CN113269395A - Water environment risk pre-judging method and system based on pressure state feedback framework - Google Patents
Water environment risk pre-judging method and system based on pressure state feedback framework Download PDFInfo
- Publication number
- CN113269395A CN113269395A CN202110411022.7A CN202110411022A CN113269395A CN 113269395 A CN113269395 A CN 113269395A CN 202110411022 A CN202110411022 A CN 202110411022A CN 113269395 A CN113269395 A CN 113269395A
- Authority
- CN
- China
- Prior art keywords
- water environment
- risk
- environment risk
- evaluation
- evaluation index
- Prior art date
- Legal status (The legal status is an assumption and is not a legal conclusion. Google has not performed a legal analysis and makes no representation as to the accuracy of the status listed.)
- Pending
Links
- XLYOFNOQVPJJNP-UHFFFAOYSA-N water Substances O XLYOFNOQVPJJNP-UHFFFAOYSA-N 0.000 title claims abstract description 133
- 238000000034 method Methods 0.000 title claims abstract description 38
- 238000011156 evaluation Methods 0.000 claims abstract description 119
- 239000011159 matrix material Substances 0.000 claims abstract description 18
- XKMRRTOUMJRJIA-UHFFFAOYSA-N ammonia nh3 Chemical compound N.N XKMRRTOUMJRJIA-UHFFFAOYSA-N 0.000 claims description 9
- 230000007246 mechanism Effects 0.000 claims description 7
- OAICVXFJPJFONN-UHFFFAOYSA-N Phosphorus Chemical compound [P] OAICVXFJPJFONN-UHFFFAOYSA-N 0.000 claims description 5
- QVGXLLKOCUKJST-UHFFFAOYSA-N atomic oxygen Chemical compound [O] QVGXLLKOCUKJST-UHFFFAOYSA-N 0.000 claims description 5
- 238000004364 calculation method Methods 0.000 claims description 5
- 229910052760 oxygen Inorganic materials 0.000 claims description 5
- 239000001301 oxygen Substances 0.000 claims description 5
- 229910052698 phosphorus Inorganic materials 0.000 claims description 5
- 239000011574 phosphorus Substances 0.000 claims description 5
- 230000008569 process Effects 0.000 claims description 5
- 238000004590 computer program Methods 0.000 claims description 4
- 238000005192 partition Methods 0.000 claims description 4
- 238000004422 calculation algorithm Methods 0.000 description 12
- 241000728173 Sarima Species 0.000 description 9
- 238000012360 testing method Methods 0.000 description 7
- 238000012549 training Methods 0.000 description 7
- 230000007613 environmental effect Effects 0.000 description 5
- 230000002550 fecal effect Effects 0.000 description 5
- 230000006870 function Effects 0.000 description 5
- 238000004458 analytical method Methods 0.000 description 4
- 238000004140 cleaning Methods 0.000 description 4
- 238000013178 mathematical model Methods 0.000 description 4
- 238000012544 monitoring process Methods 0.000 description 4
- 239000010865 sewage Substances 0.000 description 4
- 241000588724 Escherichia coli Species 0.000 description 3
- 230000009286 beneficial effect Effects 0.000 description 3
- 238000004088 simulation Methods 0.000 description 3
- IJGRMHOSHXDMSA-UHFFFAOYSA-N Atomic nitrogen Chemical compound N#N IJGRMHOSHXDMSA-UHFFFAOYSA-N 0.000 description 2
- 238000010219 correlation analysis Methods 0.000 description 2
- 230000000694 effects Effects 0.000 description 2
- 239000003344 environmental pollutant Substances 0.000 description 2
- 238000005457 optimization Methods 0.000 description 2
- 231100000719 pollutant Toxicity 0.000 description 2
- 230000003068 static effect Effects 0.000 description 2
- 238000012795 verification Methods 0.000 description 2
- 239000004912 1,5-cyclooctadiene Substances 0.000 description 1
- 230000002159 abnormal effect Effects 0.000 description 1
- 230000001133 acceleration Effects 0.000 description 1
- 230000015572 biosynthetic process Effects 0.000 description 1
- 230000001413 cellular effect Effects 0.000 description 1
- 238000011161 development Methods 0.000 description 1
- 238000010586 diagram Methods 0.000 description 1
- 238000009792 diffusion process Methods 0.000 description 1
- 238000005516 engineering process Methods 0.000 description 1
- 230000006872 improvement Effects 0.000 description 1
- 238000012986 modification Methods 0.000 description 1
- 230000004048 modification Effects 0.000 description 1
- 229910052757 nitrogen Inorganic materials 0.000 description 1
- 238000012545 processing Methods 0.000 description 1
- 230000009467 reduction Effects 0.000 description 1
- 238000012216 screening Methods 0.000 description 1
- 238000010187 selection method Methods 0.000 description 1
- 239000007787 solid Substances 0.000 description 1
- 238000007619 statistical method Methods 0.000 description 1
- 239000013589 supplement Substances 0.000 description 1
- 239000002352 surface water Substances 0.000 description 1
- 230000001360 synchronised effect Effects 0.000 description 1
- 238000003786 synthesis reaction Methods 0.000 description 1
- 238000012876 topography Methods 0.000 description 1
Images
Classifications
-
- G—PHYSICS
- G06—COMPUTING; CALCULATING OR COUNTING
- G06Q—INFORMATION AND COMMUNICATION TECHNOLOGY [ICT] SPECIALLY ADAPTED FOR ADMINISTRATIVE, COMMERCIAL, FINANCIAL, MANAGERIAL OR SUPERVISORY PURPOSES; SYSTEMS OR METHODS SPECIALLY ADAPTED FOR ADMINISTRATIVE, COMMERCIAL, FINANCIAL, MANAGERIAL OR SUPERVISORY PURPOSES, NOT OTHERWISE PROVIDED FOR
- G06Q10/00—Administration; Management
- G06Q10/06—Resources, workflows, human or project management; Enterprise or organisation planning; Enterprise or organisation modelling
- G06Q10/063—Operations research, analysis or management
- G06Q10/0635—Risk analysis of enterprise or organisation activities
-
- G—PHYSICS
- G06—COMPUTING; CALCULATING OR COUNTING
- G06Q—INFORMATION AND COMMUNICATION TECHNOLOGY [ICT] SPECIALLY ADAPTED FOR ADMINISTRATIVE, COMMERCIAL, FINANCIAL, MANAGERIAL OR SUPERVISORY PURPOSES; SYSTEMS OR METHODS SPECIALLY ADAPTED FOR ADMINISTRATIVE, COMMERCIAL, FINANCIAL, MANAGERIAL OR SUPERVISORY PURPOSES, NOT OTHERWISE PROVIDED FOR
- G06Q10/00—Administration; Management
- G06Q10/06—Resources, workflows, human or project management; Enterprise or organisation planning; Enterprise or organisation modelling
- G06Q10/063—Operations research, analysis or management
- G06Q10/0639—Performance analysis of employees; Performance analysis of enterprise or organisation operations
- G06Q10/06393—Score-carding, benchmarking or key performance indicator [KPI] analysis
-
- G—PHYSICS
- G06—COMPUTING; CALCULATING OR COUNTING
- G06Q—INFORMATION AND COMMUNICATION TECHNOLOGY [ICT] SPECIALLY ADAPTED FOR ADMINISTRATIVE, COMMERCIAL, FINANCIAL, MANAGERIAL OR SUPERVISORY PURPOSES; SYSTEMS OR METHODS SPECIALLY ADAPTED FOR ADMINISTRATIVE, COMMERCIAL, FINANCIAL, MANAGERIAL OR SUPERVISORY PURPOSES, NOT OTHERWISE PROVIDED FOR
- G06Q50/00—Information and communication technology [ICT] specially adapted for implementation of business processes of specific business sectors, e.g. utilities or tourism
- G06Q50/10—Services
- G06Q50/26—Government or public services
Landscapes
- Business, Economics & Management (AREA)
- Human Resources & Organizations (AREA)
- Engineering & Computer Science (AREA)
- Economics (AREA)
- Strategic Management (AREA)
- Tourism & Hospitality (AREA)
- Development Economics (AREA)
- Educational Administration (AREA)
- Entrepreneurship & Innovation (AREA)
- General Physics & Mathematics (AREA)
- Marketing (AREA)
- Physics & Mathematics (AREA)
- General Business, Economics & Management (AREA)
- Theoretical Computer Science (AREA)
- Operations Research (AREA)
- Quality & Reliability (AREA)
- Game Theory and Decision Science (AREA)
- Health & Medical Sciences (AREA)
- General Health & Medical Sciences (AREA)
- Primary Health Care (AREA)
- Management, Administration, Business Operations System, And Electronic Commerce (AREA)
Abstract
The invention relates to the technical field of water environment risk evaluation, in particular to a water environment risk pre-judging method and a water environment risk pre-judging system based on a pressure state feedback frame, wherein the method comprises the following steps: collecting historical data of the water environment risk of the river network area, and constructing an evaluation index system of the water environment risk of the river network area with a hierarchical structure relationship based on the historical data; calculating the weight of each evaluation index in the risk evaluation index system, calculating the membership degree of each evaluation index in the evaluation index system to the evaluation level, establishing a fuzzy relation matrix based on the membership degree, and determining the final evaluation result of the evaluation index based on the fuzzy relation matrix; under a pressure state feedback frame, determining an evaluation result of the water environment risk of the river network area, obtaining a risk regulation and control suggestion based on the evaluation result of the water environment risk of the river network area, and carrying out scene water environment risk pre-judgment.
Description
Technical Field
The invention relates to the technical field of water environment risk evaluation, in particular to a water environment risk pre-judging method and system based on a pressure state feedback framework.
Background
With the rapid development of social economy, industry and agriculture and the continuous acceleration of urbanization process, the environmental pressure of each region is increased day by day, and the environmental awareness of people is gradually enhanced. With the wide operation of risk evaluation concepts in various industries, water environment risk evaluation gradually enters the public field of vision. At present, common water environment risk evaluation methods include a graph superposition method, an information diffusion method, an index system method, fuzzy mathematics synthesis and the like. The water environment risk evaluation index system is an important step of water environment risk evaluation, most of the existing water environment risk evaluation index systems adopt static index systems, and an index system considering water quality prediction of a river network under a risk dynamic regulation strategy is lacked. The commonly used mathematical model for predicting the water quality of the river network mainly comprises two categories: a water quality mechanism mathematical model and a water quality data driving class mathematical model.
Most of river network water quality mathematical models adopted by the existing water environment risk evaluation adopt a single static model to predict water quality, and the applicability and the simulation precision in practical application are to be improved.
Disclosure of Invention
The invention aims to provide a water environment risk pre-judging method and system based on a pressure state feedback framework, which are used for solving one or more technical problems in the prior art and at least provide a beneficial selection or creation condition.
In order to achieve the purpose, the invention provides the following technical scheme:
a water environment risk pre-judging method based on a pressure state feedback framework comprises the following steps:
s100, collecting historical data of the water environment risk of the river network area, and constructing an evaluation index system of the water environment risk of the river network area with a hierarchical structure relationship based on the historical data;
s200, calculating the membership degree of each evaluation index in the evaluation index system to the evaluation grade, establishing a fuzzy relation matrix based on the membership degree, and determining the final evaluation result of the evaluation index based on the fuzzy relation matrix;
step S300, determining an evaluation result of the water environment risk of the river network area under a pressure state feedback framework, obtaining a risk regulation and control suggestion based on the evaluation result of the water environment risk of the river network area, and performing scene water environment risk pre-judgment.
Further, the historical data of the water environment risk in the river network area comprises: sample ammonia nitrogen, total phosphorus, dissolved oxygen, and permanganate index.
Further, the evaluation index system of the water environment risk in the river network area consists of a target layer, a standard layer and an index layer.
Further, in step S100, the constructing an evaluation index system of the water environment risk of the river network region with a hierarchical structure relationship based on the historical data includes:
and determining the weight of each evaluation index in the risk evaluation index system by using an analytic hierarchy process, and constructing a hierarchical structure relationship according to the weight and the membership of each evaluation index.
Further, the step S200 includes:
step S210, performing membership calculation on each evaluation index to obtain the membership of each evaluation index, wherein the evaluation indexes are divided into a reverse index and a forward index;
s220, establishing an index system according to each level relation of the index system, and establishing a fuzzy relation matrix according to the membership degree of each evaluation index;
and step S230, sequentially performing primary and secondary evaluation according to the weight of each evaluation index and the fuzzy relation matrix, and taking the risk grade determined according to the maximum membership rule as the final evaluation result of the evaluation index.
Further, the step S300 includes:
s310, determining the source intensity of a river network area under a pressure state feedback frame;
s320, predicting index values of an evaluation index system by adopting a prediction model system of the water environment risk of the river network area;
and S330, establishing a risk engineering regulation measure according to the water environment risk evaluation leading factor of the river network area, the river network risk grade division and the partition.
Further, the prediction model system of the river network area water environment risk comprises a data driving model, a combined model and a mechanism model.
A computer-readable storage medium, wherein a water environment risk pre-judging program based on a pressure state feedback framework is stored on the computer-readable storage medium, and when being executed by a processor, the water environment risk pre-judging program based on the pressure state feedback framework realizes the steps of the water environment risk pre-judging method based on the pressure state feedback framework as described in any one of the above.
A water environment risk prediction system based on a pressure state feedback framework, the system comprising:
at least one processor;
at least one memory for storing at least one program;
when the at least one program is executed by the at least one processor, the at least one processor is enabled to implement any one of the methods for predicting risk of aquatic environment based on the pressure state feedback framework.
The invention has the beneficial effects that: the invention discloses a water environment risk pre-judging method and a water environment risk pre-judging system based on a pressure state feedback frame.
Drawings
In order to more clearly illustrate the embodiments of the present invention or the technical solutions in the prior art, the drawings needed to be used in the embodiments will be briefly described below, and it is obvious that the drawings in the following description are only some embodiments of the present invention, and it is obvious for those skilled in the art to obtain other drawings without inventive exercise.
FIG. 1 is a schematic flow chart of a water environment risk prediction method based on a pressure state feedback framework in an embodiment of the invention;
FIG. 2 is a schematic flow chart of a water environment risk evaluation method in an embodiment of the invention;
fig. 3 is a schematic structural diagram of a prediction model system for water environment risk in river network areas in the embodiment of the invention.
Detailed Description
The conception, specific structure and technical effects of the present application will be described clearly and completely with reference to the following embodiments and the accompanying drawings, so that the purpose, scheme and effects of the present application can be fully understood. It should be noted that the embodiments and features of the embodiments in the present application may be combined with each other without conflict.
Referring to fig. 1 and fig. 2, as shown in fig. 1, a method for predicting water environment risk based on a pressure state feedback framework according to an embodiment of the present application is provided, where the method includes the following steps:
s100, collecting historical data of the water environment risk of the river network area, and constructing an evaluation index system of the water environment risk of the river network area with a hierarchical structure relationship based on the historical data;
s200, calculating the membership degree of each evaluation index in the evaluation index system to the evaluation grade, establishing a fuzzy relation matrix based on the membership degree, and determining the final evaluation result of the evaluation index based on the fuzzy relation matrix;
step S300, determining an evaluation result of the water environment risk of the river network area under a pressure state feedback framework, obtaining a risk regulation and control suggestion based on the evaluation result of the water environment risk of the river network area, and performing scene water environment risk pre-judgment.
In the embodiment provided by the invention, under a pressure state feedback frame, according to the analysis of the water environment pressure and state, a fuzzy comprehensive evaluation method is adopted, a water quality data drive model and a water quality mechanism model are combined for water quality prediction, and a river network area water environment risk evaluation system is used as a dynamic whole organically combined by identification, analysis and regulation, so that a comprehensive dynamic water environment risk evaluation method is constructed, the early warning of the area water environment risk level is realized, and the risk evaluation of the water environment with the water environment risk level can be carried out through a risk regulation strategy in a dynamic regulation and control mode.
In a preferred embodiment, the historical data of the water environment risk in the river network area comprises: sample ammonia nitrogen, total phosphorus, dissolved oxygen, and permanganate index.
In a preferred embodiment, the evaluation index system for the water environment risk in the river network area consists of a target layer, a criterion layer and an index layer.
As an improvement of the above embodiment, in step S100, the constructing an evaluation index system of the water environment risk of the river network region with a hierarchical structure relationship based on the historical data includes:
and determining the weight of each evaluation index in the risk evaluation index system by using an analytic hierarchy process, and constructing a hierarchical structure relationship according to the weight and the membership of each evaluation index.
Specifically, the indexes at the same level are compared pairwise by using an analytic hierarchy process according to the hierarchical structure relationship of an index system, the relative importance of the indexes is determined according to the 1-9 scale meanings, and a judgment matrix is constructed. And calculating the ratio of the index layer to the standard layer and the ratio of the standard layer to the target layer by adopting a geometric mean method, sharing a secondary weight value, and expressing the secondary weight value in a vector form. And finally, carrying out consistency check on the calculation result, and ensuring that the critical ratio is less than 0.1, namely judging that the matrix has better transitivity and consistency.
As a modification of the above embodiment, the step S200 includes:
step S210, performing membership calculation on each evaluation index to obtain the membership of each evaluation index, wherein the evaluation indexes are divided into a reverse index and a forward index, and the membership calculation mode of the evaluation indexes is as follows:
for the reverse index, the smaller the index value, the higher the water environment risk:
when x isi>ci,1When r isi,1=1,ri,2=ri,3=…=ri,K=0;
When c is going toi,k≥xi≥ci,k+1When the temperature of the water is higher than the set temperature,
when x isi<ci,KWhen r isi,1=ri,2=…=ri,K-1=0,ri,K=1;
For the forward index, the larger the index value, the higher the water environment risk:
when x isi<ci,1When r isi,1=1,ri,2=ri,3=…=ri,K=0;
When x isi>ci,KWhen r isi,1=ri,2=…=ri,K-1=0,ri,K=1;
Wherein x isiIs the index value of the i-th term, ci,kEvaluation criterion of the kth order of the i-th index, ri,kRepresenting the relative membership degree of the i index to the k level risk degree, N being the evaluation risk, etcThe number of indexes in the grade, K is the grade number of the evaluation risk degree, ai,kThe K-th level evaluation standard of the i-th index is expressed, and K belongs to [1, K ]]。
S220, establishing an index system according to each level relation of the index system, and establishing a fuzzy relation matrix according to the membership degree of each evaluation index;
wherein the fuzzy relation matrix is represented as:
and step S230, sequentially performing primary and secondary evaluation according to the weight of each evaluation index and the fuzzy relation matrix, and taking the risk grade determined according to the maximum membership rule as the final evaluation result of the evaluation index.
Specifically, the final evaluation result of the evaluation index is calculated according to the following formula:
Bi=WiRi=(bi1,bi2,…,biK)
B=WR=(b1,b2,…,bK)
wherein, biIn order to obtain the membership degree of the evaluation index to the ith grade and W is the weight of each evaluation index, in the embodiment provided by the invention, since the risk evaluation index system of the river network area water environment is divided into 3 layers, so that n is 3, and max { b is takeniAnd (6) taking the corresponding risk grade as a final evaluation result of the evaluation index.
In a preferred embodiment, the step S300 includes:
s310, determining the source intensity of a river network area under a pressure state feedback frame;
s320, predicting index values of an evaluation index system by adopting a prediction model system of the water environment risk of the river network area;
referring to fig. 3, in a preferred embodiment, the prediction model system of the river network region water environmental risk includes a data-driven model, a combined model and a mechanism model.
In a preferred embodiment, the data-driven model is determined by:
data cleaning: performing data cleaning on historical data; the step of cleaning the historical data refers to cleaning the water quality data, eliminating abnormal data and mastering the index time sequence correlation of a risk evaluation index system by using a basic statistical method and correlation analysis, so that the prediction precision is improved.
Calculating a correlation coefficient: calculating a correlation coefficient by adopting a Pearson method;
training a model: randomly splitting the washed historical data into two unequal parts, wherein more parts of data are used as training sets, and less parts of data are used as test sets; respectively establishing SARIMA and LSTM algorithm models in a training set; and (4) acting the model on the test set, feeding back the test result in real time and carrying out continuous model optimization.
In a preferred embodiment, the combined model is formed by performing optimized combination based on SARIMA and LSTM algorithm models; specifically, the combined model is determined by:
respectively calculating predicted values obtained by the SARIMA algorithm model, the LSTM algorithm model and the combined model, and taking a model with the minimum average error rate and the minimum root mean square error of the predicted values and actual values as an optimal prediction model;
selecting the optimal prediction model refers to respectively calculating predicted values obtained by the SARIMA algorithm model, the LSTM algorithm model and the combined model, selecting the optimal prediction model according to the average error rate and the root mean square error of the predicted values and the actual values, wherein the smaller the average error rate and the root mean square error of the predicted values and the actual values of the model are, the better the model is.
The average error rate is calculated as:
the root mean square error is calculated as:
wherein: xi represents the model predicted value, Yi represents the actual predicted value, and n represents the total number of predicted values.
The mechanism model is a one-dimensional river network hydrodynamic water quality model established by using data of the terrain, water level, flow and water quality of a river network through parameter adjustment and verification.
And S330, establishing a risk engineering regulation measure according to the water environment risk evaluation leading factor of the river network area, the river network risk grade division and the partition.
In this embodiment, the pressure, state, and feedback under the pressure state feedback frame are finally determined.
The pressure is obtained by carrying out strong accounting on the source of the river network area according to the current situation and the risk engineering regulation and control measures;
the states are: predicting an index value of a risk evaluation index system of the water environment of the river network region under the pressure;
the feedback is as follows: and (3) according to the water environment risk evaluation leading factors of the river network region, the classification of the river network risk grades and the partition establishment of risk engineering regulation and control measures, wherein the risk engineering regulation and control measures comprise the steps of upgrading and emission reduction, discharge port optimization, ecological water supplement and gate dam regulation and control.
In this embodiment, starting from index data of a water environment risk evaluation index system in a river network region, three models, namely a SARIMA algorithm, an LSTM algorithm, a combination model and a one-dimensional river network hydrodynamic water quality model, are established from water quality monitoring data and a motion mechanism direction of pollutants in the water environment respectively, and indexes of the water environment risk evaluation index system in different river network regions are predicted, so that the river network region water environment risk evaluation index system is used as a dynamic whole organically combined by recognition, analysis and regulation, and a comprehensive system dynamic water environment risk evaluation method is formed. Aiming at indexes (such as dissolved oxygen, nitrogen, phosphorus and COD) of the water environment risk evaluation index system in different river network regions, SARIMA (software development technology), LSTM (least squares) algorithm and combined model simulation are applied, the prediction precision is dynamically tracked, an index optimal prediction model is adjusted, a one-dimensional river network hydrodynamic water quality model under the risk engineering regulation and control measures is established, and the prediction and prediction pre-judgment precision of the water environment risk evaluation in the river network regions can be effectively improved.
The following is a specific embodiment of the present invention:
according to the water quality data of a monitored cross section of a river in Changzhou city on a day of 2019, after water quality index damage and correlation analysis, water temperature and PH have no obvious influence on the environmental risk of river water, and no obvious correlation exists among indexes, primary index screening is carried out, then a fuzzy comprehensive evaluation method is adopted, and no risk (not monitored), extremely low risk (deviation degree of 50%), low risk (deviation degree of 30%)), moderate risk (deviation degree of 0)), high risk (deviation degree of-30%) and extremely high risk (deviation degree of-50%) are formulated according to the surface water environmental quality standard and the water quality standard deviation degree, the cross section water quality standard is a level II standard, the final water environment risk of the cross section is determined to be extremely high risk, and the risk leading factors are fecal colibacillus and ammonia nitrogen.
Table 1: index weight and fuzzy matrix in index system for water environment risk evaluation
According to the water quality data of a certain monitoring section of the river in Changzhou city in 2018 and 2020, historical data (daily average value) such as ammonia nitrogen, total phosphorus, dissolved oxygen and permanganate index of a sample are divided into 300 records in a training set, and 128 records in a testing set; respectively establishing prediction models of SARIMA and LSTM algorithms of each evaluation index of the monitoring section by using a training set, and continuously carrying out model training until the test prediction error rate is less than 30%; performing test verification based on the test set, and respectively calculating the root mean square error and the average error rate of the SARIMA, the LSTM algorithm model and the combined model by adopting an optimal prediction model selection method to obtain an optimal model of the specific index of the monitoring section; and dynamically tracking the prediction precision, analyzing the stability of the model, training the model of a new sample when the average error rate is not less than 30%, and dynamically adjusting the optimal prediction model.
According to the topography, the synchronous water level, the flow and the water quality data of the river network area where the river is located in Changzhou city, a one-dimensional river network hydrodynamic water quality model is established, the average error of the model simulation flow is 10%, and the water quality rate error is within 30%.
When the water environment risk is predicted under the conventional strong source pressure, the SARIMA, LSTM algorithm model and the combined model optimal model are adopted for prediction, the index value of the water environment risk evaluation index system is dynamically updated, the water environment risk of the section is predicted in the next 1 day, and the risk is reduced to high risk. The risk leading factors are fecal coliform and ammonia nitrogen. According to the source tracing analysis of pollutants, fecal escherichia coli and ammonia nitrogen exceeding standards are possibly influenced by sewage discharge of a sewage treatment plant, the emission standard of fecal escherichia coli and ammonia nitrogen of the sewage treatment plant is improved, and the emission amount of fecal escherichia coli and ammonia nitrogen discharged from a sewage treatment plant into a river is reduced through accounting. Under the strong pressure of the risk engineering regulation and control measure source, a one-dimensional river network hydrodynamic water quality model is adopted for prediction, the index value of the water environment risk evaluation index system is dynamically updated, the water environment risk of the section is predicted under the risk engineering regulation and control measure, and the specific risk engineering regulation and control measure is determined.
Corresponding to the method of fig. 1, an embodiment of the present invention further provides a computer-readable storage medium, where a water environment risk pre-judging program based on a pressure state feedback framework is stored on the computer-readable storage medium, and when the water environment risk pre-judging program based on the pressure state feedback framework is executed by a processor, the steps of the water environment risk pre-judging method based on the pressure state feedback framework as described in any one of the above embodiments are implemented.
Corresponding to the method in fig. 1, an embodiment of the present invention further provides a water environment risk pre-determination system based on a pressure state feedback framework, where the system includes:
at least one processor;
at least one memory for storing at least one program;
when the at least one program is executed by the at least one processor, the at least one processor is enabled to implement the method for predicting risk of aquatic environment based on the pressure state feedback framework according to any of the embodiments.
The contents in the above method embodiments are all applicable to the present system embodiment, the functions specifically implemented by the present system embodiment are the same as those in the above method embodiment, and the beneficial effects achieved by the present system embodiment are also the same as those achieved by the above method embodiment.
The Processor may be a Central-Processing Unit (CPU), other general-purpose Processor, a Digital Signal Processor (DSP), an Application-Specific-Integrated-Circuit (ASIC), a Field-Programmable Gate array (FPGA) or other Programmable logic device, a discrete Gate or transistor logic device, a discrete hardware component, or the like. The general processor can be a microprocessor or the processor can be any conventional processor and the like, the processor is a control center of the water environment risk pre-judging system based on the pressure state feedback framework, and various interfaces and lines are utilized to connect various parts of the operable device of the whole water environment risk pre-judging system based on the pressure state feedback framework.
The memory can be used for storing the computer program and/or the module, and the processor can realize various functions of the water environment risk pre-judging system based on the pressure state feedback framework by operating or executing the computer program and/or the module stored in the memory and calling the data stored in the memory. The memory may mainly include a storage program area and a storage data area, wherein the storage program area may store an operating system, an application program required by at least one function (such as a sound playing function, an image playing function, etc.), and the like; the storage data area may store data (such as audio data, a phonebook, etc.) created according to the use of the cellular phone, and the like. In addition, the memory may include high speed random access memory, and may also include non-volatile memory, such as a hard disk, a memory, a plug-in hard disk, a Smart-Media-Card (SMC), a Secure-Digital (SD) Card, a Flash-memory Card (Flash-Card), at least one magnetic disk storage device, a Flash memory device, or other volatile solid state storage device.
While the description of the present application has been made in considerable detail and with particular reference to a few illustrated embodiments, it is not intended to be limited to any such details or embodiments or any particular embodiments, but it is to be construed that the present application effectively covers the intended scope of the application by reference to the appended claims, which are interpreted in view of the broad potential of the prior art. Further, the foregoing describes the present application in terms of embodiments foreseen by the inventor for which an enabling description was available, notwithstanding that insubstantial changes from the present application, not presently foreseen, may nonetheless represent equivalents thereto.
Claims (9)
1. A water environment risk pre-judging method based on a pressure state feedback framework is characterized by comprising the following steps:
s100, collecting historical data of the water environment risk of the river network area, and constructing an evaluation index system of the water environment risk of the river network area with a hierarchical structure relationship based on the historical data;
s200, calculating the membership degree of each evaluation index in the evaluation index system to the evaluation grade, establishing a fuzzy relation matrix based on the membership degree, and determining the final evaluation result of the evaluation index based on the fuzzy relation matrix;
step S300, determining an evaluation result of the water environment risk of the river network area under a pressure state feedback framework, obtaining a risk regulation and control suggestion based on the evaluation result of the water environment risk of the river network area, and performing scene water environment risk pre-judgment.
2. The method for predicting water environment risk based on the pressure state feedback framework as claimed in claim 1, wherein the historical data of the water environment risk in the river network area comprises: sample ammonia nitrogen, total phosphorus, dissolved oxygen, and permanganate index.
3. The method for pre-judging water environment risk based on the pressure state feedback framework as claimed in claim 2, wherein the evaluation index system of water environment risk in river network area is composed of a target layer, a standard layer and an index layer.
4. The method as claimed in claim 3, wherein in step S100, the step of constructing an evaluation index system of the water environment risk of the river network region with a hierarchical structure relationship based on the historical data includes:
and determining the weight of each evaluation index in the risk evaluation index system by using an analytic hierarchy process, and constructing a hierarchical structure relationship according to the weight and the membership of each evaluation index.
5. The method for predicting water environment risk based on pressure state feedback framework according to claim 4, wherein the step S200 comprises:
step S210, performing membership calculation on each evaluation index to obtain the membership of each evaluation index, wherein the evaluation indexes are divided into a reverse index and a forward index;
s220, establishing an index system according to each level relation of the index system, and establishing a fuzzy relation matrix according to the membership degree of each evaluation index;
and step S230, sequentially performing primary and secondary evaluation according to the weight of each evaluation index and the fuzzy relation matrix, and taking the risk grade determined according to the maximum membership rule as the final evaluation result of the evaluation index.
6. The method for predicting water environment risk based on pressure state feedback framework according to claim 5, wherein the step S300 comprises:
s310, determining the source intensity of a river network area under a pressure state feedback frame;
s320, predicting index values of an evaluation index system by adopting a prediction model system of the water environment risk of the river network area;
and S330, establishing a risk engineering regulation measure according to the water environment risk evaluation leading factor of the river network area, the river network risk grade division and the partition.
7. The method for predicting water environment risk based on the pressure state feedback framework as claimed in claim 6, wherein the model system for predicting water environment risk in the river network region comprises a data-driven model, a combined model and a mechanism model.
8. A computer-readable storage medium, wherein a computer program is stored on the computer-readable storage medium, and when being executed by a processor, the computer program implements the steps of the method for predicting water environment risk based on pressure state feedback framework according to any one of claims 1 to 7.
9. A water environment risk pre-judging system based on a pressure state feedback framework is characterized by comprising:
at least one processor;
at least one memory for storing at least one program;
when the at least one program is executed by the at least one processor, the at least one processor may implement the method for predicting risk of aquatic environment according to any one of claims 1 to 7 based on the pressure state feedback framework.
Priority Applications (1)
Application Number | Priority Date | Filing Date | Title |
---|---|---|---|
CN202110411022.7A CN113269395A (en) | 2021-04-16 | 2021-04-16 | Water environment risk pre-judging method and system based on pressure state feedback framework |
Applications Claiming Priority (1)
Application Number | Priority Date | Filing Date | Title |
---|---|---|---|
CN202110411022.7A CN113269395A (en) | 2021-04-16 | 2021-04-16 | Water environment risk pre-judging method and system based on pressure state feedback framework |
Publications (1)
Publication Number | Publication Date |
---|---|
CN113269395A true CN113269395A (en) | 2021-08-17 |
Family
ID=77228821
Family Applications (1)
Application Number | Title | Priority Date | Filing Date |
---|---|---|---|
CN202110411022.7A Pending CN113269395A (en) | 2021-04-16 | 2021-04-16 | Water environment risk pre-judging method and system based on pressure state feedback framework |
Country Status (1)
Country | Link |
---|---|
CN (1) | CN113269395A (en) |
Cited By (2)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
CN113959499A (en) * | 2021-11-03 | 2022-01-21 | 中国海洋大学 | Deep-sea mining ecological environment in-situ long-term automatic monitoring station and evaluation method thereof |
CN116070886A (en) * | 2023-04-04 | 2023-05-05 | 水利部交通运输部国家能源局南京水利科学研究院 | Multidimensional adaptive regulation and control method and system for water resource system |
Citations (4)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
CN106021946A (en) * | 2016-05-30 | 2016-10-12 | 北京师范大学 | Risk fuzzy synthetic evaluation method for regional water environment |
CN106846178A (en) * | 2017-02-13 | 2017-06-13 | 水利部交通运输部国家能源局南京水利科学研究院 | A kind of river type water head site comprehensive safety evaluation method |
KR20170131047A (en) * | 2016-05-20 | 2017-11-29 | 고려대학교 산학협력단 | A method for calculating environment risk index affecting chemical accident |
CN110851768A (en) * | 2019-11-13 | 2020-02-28 | 四川大学 | Multilayer fuzzy evaluation method for barrier lake |
-
2021
- 2021-04-16 CN CN202110411022.7A patent/CN113269395A/en active Pending
Patent Citations (4)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
KR20170131047A (en) * | 2016-05-20 | 2017-11-29 | 고려대학교 산학협력단 | A method for calculating environment risk index affecting chemical accident |
CN106021946A (en) * | 2016-05-30 | 2016-10-12 | 北京师范大学 | Risk fuzzy synthetic evaluation method for regional water environment |
CN106846178A (en) * | 2017-02-13 | 2017-06-13 | 水利部交通运输部国家能源局南京水利科学研究院 | A kind of river type water head site comprehensive safety evaluation method |
CN110851768A (en) * | 2019-11-13 | 2020-02-28 | 四川大学 | Multilayer fuzzy evaluation method for barrier lake |
Non-Patent Citations (9)
Title |
---|
俞永梅;张怀春;: "上海市水资源生态风险评价及驱动因素分析", 人民长江, no. 15, pages 86 - 89 * |
周林飞;许士国;孙万光;: "基于压力-状态-响应模型的扎龙湿地健康水循环评价研究", 水科学进展, no. 02, 15 March 2008 (2008-03-15), pages 205 - 213 * |
周林飞;许士国;孙万光;: "基于压力-状态-响应模型的扎龙湿地健康水循环评价研究", 水科学进展, no. 02, pages 205 - 213 * |
孙小凤: ""苏南新型农业社区水生态环境健康综合评价与分析"", 《中国农村水利水电》, no. 5, pages 133 - 138 * |
徐洪波;: "城市水环境整治项目绩效评价研究――基于D-S证据理论", 技术经济与管理研究, no. 06, pages 86 - 89 * |
徐瑞: ""基于 SARIMA-LSTM 的北仑河口水质预测方法研究及应用"", 《中国优秀硕士学位论文全文数据库工程科技Ⅰ辑》, no. 01, pages 027 - 1026 * |
徐瑞: ""基于SARIMA-LSTM...河口水质预测方法研究及应用"", 《中国优秀硕士学位论文全文数据库工程科技Ⅰ辑》, no. 01, 15 January 2021 (2021-01-15), pages 027 - 1026 * |
李章平;周念清;沈新平;刘晓群;: "基于循环组合模型的洞庭湖流域水资源短缺风险评价", 水电能源科学, no. 01, pages 15 - 19 * |
董会娇;: "水质风险综合评判模型研究", 陕西水利, no. 03, pages 124 - 128 * |
Cited By (3)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
CN113959499A (en) * | 2021-11-03 | 2022-01-21 | 中国海洋大学 | Deep-sea mining ecological environment in-situ long-term automatic monitoring station and evaluation method thereof |
CN116070886A (en) * | 2023-04-04 | 2023-05-05 | 水利部交通运输部国家能源局南京水利科学研究院 | Multidimensional adaptive regulation and control method and system for water resource system |
CN116070886B (en) * | 2023-04-04 | 2023-06-20 | 水利部交通运输部国家能源局南京水利科学研究院 | Multidimensional adaptive regulation and control method and system for water resource system |
Similar Documents
Publication | Publication Date | Title |
---|---|---|
Nourani et al. | Artificial intelligence based ensemble modeling of wastewater treatment plant using jittered data | |
AU2020103356A4 (en) | Method and device for building river diatom bloom warning model | |
Feng et al. | A risk assessment model of water shortage based on information diffusion technology and its application in analyzing carrying capacity of water resources | |
CN110969346B (en) | River basin water ecological function partition treatment demand evaluation method based on index screening | |
CN113269395A (en) | Water environment risk pre-judging method and system based on pressure state feedback framework | |
CN104680015A (en) | Online soft measurement method for sewage treatment based on quick relevance vector machine | |
CN111260117B (en) | CA-NARX water quality prediction method based on meteorological factors | |
CN106529732A (en) | Carbon emission efficiency prediction method based on neural network and random frontier analysis | |
Wang et al. | A full-view management method based on artificial neural networks for energy and material-savings in wastewater treatment plants | |
CN112966891A (en) | River water environment quality prediction method | |
CN112765902B (en) | Soft measurement modeling method for COD concentration in rural domestic sewage treatment process based on TentFWA-GD RBF neural network | |
CN103793604A (en) | Sewage treatment soft measuring method based on RVM | |
Harrou et al. | Energy consumption prediction in water treatment plants using deep learning with data augmentation | |
CN105549009A (en) | SAR image CFAR target detection method based on super pixels | |
CN118225994B (en) | Seaweed propagation environment monitoring method based on wireless sensor | |
CN110648215A (en) | Distributed scoring card model building method | |
CN110163537B (en) | Water eutrophication evaluation method based on trapezoidal cloud model | |
CN113592278A (en) | SBM water environment bearing capacity evaluation method considering unexpected output | |
Huang et al. | Prediction of chlorophyll a and risk assessment of water blooms in Poyang Lake based on a machine learning method | |
Makumbura et al. | Advancing water quality assessment and prediction using machine learning models, coupled with explainable artificial intelligence (XAI) techniques like shapley additive explanations (SHAP) for interpreting the black-box nature | |
CN111724030A (en) | Water quality comprehensive evaluation method, model, device and storage medium | |
Chang et al. | Soft measurement of effluent index in sewage treatment process based on overcomplete broad learning system | |
CN116913415A (en) | Precise dosing dephosphorization control method, system, equipment and readable storage medium | |
CN115394381B (en) | High-entropy alloy hardness prediction method and device based on machine learning and two-step data expansion | |
CN114755387B (en) | Water body monitoring point location optimization method based on hypothesis testing method |
Legal Events
Date | Code | Title | Description |
---|---|---|---|
PB01 | Publication | ||
PB01 | Publication | ||
SE01 | Entry into force of request for substantive examination | ||
SE01 | Entry into force of request for substantive examination |