Ecological recovery method and apparatus for polluted river in basin, and electronic device

Abstract

Provided in the present invention are an ecological recovery method and apparatus for a polluted river in a basin, and an electronic device. The method comprises: acquiring state information of a polluted river; on the basis of the state information, determining an implementation starting stage and an ecological recovery objective; then determining feedback indicators, feedback sub-indicators corresponding to the feedback indicators, and implementation schemes corresponding to the implementation starting stage; on the basis of the feedback indicators, the feedback sub-indicators and the ecological recovery objective, determining a first importance ranking of the implementation schemes; according to the first importance ranking, using the implementation schemes to perform implementation; on the basis of obtained implementation results, determining a second importance ranking of the implementation schemes, and according to the second importance ranking, performing implementation until the implementation starting stage meets the ecological recovery objective; and then performing a next implementation stage following the implementation starting stage, such that the next implementation stage meets a corresponding ecological recovery objective. The method improves the stability of ecological recovery and the accuracy of targeting treatment issues, and reduces monitoring expenses and treatment costs.

Description

Method and device for ecological recovery of polluted river in river basin and electronic equipment

[0001] Cross-reference to Related Applications

[0002] The present application claims priority from the Chinese patent application No. 2024105860741 entitled "Method and device for ecological recovery of polluted river in river basin and electronic equipment" filed on May 13, 2024 with the China Patent Office, the content of which is incorporated herein by reference in its entirety. TECHNICAL FIELD

[0003] The present application relates to the technical field of environmental engineering, in particular to a method and device for ecological recovery of polluted river in river basin and electronic equipment. BACKGROUND

[0004] Under the strong interference of human activities, the water ecological process of urban water environment is undergoing profound changes. Water resource shortage, water environment pollution and water ecological degradation and other primary and secondary water-related problems are becoming increasingly prominent. Under the interaction of resource-based and pollution-based water shortage, the water ecological environment is deteriorating, and the restoration and remediation are becoming more difficult, which has become a difficult point for water ecological environment protection in China.

[0005] The existing engineering guidelines for river management are one-way implementation measures, which do not set up feedback mechanisms according to actual conditions, cannot guarantee the implementation effect of each stage and adjust the scheme scientifically in real time, and therefore cause the instability of the management effect to occur frequently. On the other hand, in the process of engineering implementation, the indicators concerned are different corresponding to different ecological recovery stages, and the indicators of different stages cannot be focused on, which not only makes it difficult to focus on the management problems, but also easily increases the monitoring cost and management cost. SUMMARY

[0006] Therefore, the purpose of the present application is to provide a method and device for ecological recovery of polluted river in river basin and electronic equipment to improve the stability of ecological recovery and the accuracy of focusing on management problems, and to reduce the monitoring cost and management cost.

[0007] In a first aspect, an embodiment of the present application provides a method for ecological recovery of a polluted river in a river basin, comprising: obtaining state information of the polluted river; determining an implementation starting stage and an ecological recovery target based on the state information; determining a feedback index, a sub-feedback index corresponding to the feedback index, and an implementation scheme corresponding to the implementation starting stage based on the implementation starting stage; determining a first importance ranking of the implementation scheme based on the feedback index, the sub-feedback index, and the ecological recovery target; implementing the implementation scheme according to the first importance ranking to obtain an implementation result; determining a second importance ranking of the implementation scheme based on the implementation result, and implementing the implementation scheme according to the second importance ranking until the implementation starting stage meets the ecological recovery target; and if the implementation starting stage is not the last implementation stage of the ecological recovery, proceeding to a next implementation stage after the implementation starting stage to make the next implementation stage meet a corresponding ecological recovery target.

[0008] In a preferred embodiment of the present application, the state information includes river water quantity information, river water quality information, and river biodiversity information, and the determination of the implementation starting stage based on the state information comprises: if the river water quality information is of a first category, the implementation starting stage is a stage of reducing pollution into the river basin; if the river water quality information is of a second category and no sewage management system is previously set in the river basin of the polluted river, the implementation starting stage is the stage of reducing pollution into the river basin; if the river water quality information is of the second category and a sewage management system is previously set in the river basin of the polluted river and a specified index in the river basin of the polluted river does not meet a standard, the implementation starting stage is a stage of rectifying internal source pollution in the river; if the river water quality information is of the second category and a sewage management system is previously set in the river basin of the polluted river and the river water quantity information is insufficient, the implementation starting stage is a stage of guaranteeing ecological base flow of the river; if the river water quality information is of the second category and a sewage management system is previously set in the river basin of the polluted river and both the river water quantity information and the river water quality information meet the standard and the river biodiversity information indicates that the river is to be recovered, the implementation starting stage is a stage of reconstructing ecological space in the river basin; and the first category indicates that the river water quality is between obvious blackening and foul smell and inferior V-class water quality, and the second category indicates that the river water quality is at or better than V-class water quality.

[0009] In a preferred embodiment of the present application, the feedback index is a plurality of feedback indexes, and the determination of the first importance ranking of the implementation scheme based on the feedback index, the sub-feedback index, and the ecological recovery target comprises: constructing a fuzzy complementary matrix by pairwise analysis of the feedback indexes; determining a weight value of the sub-feedback index based on the fuzzy complementary matrix; determining a comprehensive weight value relative to the ecological recovery target based on the weight value of the sub-feedback index; and determining the first importance ranking of the implementation scheme based on the comprehensive weight value.

[0010] In the preferred embodiment of the present application, the comprehensive weight value of the relative ecological recovery target based on the weight value of the sub-feedback index comprises: comparing the weight values of the alternative implementation schemes based on the weight values of the sub-feedback indexes, to obtain the weight values of the alternative implementation schemes; and determining the comprehensive weight value of the relative ecological recovery target based on the weight values of the alternative implementation schemes.

[0011] In the preferred embodiment of the present application, the second importance ranking of the implementation scheme based on the implementation result comprises: if the feedback index and / or the sub-feedback index do not meet the standard, determining the second importance ranking of the implementation scheme based on the feedback index and the sub-feedback index after the implementation of the implementation scheme.

[0012] In the preferred embodiment of the present application, before the implementation of the implementation scheme according to the first importance ranking to obtain the implementation result, the method further comprises: determining the first weight order of the feedback index and the second weight order of the sub-feedback index; and the implementation of the implementation scheme according to the first importance ranking to obtain the implementation result comprises: after the implementation of the implementation scheme according to the first importance ranking, checking whether the feedback index and the sub-feedback index meet the standard based on the first weight order and the second weight order; and taking the meeting of the feedback index and the sub-feedback index as the implementation result.

[0013] In the preferred embodiment of the present application, the implementation stage of the ecological recovery comprises: a stage of reducing pollution into a river basin, a stage of rectifying internal pollution in a river, a stage of guaranteeing ecological base flow of a river, and a stage of reconstructing ecological space of a river basin; the implementation scheme corresponding to the stage of reducing pollution into a river basin comprises: weaving nets into pieces, clearing up the source, dredging water, and upgrading and improving water plants; the implementation scheme corresponding to the stage of rectifying internal pollution in a river comprises: dredging pipe networks and dredging rivers; the implementation scheme corresponding to the stage of guaranteeing ecological base flow of a river comprises: ecological water supplement and recycled water supplement; and the implementation scheme corresponding to the stage of reconstructing ecological space of a river basin comprises: rectifying small lakes, ponds and reservoirs, artificial wetlands, and landscape corridors.

[0014] In the second aspect, the embodiments of the present application further provide an ecological recovery device for a polluted river basin, comprising: a state information acquisition module configured to acquire state information of the polluted river basin; a first determination module configured to determine an implementation starting stage and an ecological recovery target based on the state information; a second determination module configured to determine a feedback index, a sub-feedback index corresponding to the feedback index, and an implementation scheme corresponding to the implementation starting stage based on the implementation starting stage; an importance ranking determination module configured to determine a first importance ranking of the implementation scheme based on the feedback index, the sub-feedback index, and the ecological recovery target; a first implementation scheme implementation module configured to implement the implementation scheme according to the first importance ranking to obtain an implementation result; and a second implementation scheme implementation module configured to determine a second importance ranking of the implementation scheme based on the implementation result and implement the implementation scheme according to the second importance ranking.

[0015] In a third aspect, an electronic device is provided, which includes a processor and a memory. The memory stores computer executable instructions that are executable by the processor. The processor executes the computer executable instructions to implement the method for ecological recovery of a polluted river in a river basin according to the first aspect.

[0016] In a fourth aspect, a computer readable storage medium is provided, which stores computer executable instructions. When the computer executable instructions are invoked and executed by a processor, the computer executable instructions cause the processor to implement the method for ecological recovery of a polluted river in a river basin according to the first aspect.

[0017] The embodiments of the present application have the following beneficial effects:

[0018] The embodiments of the present application provide a method and device for ecological recovery of a polluted river in a river basin and an electronic device. The state information of the polluted river is obtained, the implementation starting stage and the ecological recovery target are determined based on the state information, the feedback index, the sub-feedback index corresponding to the feedback index and the implementation scheme corresponding to the implementation starting stage are determined based on the implementation starting stage, the first importance ranking of the implementation scheme is determined based on the feedback index, the sub-feedback index and the ecological recovery target, the implementation scheme is implemented according to the first importance ranking, the implementation result is obtained, the second importance ranking of the implementation scheme is determined based on the implementation result, the implementation scheme is implemented according to the second importance ranking, and the next implementation stage after the implementation starting stage is implemented until the implementation starting stage meets the ecological recovery target, so that the next implementation stage meets the corresponding ecological recovery target. In this way, the feedback index and the sub-feedback index of different implementation stages can be focused on, the problem can be accurately focused on, the monitoring cost and the treatment cost are reduced, the implementation scheme can be adjusted in real time according to the implementation result, and the stability of the ecological recovery is improved.

[0019] Other features and advantages of the present disclosure will be illustrated in the following description, or can be learned from the description, or can be determined without doubt, or can be known by implementing the above-mentioned technologies of the present disclosure.

[0020] In order to make the above-mentioned purposes, features and advantages of the present disclosure more obvious and easy to understand, the following preferred embodiments are specifically described in detail below, and the accompanying drawings are referred to. BRIEF DESCRIPTION OF DRAWINGS

[0021] In order to more clearly illustrate the technical solutions in the specific embodiments or the prior art of the present application, the drawings required to be used in the specific embodiments or the prior art description will be briefly introduced as follows. Obviously, the drawings in the following description are some embodiments of the present application, and other drawings can be obtained by those skilled in the art without any creative effort on the basis of these drawings.

[0022] Fig. 1a is a flow chart of a method for ecological recovery of a polluted river in a drainage basin according to an embodiment of the present application;

[0023] Fig. 1b is an implementation flow chart of a method for ecological recovery of a polluted river in a drainage basin according to an embodiment of the present application;

[0024] Fig. 2 is a flow chart of another method for ecological recovery of a polluted river in a drainage basin according to an embodiment of the present application;

[0025] Fig. 3 is a structural schematic diagram of an ecological recovery device for a polluted river in a drainage basin according to an embodiment of the present application;

[0026] Fig. 4 is a structural schematic diagram of an electronic device according to an embodiment of the present application. DETAILED DESCRIPTION

[0027] In order to make the objects, technical solutions and advantages of the embodiments of the present application clearer, the technical solutions of the present application will be described clearly and completely below with reference to the drawings. Obviously, the described embodiments are some of the embodiments of the present application, but not all the embodiments. Based on the embodiments in the present application, all other embodiments obtained by those skilled in the art without any creative effort belong to the scope of protection of the present application.

[0028] Under the strong interference of human activities, the water ecological process of urban water environment is undergoing profound changes. The original and secondary water-related problems such as water shortage, water environment pollution and water ecological degradation are becoming increasingly prominent. Under the interaction of resource-based and pollution-based water shortage, the water ecological environment is deteriorating, and the restoration and treatment are becoming more difficult, which has become a difficult point in the protection of water ecological environment in China.

[0029] The existing engineering guidelines for river management are one-way implementation measures, which cannot set up feedback mechanisms according to actual conditions, cannot guarantee the implementation effect of each stage and adjust the scheme in real time, and therefore cause the instability of the management effect. On the other hand, in the process of engineering implementation, different indicators are concerned corresponding to different ecological recovery stages, and the indicators of different stages cannot be focused on, which not only makes it difficult to focus on the management problem, but also increases the monitoring cost and management cost.

[0030] In fact, the ecological recovery of a polluted river in a basin is a continuous and gradual process, and the ecological recovery paths of different rivers are not exactly the same and need to be adjusted to local conditions. In the gradual process, the goals implemented at each stage are different, and the indicators of the sections focused on are also different. These indicators are the test standards for the implementation results of the previous stage and the key points for determining the next stage. However, there is still a lack of implementation plans and paths for the ecological recovery of rivers with different degrees of pollution under strong human activities with a feedback mechanism. Considering that the ecological recovery of rivers in a basin is a systematic and multi-coupling progressive process, in the implementation process of the ecological recovery of a polluted river in a strong human activity basin, the actual situation of the basin should be combined with the index feedback to implement the stage-by-stage goals, and the implementation plan should be flexibly adjusted according to the index feedback.

[0031] Based on this, the ecological recovery method, device and electronic equipment provided by the embodiment of the present application can obtain the state information of the polluted river, determine the implementation starting stage and the ecological recovery target based on the state information, determine the feedback index, the sub-feedback index corresponding to the feedback index and the implementation plan corresponding to the implementation starting stage based on the implementation starting stage, determine the first importance order of the implementation plan based on the feedback index, the sub-feedback index and the ecological recovery target, implement the implementation plan according to the first importance order to obtain the implementation result, finally determine the second importance order of the implementation plan based on the implementation result, and implement the implementation plan according to the second importance order until the implementation starting stage meets the ecological recovery target, and then the next implementation stage after the implementation starting stage is implemented, so that the next implementation stage meets the corresponding ecological recovery target. In this way, the feedback index and the sub-feedback index of different implementation stages can be targeted, the problem can be accurately focused on, the monitoring cost and the treatment cost can be reduced, and the stability of the ecological recovery can be improved according to the implementation result.

[0032] In order to facilitate the understanding of the embodiment, first, a method for ecological recovery of a polluted river in a basin disclosed by the embodiment of the present application is introduced in detail.

[0033] Embodiment 1

[0034] The embodiment of the present application provides a method for ecological recovery of a polluted river in a basin. Fig. 1a is a flow chart of the method for ecological recovery of a polluted river in a basin provided by the embodiment of the present application. As shown in Fig. 1a, the method for ecological recovery of a polluted river in a basin can include the following steps:

[0035] In step S101, the state information of the polluted river is obtained.

[0036] The state information includes river water quantity information, river water quality information and river biodiversity information, and the state information of the polluted river can be obtained through water quality, water quantity and biological monitoring.

[0037] In step S102, a starting stage of implementation and an ecological recovery target are determined based on the state information.

[0038] The starting stage of implementation of the ecological recovery includes: a stage of reducing pollution into a river basin, a stage of regulating internal source pollution in a river channel, a stage of guaranteeing ecological base flow of a river, and a stage of reconstructing ecological space in a river basin.

[0039] The ecological recovery target corresponding to the stage of reducing pollution into a river basin is overall black elimination, the ecological recovery target corresponding to the stage of regulating internal source pollution in a river channel is stable black elimination, the ecological recovery target corresponding to the stage of guaranteeing ecological base flow of a river is water quality improvement, and the ecological recovery target corresponding to the stage of reconstructing ecological space in a river basin is ecological restoration.

[0040] Specifically, in the case that the river water quality information is of a first category, the starting stage of implementation is the stage of reducing pollution into a river basin.

[0041] The first category represents that the river water quality is between obvious blackening and stench to inferior V-class water quality.

[0042] Specifically, in the case that the river water quality information is of a second category and a sewage management system is previously set in the river basin of the polluted river, if a specified index in the river basin of the polluted river is not up to standard, the starting stage of implementation is the stage of regulating internal source pollution in a river channel.

[0043] The specified index can be a concentration of a nutrient salt pollutant, a concentration of a heavy metal pollutant, and a concentration of a trace pollutant, and the specified index not up to standard means that the specified index exceeds a pre-set concentration threshold.

[0044] The second category represents that the river water quality is at or better than V-class water quality, and the sewage management system can include a perfect rain and sewage pipe network system and a sewage treatment facility.

[0045] Specifically, in the case that the river water quality information is of the second category and the sewage management system is not previously set in the river basin of the polluted river, the starting stage of implementation is the stage of reducing pollution into a river basin.

[0046] Specifically, in the case that the river water quality information is of the second category and the sewage management system is previously set in the river basin of the polluted river, if the river water quantity information and the river water quality information are both up to standard, and the river biodiversity information represents a to-be-recovered condition, the starting stage of implementation is the stage of reconstructing ecological space in a river basin.

[0047] Specifically, in the case that the river water quality information is of the second category and the sewage management system is previously set in the river basin of the polluted river, if the river water quantity information is river water quantity deficiency, the starting stage of implementation is the stage of guaranteeing ecological base flow of a river.

[0048] Specifically, in the case that the river water quality information is the second category and the sewage management system is pre-set in the basin of the polluted river, if the river water quantity information and the river water quality information are both up to standard and the river biodiversity information represents the condition to be recovered, the implementation starting stage is the stage of reconstructing the ecological space of the basin.

[0049] In step S103, the feedback index, the sub-feedback index corresponding to the feedback index, and the implementation scheme corresponding to the implementation starting stage are determined based on the implementation starting stage.

[0050] The feedback index can include physical index, chemical index, nutrient salt index, municipal index, unconventional index, hydrology index, and ecological index.

[0051] The sub-feedback index corresponding to the physical index can include transparency and odor; the sub-feedback index corresponding to the chemical index can include chemical oxygen demand (COD), dissolved oxygen, potential of hydrogen (PH), oxidation-reduction potential, chlorophyll, and dissolved organic carbon; the sub-feedback index corresponding to the nutrient salt index can include ammonia nitrogen, total nitrogen, and total phosphorus; the sub-feedback index corresponding to the municipal index can include pipe network density, sewage collection rate, rain and sewage pipe network diversion ratio, domestic sewage treatment rate, and sewage pipe access point of drainage area; the sub-feedback index corresponding to the unconventional index can include unconventional pollutants according to the actual conditions of the basin, such as heavy metals, persistent organic pollutants, etc.; the sub-feedback index corresponding to the hydrology index can include flow rate, water level, and water system connectivity; and the sub-feedback index corresponding to the ecological index can include biodiversity, indicator species, number of water bodies in which native fish or aquatic plants are reproduced, proportion of river ecological shoreline, length of greenway construction, and ecological space connectivity.

[0052] The implementation scheme corresponding to the stage of reducing pollution into the river basin includes: weaving nets into pieces, clearing the source, dredging the river, and upgrading and improving the water plant; the implementation scheme corresponding to the stage of treating the endogenous pollution in the river includes: pipe network dredging and river dredging; the implementation scheme corresponding to the stage of guaranteeing the ecological base flow of the river includes: ecological water regulation and replenishment and reclaimed water replenishment; and the implementation scheme corresponding to the stage of reconstructing the ecological space of the basin includes: small lake pond reservoir regulation, artificial wetland, and landscape corridor.

[0053] The feedback index corresponding to the stage of reducing pollution into the river basin can include physical index, chemical index, nutrient salt index, and municipal index. The sub-feedback index corresponding to the physical index is transparency and odor; the sub-feedback index corresponding to the chemical index is COD; the sub-feedback index corresponding to the nutrient salt index is ammonia nitrogen and total phosphorus; and the sub-feedback index corresponding to the municipal index is pipe network density, sewage collection rate, rain and sewage pipe network diversion ratio, domestic sewage treatment rate, and sewage pipe access point of drainage area.

[0054] The feedback indicators corresponding to the stage of treating the endogenous pollution of the river channel can include physical indicators, chemical indicators, nutrient salt indicators, and unconventional indicators. The sub-feedback indicators corresponding to the physical indicators are transparency and odor; the sub-feedback indicators corresponding to the chemical indicators are dissolved oxygen, pH, oxidation-reduction potential, chlorophyll, dissolved organic carbon, and COD; the sub-feedback indicators corresponding to the nutrient salt indicators are ammonia nitrogen, total nitrogen, and total phosphorus; and the sub-feedback indicators corresponding to the unconventional indicators are unconventional pollutants determined according to the actual situation of the river basin.

[0055] The feedback indicators corresponding to the stage of guaranteeing the ecological base flow of the river can include chemical indicators, nutrient salt indicators, and hydrodynamic indicators. The sub-feedback indicators corresponding to the chemical indicators are dissolved oxygen, pH, oxidation-reduction potential, chlorophyll, dissolved organic carbon, and COD; the sub-feedback indicators corresponding to the nutrient salt indicators are ammonia nitrogen, total nitrogen, and total phosphorus; and the sub-feedback indicators corresponding to the hydrodynamic indicators are flow velocity and water level.

[0056] The feedback indicators corresponding to the stage of reconstructing the ecological space of the river basin can include chemical indicators, nutrient salt indicators, and ecological indicators. The sub-feedback indicators corresponding to the chemical indicators are dissolved oxygen, pH, oxidation-reduction potential, chlorophyll, dissolved organic carbon, and COD; the sub-feedback indicators corresponding to the nutrient salt indicators are ammonia nitrogen, total nitrogen, and total phosphorus; and the sub-feedback indicators corresponding to the ecological indicators are biodiversity.

[0057] It should be noted that the feedback indicators, the sub-feedback indicators, and the implementation schemes can be adjusted according to actual concerns, technical progress, and the like.

[0058] Step S104, determining a first importance ranking of the implementation schemes based on the feedback indicators, the sub-feedback indicators, and the ecological recovery target.

[0059] In the determination of the first importance ranking, the first weight order of the feedback indicators and the second weight order of the sub-feedback indicators can be determined simultaneously. Specifically, the weight values of the feedback indicators and the weight values of the sub-feedback indicators can be determined by constructing a fuzzy complementary matrix, and the weight values of the feedback indicators and the weight values of the sub-feedback indicators are sorted respectively to obtain the first weight order and the second weight order.

[0060] The comprehensive weight values of the relative ecological recovery targets can be determined by the weight values of the sub-feedback indicators, and the first importance ranking of the implementation schemes can be determined by the comprehensive weight values.

[0061] Step S105, implementing the implementation schemes according to the first importance ranking to obtain an implementation result.

[0062] The first importance ranking represents the order of implementation of the various embodiments, and the embodiments are implemented in the order of the first importance ranking to treat the polluted river in the basin.

[0063] The implementation result can represent whether the feedback indicators and / or the sub-feedback indicators meet the standards.

[0064] Specifically, after the implementation of the embodiments according to the first importance ranking, whether the feedback indicators and the sub-feedback indicators meet the standards is investigated based on the first weight order and the second weight order; and the meeting of the standards of the feedback indicators and the sub-feedback indicators is taken as the implementation result.

[0065] The first weight order represents the importance ranking of the feedback indicators, and the second weight order represents the importance ranking of the sub-feedback indicators; if the feedback indicators and the sub-feedback indicators with the highest weights meet the standards, it can be considered that the corresponding stages have completed the ecological recovery target.

[0066] In step S106, the second importance ranking of the implementation scheme is determined based on the implementation result, and the implementation scheme is implemented according to the second importance ranking until the implementation starting stage meets the ecological recovery target.

[0067] If the implementation result represents that the feedback indicators and / or the sub-feedback indicators do not meet the standards, the second importance ranking of the implementation scheme is determined based on the feedback indicators after the implementation of the implementation scheme and the sub-feedback indicators after the implementation of the implementation scheme.

[0068] The feedback indicators and the sub-feedback indicators are investigated after each implementation of the implementation scheme, and in the case that the feedback indicators and / or the sub-feedback indicators do not meet the standards, the importance ranking of the implementation scheme is updated based on the feedback indicators and the sub-feedback indicators, and the implementation is continued according to the importance ranking until the implementation starting stage meets the ecological recovery target.

[0069] The weight value of the feedback indicators is determined based on the fuzzy complementary matrix; and the comprehensive weight value of the sub-feedback indicators is determined based on the weight value of the feedback indicators and the weight value of the sub-feedback indicators.

[0070] In step S107, if the implementation starting stage is not the last implementation stage of the ecological recovery, the next implementation stage after the implementation starting stage is implemented to make the next implementation stage meet the corresponding ecological recovery target.

[0071] The implementation stages of ecological recovery can be in the following order: reducing pollution into the river basin stage, rectifying endogenous pollution in the river channel stage, ensuring ecological base flow of the river stage, and reconstructing ecological space in the river basin stage. When one implementation starting stage is carried out and the corresponding ecological recovery target is met in the implementation starting stage, the next implementation stage is carried out until all subsequent implementation stages meet the corresponding ecological recovery target.

[0072] For example, the implementation starting stage is the reconstructing ecological space in the river basin stage, and after the corresponding ecological recovery target is met in the reconstructing ecological space in the river basin stage, the pollution river is treated.

[0073] For example, the implementation starting stage is the rectifying endogenous pollution in the river channel stage, and after the corresponding ecological recovery target is met in the rectifying endogenous pollution in the river channel stage, the river ecological base flow guarantee stage and the reconstructing ecological space in the river basin stage are required to meet the corresponding ecological recovery target in turn before the pollution river is treated.

[0074] In practical application, the most concerned feedback indicators, sub-feedback indicators and the most effective implementation scheme in the river basin can be selected according to different river characteristics and implementation schemes. Based on this, a feedback mechanism in the implementation process of ecological recovery of the polluted river in the river basin is formed, which can not only make decisions according to local conditions, but also adjust the implementation scheme and the ecological recovery target in real time, and has strong flexibility and accuracy.

[0075] For the convenience of understanding, FIG. 1b is an implementation flowchart of the ecological recovery method of the polluted river in the river basin provided by the embodiment of the present application, as shown in FIG. 1b, regarding the ecological recovery path of the polluted river in the river basin, the state information of the polluted river is obtained, then the implementation starting stage and the ecological recovery target are determined according to the state information, then the implementation scheme corresponding to the implementation starting stage is determined, and whether to enter the next implementation stage is evaluated according to the feedback indicators after the implementation scheme is implemented, until the corresponding ecological recovery target is completed.

[0076] In the implementation starting stage, if the river water quality information is the first category, the implementation starting stage is the reduction of basin pollution into river stage; if the river water quality information is the second category and the basin of the polluted river is provided with a sewage management system in advance, if the designated index in the basin of the polluted river does not meet the standard, the implementation starting stage is the regulation of river in-source pollution stage; if the river water quality information is the second category and the basin of the polluted river is not provided with a sewage management system in advance, the implementation starting stage is the reduction of basin pollution into river stage; if the river water quality information is the second category and the basin of the polluted river is provided with a sewage management system in advance, if the river water quantity information is river water quantity deficiency, the implementation starting stage is the guarantee of river ecological base flow stage; if the river water quality information is the second category and the basin of the polluted river is provided with a sewage management system in advance, if the river water quantity information and the river water quality information both meet the standard, and the river biodiversity information represents the condition of being to be recovered, the implementation starting stage is the reconstruction of basin ecological space stage.

[0077] The implementation schemes of the reduction of basin pollution into river stage, the regulation of river in-source pollution stage, the guarantee of river ecological base flow stage and the reconstruction of basin ecological space stage each have a corresponding first importance order, and the implementation of the implementation scheme is started from the first importance order corresponding to the implementation starting stage to implement the basin polluted river, and in the process of implementation, the current ecological recovery condition is judged by whether the sub feedback index meets the standard, the ecological recovery target corresponding to the implementation scheme is confirmed to be completed in the case that the sub feedback index meets the standard, and the second importance order of the implementation scheme is determined again according to the feedback index after implementation and the sub feedback index after implementation to continue the implementation in the case that the sub feedback index does not meet the standard, until the ecological recovery target is completed.

[0078] The ecological recovery method of the basin polluted river provided by the embodiment of the application can obtain the state information of the polluted river, determine the implementation starting stage and the ecological recovery target based on the state information, determine the feedback index, the sub feedback index corresponding to the feedback index and the implementation scheme corresponding to the implementation starting stage based on the implementation starting stage, determine the first importance order of the implementation scheme based on the feedback index, the sub feedback index and the ecological recovery target, implement the implementation scheme according to the first importance order to obtain the implementation result, finally determine the second importance order of the implementation scheme based on the implementation result, implement the implementation scheme according to the second importance order, until the implementation starting stage meets the ecological recovery target, and then the next implementation stage after the implementation starting stage is implemented, so that the next implementation stage meets the corresponding ecological recovery target. In this way, the feedback index and the sub feedback index of different implementation stages can be targeted, the problem of governance can be accurately focused, the monitoring cost and the governance cost are reduced, and the implementation scheme can be adjusted in real time according to the implementation result, and the stability of ecological recovery is improved.

[0079] Embodiment 2

[0080] The embodiment of the present application also provides another ecological recovery method of a river polluted by a basin; the method is realized on the basis of the method of the embodiment; and the method mainly describes a specific implementation manner of determining the first importance ranking of an implementation scheme based on feedback indexes, sub-feedback indexes and ecological recovery targets.

[0081] FIG. 2 is a flowchart of another ecological recovery method of a river polluted by a basin provided by the embodiment of the present application; as shown in FIG. 2, the first importance ranking of the implementation scheme based on the feedback indexes, the sub-feedback indexes and the ecological recovery targets can include the following steps:

[0082] In step S201, the feedback indexes are analyzed two by two to construct a fuzzy complementary matrix.

[0083] In the step, the feedback indexes are scaled according to a preset number of scales, which can be scaled by human marking, such as marking by experts, designers, operation and maintenance personnel, the public, etc., or machine marking, such as marking by a pre-trained model.

[0084] Specifically, the number of scales can be 0.1-0.9; the number of scales of 0.1-0.4 represents that if element ai is compared with element aj to obtain judgment rij, then the judgment obtained by comparing element aj with element ai is rij=1-rji; the number of scales of 0.5 represents that the two elements are equally important; the number of scales of 0.6 represents that one element is slightly more important than the other element in the comparison of the two elements; the number of scales of 0.7 represents that one element is slightly more obvious than the other element in the comparison of the two elements; the number of scales of 0.8 represents that one element is much more important than the other element in the comparison of the two elements; and the number of scales of 0.9 represents that one element is extremely more important than the other element in the comparison of the two elements.

[0085] For the convenience of understanding, taking the stage of reducing basin pollution into a river as an example, the constructed fuzzy complementary matrix of the feedback indexes is shown in Table 1.

[0086] Table 1

[0087] In the table, A represents the stage of reducing basin pollution into a river, B1 represents a physical index corresponding to the stage of reducing basin pollution into a river, B2 represents a chemical index corresponding to the stage of reducing basin pollution into a river, B3 represents a nutrient salt index corresponding to the stage of reducing basin pollution into a river, B4 represents a municipal index corresponding to the stage of reducing basin pollution into a river, bij represents the number of scales of Bi compared with Bj. ri represents the sum of the numbers of scales of the i-th row, and bk represents the number of scales of the k-th feedback index.

[0088] Step S202, determining the weight value of the sub-feedback index based on the fuzzy complementary matrix.

[0089] wherein the sum of each row of the matrix B = bij (n x n) is ri represents the ith row, that is, the index B1 relative to, bik represents the scale quantity corresponding to the kth column of the ith row, that is, the importance of the ith index relative to the jth index, and n represents the feedback index participating in the scale.

[0090] Further, by obtaining a fuzzy consistency matrix R = (rij) n x n, and performing normalization processing on the matrix R to obtain a factor ordering vector W = (W1, W2,..., Wn) T wherein the W vector satisfies wherein n represents the matrix order, a = (n-1) / 2, and ∑W i = 1.

[0091] For the convenience of understanding, taking the stage of reducing pollution into river basin as an example, the fuzzy consistency matrix and the weight value are shown in Table 2.

[0092] Table 2

[0093] Wherein, the weight value of the feedback index shows the importance degree of the feedback index in the corresponding implementation stage, the greater the weight value, the more important the feedback index, and the weight value of the sub-feedback index is calculated in the same way.

[0094] Step S203, determining the comprehensive weight value of the relative ecological recovery target based on the weight value of the sub-feedback index.

[0095] Specifically, determining the comprehensive weight value of the relative ecological recovery target based on the weight value of the sub-feedback index can include: comparing the weight values of the alternative implementation schemes based on the weight values of the sub-feedback indexes, to obtain the weight values of the alternative implementation schemes; and determining the comprehensive weight value of the relative ecological recovery target based on the weight values of the alternative implementation schemes.

[0096] Wherein, the alternative implementation scheme is at least one of the implementation schemes.

[0097] Wherein, the comprehensive weight value of the sub-feedback index can be determined based on the weight value of the sub-feedback index, and the comprehensive weight value of the alternative implementation scheme relative to the ecological recovery target is calculated in combination with the comprehensive weight value of the sub-feedback index.

[0098] For the convenience of understanding, the calculation method of the comprehensive weight value of the sub-feedback indicators is shown in Table 3, taking the stage of reducing pollution into a river basin as an example. In Table 3, the transparency and odor are the sub-feedback indicators corresponding to the physical indicators of the stage of reducing pollution into a river basin, the COD is the sub-feedback indicator corresponding to the chemical indicators of the stage of reducing pollution into a river basin, the ammonia nitrogen and total phosphorus are the sub-feedback indicators corresponding to the nutrient salt indicators of the stage of reducing pollution into a river basin, and the pipe network density, sewage collection rate, rain and sewage pipe network diversion ratio, domestic sewage treatment rate, and sewage pipe access point of a drainage area are the sub-feedback indicators corresponding to the municipal indicators of the stage of reducing pollution into a river basin.

[0099] Table 3

[0100] For the convenience of understanding, the calculation method of the comprehensive weight value of the sub-feedback indicators is shown in Table 3, taking the stage of reducing pollution into a river basin as an example. In Table 3, the transparency and odor are the sub-feedback indicators corresponding to the physical indicators of the stage of reducing pollution into a river basin, the COD is the sub-feedback indicator corresponding to the chemical indicators of the stage of reducing pollution into a river basin, the ammonia nitrogen and total phosphorus are the sub-feedback indicators corresponding to the nutrient salt indicators of the stage of reducing pollution into a river basin, and the pipe network density, sewage collection rate, rain and sewage pipe network diversion ratio, domestic sewage treatment rate, and sewage pipe access point of a drainage area are the sub-feedback indicators corresponding to the municipal indicators of the stage of reducing pollution into a river basin.

[0101] Table 4

[0102] In step S204, the first importance ranking of the implementation scheme is determined based on the comprehensive weight value.

[0103] The first importance ranking is obtained by ranking the implementation schemes based on the comprehensive weight value of the implementation schemes relative to the ecological recovery target.

[0104] The ecological recovery method of the river basin pollution river provided by the embodiment of the present application can determine the weight value of the feedback indicators and the sub-feedback indicators corresponding to the implementation stage and the weight of the corresponding implementation scheme based on the fuzzy multi-level analysis feedback method. The importance ranking of the implementation scheme in the implementation stage and the weight ranking of the feedback indicators and the sub-feedback indicators are determined, and then the implementation scheme is executed through the importance ranking, and it is examined whether the ecological recovery target is achieved through the weight ranking, the monitoring cost and the treatment cost are reduced, and the stability of the ecological recovery is improved.

[0105] Embodiment 3

[0106] Corresponding to the method embodiments described above, the embodiments of the present application provide a device for ecological recovery of a polluted river in a river basin. FIG. 3 is a structural schematic diagram of a device for ecological recovery of a polluted river in a river basin according to an embodiment of the present application. As shown in FIG. 3, the device for ecological recovery of a polluted river in a river basin can include:

[0107] a state information obtaining module 301 configured to obtain state information of the polluted river.

[0108] a first determining module 302 configured to determine a starting stage and an ecological recovery target based on the state information.

[0109] a second determining module 303 configured to determine a feedback index, a sub-feedback index corresponding to the feedback index, and an implementation scheme corresponding to the starting stage based on the starting stage.

[0110] an importance ranking determining module 304 configured to determine a first importance ranking of the implementation scheme based on the feedback index, the sub-feedback index, and the ecological recovery target.

[0111] a first implementation scheme implementing module 305 configured to implement the implementation scheme according to the first importance ranking, to obtain an implementation result.

[0112] a second implementation scheme implementing module 306 configured to determine a second importance ranking of the implementation scheme based on the implementation result, and implement the implementation scheme according to the second importance ranking, until the starting stage meets the ecological recovery target.

[0113] a third implementation scheme implementing module 307 configured to, if the starting stage is not the last implementation stage of the ecological recovery, implement a next implementation stage after the starting stage, to make the next implementation stage meet a corresponding ecological recovery target.

[0114] The ecological recovery device for the polluted river basin provided by the embodiment of the present application can obtain the state information of the polluted river, determine the implementation starting stage and the ecological recovery target based on the state information, determine the feedback index, the sub-feedback index corresponding to the feedback index and the implementation scheme corresponding to the implementation starting stage based on the implementation starting stage, determine the first importance ranking of the implementation scheme based on the feedback index, the sub-feedback index and the ecological recovery target, implement the implementation scheme according to the first importance ranking, obtain the implementation result, finally determine the second importance ranking of the implementation scheme based on the implementation result, implement the implementation scheme according to the second importance ranking, and implement the next implementation stage after the implementation starting stage until the implementation starting stage meets the ecological recovery target, so that the next implementation stage meets the corresponding ecological recovery target. In this way, the feedback index and the sub-feedback index of different implementation stages can be targeted, the problem can be accurately focused, the monitoring cost and the treatment cost are reduced, and the implementation scheme can be adjusted in real time according to the implementation result, so that the stability of the ecological recovery is improved.

[0115] In some embodiments, the state information includes river water quantity information, river water quality information and river biodiversity information, and the first determination module is further configured to: if the river water quality information is a first type, the implementation starting stage is a stage of reducing pollution into the river basin; if the river water quality information is a second type and no sewage management system is previously set in the river basin, the implementation starting stage is the stage of reducing pollution into the river basin; if the river water quality information is the second type and a sewage management system is previously set in the river basin and a specified index in the river basin does not meet the standard, the implementation starting stage is a stage of rectifying the river in-source pollution; if the river water quality information is the second type and a sewage management system is previously set in the river basin and the river water quantity information is insufficient, the implementation starting stage is a stage of guaranteeing the river ecological base flow; if the river water quality information is the second type and a sewage management system is previously set in the river basin and both the river water quantity information and the river water quality information meet the standard and the river biodiversity information indicates that the river needs to be recovered, the implementation starting stage is a stage of reconstructing the ecological space of the river basin; wherein the first type indicates that the river water quality is between obvious blackening and foul smell and inferior V-type water quality, and the second type indicates that the river water quality is at or better than V-type water quality.

[0116] In some embodiments, the feedback index is multiple, and the importance ranking determination module is further configured to: analyze the feedback index two by two to construct a fuzzy complementary matrix; determine the weight value of the sub-feedback index based on the fuzzy complementary matrix; determine the comprehensive weight value of the relative ecological recovery target based on the weight value of the sub-feedback index; and determine the first importance ranking of the implementation scheme based on the comprehensive weight value.

[0117] In some embodiments, the importance ranking determination module is further configured to determine a weight value of each of the candidate implementation schemes based on a weight value of each of the sub-feedback indicators, and determine a comprehensive weight value of each of the candidate implementation schemes based on the weight value of each of the candidate implementation schemes.

[0118] In some embodiments, the second implementation scheme implementation module is further configured to, if the implementation result indicates that the feedback indicator and / or the sub-feedback indicator is not up to standard, determine a second importance ranking of the implementation scheme based on the feedback indicator and the sub-feedback indicator after implementation of the implementation scheme.

[0119] In some embodiments, the importance ranking determination module is further configured to determine a first weight order of the feedback indicators and a second weight order of the sub-feedback indicators.

[0120] In some embodiments, the first implementation scheme implementation module is configured to, after implementation of the implementation scheme according to the first importance ranking, determine whether the feedback indicators and the sub-feedback indicators are up to standard based on the first weight order and the second weight order, and take the up-to-standard situation of the feedback indicators and the sub-feedback indicators as the implementation result.

[0121] In some embodiments, the implementation stages of the ecological recovery include a pollution reduction into river stage, a river channel endogenous pollution rectification stage, a river ecological base flow guarantee stage and a river basin ecological space reconstruction stage; the implementation scheme corresponding to the pollution reduction into river stage includes network patching, source purification, water channel regulation and bank regulation, and water plant upgrading and quality improvement; the implementation scheme corresponding to the river channel endogenous pollution rectification stage includes pipe network dredging and river channel dredging; the implementation scheme corresponding to the river ecological base flow guarantee stage includes ecological water supplement and reclaimed water supplement; and the implementation scheme corresponding to the river basin ecological space reconstruction stage includes small lake, pond and reservoir rectification, artificial wetland and landscape corridor.

[0122] The device provided by the embodiments of the present application has the same implementation principle, technical effects and the above-mentioned method embodiments. For brevity, the part not mentioned in the device embodiment part can be referred to the corresponding content in the above-mentioned method embodiments.

[0123] Embodiment 4

[0124] The embodiments of the present application further provide an electronic device for running the above-mentioned ecological recovery method of a river basin pollution river; referring to a structural schematic diagram of an electronic device shown in FIG. 4, the electronic device comprises a memory 400 and a processor 401, wherein the memory 400 is configured to store one or more computer instructions, and the one or more computer instructions are executed by the processor 401 to implement the above-mentioned ecological recovery method of a river basin pollution river.

[0125] Further, the electronic device shown in FIG. 4 further includes a bus 402 and a communication interface 403, and the processor 401, the communication interface 403 and the memory 400 are connected through the bus 402.

[0126] The memory 400 can include a high-speed random access memory (RAM) and can further include a non-volatile memory such as at least one disk memory. The communication connection between the system network element and at least one other network element is realized through at least one communication interface 403 (which can be wired or wireless), and the Internet, a wide area network, a local area network, a metropolitan area network, etc. can be used. The bus 402 can be an ISA bus, a PCI bus, an EISA bus, etc. The bus can be divided into an address bus, a data bus, a control bus, etc. For ease of representation, only one bidirectional arrow is shown in FIG. 4, but it does not mean that there is only one bus or only one type of bus.

[0127] The processor 401 can be an integrated circuit chip with signal processing capability. In the implementation process, each step of the above method can be completed by integrated logic circuits of hardware in the processor 401 or instructions in the form of software. The above processor 401 can be a general-purpose processor, including a central processing unit (CPU), a network processor (NP), etc.; it can also be a digital signal processor (DSP), an application specific integrated circuit (ASIC), a field programmable gate array (FPGA) or other programmable logic devices, discrete gates or transistor logic devices, discrete hardware components. Each method, step and logic block disclosed in the embodiment of the present application can be implemented or executed. The general-purpose processor can be a microprocessor or the processor can also be any conventional processor. The steps of the method disclosed in combination with the embodiment of the present application can be directly embodied as a hardware code processor for execution, or a combination of hardware and software modules in the code processor for execution. The software module can be located in a random access memory, a flash memory, a read-only memory, a programmable read-only memory, an electrically erasable programmable memory, a register, etc. The storage medium in the art. The storage medium is located in the memory 400, and the processor 401 reads the information in the memory 400, and combines the hardware to complete the steps of the method of the above embodiment.

[0128] The embodiment of the present application further provides a computer readable storage medium, which stores computer executable instructions, and the computer executable instructions cause the processor to implement the ecological recovery method of the polluted river in a river basin when the computer executable instructions are called and executed by the processor.

[0129] The computer program product for implementing the ecological recovery method of the polluted river in a river basin provided by the embodiment of the present application comprises a computer readable storage medium storing non-volatile program codes executable by the processor, and the program codes comprise instructions for executing the method described in the foregoing method embodiment.

[0130] Those skilled in the art can clearly understand that, for the convenience and brevity of description, the specific working process of the system, device and unit described above can refer to the corresponding process in the foregoing method embodiment, and will not be repeated here.

[0131] In the several embodiments of the present application, it should be understood that the disclosed system, device and method can be implemented in other ways. The device embodiments described above are only schematic. For example, the division of the units is only a logical function division, and there can be another division manner in actual implementation. For example, a plurality of units or components can be combined or integrated into another system, or some features can be ignored or not executed. In addition, the displayed or discussed mutual coupling or direct coupling or communication connection can be indirect coupling or communication connection through some communication interfaces, devices or units, and can be electrical, mechanical or other forms.

[0132] The units described as separate components can or can not be physically separate, and the components displayed as units can or can not be physical units, that is, they can be located in one place, or can be distributed on a plurality of network units. According to actual needs, part or all of the units can be selected to achieve the purpose of the embodiment scheme.

[0133] In addition, each functional unit in each embodiment of the present application can be integrated into a processing unit, or each unit can exist physically independently, or two or more units can be integrated into one unit.

[0134] If the functions are realized in the form of software function units and sold or used as independent products, they can be stored in a nonvolatile computer readable storage medium executable by a processor. Based on this understanding, the technical solutions of the present application or the part of the prior art that essentially contributes or the part of the technical solutions can be embodied in the form of a software product. The computer software product is stored in a storage medium and includes a plurality of instructions for causing a computer device (which can be a personal computer, a server, or a network device, etc.) to execute all or part of the steps of the method described in the various embodiments of the present application. The aforementioned storage medium includes a U disk, a mobile hard disk, a read-only memory (ROM, Read-Only Memory), a random access memory (RAM, Random Access Memory), a magnetic disk or an optical disk, and various media that can store program codes.

[0135] Finally, it should be noted that the above-described embodiments are only specific implementations of the present application, which are used to illustrate the technical solutions of the present application, but not to limit them. The protection scope of the present application is not limited thereto. Although the present application has been described in detail with reference to the foregoing embodiments, those skilled in the art should understand that any person skilled in the art can modify or easily think of changes to the technical solutions described in the foregoing embodiments within the technical scope disclosed by the present application, or make equivalent replacements to some of the technical features. The modifications, changes or replacements do not make the corresponding technical solutions deviate from the spirit and scope of the technical solutions of the embodiments of the present application, and should be covered within the protection scope of the present application. Therefore, the protection scope of the present application should be subject to the protection scope of the claims.

Claims

1. A method of ecological restoration of a polluted river of a river basin, characterized in that, The method comprises: acquiring state information of a polluted river; determining an implementation starting stage and an ecological recovery target based on the state information; determining a feedback index, a sub-feedback index corresponding to the feedback index, and an implementation scheme corresponding to the implementation starting stage based on the implementation starting stage; determining a first importance ranking of the implementation scheme based on the feedback index, the sub-feedback index, and the ecological recovery target; implementing the implementation scheme according to the first importance ranking to obtain an implementation result; determining a second importance ranking of the implementation scheme based on the implementation result, and implementing the implementation scheme according to the second importance ranking until the implementation starting stage meets the ecological recovery target; if the implementation starting stage is not the last implementation stage of ecological recovery, then proceeding to a next implementation stage after the implementation starting stage to make the next implementation stage meet a corresponding ecological recovery target.

2. The method of claim 1, wherein, The state information comprises river water quantity information, river water quality information, and river biodiversity information, and the determination of the implementation starting stage based on the state information comprises: if the river water quality information is of a first category, then the implementation starting stage is a stage of reducing pollution into the river from the river basin; if the river water quality information is of a second category and no sewage management system is previously set in the river basin of the polluted river, then the implementation starting stage is the stage of reducing pollution into the river from the river basin; if the river water quality information is of the second category and a sewage management system is previously set in the river basin of the polluted river and a specified index in the river basin does not meet a standard, then the implementation starting stage is a stage of rectifying in-river source pollution; if the river water quality information is of the second category, a sewage management system is previously set in the river basin of the polluted river, and the river water quantity information is that the river water quantity is insufficient, then the implementation starting stage is a stage of guaranteeing ecological base flow of the river; if the river water quality information is of the second category, a sewage management system is previously set in the river basin of the polluted river, and both the river water quantity information and the river water quality information meet the standards, and the river biodiversity information indicates that the river is to be recovered, then the implementation starting stage is a stage of reconstructing ecological space of the river basin; wherein the first category indicates that the river water quality is between obvious blackening and foul smell and inferior V-class water quality, and the second category indicates that the river water quality is at or better than V-class water quality.

3. The method of claim 1, wherein, The feedback index is multiple, and the determination of the first importance ranking of the implementation scheme based on the feedback index, the sub-feedback index, and the ecological recovery target comprises: constructing a fuzzy complementary matrix by pairwise analysis of the feedback index; determining a weight value of the sub-feedback index based on the fuzzy complementary matrix; determining a comprehensive weight value relative to the ecological recovery target based on the weight value of the sub-feedback index; determining the first importance ranking of the implementation scheme based on the comprehensive weight value.

4. The method of claim 3, wherein, The determination of the comprehensive weight value relative to the ecological recovery target based on the weight value of the sub-feedback index comprises: pairwise comparison of alternative implementation schemes based on the weight value of the sub-feedback index to obtain a weight value of the alternative implementation schemes; Determine a comprehensive weight value relative to the ecological recovery target based on weight values of the alternative implementation schemes.

5. The method of claim 3, wherein, The determining the second importance ranking of the implementation scheme based on the implementation result includes: If the implementation result represents that the feedback indicators and / or the sub-feedback indicators do not meet the standards, determining the second importance ranking of the implementation scheme based on the feedback indicators and the sub-feedback indicators after the implementation of the implementation scheme.

6. The method of claim 1, wherein, Before the implementation of the implementation scheme according to the first importance ranking to obtain the implementation result, the method further includes: Determining a first weight order of the feedback indicators and a second weight order of the sub-feedback indicators; The implementation of the implementation scheme according to the first importance ranking to obtain the implementation result includes: After the implementation of the implementation scheme according to the first importance ranking, checking whether the feedback indicators and the sub-feedback indicators meet the standards based on the first weight order and the second weight order; Taking the meeting standards of the feedback indicators and the sub-feedback indicators as the implementation result.

7. The method according to any one of claims 1 to 6, characterized in that, The implementation stages of ecological recovery include: a stage of reducing pollution into a river in a basin, a stage of rectifying internal source pollution in a river, a stage of guaranteeing ecological base flow of a river, and a stage of reconstructing ecological space in a basin; the implementation scheme corresponding to the stage of reducing pollution into a river in a basin includes: weaving nets into pieces, clearing up the source, dredging water and shore, and upgrading and improving water plants; the implementation scheme corresponding to the stage of rectifying internal source pollution in a river includes: dredging pipes and dredging rivers; the implementation scheme corresponding to the stage of guaranteeing ecological base flow of a river includes: ecological water supplement and recycled water supplement; and the implementation scheme corresponding to the stage of reconstructing ecological space in a basin includes: small lake pond regulation, artificial wetland, and landscape corridor.

8. An ecological restoration device for a polluted river of a river basin, characterized by, The device includes: A state information acquisition module configured to acquire state information of a polluted river; A first determination module configured to determine an implementation starting stage and an ecological recovery target based on the state information; A second determination module configured to determine feedback indicators, sub-feedback indicators corresponding to the feedback indicators, and implementation schemes corresponding to the implementation starting stage based on the implementation starting stage; An importance ranking determination module configured to determine a first importance ranking of the implementation schemes based on the feedback indicators, the sub-feedback indicators, and the ecological recovery target; A first implementation scheme implementation module configured to implement the implementation schemes according to the first importance ranking to obtain implementation results; A second implementation scheme implementation module configured to determine a second importance ranking of the implementation schemes based on the implementation results, and implement the implementation schemes according to the second importance ranking until the implementation starting stage meets the ecological recovery target; A third implementation scheme implementation module configured to, if the implementation starting stage is not the last implementation stage of ecological recovery, proceed to a next implementation stage after the implementation starting stage to make the next implementation stage meet a corresponding ecological recovery target. A state information acquisition module configured to acquire state information of a polluted river; A first determination module configured to determine an implementation starting stage and an ecological recovery target based on the state information; A second determination module configured to determine feedback indicators, sub-feedback indicators corresponding to the feedback indicators, and implementation schemes corresponding to the implementation starting stage based on the implementation starting stage; An importance ranking determination module configured to determine a first importance ranking of the implementation schemes based on the feedback indicators, the sub-feedback indicators, and the ecological recovery target; A first implementation scheme implementation module configured to implement the implementation schemes according to the first importance ranking to obtain implementation results; A second implementation scheme implementation module configured to determine a second importance ranking of the implementation schemes based on the implementation results, and implement the implementation schemes according to the second importance ranking until the implementation starting stage meets the ecological recovery target; A third implementation scheme implementation module configured to, if the implementation starting stage is not the last implementation stage of ecological recovery, proceed to a next implementation stage after the implementation starting stage to make the next implementation stage meet a corresponding ecological recovery target.

9. An electronic device, comprising: A computer readable storage medium storing computer executable instructions that, when called and executed by a processor, cause the processor to implement the method of ecological restoration of a polluted river basin of any one of claims 1 to 7.

10. A computer-readable storage medium, characterized in that, The computer readable storage medium stores computer executable instructions that, when called and executed by a processor, cause the processor to implement the method of ecological restoration of a polluted river basin of any one of claims 1 to 7.

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