that: include, The digital twin module constructs a digital ecological environment model in the region based on the acquired water conservancy information, including a single digital water area unit and a digital ecological environment twin unit. Each unit contains multiple fluctuation points, which are sent as input to the digital ecological environment model. The model outputs a single water area dynamic expectation map, which includes a water area change curve and an ecological simulation change map. The digital water area unit is a single water area digital simulation body set in the region, and the digital ecological environment twin unit is an ecological simulation monomer set around the water area digital simulation body. Early warning module, calculates the flood discharge buffer of multiple ecological simulation units and flood discharge peak of water area digital simulation body , combined with multiple water area dynamic expectation maps, flood discharge warning response is carried out, among which the flood discharge buffer degree is used to evaluate the impact of the environment on the water area, and the flood discharge peak degree is used to evaluate the flood discharge trend.

2. The intelligent digital dynamic water conservancy management and control system as claimed in claim 1, characterized in that: The construction process of the digital ecological environment model includes: S1: Parameter location extraction of water conservancy information, first digital simulation of water area, then digital simulation of ecology; S2: Set flood discharge environmental parameters as fluctuation points, obtain historical flood discharge environmental parameters and flood discharge results, and train the digital ecological environment model; S3: The trained digital ecological environment model is used to combine the water area digital and ecological digital images.

3. A smart digital dynamic water conservancy management and control system as claimed in claim 2, characterized in that: Water conservancy information includes the geographical information, ecological environment information, and artificial environment information of the water area. The flood discharge environmental parameters include rainfall, wind speed, vegetation rate, runoff rate, soil moisture, temperature, fire fighting rate, water area depth, and bottom sediment amount.

4. A smart digital dynamic water conservancy management and control system as claimed in claim 3, characterized in that: Flood discharge buffer degree of ecological simulation unit The calculation of is as follows, ， Flood discharge peak of digital simulation body of water area The calculation of is as follows, ， , ， In the formula, is the vegetation rate of the environment, is the runoff rate of the water area, is the ambient soil moisture, is the flood discharge velocity, is the flood discharge cross-sectional area, is the water depth, is the water flow velocity, is the cross section of the water area at the flood discharge location, is the mean flood discharge volume, The fire rate.

5. The intelligent digital dynamic water conservancy management and control system as claimed in claim 4, characterized in that: Runoff rate The ratio of water inflow at the beginning of the water area to water outflow at the end of the water area, firefighting rate The response efficiency of artificial flood discharge.

6. A smart digital dynamic water conservancy management and control system as claimed in claim 5, characterized in that: The flood discharge warning response includes a multi-level response for the corresponding area. When the responses triggered by adjacent waters in the area are different, a digital simulation of the inter-regional drop is performed for multiple adjacent digital ecological environment models. Specifically, adjacent digital ecological environment units and digital ecological environment twin units in multiple adjacent digital ecological environment models are obtained respectively, a digital simulation unit of the post-breach environment is constructed, and the flood discharge environment parameters to be improved in the calculation environment are calculated.

7. A smart digital dynamic water conservancy management and control system as claimed in claim 6, characterized in that: The water area is a single runoff of a specific length. The specific length is calculated based on the water conservancy information in the area. A runoff contains at least one water area, and the ecological simulation unit contains a water area digital simulation body.

8. A smart digital dynamic water conservancy control method, based on the smart digital dynamic water conservancy control system of claim 7, characterized in that: The following steps are also included, ST1: Divide the water area and its surrounding environment, simulate the dynamic digital water environment, and build digital ecological environment models for multiple water areas in the region; ST2: Count flood discharge environmental parameters and calculate the flood discharge buffer of the environment and flood discharge peaks in water areas , when the flood peak When the flood discharge peak is positive, step ST4 is executed. When it is negative, execute step ST3; ST3: Combined with the water area dynamic forecast map, when the water area change curve decreases, the secondary flood discharge response is initiated; ST4: Combined with the water area dynamic forecast map, when the water area change curve rises, the first-level flood discharge response is initiated to increase the flood discharge buffer , reducing flood discharge peak , until the peak flood discharge Is negative.

9. A smart digital dynamic water conservancy control method as claimed in claim 8, characterized in that: In step ST1, the method for dividing the environment around the water area is to take the water area as the center, calculate the environmental boundary according to the volume of the water area, and obtain the spatiotemporal data, sensor data, and experimental observation data of the environmental ecology within the boundary.

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