Method and device for identifying water ecological information of various water bodies based on dissolved oxygen

Abstract

The present application relates to a method and device for identifying water ecological information of various water areas based on dissolved oxygen. The method includes: obtaining water ecological detection information of different water areas and water sample data of each location point, and identifying the water area type and index value of each water ecological index corresponding to each water area; for each water area type, identifying the dissolved oxygen data of each location point of each water area, thereby generating dissolved oxygen distribution information of each water area; generating a dissolved oxygen water ecological identification strategy for the water area type, and collecting the target water area type of the target water area and the current water sample data of each target location point of the target water area; based on the current water sample data of each target location point, identifying the target water ecological information of the target water area through the dissolved oxygen water ecological identification strategy of the target water area type. The use of this method can improve the accuracy of analyzing water ecological information of different water areas through dissolved oxygen data.

Description

Technical Field

[0001] The present application relates to the technical field of water ecological analysis, and in particular to a method and device for identifying water ecological information of various water bodies based on dissolved oxygen. Background Art

[0002] Water ecological criteria (WEC) are used to describe the concentration or level of environmental factors (biological, physical, chemical, and habitat) that do not threaten the composition, structure, and function of an ecosystem, with the goal of protecting the ecological integrity of the water ecosystem. Based on these factors, they are categorized into biological, physical, and chemical, and habitat criteria. Current research on conventional physical and chemical indexes primarily measures water quality from physical and chemical perspectives, rather than considering the overall perspective of the aquatic ecosystem. Complex interactions and ecological balances exist within aquatic ecosystems, and these interactions form a complex ecological network. Therefore, to more scientifically protect and assess water quality, conventional physical and chemical indexes should be developed based on the biological integrity and species diversity of aquatic ecosystems. Dissolved oxygen (DO), a key component of conventional physical and chemical water indices, is crucial for conducting research on water ecological criteria. However, different aquatic organisms have different DO requirements. When DO concentrations fall below 2 mg / L, it threatens the survival of most aquatic organisms, leading to a decrease in biodiversity and the appearance of black and odorous water. Therefore, how to improve the accuracy of dissolved oxygen monitoring in different water bodies and waters with different functions is one of the important studies for evaluating the water ecological integrity of different water bodies and waters with different functions.

[0003] The traditional method of detecting dissolved oxygen is to manually sample and analyze different water bodies and waters with different functions to obtain dissolved oxygen data for each water area, and then analyze the water ecological information of each water area. However, the accuracy of biodiversity information obtained by manual sampling and analysis depends on the accuracy of identifying the correlation information between different water ecological information and dissolved oxygen data. The accuracy of water ecological information obtained by simply sampling water samples for analysis has a large deviation, which leads to low accuracy in analyzing water ecological information of different water areas through dissolved oxygen data. Summary of the Invention

[0004] Based on this, it is necessary to provide a method and device for identifying water ecological information of various water bodies based on dissolved oxygen to address the above technical problems.

[0005] In a first aspect, the present application provides a method for identifying water ecological information of various water bodies based on dissolved oxygen, comprising:

[0006] Acquire water ecological detection information of different water areas and water sample data of various locations in different water areas, and identify the water type corresponding to each water area and the index value of each water ecological index of each water area based on the water ecological detection information of each water area;

[0007] For each water area type, based on the water sample data of each location point in each water area of ​​the water area type, identifying the dissolved oxygen data of each location point in each water area, and generating the dissolved oxygen distribution information of each water area based on the dissolved oxygen data of each location point in each water area;

[0008] Based on the dissolved oxygen distribution information of each water area and the index value of each water ecological index of each water area, a dissolved oxygen water ecological identification strategy for the water area type is generated, and the target water area type and current water sample data of each target location point of the target water area are collected;

[0009] Based on the current water sample data of each of the target locations, the target water ecological information of the target water area is identified through the dissolved oxygen water ecological identification strategy of the target water area type.

[0010] Optionally, the identifying of the water type corresponding to each water area and the index value of each water ecological index of each water area based on the water ecological detection information of each water area includes:

[0011] For each water area, based on the water ecological information of the water area, identify the water ecological data of each water ecological type of the water area, and query the water ecological data range of each water ecological type of each water area type in the water ecological database;

[0012] Based on the water ecological data range of each water ecological type of each water area type and the water ecological data of each water ecological type of the water area, the water area type corresponding to the water area is identified, and the water ecological index evaluation strategy of the water area type is searched in the water area database;

[0013] Based on the water ecological data of each water ecological type of the water area type, the index value of each water ecological index of the water area is evaluated by the water ecological index evaluation strategy of the water area type.

[0014] Optionally, the identifying the dissolved oxygen data of each location point in each water area based on the water sample data of each location point in each water area type includes:

[0015] For each water area, based on the water sample data of each location point in the water area, water sample detection information of each location point is identified by a water sample detection device;

[0016] Based on the water sample detection information of each location point, the dissolved oxygen content of each location point and the dissolved oxygen change data of each location point are identified, and the dissolved oxygen content of each location point and the dissolved oxygen change data of each location point are used as the dissolved oxygen data of each location point.

[0017] Optionally, generating the dissolved oxygen distribution information of each water area based on the dissolved oxygen data of each location point in each water area includes:

[0018] For each water area, based on the dissolved oxygen content at each location point in the water area and the dissolved oxygen change data at each location point in the water area, each location point is processed for dissolved oxygen gradient distribution to obtain sub-dissolved oxygen distribution information of the water area corresponding to each location point;

[0019] Based on the sub-dissolved oxygen distribution information corresponding to each location point and the location information of each location point in the water area, the sub-dissolved oxygen distribution information corresponding to each location point is subjected to distribution fusion processing to obtain the dissolved oxygen distribution information of each water area.

[0020] Optionally, the water ecological index includes a diversity index and a uniformity index. The dissolved oxygen water ecological identification strategy for the water area type is generated based on the dissolved oxygen distribution information of each water area and the index value of each water ecological index of each water area, including:

[0021] For each water area, generating aquatic biodiversity distribution information of the water area based on the index value of the diversity index of the water area, and generating dissolved oxygen diversity association information of the water area based on the aquatic biodiversity distribution information of the water area and the dissolved oxygen distribution information of the water area;

[0022] Based on the dissolved oxygen diversity correlation information of each water area of ​​the water area type, generating a dissolved oxygen water ecological diversity correlation formula of the water area type, and obtaining an initial water biodiversity fitting formula of the water area type;

[0023] Based on the initial biodiversity fitting formula of the water area type and the dissolved oxygen water ecological diversity association formula of the water area type, a dissolved oxygen diversity identification strategy for the water area type is generated, and the uniformity index is replaced by the diversity index, and the initial water biological uniformity fitting formula is replaced by the initial water biodiversity fitting formula, and the step of returning to execute the index value based on the diversity index of the water area and generating the diversity index distribution information of the water area is returned to obtain the dissolved oxygen uniformity identification strategy for the water area type;

[0024] The dissolved oxygen diversity identification strategy of the water area type and the dissolved oxygen uniformity identification strategy of the water area type are used as the dissolved oxygen water ecology identification strategy of the water area type.

[0025] Optionally, the identifying target water ecological information of the target water area by using the dissolved oxygen water ecological identification strategy of the target water area type based on the current water sample data of each target location point includes:

[0026] Identifying the dissolved oxygen distribution information of the target water area based on the current water sample data of each target location point;

[0027] Based on the dissolved oxygen distribution information of the target water area, identifying the target water biodiversity distribution information of the target water area and the target water biological uniformity distribution information of the target water area by using the dissolved oxygen diversity identification strategy of the target water area type and the dissolved oxygen uniformity identification strategy of the target water area type;

[0028] Identifying an index value of a diversity index of the target water area based on target aquatic biodiversity distribution information of the target water area, and identifying an index value of a uniformity index of the target water area based on target aquatic biodiversity uniformity distribution information of the target water area;

[0029] Based on the index value of the diversity index of the target water area and the index value of the uniformity index of the target water area, target water ecological information of the target water area is identified.

[0030] In a second aspect, the present application also provides a device for identifying water ecological information of various water bodies based on dissolved oxygen, comprising:

[0031] An acquisition module is used to obtain water ecological detection information of different water areas and water sample data of various locations in different water areas, and based on the water ecological detection information of each water area, identify the water area type corresponding to each water area and the index value of each water ecological index of each water area;

[0032] a generating module for identifying, for each water area type, dissolved oxygen data at each location point in each water area of ​​the water area type based on the water sample data at each location point in each water area of ​​the water area type, and generating dissolved oxygen distribution information for each water area based on the dissolved oxygen data at each location point in each water area;

[0033] An acquisition module is used to generate a dissolved oxygen water ecological identification strategy for the water area type based on the dissolved oxygen distribution information of each water area and the index value of each water ecological index of each water area, and to collect the target water area type of the target water area and the current water sample data of each target location point of the target water area;

[0034] The identification module is used to identify the target water ecological information of the target water area based on the current water sample data of each target location point and the dissolved oxygen water ecological identification strategy of the target water area type.

[0035] Optionally, the acquisition module is specifically configured to:

[0036] For each water area, based on the water ecological information of the water area, identify the water ecological data of each water ecological type of the water area, and query the water ecological data range of each water ecological type of each water area type in the water ecological database;

[0037] Based on the water ecological data range of each water ecological type of each water area type and the water ecological data of each water ecological type of the water area, the water area type corresponding to the water area is identified, and the water ecological index evaluation strategy of the water area type is searched in the water area database;

[0038] Based on the water ecological data of each water ecological type of the water area type, the index value of each water ecological index of the water area is evaluated by the water ecological index evaluation strategy of the water area type.

[0039] Optionally, the generating module is specifically configured to:

[0040] For each water area, based on the water sample data of each location point in the water area, water sample detection information of each location point is identified by a water sample detection device;

[0041] Based on the water sample detection information of each location point, the dissolved oxygen content of each location point and the dissolved oxygen change data of each location point are identified, and the dissolved oxygen content of each location point and the dissolved oxygen change data of each location point are used as the dissolved oxygen data of each location point.

[0042] Optionally, the generating module is specifically configured to:

[0043] For each water area, based on the dissolved oxygen content at each location point in the water area and the dissolved oxygen change data at each location point in the water area, each location point is processed for dissolved oxygen gradient distribution to obtain sub-dissolved oxygen distribution information of the water area corresponding to each location point;

[0044] Based on the sub-dissolved oxygen distribution information corresponding to each location point and the location information of each location point in the water area, the sub-dissolved oxygen distribution information corresponding to each location point is subjected to distribution fusion processing to obtain the dissolved oxygen distribution information of each water area.

[0045] Optionally, the acquisition module is specifically used to:

[0046] For each water area, generating aquatic biodiversity distribution information of the water area based on the index value of the diversity index of the water area, and generating dissolved oxygen diversity association information of the water area based on the aquatic biodiversity distribution information of the water area and the dissolved oxygen distribution information of the water area;

[0047] Based on the dissolved oxygen diversity correlation information of each water area of ​​the water area type, generating a dissolved oxygen water ecological diversity correlation formula of the water area type, and obtaining an initial water biodiversity fitting formula of the water area type;

[0048] Based on the initial biodiversity fitting formula of the water area type and the dissolved oxygen water ecological diversity association formula of the water area type, a dissolved oxygen diversity identification strategy for the water area type is generated, and the uniformity index is replaced by the diversity index, and the initial water biological uniformity fitting formula is replaced by the initial water biodiversity fitting formula, and the step of returning to execute the index value based on the diversity index of the water area and generating the diversity index distribution information of the water area is returned to obtain the dissolved oxygen uniformity identification strategy for the water area type;

[0049] The dissolved oxygen diversity identification strategy of the water area type and the dissolved oxygen uniformity identification strategy of the water area type are used as the dissolved oxygen water ecology identification strategy of the water area type.

[0050] Optionally, the identification module is specifically configured to:

[0051] Identifying the dissolved oxygen distribution information of the target water area based on the current water sample data of each target location point;

[0052] Based on the dissolved oxygen distribution information of the target water area, identifying the target water biodiversity distribution information of the target water area and the target water biological uniformity distribution information of the target water area by using the dissolved oxygen diversity identification strategy of the target water area type and the dissolved oxygen uniformity identification strategy of the target water area type;

[0053] Identifying an index value of a diversity index of the target water area based on target aquatic biodiversity distribution information of the target water area, and identifying an index value of a uniformity index of the target water area based on target aquatic biodiversity uniformity distribution information of the target water area;

[0054] Based on the index value of the diversity index of the target water area and the index value of the uniformity index of the target water area, target water ecological information of the target water area is identified.

[0055] In a third aspect, the present application provides a computer device comprising a memory and a processor, wherein the memory stores a computer program, and the processor implements the steps of any one of the methods described in the first aspect when executing the computer program.

[0056] In a fourth aspect, the present application provides a computer-readable storage medium having a computer program stored thereon, wherein the computer program, when executed by a processor, implements the steps of any one of the methods in the first aspect.

[0057] In a fifth aspect, the present application provides a computer program product, wherein the computer program product comprises a computer program, and when the computer program is executed by a processor, the steps of any one of the methods in the first aspect are implemented.

[0058] The above-mentioned method and device for identifying water ecological information of each water area based on dissolved oxygen obtains water ecological detection information of different water areas and water sample data of each location point of different water areas, and identifies the water area type corresponding to each water area and the index value of each water ecological index of each water area based on the water ecological detection information of each water area; for each water area type, based on the water sample data of each location point of each water area of ​​the water area type, identifies the dissolved oxygen data of each location point of each water area, and generates the dissolved oxygen distribution information of each water area based on the dissolved oxygen data of each said location point of each water area; based on the dissolved oxygen distribution information of each water area and the index value of each water ecological index of each water area, generates a dissolved oxygen water ecological identification strategy for the water area type, and collects the target water area type of the target water area and the current water sample data of each target location point of the target water area; based on the current water sample data of each said target location point, identifies the target water ecological information of the target water area through the dissolved oxygen water ecological identification strategy of the target water area type. This solution analyzes the dissolved oxygen water ecological identification strategy for each water type by analyzing the water ecological monitoring information obtained after conducting water ecological testing on each water area of ​​different types, as well as the dissolved oxygen data corresponding to the water sample data at each location. By identifying dissolved oxygen data for different water areas, the target water ecological information of the target water area can be analyzed and identified using the dissolved oxygen water ecological identification strategy for each water area type, thereby improving the comprehensiveness and accuracy of identifying the target water ecological information of the target water area. Furthermore, by constructing dissolved oxygen water ecological identification strategies for different water types and then analyzing the water ecological information of different water types, this solution improves the accuracy of analyzing the water ecological information of different water areas using dissolved oxygen data. BRIEF DESCRIPTION OF THE DRAWINGS

[0059] In order to more clearly illustrate the technical solutions in the embodiments of the present application or related technologies, the following briefly introduces the drawings required for use in the embodiments of the present application or related technical descriptions. Obviously, the drawings described below are only some embodiments of the present application. For ordinary technicians in this field, other related drawings can be obtained based on these drawings without paying any creative work.

[0060] Figure 1 Schematic diagram of a flow chart of a method for identifying water ecological information of various water areas based on dissolved oxygen in one embodiment;

[0061] Figure 2is a correlation diagram corresponding to dissolved oxygen diversity correlation information in one embodiment;

[0062] Figure 3 is a correlation diagram corresponding to dissolved oxygen uniformity correlation information in one embodiment;

[0063] Figure 4 Schematic diagram of a flow chart of an example of identifying water ecological information of various water bodies based on dissolved oxygen in one embodiment;

[0064] Figure 5 1 is a structural block diagram of a device for identifying water ecological information of various water areas based on dissolved oxygen in one embodiment;

[0065] Figure 6 FIG. 1 is a diagram showing the internal structure of a computer device in one embodiment. DETAILED DESCRIPTION

[0066] In order to make the purpose, technical solutions and advantages of this application more clear, the following further describes this application in detail with reference to the accompanying drawings and embodiments. It should be understood that the specific embodiments described herein are only used to explain this application and are not intended to limit this application.

[0067] The method for identifying water ecological information of each water area based on dissolved oxygen provided in the embodiment of the present application can be applied to the application environment of water ecological information identification of water areas. The method can be applied to a terminal, a server, or a system including a terminal and a server, and is implemented through the interaction between the terminal and the server. The terminal can be, but is not limited to, various personal computers, laptops, and the like. After the terminal performs water ecological detection on each water area of ​​different water types, the water ecological monitoring information obtained and the dissolved oxygen data corresponding to the water sample data at each location point are obtained, thereby analyzing the dissolved oxygen water ecological identification strategy of each water area type, so that by performing dissolved oxygen data identification on different water areas, the target water ecological information of the target water area can be analyzed and identified through the dissolved oxygen water ecological identification strategy of the water area type to which each water area belongs, thereby improving the comprehensiveness and accuracy of identifying the target water ecological information of the target water area. In addition, this solution improves the accuracy of analyzing the water ecological information of different water areas through dissolved oxygen data by constructing dissolved oxygen water ecological identification strategies for different water areas respectively, and then analyzing the water ecological information of different water areas.

[0068] In an exemplary embodiment, Figure 1 As shown, a method for identifying water ecological information of various water areas based on dissolved oxygen is provided, and the method is described by taking the application of the method to a terminal as an example, including the following steps S101 to S104.

[0069] Step S101, obtain water ecological detection information of different water areas and water sample data of each location point of different water areas, and based on the water ecological detection information of each water area, identify the water area type corresponding to each water area and the index value of each water ecological index of each water area.

[0070] In this embodiment, the terminal obtains water ecology detection information for different water areas in response to a user's water ecology detection operation. Furthermore, in response to the user's water sample data upload operation, the terminal obtains water sample data for each location point in the different water areas. Different water areas refer to water areas of different water types, including, but not limited to, freshwater water types (including lakes, rivers, ponds, reservoirs, drinking water, and flood storage areas), and seawater water types (including bays, shallow oceans, and deep oceans). The water areas corresponding to each water type can be water areas in different regions, such as water areas of the same type in different cities within a country, water areas of the same type in different temperature zones, or water areas of the same type in different environments. The water ecology detection information includes water ecology data for each water ecology type, including, for example, water biomass types, water density types, and water quality data types for different aquatic organisms. The location points can be locations within each area of ​​the water area, locations at different depths, or locations encompassing both locations and depths. Among them, each location point is the center point of a unit location range in the water area, and the unit location range can be a range with a radius of 1m, 3m, 5m, or 10m, and the water sample data of each location point includes the sub-water sample data collected from sampling points at different intervals from the center point in the unit location range corresponding to the location segment, to obtain the water sample data of the center point.

[0071] In step S102, for each water area type, based on the water sample data of each location point of each water area of ​​the water area type, the dissolved oxygen data of each location point of each water area is identified, and based on the dissolved oxygen data of each location point of each water area, the dissolved oxygen distribution information of each water area is generated.

[0072] In this embodiment, for each water area type, the terminal identifies the dissolved oxygen data for each location point in each water area based on the water sample data for each location point in each water area type, and generates dissolved oxygen distribution information for each water area based on the dissolved oxygen data for each location point in each water area. The dissolved oxygen data for each location point includes the dissolved oxygen content at each location point and the dissolved oxygen change data corresponding to each location point. The specific identification process will be described in detail later. The dissolved oxygen distribution information for each water area is the distribution information of the dissolved oxygen content at different locations in the water area. The specific identification process will be described in detail later.

[0073] Step S103, based on the dissolved oxygen distribution information of each water area and the index value of each water ecological index of each water area, a dissolved oxygen water ecological identification strategy for the water area type is generated, and the target water area type of the target water area and the current water sample data of each target location point of the target water area are collected.

[0074] In this embodiment, the terminal generates a dissolved oxygen water ecological identification strategy for each water area based on the dissolved oxygen distribution information of each water area and the index values ​​of each water ecological index for each water area. It also collects the target water area type and current water sample data for each target location of the target water area. The dissolved oxygen water ecological identification strategy includes a dissolved oxygen diversity identification strategy for that water area type and a dissolved oxygen uniformity identification strategy for that water area type. The specific generation process will be described in detail later.

[0075] Step S104 : Based on the current water sample data of each target location point, target water ecological information of the target water area is identified through a dissolved oxygen water ecological identification strategy of the target water area type.

[0076] In this embodiment, the terminal uses the current water sample data at each target location and the dissolved oxygen water ecological identification strategy for the target water area type to identify the target water ecological information of the target water area. This target ecological information includes the index value of the target water area's diversity index and the index value of the target water area's uniformity index. The specific identification process will be described in detail later.

[0077] Based on the above scheme, after conducting water ecological testing on each water area of ​​different water types, the water ecological monitoring information obtained, as well as the dissolved oxygen data corresponding to the water sample data at each location, are used to analyze the dissolved oxygen water ecological identification strategy for each water area type. By identifying dissolved oxygen data for different water areas, the target water ecological information of the target water area can be analyzed and identified using the dissolved oxygen water ecological identification strategy for the water area type to which each water area belongs, thereby improving the comprehensiveness and accuracy of identifying the target water ecological information of the target water area. Furthermore, by constructing dissolved oxygen water ecological identification strategies for different water areas and then analyzing the water ecological information of different water areas, this scheme improves the accuracy of analyzing the water ecological information of different water areas using dissolved oxygen data.

[0078] Optionally, based on the water ecological detection information of each water area, the water area type corresponding to each water area and the index value of each water ecological index of each water area are identified, including: for each water area, based on the water ecological information of the water area, the water ecological data of each water ecological type of the water area are identified, and in the water ecological database, the water ecological data range of each water ecological type of each water area type is queried; based on the water ecological data range of each water ecological type of each water area type and the water ecological data of each water ecological type of the water area, the water area type corresponding to the water area is identified, and the water ecological index evaluation strategy of the water area type is queried in the water area database; based on the water ecological data of each water ecological type of the water area type, the index value of each water ecological index of the water area is evaluated through the water ecological index evaluation strategy of the water area type.

[0079] In this embodiment, for each water area, the terminal identifies the water ecological data for each water ecological type based on the water ecological information of the water area and queries the water ecological data range for each water ecological type in the water ecological database. The water ecological database stores the water ecological types corresponding to each water area type and the water ecological data range for each water ecological type. The terminal then identifies the initial water area type for each water ecological type based on the water ecological data range and the water ecological data for each water ecological type. Based on the water ecological data range to which the water ecological data for each water ecological type belongs, the terminal selects the corresponding water area type from each initial water area type. The terminal then identifies the corresponding water area type and queries the water ecological index evaluation strategy for that water area type in the water ecological database. The water ecological index evaluation strategies include a water ecological diversity index evaluation strategy and a water ecological uniformity index evaluation strategy. Each water ecological diversity index evaluation strategy includes indicator values ​​corresponding to the water biomass ranges for different aquatic organism types. The water ecological uniformity index evaluation strategy includes index values ​​corresponding to various aquatic species density ranges for different aquatic species types and various water quality data ranges for different water quality data types. Based on the water ecological data for each water ecological type, the terminal uses the water ecological index evaluation strategy for that water area type to evaluate the index values ​​for each water ecological index.

[0080] As shown in Table 1, the water ecological diversity level corresponding to the index value of each water ecological index.

[0081] Table 1: Ecological diversity levels of water bodies

[0082]

[0083] Based on the above scheme, the water ecological type of each water area is determined by performing a database query based on the water ecological data of each water ecological type, and the water ecological type of each water area is determined. Based on the water ecological index evaluation strategy of each water ecological type, water ecological evaluation processing is performed to obtain the index value of each water ecological index of the water area, thereby improving the accuracy of identifying the water ecological type of each water area and the accuracy of identifying the index value of each water ecological index of each water area.

[0084] Optionally, based on the water sample data of each location point in each water area of ​​the water area type, the dissolved oxygen data of each location point in each water area is identified, including: for each water area, based on the water sample data of each location point in the water area, using a water sample detection device, identifying the water sample detection information of each location point; based on the water sample detection information of each location point, identifying the dissolved oxygen content of each location point and the dissolved oxygen change data of each location point, and using the dissolved oxygen content of each location point and the dissolved oxygen change data of each location point as the dissolved oxygen data of each location point.

[0085] In this embodiment, the terminal uses a water sampling device to identify water sample information for each water area based on water sample data from each location within the water area. The water sampling device is a dissolved oxygen detector. The water sample information for each location includes the dissolved oxygen content of each sampling point within the unit location range to which the location belongs.

[0086] Based on the water sample detection information at each location, the terminal identifies the dissolved oxygen content at each location and calculates the dissolved oxygen content of each sampling point in descending order according to the distance between each sampling point and the location point, obtaining the sub-dissolved oxygen change data for each sampling point. The terminal then arranges and distributes the sub-dissolved oxygen change data for each sampling point in order of distance from each sampling point to the location point, obtaining the dissolved oxygen change data for each location point. Finally, the terminal uses the dissolved oxygen content and dissolved oxygen change data for each location point as the dissolved oxygen data for each location point.

[0087] Based on the above scheme, the dissolved oxygen content of each location point is detected and the dissolved oxygen change data is calculated to obtain the dissolved oxygen data of each location point, thereby improving the comprehensiveness and accuracy of the identification of the dissolved oxygen and dissolved oxygen distribution at each location point.

[0088] Optionally, based on the dissolved oxygen data of each location point in each water area, the dissolved oxygen distribution information of each water area is generated, including: for each water area, based on the dissolved oxygen content of each location point in the water area and the dissolved oxygen change data of each location point in the water area, each location point is subjected to dissolved oxygen gradient distribution processing to obtain the sub-dissolved oxygen distribution information of the water area corresponding to each location point; based on the sub-dissolved oxygen distribution information corresponding to each location point and the position information of each location point in the water area, the sub-dissolved oxygen distribution information corresponding to each location point is subjected to distribution fusion processing to obtain the dissolved oxygen distribution information of each water area.

[0089] In this embodiment, the terminal performs dissolved oxygen gradient distribution processing on each water area based on the dissolved oxygen content and dissolved oxygen variation data at each location in the water area, thereby obtaining sub-dissolved oxygen distribution information for each location. The sub-dissolved oxygen distribution information for each location is the decreasing dissolved oxygen content distribution information for that location within the water area.

[0090] Then, based on the sub-dissolved oxygen distribution information corresponding to each location point and the location information of each location point in the water area, the terminal performs distribution fusion processing on the sub-dissolved oxygen distribution information corresponding to each location point to obtain the dissolved oxygen distribution information of each water area. The distribution fusion processing is to fuse the sub-dissolved oxygen distribution information of each location point into a single distribution information using a normal distribution fitting strategy to obtain the dissolved oxygen distribution information of the water area.

[0091] Based on the above solution, the dissolved oxygen distribution information of each location point is distributed and fused to obtain the dissolved oxygen distribution information of the water area, thereby improving the accuracy of the obtained dissolved oxygen distribution information.

[0092] Optionally, the water ecological index includes a diversity index and a uniformity index. Based on the dissolved oxygen distribution information of each water area and the index value of each water ecological index of each water area, a dissolved oxygen water ecological identification strategy for the water area type is generated, including: for each water area, based on the index value of the diversity index of the water area, generating the aquatic biodiversity distribution information of the water area, and based on the aquatic biodiversity distribution information of the water area and the dissolved oxygen distribution information of the water area, generating the dissolved oxygen diversity association information of the water area; based on the dissolved oxygen diversity association information of each water area of ​​the water area type, generating the dissolved oxygen water ecological diversity association formula of the water area type, and obtaining the initial aquatic biodiversity fitting formula of the water area type; based on the initial biodiversity fitting formula of the water area type and the dissolved oxygen water ecological diversity association formula of the water area type, generating the dissolved oxygen diversity identification strategy of the water area type, and replacing the diversity index with the uniformity index, replacing the initial aquatic biodiversity fitting formula with the initial aquatic biodiversity fitting formula, returning to execute the index value based on the diversity index of the water area, generating the diversity index distribution information step of the water area, and obtaining the dissolved oxygen uniformity identification strategy of the water area type; using the dissolved oxygen diversity identification strategy of the water area type and the dissolved oxygen uniformity identification strategy of the water area type as the dissolved oxygen water ecological identification strategy of the water area type.

[0093] In this embodiment, for each water area, the terminal generates the aquatic biodiversity distribution information of the water area based on the index value of the water area's diversity index, and generates the dissolved oxygen diversity association information of the water area based on the aquatic biodiversity distribution information of the water area and the dissolved oxygen distribution information of the water area. Figure 2 、 Figure 3 The following diagrams show the corresponding correlation graphs for dissolved oxygen diversity and uniformity, respectively. When generating the dissolved oxygen diversity and uniformity information for a water area, the correlation information essentially represents the correlation formulas between different dissolved oxygen concentrations and the diversity index, and between different dissolved oxygen concentrations and the uniformity index.

[0094] Then, based on the dissolved oxygen diversity association information of each water area of ​​the water area type, the terminal generates a dissolved oxygen water ecological diversity association formula for the water area type and obtains an initial water biodiversity fitting formula for the water area type. Next, based on the initial biodiversity fitting formula for the water area type and the dissolved oxygen water ecological diversity association formula for the water area type, the terminal generates a dissolved oxygen diversity identification strategy for the water area type, replaces the diversity index with the uniformity index, replaces the initial water biodiversity fitting formula with the initial water biodiversity fitting formula, returns to execute the indicator value based on the water area diversity index, generates the water area diversity index distribution information step, and obtains the dissolved oxygen uniformity identification strategy for the water area type.

[0095] Finally, the terminal uses the dissolved oxygen diversity identification strategy of water area types and the dissolved oxygen uniformity identification strategy of water area types as the dissolved oxygen water ecological identification strategy of water area types.

[0096] When generating the dissolved oxygen diversity identification strategy, the initial biodiversity fitting formula obtained is:

[0097]

[0098] Where: FV—physical and chemical index concentration value before diversity index correction, g / L;

[0099] K—physical and chemical indicators—diversity index slope, dimensionless;

[0100] —The diversity index value corresponding to FV before diversity index correction, dimensionless;

[0101] C—constant, intercept, dimensionless;

[0102] B—diversity index correction value, see Table 1 for details.

[0103] The dissolved oxygen-diversity index (H) correlation formula is:

[0104] LgDO=0.188lgH+0.828

[0105] Based on this correlation formula and the initial biodiversity fitting formula, the generated dissolved oxygen diversity identification strategy for water types is:

[0106]

[0107] F —Concentration value of physical and chemical indicators after diversity index correction, g / L;

[0108] When the corrected diversity index H=1,

[0109] When the corrected diversity index H=2,

[0110] When the corrected diversity index H=3,

[0111] When generating a dissolved oxygen uniformity identification strategy, the differences from the above-mentioned dissolved oxygen diversity identification strategy are as follows:

[0112] The formula related to dissolved oxygen-uniformity index (J) is:

[0113] LgDO=0.163lgH+0.965

[0114] Based on this correlation formula and the initial biodiversity fitting formula, the generated dissolved oxygen uniformity identification strategy for water types is:

[0115]

[0116] When the corrected uniformity index J=0.3,

[0117] When the corrected uniformity index J=0.5,

[0118] When the corrected uniformity index J=0.8,

[0119] Based on the above scheme, strategies are generated from two perspectives: dissolved oxygen diversity identification strategy and dissolved oxygen uniformity identification strategy, which improves the accuracy and comprehensiveness of the generated dissolved oxygen water ecological identification strategy for water types.

[0120] Optionally, based on the current water sample data of each target location point, the target water ecological information of the target water area is identified through the dissolved oxygen water ecological identification strategy of the target water area type, including: based on the current water sample data of each target location point, the dissolved oxygen distribution information of the target water area is identified; based on the dissolved oxygen distribution information of the target water area, the target water biodiversity distribution information of the target water area and the target water biological uniformity distribution information of the target water area are identified respectively through the dissolved oxygen diversity identification strategy of the target water area type and the dissolved oxygen uniformity identification strategy of the target water area type; based on the target water biodiversity distribution information of the target water area, the index value of the diversity index of the target water area is identified, and based on the target water biological uniformity distribution information of the target water area, the index value of the uniformity index of the target water area is identified; based on the index value of the diversity index of the target water area and the index value of the uniformity index of the target water area, the target water ecological information of the target water area is identified.

[0121] In this embodiment, the terminal identifies the dissolved oxygen distribution information of the target water area based on the current water sample data of each target location point. The identification process of the dissolved oxygen distribution information here is the same as the process of identifying the dissolved oxygen distribution information above, and this solution does not provide redundant descriptions. Then, based on the dissolved oxygen distribution information of the target water area, the terminal uses the dissolved oxygen diversity identification strategy of the target water area type and the dissolved oxygen uniformity identification strategy of the target water area type to respectively identify the target water biodiversity distribution information of the target water area and the target water biological uniformity distribution information of the target water area. Thereafter, the terminal identifies the index value of the diversity index of the target water area based on the target water biodiversity distribution information of the target water area, and identifies the index value of the uniformity index of the target water area based on the target water biological uniformity distribution information of the target water area. Then, based on Table 1, the terminal identifies the diversity level and uniformity level of the target water area, and uses the diversity level and uniformity level of the target water area as the target water ecological information of the target water area.

[0122] Based on the above scheme, by obtaining the water area type of the water area and the current water sample data of each location point, the target water ecological information of the target water area is directly analyzed, thereby improving the comprehensiveness and accuracy of the identification of the target water ecological information.

[0123] This application also provides an example of identifying water ecological information of various water bodies based on dissolved oxygen, as shown in FIG4 . The specific processing process includes the following steps:

[0124] Step S401: Acquire water ecological detection information of different water areas and water sample data of various locations in different water areas.

[0125] Step S402 , for each water area, based on the water ecological information of the water area, identifying the water ecological data of each water ecological type of the water area, and querying the water ecological data range of each water ecological type of each water area type in the water ecological database.

[0126] Step S403, based on the water ecological data range of each water ecological type of each water area type and the water ecological data of each water ecological type of the water area, identify the water area type corresponding to the water area, and query the water ecological index evaluation strategy of the water area type in the water area database.

[0127] Step S404 : Based on the water ecological data of each water ecological type of the water area type, the index value of each water ecological index of the water area type is evaluated by the water ecological index evaluation strategy of the water area type.

[0128] Step S405 : for each water area, based on the water sample data of each location point in the water area, water sample detection information of each location point is identified by a water sample detection device.

[0129] Step S406: Based on the water sample detection information of each location point, identify the dissolved oxygen content of each location point and the dissolved oxygen change data of each location point, and use the dissolved oxygen content of each location point and the dissolved oxygen change data of each location point as the dissolved oxygen data of each location point.

[0130] Step S407 : for each water area, based on the dissolved oxygen content at each location point in the water area and the dissolved oxygen change data at each location point in the water area, a dissolved oxygen gradient distribution process is performed on each location point to obtain sub-dissolved oxygen distribution information of the water area corresponding to each location point.

[0131] Step S408 : Based on the sub-dissolved oxygen distribution information corresponding to each location point and the location information of each location point in the water area, the sub-dissolved oxygen distribution information corresponding to each location point is subjected to distribution fusion processing to obtain the dissolved oxygen distribution information of each water area.

[0132] Step S409 : for each water area, generating aquatic biodiversity distribution information of the water area based on the index value of the water area diversity index, and generating dissolved oxygen diversity association information of the water area based on the aquatic biodiversity distribution information of the water area and the dissolved oxygen distribution information of the water area.

[0133] Step S410 : generating a dissolved oxygen water ecological diversity correlation formula of the water area type based on the dissolved oxygen diversity correlation information of each water area type, and obtaining an initial water biodiversity fitting formula of the water area type.

[0134] Step S411, based on the initial biodiversity fitting formula of the water area type and the dissolved oxygen water ecological diversity association formula of the water area type, generate a dissolved oxygen diversity identification strategy for the water area type, replace the diversity index with the uniformity index, replace the initial water biological uniformity fitting formula with the initial water biodiversity fitting formula, return to execute the indicator value based on the water area diversity index, generate the water area diversity index distribution information step, and obtain the dissolved oxygen uniformity identification strategy for the water area type.

[0135] In step S412, the dissolved oxygen diversity identification strategy of the water area type and the dissolved oxygen uniformity identification strategy of the water area type are used as the dissolved oxygen water ecology identification strategy of the water area type.

[0136] Step S413 , collecting the target water area type of the target water area and current water sample data of each target location point of the target water area.

[0137] Step S414: identifying the dissolved oxygen distribution information of the target water area based on the current water sample data of each target location point.

[0138] Step S415 , based on the dissolved oxygen distribution information of the target water area, target water biodiversity distribution information and target water biological uniformity distribution information of the target water area are identified respectively through the dissolved oxygen diversity identification strategy of the target water area type and the dissolved oxygen uniformity identification strategy of the target water area type.

[0139] Step S416 , identifying an index value of the diversity index of the target water area based on the target aquatic biodiversity distribution information of the target water area, and identifying an index value of the uniformity index of the target water area based on the target aquatic biodiversity uniformity distribution information of the target water area.

[0140] Step S417 : identifying target water ecological information of the target water area based on the index value of the diversity index of the target water area and the index value of the uniformity index of the target water area.

[0141] It should be understood that, although the various steps in the flowcharts involved in the various embodiments described above are displayed in sequence according to the instructions of the arrows, these steps are not necessarily executed in sequence in the order indicated by the arrows. Unless otherwise specified herein, there is no strict order restriction on the execution of these steps, and these steps can be executed in other orders. Moreover, at least a portion of the steps in the flowcharts involved in the various embodiments described above can include multiple steps or multiple stages, and these steps or stages are not necessarily executed and completed at the same time, but can be executed at different times, and the execution order of these steps or stages is not necessarily to be carried out in sequence, but can be executed in turn or alternately with other steps or at least a portion of steps or stages in other steps.

[0142] Based on the same inventive concept, the embodiments of the present application also provide a device for identifying water ecological information of each water area based on dissolved oxygen, which is used to implement the aforementioned method for identifying water ecological information of each water area based on dissolved oxygen. The implementation solution provided by this device is similar to the implementation solution described in the aforementioned method. Therefore, the specific limitations of one or more embodiments of the device for identifying water ecological information of each water area based on dissolved oxygen provided below can be found in the limitations of the method for identifying water ecological information of each water area based on dissolved oxygen, and will not be repeated here.

[0143] In an exemplary embodiment, Figure 5 As shown, a device for identifying water ecological information of various water areas based on dissolved oxygen is provided, comprising: an acquisition module 510, a generation module 520, a collection module 530 and an identification module 540, wherein:

[0144] An acquisition module 510 is configured to acquire water ecological detection information of different water areas and water sample data of various locations in different water areas, and identify the water area type corresponding to each water area and the index value of each water ecological index of each water area based on the water ecological detection information of each water area;

[0145] a generating module 520 for identifying, for each water area type, dissolved oxygen data at each location point in each water area of ​​the water area type based on the water sample data at each location point in each water area of ​​the water area type, and generating dissolved oxygen distribution information for each water area based on the dissolved oxygen data at each location point in each water area;

[0146] The acquisition module 530 is used to generate a dissolved oxygen water ecological identification strategy for the water area type based on the dissolved oxygen distribution information of each water area and the index value of each water ecological index of each water area, and to collect the target water area type of the target water area and the current water sample data of each target location point of the target water area;

[0147] The identification module 540 is configured to identify the target water ecological information of the target water area based on the current water sample data of each target location point and through the dissolved oxygen water ecological identification strategy of the target water area type.

[0148] Optionally, the acquisition module 510 is specifically configured to:

[0149] For each water area, based on the water ecological information of the water area, identify the water ecological data of each water ecological type of the water area, and query the water ecological data range of each water ecological type of each water area type in the water ecological database;

[0150] Based on the water ecological data range of each water ecological type of each water area type and the water ecological data of each water ecological type of the water area, the water area type corresponding to the water area is identified, and the water ecological index evaluation strategy of the water area type is searched in the water area database;

[0151] Based on the water ecological data of each water ecological type of the water area type, the index value of each water ecological index of the water area is evaluated by the water ecological index evaluation strategy of the water area type.

[0152] Optionally, the generating module 520 is specifically configured to:

[0153] For each water area, based on the water sample data of each location point in the water area, water sample detection information of each location point is identified by a water sample detection device;

[0154] Based on the water sample detection information of each location point, the dissolved oxygen content of each location point and the dissolved oxygen change data of each location point are identified, and the dissolved oxygen content of each location point and the dissolved oxygen change data of each location point are used as the dissolved oxygen data of each location point.

[0155] Optionally, the generating module 520 is specifically configured to:

[0156] For each water area, based on the dissolved oxygen content at each location point in the water area and the dissolved oxygen change data at each location point in the water area, each location point is processed for dissolved oxygen gradient distribution to obtain sub-dissolved oxygen distribution information of the water area corresponding to each location point;

[0157] Based on the sub-dissolved oxygen distribution information corresponding to each location point and the location information of each location point in the water area, the sub-dissolved oxygen distribution information corresponding to each location point is subjected to distribution fusion processing to obtain the dissolved oxygen distribution information of each water area.

[0158] Optionally, the acquisition module 530 is specifically configured to:

[0159] For each water area, generating aquatic biodiversity distribution information of the water area based on the index value of the diversity index of the water area, and generating dissolved oxygen diversity association information of the water area based on the aquatic biodiversity distribution information of the water area and the dissolved oxygen distribution information of the water area;

[0160] Based on the dissolved oxygen diversity correlation information of each water area of ​​the water area type, generating a dissolved oxygen water ecological diversity correlation formula of the water area type, and obtaining an initial water biodiversity fitting formula of the water area type;

[0161] Based on the initial biodiversity fitting formula of the water area type and the dissolved oxygen water ecological diversity association formula of the water area type, a dissolved oxygen diversity identification strategy for the water area type is generated, and the uniformity index is replaced by the diversity index, and the initial water biological uniformity fitting formula is replaced by the initial water biodiversity fitting formula, and the step of returning to execute the index value based on the diversity index of the water area and generating the diversity index distribution information of the water area is returned to obtain the dissolved oxygen uniformity identification strategy for the water area type;

[0162] The dissolved oxygen diversity identification strategy of the water area type and the dissolved oxygen uniformity identification strategy of the water area type are used as the dissolved oxygen water ecology identification strategy of the water area type.

[0163] Optionally, the identification module 540 is specifically configured to:

[0164] Identifying the dissolved oxygen distribution information of the target water area based on the current water sample data of each target location point;

[0165] Based on the dissolved oxygen distribution information of the target water area, identifying the target water biodiversity distribution information of the target water area and the target water biological uniformity distribution information of the target water area by using the dissolved oxygen diversity identification strategy of the target water area type and the dissolved oxygen uniformity identification strategy of the target water area type;

[0166] Identifying an index value of a diversity index of the target water area based on target aquatic biodiversity distribution information of the target water area, and identifying an index value of a uniformity index of the target water area based on target aquatic biodiversity uniformity distribution information of the target water area;

[0167] Based on the index value of the diversity index of the target water area and the index value of the uniformity index of the target water area, target water ecological information of the target water area is identified.

[0168] Each module in the aforementioned device for identifying water ecological information of various water bodies based on dissolved oxygen can be implemented in whole or in part through software, hardware, or a combination thereof. Each module can be embedded in or independent of a processor in a computer device in the form of hardware, or can be stored in a memory in the computer device in the form of software, so that the processor can call and execute the corresponding operations of each module.

[0169] In an exemplary embodiment, a computer device is provided. The computer device may be a terminal, and its internal structure diagram may be as shown in FIG. Figure 6As shown. The computer device includes a processor, memory, an input / output interface, a communication interface, a display unit, and an input device. The processor, memory, and input / output interface are connected via a system bus, and the communication interface, display unit, and input device are connected to the system bus via the input / output interface. The processor of the computer device is used to provide computing and control capabilities. The memory of the computer device includes a non-volatile storage medium and internal memory. The non-volatile storage medium stores an operating system and computer programs. The internal memory provides an environment for the operation of the operating system and computer programs in the non-volatile storage medium. The input / output interface of the computer device is used to exchange information between the processor and external devices. The communication interface of the computer device is used to communicate with external terminals via wired or wireless means, and the wireless means can be implemented via Wi-Fi, mobile cellular networks, near-field communication (NFC), or other technologies. When executed by the processor, the computer program implements a method for identifying water ecological information of various water bodies based on dissolved oxygen. The display unit of the computer device is used to form a visually visible image, and can be a display screen, a projection device, or a virtual reality imaging device. The display screen can be a liquid crystal display screen or an electronic ink display screen, and the input device of the computer device can be a touch layer covering the display screen, or a button, trackball or touchpad set on the computer device casing, or an external keyboard, touchpad or mouse.

[0170] Those skilled in the art will understand that Figure 6 The structure shown in the figure is only a block diagram of a part of the structure related to the solution of the present application, and does not constitute a limitation on the computer device to which the solution of the present application is applied. The specific computer device may include more or fewer components than shown in the figure, or combine certain components, or have a different component arrangement.

[0171] In an exemplary embodiment, a computer device is provided, including a memory and a processor, wherein a computer program is stored in the memory, and the processor implements the steps of any one of the methods in the first aspect when executing the computer program.

[0172] In one embodiment, a computer-readable storage medium is provided, on which a computer program is stored. When the computer program is executed by a processor, the steps of any one of the methods in the first aspect are implemented.

[0173] In one embodiment, a computer program product is provided, comprising a computer program, which implements the steps of any one of the methods of the first aspect when executed by a processor.

[0174] It should be noted that the user information (including but not limited to user device information, user personal information, etc.) and data (including but not limited to data used for analysis, stored data, displayed data, etc.) involved in this application are all information and data authorized by the user or fully authorized by all parties, and the collection, use and processing of relevant data must comply with relevant regulations.

[0175] Those skilled in the art will understand that all or part of the processes in the above-mentioned embodiments can be implemented by instructing the relevant hardware through a computer program. The computer program can be stored in a non-volatile computer-readable storage medium. When the computer program is executed, it can include the processes of the embodiments of the above-mentioned methods. In particular, any reference to memory, database, or other media used in the embodiments provided in this application can include at least one of non-volatile memory and volatile memory. Non-volatile memory can include read-only memory (ROM), magnetic tape, floppy disk, flash memory, optical memory, high-density embedded non-volatile memory, resistive random access memory (ReRAM), magnetic random access memory (MRAM), ferroelectric random access memory (FRAM), phase change memory (PCM), graphene memory, etc. Volatile memory can include random access memory (RAM) or external cache memory, etc. By way of illustration and not limitation, RAM can take various forms, such as static random access memory (SRAM) or dynamic random access memory (DRAM). The databases involved in the various embodiments provided herein may include at least one of a relational database and a non-relational database. Non-relational databases may include, but are not limited to, blockchain-based distributed databases. The processors involved in the various embodiments provided herein may be, but are not limited to, general-purpose processors, central processing units (CPUs), graphics processing units (GPUs), digital signal processors (DSPs), programmable logic devices (PLDs), quantum computing-based data processing logic devices, artificial intelligence (AI) processors, and the like.

[0176] The technical features of the above embodiments can be combined arbitrarily. In order to make the description concise, not all possible combinations of the technical features in the above embodiments are described. However, as long as there is no contradiction in the combination of these technical features, they should be considered to be within the scope of this application.

[0177] The above-described embodiments merely represent several implementation methods of the present application. While the descriptions are relatively specific and detailed, they should not be construed as limiting the scope of the present application. It should be noted that a person of ordinary skill in the art may make various modifications and improvements without departing from the spirit of the present application, and these modifications and improvements fall within the scope of protection of the present application. Therefore, the scope of protection of the present application shall be determined by the appended claims.

Claims

1. A method for identifying water ecological information of various water areas based on dissolved oxygen, characterized in that: The method comprises: Obtain water ecological detection information of different water areas and water sample data of various locations in different water areas; For each water area, based on the water ecological information of the water area, identify the water ecological data of each water ecological type of the water area, and query the water ecological data range of each water ecological type of each water area type in the water ecological database; Based on the water ecological data range of each water ecological type of each water area type and the water ecological data of each water ecological type of the water area, the water area type corresponding to the water area is identified, and the water ecological index evaluation strategy of the water area type is searched in the water area database; Based on the water ecological data of each water ecological type of the water area type, the index value of each water ecological index of the water area is evaluated by the water ecological index evaluation strategy of the water area type; The water ecological index includes a diversity index and a uniformity index; For each water area type, based on the water sample data of each location point in each water area of ​​the water area type, identifying the dissolved oxygen data of each location point in each water area, and generating the dissolved oxygen distribution information of each water area based on the dissolved oxygen data of each location point in each water area; For each water area, generating aquatic biodiversity distribution information of the water area based on the index value of the diversity index of the water area, and generating dissolved oxygen diversity association information of the water area based on the aquatic biodiversity distribution information of the water area and the dissolved oxygen distribution information of the water area; Based on the dissolved oxygen diversity correlation information of each water area of ​​the water area type, generating a dissolved oxygen water ecological diversity correlation formula of the water area type, and obtaining an initial water biodiversity fitting formula of the water area type; Based on the initial biodiversity fitting formula of the water area type and the dissolved oxygen water ecological diversity association formula of the water area type, a dissolved oxygen diversity identification strategy for the water area type is generated, and the diversity index is replaced by the uniformity index, and the initial water biological uniformity fitting formula is replaced by the initial water biodiversity fitting formula, and the step of returning to execute the index value based on the diversity index of the water area and generating the diversity index distribution information of the water area is returned to obtain the dissolved oxygen uniformity identification strategy for the water area type; Using the dissolved oxygen diversity identification strategy of the water area type and the dissolved oxygen uniformity identification strategy of the water area type as the dissolved oxygen water ecology identification strategy of the water area type; Collecting target water area types and current water sample data of each target location point in the target water area; Based on the current water sample data of each of the target locations, the target water ecological information of the target water area is identified through the dissolved oxygen water ecological identification strategy of the target water area type.

2. The method according to claim 1, characterized in that The step of identifying dissolved oxygen data at each location point in each water area based on the water sample data at each location point in each water area type includes: For each water area, based on the water sample data of each location point in the water area, water sample detection information of each location point is identified by a water sample detection device; Based on the water sample detection information of each location point, the dissolved oxygen content of each location point and the dissolved oxygen change data of each location point are identified, and the dissolved oxygen content of each location point and the dissolved oxygen change data of each location point are used as the dissolved oxygen data of each location point.

3. The method according to claim 2, characterized in that Generating the dissolved oxygen distribution information of each water area based on the dissolved oxygen data of each location point in each water area includes: For each water area, based on the dissolved oxygen content at each location point in the water area and the dissolved oxygen change data at each location point in the water area, each location point is processed for dissolved oxygen gradient distribution to obtain sub-dissolved oxygen distribution information of the water area corresponding to each location point; Based on the sub-dissolved oxygen distribution information corresponding to each location point and the location information of each location point in the water area, the sub-dissolved oxygen distribution information corresponding to each location point is subjected to distribution fusion processing to obtain the dissolved oxygen distribution information of each water area.

4. The method according to claim 1, wherein The target water ecological information of the target water area is identified based on the current water sample data of each target location point and through the dissolved oxygen water ecological identification strategy of the target water area type, including: Identifying the dissolved oxygen distribution information of the target water area based on the current water sample data of each target location point; Based on the dissolved oxygen distribution information of the target water area, identifying the target water biodiversity distribution information of the target water area and the target water biological uniformity distribution information of the target water area by using the dissolved oxygen diversity identification strategy of the target water area type and the dissolved oxygen uniformity identification strategy of the target water area type; Identifying an index value of a diversity index of the target water area based on target aquatic biodiversity distribution information of the target water area, and identifying an index value of a uniformity index of the target water area based on target aquatic biodiversity uniformity distribution information of the target water area; Based on the index value of the diversity index of the target water area and the index value of the uniformity index of the target water area, target water ecological information of the target water area is identified.

5. A device for identifying water ecological information of various water areas based on dissolved oxygen, characterized in that: The device comprises: An acquisition module is used to obtain water ecological detection information of different water areas and water sample data of various location points in different water areas; for each water area, based on the water ecological information of the water area, the water ecological data of each water ecological type of the water area is identified, and the water ecological data range of each water ecological type of each water area type is queried in the water ecological database; based on the water ecological data range of each water ecological type of each water area type and the water ecological data of each water ecological type of the water area, the water area type corresponding to the water area is identified, and the water ecological index evaluation strategy of the water area type is queried in the water area database; based on the water ecological data of each water ecological type of the water area type, the index value of each water ecological index of the water area is evaluated by the water ecological index evaluation strategy of the water area type; the water ecological index includes a diversity index and a uniformity index; a generating module for identifying, for each water area type, dissolved oxygen data at each location point in each water area of ​​the water area type based on the water sample data at each location point in each water area of ​​the water area type, and generating dissolved oxygen distribution information for each water area based on the dissolved oxygen data at each location point in each water area; A collection module is configured to generate, for each water area, aquatic biodiversity distribution information of the water area based on the index value of the diversity index of the water area, and generate dissolved oxygen diversity association information of the water area based on the aquatic biodiversity distribution information of the water area and the dissolved oxygen distribution information of the water area; generate a dissolved oxygen water ecological diversity association formula of the water area type based on the dissolved oxygen diversity association information of each water area of ​​the water area type, and obtain an initial water biodiversity fitting formula of the water area type; generate a dissolved oxygen diversity identification strategy of the water area type based on the initial biodiversity fitting formula of the water area type and the dissolved oxygen water ecological diversity association formula of the water area type, replace the diversity index with the uniformity index, replace the initial water biodiversity fitting formula with the initial water biological uniformity fitting formula, return to the step of generating the diversity index distribution information of the water area based on the index value of the diversity index of the water area, and obtain the dissolved oxygen uniformity identification strategy of the water area type; use the dissolved oxygen diversity identification strategy of the water area type and the dissolved oxygen uniformity identification strategy of the water area type as the dissolved oxygen water ecological identification strategy of the water area type, and collect current water sample data of the target water area type and each target location point of the target water area; The identification module is used to identify the target water ecological information of the target water area based on the current water sample data of each target location point and the dissolved oxygen water ecological identification strategy of the target water area type.

6. The device according to claim 5, characterized in that The generation module is specifically used to: For each water area, based on the water sample data of each location point in the water area, water sample detection information of each location point is identified by a water sample detection device; Based on the water sample detection information of each location point, the dissolved oxygen content of each location point and the dissolved oxygen change data of each location point are identified, and the dissolved oxygen content of each location point and the dissolved oxygen change data of each location point are used as the dissolved oxygen data of each location point.

7. The device according to claim 5, characterized in that The generation module is specifically used to: For each water area, based on the dissolved oxygen content at each location point in the water area and the dissolved oxygen change data at each location point in the water area, each location point is processed for dissolved oxygen gradient distribution to obtain sub-dissolved oxygen distribution information of the water area corresponding to each location point; Based on the sub-dissolved oxygen distribution information corresponding to each location point and the location information of each location point in the water area, the sub-dissolved oxygen distribution information corresponding to each location point is subjected to distribution fusion processing to obtain the dissolved oxygen distribution information of each water area.

8. A computer device comprising a memory and a processor, wherein the memory stores a computer program, wherein: When the processor executes the computer program, the steps of the method according to any one of claims 1 to 4 are implemented.

9. A computer-readable storage medium having a computer program stored thereon, characterized in that: When the computer program is executed by a processor, the steps of the method according to any one of claims 1 to 4 are implemented.

10. A computer program product comprising a computer program, characterized in that When the computer program is executed by a processor, the steps of the method according to any one of claims 1 to 4 are implemented.

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