A vegetation ecological maintenance method and system for degraded slope grassland restoration
Patent Information
- Application Number
- CN202611233472.0
- Authority / Receiving Office
- CN · China
- Patent Type
- Applications(China)
- Current Assignee / Owner
- Filing Date
- 2026-08-14
- Publication Date
- 2026-10-23
AI Technical Summary
[0003]相关技术通常通过使用草种并添加化肥的方式,但是对于草地的监控和维护不足,则不能捕捉到细微的植被和土壤特征(如植被、土壤、水文等多个关键参数),从而不能提供全面的评估、获得更准确的数据,从而可能导致退化坡草地上修复的植被再次退化
[0016]本申请提供的一种退化坡草地修复的植被生态维护方法及系统,获取目标退化坡草地的生态状态指标;其中,生态状态指标包括:植被指标、土壤指标和环境指标,植被指标表征目标退化坡草地上种植的植被的生长状态,土壤指标表征目标退化坡草地的土壤状态,环境指标表征目标退化坡草地所在区域的环境状态;基于生态状态指标,确定目标退化坡草地的生态状态趋势;其中,生态状态趋势表征目标退化坡草地的生态状态在未来时间段的预测结果;基于生态状态趋势和适合植被生长的舒适指标范围,确定目标退化坡草地的维护策略;基于维护策略,对目标退化坡草地进行生态维护;获取目标退化坡草地在维护后的修复状态指标;若修复状态指标满足预设条件,则停止维护策略;通过监测目标退化坡草地的生态状态指标,基于此预测目标退化坡草地的生态状态趋势,根据生态状态趋势确定维护策略,以提前响应目标退化坡草地的维护操作,从而可以保证目标退化坡草地的植被生存环境,提高目标退化坡草地的植被存活率,继而提高退化坡草地的修复效果。
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Figure CN122953884A_ABST
Abstract
Description
Technical Field
[0001] This application relates to the field of ecological restoration, specifically to a method and system for vegetation ecological maintenance in the restoration of degraded slope grasslands. Background Technology
[0002] As grasslands degrade to varying degrees, soil nutrients decrease, biodiversity becomes increasingly homogenized, and the environment deteriorates. Therefore, the restoration of degraded grasslands has become one of the major challenges in the field of ecology.
[0003] Related technologies typically involve using grass seeds and adding fertilizers, but insufficient monitoring and maintenance of grasslands prevent the capture of subtle vegetation and soil characteristics (such as multiple key parameters like vegetation, soil, and hydrology), thus failing to provide comprehensive assessments and obtain more accurate data. This could lead to the re-degradation of vegetation restored on degraded slopes.
[0004] Therefore, there is an urgent need for a method to maintain the vegetation restored on degraded slope grasslands. Summary of the Invention
[0005] To address the aforementioned technical problems, this application is proposed. Embodiments of this application provide a method and system for vegetation ecological maintenance in the restoration of grassland on degraded slopes.
[0006] According to one aspect of this application, a method for vegetation ecological maintenance in the restoration of degraded slope grassland is provided, comprising: obtaining ecological state indicators of a target degraded slope grassland; wherein the ecological state indicators include: vegetation indicators, soil indicators, and environmental indicators, wherein the vegetation indicators characterize the growth status of vegetation planted on the target degraded slope grassland, the soil indicators characterize the soil status of the target degraded slope grassland, and the environmental indicators characterize the environmental status of the area where the target degraded slope grassland is located; determining the ecological state trend of the target degraded slope grassland based on the ecological state indicators; wherein the ecological state trend characterizes the prediction result of the ecological state of the target degraded slope grassland in a future time period; determining a maintenance strategy for the target degraded slope grassland based on the ecological state trend and a comfortable index range suitable for vegetation growth; performing ecological maintenance on the target degraded slope grassland based on the maintenance strategy; obtaining restoration state indicators of the target degraded slope grassland after maintenance; and stopping the maintenance strategy if the restoration state indicators meet preset conditions.
[0007] In one embodiment, obtaining the ecological status indicators of the target degraded slope grassland includes: acquiring a three-dimensional geomorphic image of the target degraded slope grassland; identifying the three-dimensional geomorphic image to obtain a vegetation image on the target degraded slope grassland; and determining the vegetation indicators of the target degraded slope grassland based on the three-dimensional geomorphic image and the vegetation image.
[0008] In one embodiment, identifying the three-dimensional terrain image to obtain the vegetation image on the target degraded slope grassland includes: binarizing the three-dimensional terrain image to obtain a binarized image; and performing boundary diffusion on the center pixels of the binarized image to divide it into multiple vegetation images.
[0009] In one embodiment, determining the vegetation index of the target degraded slope grassland based on the three-dimensional landform image and the vegetation image includes: converting the three-dimensional landform image and the vegetation image into two-dimensional planar maps to obtain two-dimensional landform maps and two-dimensional vegetation maps respectively; and calculating the vegetation coverage of the target degraded slope grassland based on the two-dimensional landform maps and the two-dimensional vegetation maps.
[0010] In one embodiment, determining the vegetation index of the target degraded slope grassland based on the three-dimensional terrain image and the vegetation image includes: determining the vegetation height of each plant in the target degraded slope grassland based on the vegetation image; dividing the target degraded slope grassland into at least one vegetation zone based on the vegetation height of all plants and their corresponding locations; and determining the vegetation height of each vegetation zone based on the vegetation height of the plants in each vegetation zone.
[0011] In one embodiment, determining the ecological state trend of the target degraded slope grassland based on the ecological state indicators includes: predicting the ecological state trend of the target degraded slope grassland based on the vegetation indicators, the soil indicators, the environmental indicators, and the comfort index range.
[0012] In one embodiment, predicting the ecological state trend of the target degraded slope grassland based on the vegetation index, the soil index, and the environmental index includes: predicting the ecological state trend of the target degraded slope grassland based on the change curves of the vegetation index, the soil index, and the environmental index of the target degraded slope grassland.
[0013] In one embodiment, determining the maintenance strategy for the target degraded slope grassland based on the ecological state trend and the range of comfort indicators suitable for vegetation growth includes: if there is an indicator in the ecological state trend that is outside the range of comfort indicators, then determining the maintenance strategy for the target degraded slope grassland based on that indicator, so as to control the indicator within the corresponding range of comfort indicators.
[0014] In one embodiment, stopping the maintenance strategy if the repair status indicator meets a preset condition includes: stopping the maintenance strategy if the repair status indicator is within the range of the comfort index and the difference between the repair status indicator and the upper and lower limits of the comfort index range is greater than a preset difference threshold.
[0015] According to another aspect of this application, a vegetation ecological maintenance system for the restoration of degraded slope grassland is provided, comprising: an ecological index acquisition module for acquiring ecological state indicators of a target degraded slope grassland; wherein the ecological state indicators include: vegetation indicators, soil indicators, and environmental indicators, wherein the vegetation indicators characterize the growth status of vegetation planted on the target degraded slope grassland, the soil indicators characterize the soil status of the target degraded slope grassland, and the environmental indicators characterize the environmental status of the area where the target degraded slope grassland is located; an ecological trend determination module for determining the ecological state trend of the target degraded slope grassland based on the ecological state indicators; wherein the ecological state trend characterizes the predicted result of the ecological state of the target degraded slope grassland in a future time period; a maintenance strategy determination module for determining a maintenance strategy for the target degraded slope grassland based on the ecological state trend and a comfortable index range suitable for vegetation growth; an ecological maintenance execution module for performing ecological maintenance on the target degraded slope grassland based on the maintenance strategy; a restoration status acquisition module for acquiring restoration status indicators of the target degraded slope grassland after maintenance; and a maintenance strategy stop module for stopping the maintenance strategy if the restoration status indicators meet preset conditions.
[0016] This application provides a method and system for vegetation ecological maintenance in the restoration of degraded slope grasslands, which obtains ecological status indicators of the target degraded slope grassland. These ecological status indicators include vegetation indicators, soil indicators, and environmental indicators. Vegetation indicators characterize the growth status of vegetation planted on the target degraded slope grassland, soil indicators characterize the soil condition of the target degraded slope grassland, and environmental indicators characterize the environmental condition of the area where the target degraded slope grassland is located. Based on these ecological status indicators, the ecological status trend of the target degraded slope grassland is determined. This ecological status trend represents a prediction of the ecological status of the target degraded slope grassland over a future time period. Based on the ecological status trend and suitable vegetation... The system determines the maintenance strategy for the target degraded slope grassland by considering the range of comfortable growth indicators. Based on the maintenance strategy, ecological maintenance is carried out on the target degraded slope grassland. The restoration status indicators of the target degraded slope grassland after maintenance are obtained. If the restoration status indicators meet the preset conditions, the maintenance strategy is stopped. By monitoring the ecological status indicators of the target degraded slope grassland, the ecological status trend of the target degraded slope grassland is predicted. Based on the ecological status trend, the maintenance strategy is determined to respond to the maintenance operations of the target degraded slope grassland in advance, thereby ensuring the vegetation survival environment of the target degraded slope grassland, improving the vegetation survival rate of the target degraded slope grassland, and thus improving the restoration effect of the degraded slope grassland. Attached Figure Description
[0017] The above and other objects, features, and advantages of this application will become more apparent from the more detailed description of the embodiments of this application in conjunction with the accompanying drawings. The drawings are provided to further illustrate the embodiments of this application and form part of the specification. They are used together with the embodiments of this application to explain this application and do not constitute a limitation thereof. In the drawings, the same reference numerals generally represent the same components or steps.
[0018] Figure 1 This is a schematic flowchart of a vegetation ecological maintenance method for grassland restoration on degraded slopes provided in an exemplary embodiment of this application.
[0019] Figure 2 This is a schematic diagram of the vegetation ecological maintenance system for grassland restoration on degraded slopes provided in an exemplary embodiment of this application.
[0020] Figure 3 This is a structural diagram of an electronic device provided in an exemplary embodiment of this application. Detailed Implementation
[0021] Hereinafter, exemplary embodiments according to this application will be described in detail with reference to the accompanying drawings. Obviously, the described embodiments are merely some embodiments of this application, and not all embodiments of this application. It should be understood that this application is not limited to the exemplary embodiments described herein.
[0022] Figure 1 This is a schematic flowchart of a vegetation ecological maintenance method for grassland restoration on degraded slopes provided in an exemplary embodiment of this application. Figure 1 As shown, the vegetation ecological maintenance method for grassland restoration on this degraded slope includes the following steps: Step 110: Obtain ecological status indicators of the target degraded slope grassland.
[0023] The ecological status indicators include vegetation indicators, soil indicators, and environmental indicators. Vegetation indicators characterize the growth status of vegetation planted on the target degraded slope grassland, soil indicators characterize the soil condition of the target degraded slope grassland, and environmental indicators characterize the environmental condition of the area where the target degraded slope grassland is located. Specifically, this application uses multiple sensors to collect ecological status indicators of the target degraded slope grassland in real time. For example, soil moisture sensors collect soil moisture content in real time, meteorological sensors monitor rainfall, temperature, and humidity in real time, and soil erosion monitoring pins monitor soil erosion in real time.
[0024] Step 120: Determine the ecological status trend of the target degraded slope grassland based on ecological status indicators.
[0025] Among them, the ecological state trend represents the predicted ecological state of the target degraded slope grassland in the future time period. This application predicts the ecological state of the target degraded slope grassland in the future time period based on the ecological state indicators to obtain the ecological state trend, thereby predicting the ecological state of the target degraded slope grassland in advance, so as to realize early intervention and protect its ecological environment.
[0026] Step 130: Based on ecological status trends and the range of comfort indicators suitable for vegetation growth, determine the maintenance strategy for the target degraded slope grassland.
[0027] Based on ecological state trends and the range of comfort indicators suitable for vegetation growth, this application formulates a maintenance strategy for target degraded slope grasslands to ensure that vegetation on the target degraded slope grasslands grows within the range of these comfort indicators.
[0028] Step 140: Based on the maintenance strategy, carry out ecological maintenance on the target degraded slope grassland.
[0029] This application describes the ecological maintenance of target degraded slope grasslands based on a developed maintenance strategy, in order to improve their ecological condition.
[0030] Step 150: Obtain the restoration status indicators of the target degraded slope grassland after maintenance.
[0031] This application obtains ecological status indicators (restoration status indicators) of the target degraded slope grassland again after ecological maintenance to determine the effectiveness of the maintenance strategy.
[0032] Step 160: If the repair status indicators meet the preset conditions, then stop the maintenance strategy.
[0033] If the obtained restoration status indicators meet the preset conditions (i.e., the maintenance strategy achieves the expected purpose), the maintenance strategy is stopped; if the obtained restoration status indicators do not meet the preset conditions, it means that the maintenance strategy has not achieved the expected purpose. At this time, it is necessary to determine a new maintenance strategy based on the restoration status indicators in order to maintain the target degraded slope grassland again until the ecological status indicators of the target degraded slope grassland meet the preset conditions.
[0034] This application provides a vegetation ecological maintenance method for the restoration of degraded slope grasslands, which obtains ecological status indicators of the target degraded slope grassland. These ecological status indicators include vegetation indicators, soil indicators, and environmental indicators. Vegetation indicators characterize the growth status of vegetation planted on the target degraded slope grassland, soil indicators characterize the soil condition of the target degraded slope grassland, and environmental indicators characterize the environmental condition of the area where the target degraded slope grassland is located. Based on these ecological status indicators, the ecological status trend of the target degraded slope grassland is determined. This ecological status trend represents a prediction of the ecological status of the target degraded slope grassland over a future time period. Based on the ecological status trend and suitable conditions for vegetation growth... The system determines the maintenance strategy for the target degraded slope grassland by defining the comfort index range; based on the maintenance strategy, ecological maintenance is carried out on the target degraded slope grassland; the restoration status index of the target degraded slope grassland after maintenance is obtained; if the restoration status index meets the preset conditions, the maintenance strategy is stopped; by monitoring the ecological status index of the target degraded slope grassland, the ecological status trend of the target degraded slope grassland is predicted based on this, and the maintenance strategy is determined according to the ecological status trend to respond to the maintenance operation of the target degraded slope grassland in advance, thereby ensuring the vegetation survival environment of the target degraded slope grassland, improving the vegetation survival rate of the target degraded slope grassland, and thus improving the restoration effect of the degraded slope grassland.
[0035] In one embodiment, step 110 can be implemented as follows: acquiring a three-dimensional geomorphic image of the target degraded slope grassland; identifying the three-dimensional geomorphic image to obtain a vegetation image on the target degraded slope grassland; and determining vegetation indicators of the target degraded slope grassland based on the three-dimensional geomorphic image and the vegetation image.
[0036] This application can use equipment such as drones to periodically capture three-dimensional geomorphological images of the target degraded slope grassland, and by identifying the three-dimensional geomorphological images, obtain the vegetation images on the target degraded slope grassland, thereby determining the vegetation indicators of the target degraded slope grassland and obtaining the growth status of the vegetation on the target degraded slope grassland.
[0037] In one embodiment, step 110 can be implemented as follows: binarize the three-dimensional terrain image to obtain a binarized image; perform boundary diffusion on the center pixel of the binarized image to divide it into multiple vegetation images.
[0038] To improve the accuracy of image recognition, this application first binarizes the 3D terrain image based on the pixel values of vegetation to obtain a binarized image. Then, it performs boundary diffusion on the binarized image to divide it into multiple vegetation images. Specifically, this application can select any vegetation pixel in the binarized image as the starting pixel and perform boundary diffusion with the starting pixel as the center pixel. When the pixel values of its surrounding pixels are the same as its starting pixel (there are only two types of pixel values in the binarized image), the surrounding pixels are merged into its neighborhood and diffusion continues until pixels with different pixel values appear. Then, the expansion stops to determine the vegetation image corresponding to the vegetation pixel. Then, the above operation is repeated by selecting undetermined vegetation pixels as new starting pixels until all vegetation pixels are divided into the corresponding vegetation images, and then the division of vegetation images ends.
[0039] In one embodiment, step 110 can be implemented by converting the three-dimensional landform image and vegetation image into two-dimensional planar maps to obtain two-dimensional landform maps and two-dimensional vegetation maps respectively; and calculating the vegetation coverage of the target degraded slope grassland based on the two-dimensional landform maps and two-dimensional vegetation maps.
[0040] To simplify the calculation, this application converts the three-dimensional landform image and vegetation image into a two-dimensional planar map, thereby obtaining a two-dimensional landform map and a two-dimensional vegetation map, and calculates the proportion of the two-dimensional vegetation map in the two-dimensional landform map to obtain the vegetation coverage of the target degraded slope grassland.
[0041] In one embodiment, step 110 can be implemented as follows: based on the vegetation image, determine the vegetation height of each plant in the target degraded slope grassland; based on the vegetation height of all plants and their corresponding locations, divide the target degraded slope grassland into at least one vegetation zone; and based on the vegetation height of the plants in each vegetation zone, determine the vegetation height of the vegetation zone.
[0042] This application identifies the vegetation height of each plant in the target degraded slope grassland by recognizing vegetation images. Based on the vegetation height and corresponding location of all vegetation, the target degraded slope grassland is divided into at least one vegetation zone, where the vegetation height in each vegetation zone is relatively uniform, reflecting the growth status of the vegetation in that zone. Furthermore, for each vegetation zone, the average height of all vegetation heights is calculated as the vegetation height of that zone, thereby determining the vegetation height of each vegetation zone and enabling the adoption of corresponding maintenance strategies for different vegetation zones.
[0043] In one embodiment, step 120 can be implemented by predicting the ecological state trend of the target degraded slope grassland based on vegetation indicators, soil indicators, environmental indicators and comfort indicator ranges.
[0044] This application predicts the ecological status trend of target degraded slope grassland based on vegetation indicators, soil indicators, environmental indicators, and comfort index ranges. Among them, the comfort index range for soil organic matter content is [30, ∞), the comfort index range for soil moisture content is [15%, ∞), the comfort index range for soil erosion modulus is (-∞, 500], the comfort index range for soil pH is 6.5-8.5, the comfort index range for soil erosion reduction rate is [70%, ∞), and the comfort index range for surface runoff coefficient is (-∞, 0.3).
[0045] In one embodiment, step 120 can be implemented by predicting the ecological state trend of the target degraded slope grassland based on the change curves of vegetation indicators, soil indicators, and environmental indicators of the target degraded slope grassland.
[0046] This application periodically collects vegetation, soil, and environmental indicators of target degraded grassland slopes. Based on the collected values, it performs interpolation and fitting to obtain change curves for these indicators. According to the correspondence between these curves, the ecological state trend of the target degraded grassland slopes is predicted. Optionally, this application can input the change curves of vegetation, soil, and environmental indicators into a neural network model to obtain a relationship model between these curves. Furthermore, it combines this relationship model with soil and environmental indicators for future time periods to predict corresponding vegetation indicators. This application can also use this relationship model to adjust soil or environmental indicators to generate corresponding vegetation indicators, and use the optimal soil and environmental indicators corresponding to the vegetation indicators as key parameters to guide subsequent maintenance strategies.
[0047] In one embodiment, step 130 can be implemented as follows: if there is an indicator in the ecological state trend that is outside the comfort index range, then a maintenance strategy for the target degraded slope grassland is determined based on the indicator so as to control the indicator within the corresponding comfort index range.
[0048] If the predicted ecological state trend contains an indicator that is outside the comfort index range, it indicates that the vegetation growth status on the target degraded slope grassland is not good according to the current growth environment. At this time, the maintenance strategy for the target degraded slope grassland should be determined based on the indicator to control the indicator within the corresponding comfort index range, thereby achieving early intervention to improve the vegetation growth environment and growth status.
[0049] In one embodiment, step 160 can be implemented as follows: if the repair status index is within the comfort index range and the difference between the repair status index and the upper and lower limits of the comfort index range is greater than a preset difference threshold, then the maintenance strategy is stopped.
[0050] This application stipulates that after maintaining the target degraded slope grassland using a maintenance strategy, if the restored state index returns to the comfort index range, and the difference between the upper and lower limits of the restored state index and the comfort index range is greater than a preset difference threshold, it indicates that the restored state index is some distance from the upper and lower limits. At this point, the maintenance strategy can be stopped, and the target degraded slope grassland can be continuously monitored. Specifically, irrigation is initiated when soil moisture is less than 15% and weather forecast data indicates no rainfall in the near future. The irrigation area, irrigation volume, and irrigation method (drip irrigation or spraying) are determined based on the vegetation water requirement model (vegetation water requirement determined based on vegetation and soil indicators). When the vegetation height (after a period of planting) is less than 15cm, the amount of organic fertilizer applied is determined based on soil nutrient monitoring data and the vegetation growth model (soil nutrient requirement determined based on the correspondence between soil nutrients and vegetation height). Reseeding is initiated when vegetation coverage is less than 60%.
[0051] Figure 2 This is a schematic diagram of the vegetation ecological maintenance system for grassland restoration on degraded slopes provided in an exemplary embodiment of this application. (See diagram below.) Figure 2 As shown, the vegetation ecological maintenance system 20 for degraded slope grassland restoration includes: an ecological index acquisition module 21, used to acquire ecological status indicators of the target degraded slope grassland; wherein, the ecological status indicators include: vegetation indicators, soil indicators, and environmental indicators, whereby vegetation indicators characterize the growth status of vegetation planted on the target degraded slope grassland, soil indicators characterize the soil status of the target degraded slope grassland, and environmental indicators characterize the environmental status of the area where the target degraded slope grassland is located; an ecological trend determination module 22, used to determine the ecological status trend of the target degraded slope grassland based on the ecological status indicators; wherein, the ecological status trend characterizes the predicted result of the ecological status of the target degraded slope grassland in the future time period; a maintenance strategy determination module 23, used to determine the maintenance strategy of the target degraded slope grassland based on the ecological status trend and the range of comfortable indicators suitable for vegetation growth; an ecological maintenance execution module 24, used to perform ecological maintenance on the target degraded slope grassland based on the maintenance strategy; a restoration status acquisition module 25, used to acquire the restoration status indicators of the target degraded slope grassland after maintenance; and a maintenance strategy stop module 26, used to stop the maintenance strategy if the restoration status indicators meet preset conditions.
[0052] This application provides a vegetation ecological maintenance system for the restoration of degraded slope grasslands. An ecological indicator acquisition module 21 acquires ecological state indicators of the target degraded slope grassland. These ecological state indicators include vegetation indicators, soil indicators, and environmental indicators. Vegetation indicators characterize the growth status of vegetation planted on the target degraded slope grassland, soil indicators characterize the soil condition of the target degraded slope grassland, and environmental indicators characterize the environmental condition of the area where the target degraded slope grassland is located. An ecological trend determination module 22 determines the ecological state trend of the target degraded slope grassland based on the ecological state indicators. The ecological state trend represents a prediction of the ecological state of the target degraded slope grassland over a future time period. A maintenance strategy determination module 23 determines the ecological state trend and suitable vegetation growth conditions based on the ecological state trend. The system determines the maintenance strategy for the target degraded slope grassland based on the comfort index range; the ecological maintenance execution module 24 performs ecological maintenance on the target degraded slope grassland based on the maintenance strategy; the restoration status acquisition module 25 acquires the restoration status index of the target degraded slope grassland after maintenance; if the restoration status index meets the preset conditions, the maintenance strategy stop module 26 stops the maintenance strategy; by monitoring the ecological status index of the target degraded slope grassland, the system predicts the ecological status trend of the target degraded slope grassland based on this, and determines the maintenance strategy according to the ecological status trend, so as to respond to the maintenance operation of the target degraded slope grassland in advance, thereby ensuring the vegetation survival environment of the target degraded slope grassland, improving the vegetation survival rate of the target degraded slope grassland, and thus improving the restoration effect of the degraded slope grassland.
[0053] In one embodiment, the ecological index acquisition module 21 can be further configured to: acquire a three-dimensional geomorphic image of the target degraded slope grassland; identify the three-dimensional geomorphic image to obtain a vegetation image on the target degraded slope grassland; and determine the vegetation index of the target degraded slope grassland based on the three-dimensional geomorphic image and the vegetation image.
[0054] In one embodiment, the ecological indicator acquisition module 21 can be further configured to: binarize the three-dimensional landform image to obtain a binarized image; and perform boundary diffusion on the center pixel of the binarized image to divide it into multiple vegetation images.
[0055] In one embodiment, the ecological indicator acquisition module 21 can be further configured to: convert the three-dimensional landform image and vegetation image into a two-dimensional planar map to obtain a two-dimensional landform map and a two-dimensional vegetation map respectively; and calculate the vegetation coverage of the target degraded slope grassland based on the two-dimensional landform map and the two-dimensional vegetation map.
[0056] In one embodiment, the ecological indicator acquisition module 21 can be further configured to: determine the vegetation height of each plant in the target degraded slope grassland based on the vegetation image; divide the target degraded slope grassland into at least one vegetation zone based on the vegetation height of all plants and the corresponding vegetation location; and determine the vegetation height of the vegetation zone based on the vegetation height of the plants in each vegetation zone.
[0057] In one embodiment, the ecological trend determination module 22 can be further configured to predict the ecological state trend of the target degraded slope grassland based on vegetation indicators, soil indicators, environmental indicators and comfort indicator ranges.
[0058] In one embodiment, the ecological trend determination module 22 can be further configured to predict the ecological state trend of the target degraded slope grassland based on the change curves of vegetation indicators, soil indicators, and environmental indicators of the target degraded slope grassland.
[0059] In one embodiment, the maintenance strategy determination module 23 can be further configured to: if there is an indicator in the ecological state trend that is outside the comfort index range, then determine the maintenance strategy for the target degraded slope grassland based on the indicator, so as to control the indicator within the corresponding comfort index range.
[0060] In one embodiment, the maintenance strategy stop module 26 can be further configured to: stop the maintenance strategy if the repair status index is within the comfort index range and the difference between the repair status index and the upper and lower limits of the comfort index range is greater than a preset difference threshold.
[0061] Below, for reference Figure 3 To describe an electronic device according to embodiments of this application. For example... Figure 3 As shown, the electronic device 10 includes one or more processors 11 and memory 12.
[0062] The processor 11 may be a central processing unit (CPU) or other form of processing unit with data processing capabilities and / or instruction execution capabilities, and may control other components in the electronic device 10 to perform desired functions.
[0063] The memory 12 may include one or more computer program products, which may include various forms of computer-readable storage media, such as volatile memory and / or non-volatile memory. The volatile memory may include, for example, random access memory (RAM) and / or cache memory. The non-volatile memory may include, for example, read-only memory (ROM), hard disk, flash memory, etc. One or more computer program instructions may be stored on the computer-readable storage medium, and the processor 11 may execute the program instructions to implement the methods of the various embodiments of this application described above and / or other desired functions. Various contents such as input signals, signal components, and noise components may also be stored in the computer-readable storage medium.
[0064] In one example, the electronic device 10 may also include an input device 13 and an output device 14, which are interconnected via a bus system and / or other forms of connection mechanism (not shown).
[0065] When the electronic device is a standalone device, the input device 13 can be a communication network connector for receiving the collected input signals from the first device and the second device.
[0066] In addition, the input device 13 may also include, for example, a keyboard, a mouse, etc.
[0067] The output device 14 can output various information to the outside, including determined distance information, direction information, etc. The output device 14 may include, for example, a display, a speaker, a printer, and a communication network and its connected remote output devices, etc.
[0068] Of course, for the sake of simplicity, Figure 3 Only some of the components of the electronic device 10 relevant to this application are shown in this illustration; components such as buses, input / output interfaces, etc., are omitted. In addition, the electronic device 10 may include any other suitable components depending on the specific application.
[0069] In addition to the methods and apparatus described above, embodiments of this application may also be computer program products, which include computer program instructions that, when executed by a processor, cause the processor to perform the steps in the methods according to various embodiments of this application described in the "Exemplary Methods" section above.
[0070] The computer program product can be written in any combination of one or more programming languages to perform the operations of the embodiments of this application. The programming languages include object-oriented programming languages such as Java and C++, as well as conventional procedural programming languages such as C or similar languages. The program code can be executed entirely on the user's computing device, partially on the user's computing device, as a standalone software package, partially on the user's computing device and partially on a remote computing device, or entirely on a remote computing device or server.
[0071] Furthermore, embodiments of this application may also be computer-readable storage media storing computer program instructions thereon, which, when executed by a processor, cause the processor to perform the steps in the methods according to various embodiments of this application described in the "Exemplary Methods" section above.
[0072] The computer-readable storage medium may be any combination of one or more readable media. A readable medium may be a readable signal medium or a readable storage medium. A readable storage medium may be, for example, an electrical, magnetic, optical, electromagnetic, infrared, or semiconductor system, apparatus, or device, or any combination thereof. More specific examples of readable storage media (a non-exhaustive list) include: an electrical connection having one or more wires, a portable disk, a hard disk, random access memory (RAM), read-only memory (ROM), erasable programmable read-only memory (EPROM or flash memory), optical fiber, portable compact disk read-only memory (CD-ROM), optical storage device, magnetic storage device, or any suitable combination thereof.
[0073] The basic principles of this application have been described above with reference to specific embodiments. However, it should be noted that the advantages, benefits, and effects mentioned in this application are merely examples and not limitations, and should not be considered as essential features of each embodiment of this application. Furthermore, the specific details disclosed above are for illustrative and facilitative purposes only, and are not limitations. These details do not limit the application to the necessity of employing the aforementioned specific details for implementation.
[0074] The block diagrams of devices, apparatuses, devices, and systems involved in this application are merely illustrative examples and are not intended to require or imply that they must be connected, arranged, or configured in the manner shown in the block diagrams. As those skilled in the art will recognize, these devices, apparatuses, devices, and systems can be connected, arranged, and configured in any manner. Words such as “comprising,” “including,” “having,” etc., are open-ended terms meaning “including but not limited to,” and are used interchangeably with them. The terms “or” and “and” as used herein refer to the terms “and / or,” and are used interchangeably with them unless the context clearly indicates otherwise. The term “such as” as used herein refers to the phrase “such as but not limited to,” and is used interchangeably with it.
[0075] It should also be noted that in the apparatus, equipment, and methods of this application, the components or steps can be disassembled and / or recombined. These disassemblies and / or recombinations should be considered as equivalent solutions of this application.
[0076] The above description of the disclosed aspects is provided to enable any person skilled in the art to make or use this application. Various modifications to these aspects will be readily apparent to those skilled in the art, and the general principles defined herein can be applied to other aspects without departing from the scope of this application. Therefore, this application is not intended to be limited to the aspects shown herein, but rather to be accorded the widest scope consistent with the principles and novel features disclosed herein.
[0077] The above description has been given for purposes of illustration and description. Furthermore, this description is not intended to limit the embodiments of this application to the forms disclosed herein. Although numerous exemplary aspects and embodiments have been discussed above, those skilled in the art will recognize certain variations, modifications, alterations, additions, and sub-combinations thereof.
Claims
1. A method for vegetation ecological maintenance in the restoration of degraded slope grassland, characterized in that, include: Obtain ecological status indicators of the target degraded slope grassland; wherein, the ecological status indicators include: vegetation indicators, soil indicators and environmental indicators, the vegetation indicators characterize the growth status of the vegetation planted on the target degraded slope grassland, the soil indicators characterize the soil status of the target degraded slope grassland, and the environmental indicators characterize the environmental status of the area where the target degraded slope grassland is located. Based on the ecological state indicators, the ecological state trend of the target degraded slope grassland is determined; wherein, the ecological state trend represents the prediction result of the ecological state of the target degraded slope grassland in the future time period. Based on the ecological state trends and the range of comfort indicators suitable for vegetation growth, the maintenance strategy for the target degraded slope grassland is determined. Based on the aforementioned maintenance strategy, ecological maintenance is carried out on the target degraded slope grassland; Obtain the restoration status indicators of the target degraded slope grassland after maintenance; If the repair status indicators meet the preset conditions, the maintenance strategy is stopped.
2. The vegetation ecological maintenance method for grassland restoration on degraded slopes according to claim 1, characterized in that, The ecological status indicators for obtaining the target degraded slope grassland include: Obtain a three-dimensional geomorphological image of the target degraded slope grassland; Identify the three-dimensional terrain image to obtain a vegetation image on the target degraded slope grassland; Based on the three-dimensional terrain image and the vegetation image, the vegetation indices of the target degraded slope grassland are determined.
3. The vegetation ecological maintenance method for grassland restoration on degraded slopes according to claim 2, characterized in that, The process of identifying the three-dimensional terrain image to obtain the vegetation image on the target degraded slope grassland includes: The three-dimensional terrain image is binarized to obtain a binarized image; The central pixel of the binarized image is subjected to boundary diffusion to divide it into multiple vegetation images.
4. The vegetation ecological maintenance method for grassland restoration on degraded slopes according to claim 2, characterized in that, The determination of vegetation indicators for the target degraded slope grassland based on the three-dimensional terrain image and the vegetation image includes: The three-dimensional landform image and the vegetation image are converted into two-dimensional planar maps to obtain two-dimensional landform maps and two-dimensional vegetation maps, respectively. Based on the two-dimensional topographic map and the two-dimensional vegetation map, the vegetation coverage of the target degraded slope grassland is calculated.
5. The vegetation ecological maintenance method for grassland restoration on degraded slopes according to claim 2, characterized in that, The determination of vegetation indicators for the target degraded slope grassland based on the three-dimensional terrain image and the vegetation image includes: Based on the vegetation image, determine the vegetation height of each plant in the target degraded slope grassland; Based on the vegetation height and corresponding vegetation location of all vegetation, the target degraded slope grassland is divided into at least one vegetation zone. The vegetation height of each vegetation zone is determined based on the vegetation height in each of the vegetation zones.
6. The vegetation ecological maintenance method for grassland restoration on degraded slopes according to claim 1, characterized in that, The determination of the ecological status trend of the target degraded slope grassland based on the ecological status indicators includes: Based on the vegetation indicators, soil indicators, environmental indicators, and comfort index ranges, the ecological status trend of the target degraded slope grassland is predicted.
7. The vegetation ecological maintenance method for grassland restoration on degraded slopes according to claim 6, characterized in that, The prediction of the ecological status trend of the target degraded slope grassland based on the vegetation indicators, the soil indicators, and the environmental indicators includes: Based on the change curves of vegetation indicators, soil indicators, and environmental indicators of the target degraded slope grassland, the ecological status trend of the target degraded slope grassland is predicted.
8. The vegetation ecological maintenance method for grassland restoration on degraded slopes according to claim 1, characterized in that, The maintenance strategy for the target degraded slope grassland, determined based on the ecological state trend and the range of comfort indicators suitable for vegetation growth, includes: If there is an indicator in the ecological state trend that is outside the range of the comfort index, then the maintenance strategy for the target degraded slope grassland is determined based on the indicator in order to control the indicator within the corresponding comfort index range.
9. The vegetation ecological maintenance method for grassland restoration on degraded slopes according to claim 1, characterized in that, The step of stopping the maintenance strategy if the repair status indicator meets the preset conditions includes: If the repair status indicator is within the range of the comfort index, and the difference between the repair status indicator and the upper and lower limits of the comfort index range is greater than a preset difference threshold, then the maintenance strategy is stopped.
10. A vegetation ecological maintenance system for the restoration of degraded slope grassland, characterized in that, include: An ecological indicator acquisition module is used to acquire ecological status indicators of the target degraded slope grassland; wherein, the ecological status indicators include: vegetation indicators, soil indicators and environmental indicators, the vegetation indicators represent the growth status of the vegetation planted on the target degraded slope grassland, the soil indicators represent the soil status of the target degraded slope grassland, and the environmental indicators represent the environmental status of the area where the target degraded slope grassland is located. An ecological trend determination module is used to determine the ecological state trend of the target degraded slope grassland based on the ecological state indicators; wherein the ecological state trend represents the prediction result of the ecological state of the target degraded slope grassland in the future time period. The maintenance strategy determination module is used to determine the maintenance strategy for the target degraded slope grassland based on the ecological state trend and the range of comfort indicators suitable for vegetation growth. An ecological maintenance execution module is used to perform ecological maintenance on the target degraded slope grassland based on the maintenance strategy; The restoration status acquisition module is used to acquire the restoration status indicators of the target degraded slope grassland after maintenance; The maintenance strategy stop module is used to stop the maintenance strategy if the repair status indicator meets the preset conditions.