CN103914622B - A kind of chemical leakage fast prediction alarm emergency response decision-making method - Google Patents

A kind of chemical leakage fast prediction alarm emergency response decision-making method Download PDF

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CN103914622B
CN103914622B CN201410136961.5A CN201410136961A CN103914622B CN 103914622 B CN103914622 B CN 103914622B CN 201410136961 A CN201410136961 A CN 201410136961A CN 103914622 B CN103914622 B CN 103914622B
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leakage
wind direction
sensor
scene
data
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CN103914622A (en
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赵劲松
王冰
陈丙珍
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Tsinghua University
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Abstract

A kind of chemical leakage fast prediction alarm emergency response decision-making method of the present invention, diffusion model simulation is combined with neutral net and gas sensor system, is applied to quick early warning and the aid decision of industrial park poisonous gas leakage, including:Garden risk factors collection, for recognizing all kinds of leakage accidents that may occur;Numerical simulation, the accident to being likely to occur is simulated, and obtains the coverage of pernicious gas;Data screening, according to live part in actual sensor placement extraction and restructuring numerical simulation result;Neural metwork training, is trained using the data after screening to specific neural network model, to obtain the model parameter for particular industry garden and ambient conditions, and uses redundant data Verification;Sensing system is integrated with neural network model, and model is combined with sensor DCS.

Description

A kind of chemical leakage fast prediction alarm emergency response decision-making method
Technical field
The invention belongs to the safe early warning technical field in industrial production, more particularly to a kind of chemical leakage fast prediction Alarm emergency response decision-making method.
Background technology
Many process industries can be used or produce some harmful poisonous, pernicious gases in process of production (Such as chlorine, phosgene etc.), once there is toxic and harmful leakage accident, the toxic and harmful for leaking out in these industrial parks Serious harm may be caused to a range of mankind in periphery.When toxic and harmful leakage accident occurs, leakage Material and substantially leak position can with comparalive ease determine that but the leakage rate or leak rate of pernicious gas are then difficult Scene obtains.It is accident emergency in the diffusion tendency and coverage of the limited information prediction toxic gas of limited time utilization The important step of response process.At present, traditional numerical d ispersion forecast model, including Gaussian plume model, Fluid Mechanics Computation Model, and some more ripe diffusion simulations softwares are required for user to provide detailed source of leaks leakage rate, and Needing the regular hour to calculate can just obtain result.Therefore, the leakage rate or leakage rate of source of leaks and calculating more long These traditional gas diffusion models of time restriction accident emergency respond and aid decision during applications, they are more Ground is used for the investigation and analysis after accident occurs.Due to historical reasons, China quite a few poisonous and harmful gas may occur Revealed when there is severe toxic pernicious gas with the presence of residential block in the range of the 3~5km of industrial park periphery of body leakage accident During accident, these toxic and harmfuls are likely to diffuse to outside the battery limit (BL) of industrial park, and threat is produced to residential block.Without fast When speed effectively predicts the method for toxic and harmful range of scatter, policymaker often considers pernicious gas with the worst situation Coverage, and predicting the outcome for worst case often means that government department needs to evacuate tens of thousands of or even ten tens of thousands of people, this is It is very unpractical.Therefore a kind of method of fast and effeciently prediction harmful gases diffusion scope is responded and auxiliary for accident emergency Help decision-making significant.
Process toxic and harmful factory all can targetedly near toxic and harmful storage tank set one or Multiple harmful gas sensors, for having monitored whether that gas is leaked.These gas sensors are connected with control centre, there is provided Toxic gas leakage alarm information.But many industrial parks are without the effect for playing gas sensor completely, accident hair at present When raw, emergency response personnel can only obtain the species of gas leakage by sensor, instantaneous concentration, and can not be by these information The distribution situation of gas leakage is rapidly predicted, and then takes effective control measure, formulate rational evacuation plan.
At present, the accident consequence analysis method for commonly using in the world mainly includes using different types of numerical model (Gaussian plume model, luid mechanics computation model(CFD)And business prototype PHAST, FLACS etc. are to the accident that has occurred and that Reappeared, be illustrated in the coverage of gas leakage under the conditions of accident leakage at that time(Including dead area, severely injured area and influence Area), and study influence of the Atmospheric Diffusion condition to gas leakage range of scatter and concentration distribution.But use Numerical Model Analysis Shortcoming is the source strength that must be known by source of leaks(Leakage rate)And leakage form(Blast leakage/aperture leakage etc.), with reference to Meteorologic parameter and mass transfer diffusion equation are simulated, and model is complicated, calculate that time-consuming, it is impossible to for real-time under accident condition or Person's fast prediction.
The content of the invention
In order to overcome the shortcoming of above-mentioned prior art, it is an object of the invention to provide a kind of chemical leakage fast prediction Alarm emergency response decision-making method, risk analysis is carried out to industrial park, reveals Scene Simulation, is supplemented and is optimized garden in right amount and show Some toxic and harmful sensing systems, the toxic gas alarm system of garden is combined with gas diffusion forecast analysis, For accident emergency Response Decision provides technical support.
To achieve these goals, the technical solution adopted by the present invention is:
A kind of chemical leakage fast prediction alarm emergency response decision-making method, including risk factors collection, scene numerical value Simulation, analog result screening, neural metwork training and training result and sensing system integrated totally five stages, wherein:
Risk factors collection includes:The risk factors of chemical industrial park are recognized, quantifies each risk elements and according to identification Risk elements and its span, reasonable value simultaneously combine the various leakage scenes that may occur;
The scene numerical simulation stage includes:The leakage being likely to occur that will be constituted in garden risk factors collection step Scene be simulated, with obtain it is different leakage scenes under reveal gas coverage;
Analog result screening includes:
A kind of key parameter including in 4 placement schemes of gas sensor is optimized, is obtained using simulation Leakage Gas concentration distribution carries out simple optimizing, obtains most suitable sensor placement;
According to the sensor placement scheme for determining, the virtual detection number in the range of the measurable wind direction of sensor placement is extracted in According to this and matching environment sensitive spot gas leakage diffusion data, training data is prepared according to the training logic of neutral net And verification data;
Neural metwork training step includes:
The feedforward neural network for Function Fitting is set up, using ready training data as the defeated of neural metwork training Enter output, calculating network parameter;
Inspection data importation is input into neutral net, as a result part and neural network prediction Comparative result, assessment is pre- Survey precision;
Neutral net and sensor and garden control system integration step:
By the sunykatuib analysis of each risk source and training result and risk source and the geographical location information of environment sensitive spot Combined in the form of database and caller, and the data-interface with sensing system is provided, realize from the accident-biography The workflow of sensor alarm-model fast prediction-aid decision.
The garden risk identification part comprises the steps of:
Step one, recognized using risk assessment risks and assumptions and accident scenarios factor and judge may generation all kinds of leakages The indispensable element of scene, including risk elements and accident scenarios key element.These key elements include being not limited to specified risk material species(Have Malicious/inflammable gas or volatile liquid), reserves/consumption, storage location(Space coordinates), storage form(Pressure, temperature, if It is standby), wind speed, humidity, temperature, atmospheric stability, surrounding enviroment sensitive spot position(Space coordinates)Deng.
Step 2, the span for determining each risks and assumptions and accident situational factor respectively(For continuous variable), Sequence of values is divided with a fixed step size respectively in the span of each factor(Step-length must not exceed the factor span 10%), finally by each valued combinations of different risks and assumptions/accident scenarios factor into the substantial amounts of leakage feelings that may occur Scape.N kind risk factors are such as had, each risk factors has NiPlant value(Ni>=1, integer), then havePlant leakage Scene.
The numerical model that the scene numerical simulation stage uses includes:Gauss and class Gauss diffusion model (Gaussian Plume Model), Fluid Mechanics Computation(CFD)Model and PHAST, FLACS, SLAB, ALOHA, HGSYSTEM etc. integrate mould Type.Finally obtain J kinds leakage Scene Simulation result.
The analog result screening step needs to be laid out one group of 4 sensor optimization, and 4 sensors are using just Polygonized structure, serial number is 1~4, and the spacing of adjacent numbering sensor is equal, and Optimization Steps are as follows:
Step one, the position according to source of leaks and garden layout, the test limit of sensor, it is determined that basic layout parameter L1, the span of d and α.Wherein L1It is No. 1 distance of sensor distance source of leaks, d is sensor spacing, and α is 1-2 and 1-4 The 1/2. of sensor angle
Step 2, cardinal wind is determined according to wind frequency information, sensor is arranged symmetrically in cardinal wind leeward upwards, actual Wind direction and cardinal wind angle are β.And take a higher value β0It is interval as optimization, by its it is discrete be actual wind direction sequence (β1, β2,…,βM), sequence length is M.(Typically take β0=50 °, by interval [- 50 °, 50 °] the discrete wind direction sequence to be spaced 1 °)
Step 3, to layout parameter L1, d, α is separated into argument sequence in span, and length is respectively P1,P2,P3, CompositionPlant placement scheme.
Step 4, to kth kind placement scheme (k=1,2 ..., K) use data screening algorithm, for jth kind Scene Simulation As a result(j=1,2,…,J), it is β to filter out the placement scheme in wind directionmEfficient layout number when (m=1,2 ..., M)
Step 5, different wind direction β are calculated to kth kind placement scheme (k=1,2 ..., K)mScene when (m=1,2 ..., M) Relevance factorRecord meetsM=1,2, ..., the maximum wind direction scope W of Mk, take satisfaction { max (Wk),k=1, 2 ..., K layout for optimize be laid out.
The standard that efficient layout is judged in analog result screening step is:For any sensor layout, to specific Every kind of leakage scene under wind direction, it is called in the wind direction to have 3 or more than 3 to cover the then layout by plume in 4 sensors With the efficient layout under the conditions of leakage scene.
In affiliated analog result screening step, scene relevance factor is(m=1,2,…,Mk=1,2,…, K)。
The analog result data screening part includes following filtering algorithm:
Step one, check sensor placement parameter L1, d, α, actual wind direction β, lower wind direction sensitivity source position (L2, Y2) and Whether leakage scene sequence number J etc. meets the requirements
Step 2, the gas diffusion distance for revealing j-th scene (j=1,2 ..., J) analog result, concentration distribution expand The time of dissipating and plume width enter row interpolation, it is determined that screening starting point
Step 3, calculating parameter γ, θ24,W1, and W2, wherein γ is 2, No. 4 sensors with source of leaks as summit and master Air guiding angle, θ24For 2, No. 4 sensors with source of leaks as summit and actual wind direction angle, W1It is environment sensitive spot distance The vertical range of plume center line, W2It is the plume half-breadth at environment sensitive spot
Whether step 4, inspection sensor placement are efficient layout under the leakage scene and actual wind direction, if so, after It is continuous;If it is not, skipping and recording this leakage scene, continue step 2
Step 5, the pollution sources concentration of 3 effective sensor positions of extraction and diffusion time.
Whether step 6, inspection leakage gas can diffuse to lower wind direction environment sensitive spot, i.e. computing environment sensitive spot exists Location parameter Q in j-th leakage scenej.If it can, continue step 7, if it could not, recording this sequence number and continuing step Two.
The concentration of pernicious gas and diffusion time at step 7, the lower wind direction environment sensitive spot of extraction.
Step 8, by all sensing station concentration extracted and time value and lower wind direction sensitive spot concentration and time Value is arranged and preserved.
Whether the described method that judges gas leakage and can diffuse to lower wind direction environment sensitive spot is:Computing environment sensitive spot Location parameter Q in gas leakage plumej=W1/W2If, Qj≤ 1, then environment sensitive spot extended influence by gas leakage, instead It is then unaffected.
Neural metwork training part implementation process is as follows:
Step one, determine network inputs, using live available parameter as input, including pressure store (p), wind speed (v), Wind direction (β), temperature (T), humidity (h), atmospheric stability (S), the valid density measurement of 3 gas sensors of wind direction under risk source Value (c1,c2,c3) and time of fire alarming (t1,t2,t3), the position (L of lower wind direction sensitive spot2,Y2)
Step 2, determine network export, at following wind direction environment sensitive spot pernicious gas reach concentration (c) and the time T () is used as output.
Step 3, network internal structure determination, use feedforward neural network(BP networks), comprising a non-linear hidden layer (Sigmoid transmission functions)With a linear convergent rate layer(Linear transmission functions), network is not comprising backfeed loop.
Step 4, according to input and output requirement, be ready for and output data matrix and superfluous using data screening algorithm Remaining checking data.(Matrix column is each key element of input and output, the inputoutput data of behavior difference scene)
Step 5, using MATLAB Neural Network Toolbox, according to single unify training method neutral net is used it is defeated Enter output data training, obtain network parameter.
Step 6, the difference exported as neutral net input, comparing cell output and redundancy using redundant input data, Assessment prediction precision.
The neutral net comprises the following steps with sensing system integration section:
Step one, the area map for setting up the environment sensitive spot of wind direction under single risk source and cardinal wind.
Step 2, risk analysis is carried out to certain single risk source, recognize that possible leakage scene is simultaneously carried out to leakage scene Simulation.
Step 3, the sensor placement optimization for performing data screening step, obtain the sensor placement under cardinal wind The maximum of wind direction is applicable angle.
Step 4, under the risk source cardinal wind wind direction maximum carried out using all environment sensitive spots in angular range Data screening, obtains one group of input and output matrix of neural metwork training.
Step 5, the neutral net input and output matrix obtained using data screening are trained to be assessed with precision of prediction.
Step 6, the neural network parameter that obtains will be trained to be fabricated to the application program that can be called automatically, make sensor DCS data can be gathered by data-interface and be calculated using application program.
When step 7, true accident occur, the prefabricated application program of sensor alarm-startup-prediction leakage diffusion The influence of environmentally sensitive point(Time for including whether to influence environment sensitive spot or gas leakage to reach environment sensitive spot and dense Degree)- decision-maker judges whether to need to evacuate.
Compared with prior art, the present invention proposes a kind of the simple of sensor placement for processing toxic and harmful factory The method for quick predicting of optimization method, and introducing and employment early stage risk identification, numerical simulation and neural metwork training, so as to Accident can timely and effectively predict the range of scatter of toxic and harmful when occurring, be garden surrounding resident area evacuating personnel and Protection provides decision support.On the basis of the existing toxic and harmful sensor in garden, for garden production technology and week Surrounding environment, completes, to garden production process risk identification, to reveal Scene Simulation, improves sensor placement and carries out neutral net Training, overcomes toxic gas leakage accident and the deficiency that alarm information is not enough to support accident emergency response occurs, it is ensured that The applicability and accuracy of method.
Brief description of the drawings
Fig. 1 is the flow chart of one embodiment of the invention method.
Fig. 2 is one embodiment of the invention method application scenario schematic diagram.
Fig. 3 is the sensor placement Optimal Curve that one embodiment of the invention method is obtained.
Fig. 4 is the rudimentary algorithm that one embodiment of the invention method is used for data screening
Fig. 5 is the neural network structure figure of one embodiment of the invention method application.
Fig. 6 is verified for the neutral net redundant data of one embodiment of the invention method application.
Whether Fig. 7 is the judgement impacted to sensitizing range of the neutral net of one embodiment of the invention method application.
Specific embodiment
Describe embodiments of the present invention in detail with reference to the accompanying drawings and examples.
Fig. 1 is the flow chart of method according to an embodiment of the invention, side according to an embodiment of the invention Method includes:
- risk factors collection step
Risks and assumptions and accident scenarios factor are recognized using risk assessment and judge all kinds of leakage scenes of possible generation Indispensable element, including risk elements and accident scenarios key element.These key elements include being not limited to specified risk material species(Poisonous/easily The gas or volatile liquid of combustion), reserves/consumption, storage location(Space coordinates), storage form(Pressure, temperature, equipment)、 Wind speed, humidity, temperature, atmospheric stability, surrounding enviroment sensitive spot position(Space coordinates)Deng.Then each risk is determined respectively The span of the factor and accident situational factor(For continuous variable), respectively with certain in the span of each factor Step-length divides sequence of values(Step-length must not exceed the 10% of the factor span), finally by different risks and assumptions/accident feelings Leakage scene of each valued combinations of scape factor into substantial amounts of possible generation.Such as have n kind risk factors, each risk factors There is NiPlant value(Ni>=1, integer), then havePlant leakage scene.
- leakage Scene Simulation step
The step carries out Numerical-Mode using traditional gas diffusion model, all kinds of leakage scenes to being identified in previous step Intend, obtain the toxic and harmful diffusion data and distribution situation under different situations.Available model includes Gauss and class Gauss Diffusion model (Gaussian Plume Model), Fluid Mechanics Computation(CFD)Model and PHAST, FLACS, SLAB, ALOHA, HGSYSTEM etc..
- valid data screen step
Close the position that Fig. 2 show the risk source-plume-sensor-lower wind direction sensitive spot of valid data screening step System's figure.Analog result screening step needs to be laid out optimization to one group of 4 sensor, and 4 sensors use regular polygon Structure, serial number is 1~4, and the spacing of adjacent numbering sensor is equal.Optimization Steps are as follows:
Step one, the position according to source of leaks and garden layout, the test limit of sensor, it is determined that basic layout parameter L1, the span of d and α.Wherein L1It is No. 1 distance of sensor distance source of leaks, d is sensor spacing, and α is 1-2 and 1-4 The 1/2. of sensor angle
Step 2, cardinal wind is determined according to wind frequency information, sensor is arranged symmetrically in cardinal wind leeward upwards, actual Wind direction and cardinal wind angle are β.And take a higher value β0It is interval as optimization, by its it is discrete be actual wind direction sequence (β1, β2,…,βM), sequence length is M.(Typically take β0=50 °, by interval [- 50 °, 50 °] the discrete wind direction sequence to be spaced 1 °)
Step 3, to layout parameter L1, d, α is separated into argument sequence in span, and length is respectively P1,P2,P3, CompositionPlant placement scheme.
Step 4, to kth kind placement scheme (k=1,2 ..., K) use data screening algorithm, for jth kind Scene Simulation As a result(j=1,2,…,J), it is β to filter out the placement scheme in wind directionmEfficient layout number when (m=1,2 ..., M) Wherein efficient layout is defined as:For any sensor layout, to specific wind direction under every kind of leakage scene, in 4 sensors There are 3 or more than 3 to be covered by plume(Plume concentration can be detected)Placement scheme.
Step 5, different wind direction β are calculated to kth kind placement scheme (k=1,2 ..., K)mScene when (m=1,2 ..., M) Relevance factor(m=1,2 ..., M k=1,2 ..., K), record meetsM=1,2, ..., M's Maximum wind direction scope Wk, take satisfaction { max (Wk), k=1,2 ..., K layout for optimize be laid out.
Fig. 3 is by L1In the 27 of the value composition of=[40,60,80] m, d=[20,30,40] m and α=[30 °, 45 °, 60 °] The layout optimization result of placement scheme(Fig. 3 d).Under conditions of being 95% in scene utilization rate, sensor placement scheme L1=40m, d =20m and α=60 ° are laid out to optimize, and the maximum wind direction scope of application of the layout is 20 °~20 ° of ﹣.Determine that sensor is optimized After layout, it is simulated result using the filtering algorithm shown in Fig. 4 and screens:
Step one, check sensor placement parameter L1, d, α, actual wind direction β, lower wind direction sensitivity source position (L2, Y2) and Whether leakage scene sequence number j etc. meets the requirements
Step 2, the gas diffusion distance for revealing j-th scene (j=1,2 ..., J) analog result, concentration distribution expand The time of dissipating and plume width enter row interpolation, it is determined that screening starting point
Step 3, calculating parameter γ, θ24,W1, and W2, wherein γ is 2, No. 4 sensors with source of leaks as summit and master Air guiding angle, θ24For 2, No. 4 sensors with source of leaks as summit and actual wind direction angle, W1It is environment sensitive spot distance The vertical range of plume center line, W2It is the plume half-breadth at environment sensitive spot
Whether step 4, inspection sensor placement are efficient layout under the leakage scene and actual wind direction(Effectively sense Device number is more than 3), if so, continuing;If it is not, skipping and recording this leakage scene, continue step 2
Step 5, the pollution sources concentration of 3 effective sensor positions of extraction and diffusion time.
Whether step 6, inspection leakage gas can diffuse to lower wind direction environment sensitive spot, i.e. computing environment sensitive spot exists Location parameter Q in j-th leakage scenej=W1/W2.If it can, i.e. Qj≤ 1, continue step 7, if it could not, i.e. Qj>1, note Record this sequence number and continue step 2.
The concentration of pernicious gas and diffusion time at step 7, the lower wind direction environment sensitive spot of extraction.
Step 8, by all sensing station concentration extracted and time value and lower wind direction sensitive spot concentration and time Value is arranged and preserved.
- neural metwork training step
Neural metwork training part implementation process is as follows:
Step one, determine network inputs, using live available parameter as input, including pressure store (p), wind speed (v), Wind direction (β), temperature (T), humidity (h), atmospheric stability (S), the valid density measurement of 3 gas sensors of wind direction under risk source Value (c1,c2,c3) and time of fire alarming (t1,t2,t3), the position (L of lower wind direction sensitive spot2,Y2)
Step 2, determine network export, at following wind direction environment sensitive spot pernicious gas reach concentration (c) and the time T () is used as output.
Step 3, network internal structure determination, as shown in figure 5, using feedforward neural network(BP networks), it is non-comprising one Linear hidden layer(Sigmoid transmission functions)With a linear convergent rate layer(Linear transmission functions), network is not comprising feeding back to Road.
Step 4, according to input and output requirement, be ready for and output data matrix and superfluous using data screening algorithm Remaining checking data.(Matrix column is each key element of input and output, the inputoutput data of behavior difference scene)
Step 5, using MATLAB Neural Network Toolbox, according to single unify training method neutral net is used it is defeated Enter output data training, obtain network parameter.
Step 6, the difference exported as neutral net input, comparing cell output and redundancy using redundant input data, Assessment prediction precision.As Fig. 6 shows a neural network prediction situation for chlorine gas leakage embodiment.All subgraphs is vertical in figure Coordinate is under specific leakage situation, according to the position of 3 sensor alarm information, weather condition and lower wind direction sensitizing range Put, using neutral net to lower wind direction sensitizing range
The concentration of (a) chlorine(ppm)
B () chlorine reaches the time of sensitive position(s)
The half-breadth W2 of (c) sensitive position plume(m)
The vertical range W1 of (d) sensitive position actual wind direction of distance(m)
And the abscissa of Fig. 6 a~6d is then the result of Phast simulations, in theory, the fitting result of scatterplot should be straight in figure Line y=x, actual result shows that the only neural network prediction result of chlorine gas concentration is less than normal compared to Phast analog results(Slope is about It is 0.93), predicting the outcome for chlorine arrival time, W1 and W2 be all very accurate.
The W1 and the value of W2 obtained using Fig. 6 c and 6d can predict whether lower wind direction sensitizing range receives the prestige of chlorine leakage The side of body, as shown in fig. 7, abscissa is the quantity of the leakage scene used:
The relative error of (a) neutral net concentration prediction value and the Phast analogues value
B W1/W2 ratios that () calculates according to the W1 and W2 of neural network prediction in Fig. 6
C W1/W2 ratios that () obtains according to reconnaissance in Phast simulations and plume
D () will predict that W1/W2 and theory W1/W2 values subtract each other the logical consequence for obtaining after rounding
According to (a) it can be found that worst error of the neural network prediction value compared with theoretical value is no more than 30%, Fig. 7 b and 7c Closely, its difference shows in 7d:2780 reveal scene in, have 2 leakage scenes under wind direction sensitive spot in theory Threatened by chlorine gas leakage, but the result of neural network prediction shows that it is not on the hazard, and referred to as " fails to report ", and rate of failing to report is 0.072%;On the other hand, thanked in only 14 leakage scenes and share sensitive spot and be not on the hazard in theory, but neutral net is pre- It receives threat to survey display, referred to as " reports by mistake ", and rate of false alarm is 0.504%.
Step 7, the neural network parameter that obtains will be trained to be fabricated to the application program that can be called automatically, make sensor DCS data can be gathered by data-interface and be calculated using application program.
When step 8, true accident occur, the prefabricated application program of sensor alarm-startup-prediction leakage diffusion The influence of environmentally sensitive point(Time for including whether to influence environment sensitive spot or gas leakage to reach environment sensitive spot and dense Degree)- decision-maker judges whether to need to evacuate.

Claims (9)

1. a kind of chemical leakage fast prediction alarm emergency response decision-making method, including risk factors collection, scene Numerical-Mode Plan, analog result screening, neural metwork training and training result and sensing system integrated totally five stages:
Risk factors collection includes:The risk factors of chemical industrial park are recognized, quantifies each risk elements and according to the risk of identification Key element and its span, reasonable value simultaneously combine the various leakage scenes that may occur;
The scene numerical simulation stage includes:The leakage scene being likely to occur that will be constituted in garden risk factors collection step Be simulated, with obtain it is different leakage scenes under reveal gas coverage;
Analog result screening includes:
A kind of key parameter including in 4 placement schemes of gas sensor is optimized, the leakage obtained using simulation Gas concentration distribution carries out simple optimizing, obtains most suitable sensor placement;
According to determine sensor placement scheme, be extracted in the virtual detection data in the range of the measurable wind direction of sensor placement with And matching environment sensitive spot gas leakage diffusion data, prepare training data and school according to the training logic of neutral net Test data;
Neural metwork training step includes:
The feedforward neural network for Function Fitting is set up, the input of ready training data as neural metwork training is defeated Go out, calculating network parameter;
Inspection data importation is input into neutral net, as a result part and neural network prediction Comparative result, assessment prediction essence Degree;
Neutral net and sensor and garden control system integration step:
By the geographical location information of the sunykatuib analysis of each risk source and training result and risk source and environment sensitive spot with number Combined according to the form of storehouse and caller, and the data-interface with sensing system is provided, realize from the accident-sensor The workflow of alarm-model fast prediction-aid decision;
Characterized in that, the neutral net comprises the following steps with sensing system integration section:
Step one, the area map for setting up the environment sensitive spot of wind direction under single risk source and cardinal wind;
Step 2, risk analysis is carried out to certain single risk source, recognize that possible leakage scene is simultaneously simulated to leakage scene;
Step 3, the sensor placement optimization for performing data screening step, obtain sensor placement wind direction under cardinal wind Maximum be applicable angle;
Step 4, under the risk source cardinal wind wind direction maximum carry out data using all environment sensitive spots in angular range Screening, obtains one group of input and output matrix of neural metwork training;
Step 5, the neutral net input and output matrix obtained using data screening are trained to be assessed with precision of prediction;
Step 6, the neural network parameter that obtains will be trained to be fabricated to the application program that can be called automatically, make the DCS of sensor Data can be gathered by data-interface and calculated using application program;
When step 7, true accident occur, the prefabricated application program of sensor alarm-startup-prediction leakage diffusion couple ring Influence-the decision-maker of border sensitive spot judges whether to need to evacuate.
2. chemical leakage fast prediction alarm emergency response decision-making method according to claim 1, it is characterised in that institute Garden risk factors collection part is stated to comprise the steps of:
Step one, recognized using risk assessment risks and assumptions and accident scenarios factor and judge may generation all kinds of leakage scenes Indispensable element, including risk elements and accident scenarios key element;
Step 2, the span for determining each risks and assumptions and accident situational factor respectively, in the value model of each factor Enclose interior respectively with fixed step size division sequence of values, wherein step-length must not exceed the 10% of the factor span, finally will not The leakage scene that each valued combinations of risks and assumptions/accident scenarios factor together occur into substantial amounts of possibility, when total n kind wind During dangerous factor, each risk factors has NiPlant value, wherein Ni>=1, and NiIt is integer, then hasPlant leakage feelings Scape.
3. chemical leakage fast prediction alarm emergency response decision-making method according to claim 2, it is characterised in that institute Stating the numerical model that the scene numerical simulation stage uses includes:Gauss and class Gauss diffusion model (Gaussian Plume Model), Fluid Mechanics Computation (CFD) model and PHAST, FLACS, SLAB, ALOHA and HGSYSTEM Integrated Models, most After obtain J kinds leakage Scene Simulation result.
4. chemical leakage fast prediction alarm emergency response decision-making method according to claim 2, it is characterised in that institute State analog result screening step and one group of 4 sensor are laid out with optimization, and 4 sensors use regular polygon structure, it is suitable Sequence numbering is 1~4, and the spacing of adjacent numbering sensor is equal, and Optimization Steps are as follows:
Step one, the position according to source of leaks and garden layout, the test limit of sensor, it is determined that basic layout parameter L1, d and α Span, wherein L1It is No. 1 distance of sensor distance source of leaks, d is sensor spacing, and α is 1-2 and 1-4 sensors The 1/2 of angle;
Step 2, cardinal wind is determined according to wind frequency information, sensor is arranged symmetrically in the leeward of cardinal wind upwards, actual wind It is β to cardinal wind angle, and takes a higher value β0It is interval as optimization, by its it is discrete be actual wind direction sequence (β1, β2,…,βM), sequence length is M;
Step 3, to layout parameter L1, d, α is separated into argument sequence in span, and length is respectively P1,P2,P3, compositionPlant placement scheme;
Step 4, to kth kind placement scheme use data screening algorithm, for jth kind Scene Simulation result, filter out the layout Scheme is β in wind directionmWhen efficient layout numberWherein k=1,2 ..., K;J=1,2 ..., J;M=1,2 ..., M;
Step 5, wind direction βs different to the calculating of kth kind placement schememWhen scene relevance factorRecord meetsMaximum wind direction scope Wk, take satisfaction { max (Wk), k=1,2 ..., K layout be Optimize layout.
5. chemical leakage fast prediction alarm emergency response decision-making method according to claim 4, it is characterised in that institute State and judge that the standard of efficient layout is in analog result screening step:For any sensor layout, to specific wind direction under it is every Leakage scene is planted, it is called under the conditions of the wind direction and leakage scene there are more than 3 to cover the then layout by plume in 4 sensors Efficient layout.
6. the chemical leakage fast prediction alarm emergency response decision-making method according to claim 4 or 5, its feature exists In in affiliated analog result screening step, scene relevance factor isWherein m=1,2 ..., M;K=1, 2,…,K。
7. chemical leakage fast prediction alarm emergency response decision-making method according to claim 6, it is characterised in that institute State analog result data screening part and include following filtering algorithm:
Step one, inspection sensor placement parameter L1, d, α, actual wind direction β, lower wind direction sensitivity source position (L2,Y2) and leakage Whether scene sequence number J meets the requirements;
Step 2, the gas diffusion distance for revealing j-th Scene Simulation result, concentration distribution, diffusion time and plume width Enter row interpolation, it is determined that screening starting point, wherein j=1,2 ..., J;
Step 3, calculating parameter γ, θ2, θ4,W1, and W2, wherein γ be No. 2 or No. 4 sensors with source of leaks be summit and dominate The angle of wind direction, θ2It is No. 2 sensors with the angle that source of leaks is summit and actual wind direction, θ4For No. 4 sensors are with source of leaks Summit and the angle of actual wind direction, W1It is environment sensitive spot apart from the vertical range of plume center line, W2At environment sensitive spot Plume half-breadth;
Whether step 4, inspection sensor placement are efficient layout under the leakage scene and actual wind direction, if so, continuing;If It is not to skip and record this leakage scene, continues step 2;
Step 5, the pollution sources concentration of 3 effective sensor positions of extraction and diffusion time;
Whether step 6, inspection leakage gas can diffuse to lower wind direction environment sensitive spot, i.e. computing environment sensitive spot is at j-th Location parameter Q in leakage scenej, if it can, continue step 7, if it could not, recording this sequence number and continuing step 2;
The concentration of pernicious gas and diffusion time at step 7, the lower wind direction environment sensitive spot of extraction;
It is step 8, all sensing station concentration extracted and time value and lower wind direction sensitive spot concentration and time value is whole Manage and preserve.
8. chemical leakage fast prediction alarm emergency response decision-making method according to claim 7, it is characterised in that institute Whether the method for judging gas leakage and diffusing to lower wind direction environment sensitive spot stated is:Computing environment sensitive spot is in gas leakage Location parameter Q in plumej=W1/W2If, Qj≤ 1, then environment sensitive spot is extended influence by gas leakage, otherwise does not receive then Influence.
9. chemical leakage fast prediction alarm emergency response decision-making method according to claim 1, it is characterised in that institute State neural metwork training part implementation process as follows:
Step one, network inputs are determined, using live available parameter as input, including pressure store (p), wind speed (v), wind direction (β), temperature (T), humidity (h), atmospheric stability (S), the valid density measured value of 3 gas sensors of wind direction under risk source (c1,c2,c3) and time of fire alarming (t1,t2,t3), the position (L of lower wind direction sensitive spot2,Y2);
Step 2, determine network export, at following wind direction environment sensitive spot pernicious gas reach concentration (c) and the time (t) make It is output;
Step 3, network internal structure determination, are BP networks using feedforward neural network, comprising a non-linear hidden layer and Individual linear convergent rate layer, non-linear hidden layer takes sigmoid transmission functions, and linear convergent rate layer takes linear transmission functions, and network is not Comprising backfeed loop;
Step 4, according to input and output requirement, be ready for and output data matrix and redundancy using data screening algorithm Checking data;
Step 5, using MATLAB Neural Network Toolbox, unify training method according to single defeated using input to neutral net Go out data training, obtain network parameter;
Step 6, the difference exported as neutral net input, comparing cell output and redundancy using redundant input data, assessment Precision of prediction.
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Families Citing this family (47)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
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CN116403165B (en) * 2023-06-05 2023-08-04 交通运输部水运科学研究所 Dangerous chemical leakage emergency treatment method, dangerous chemical leakage emergency treatment device and readable storage medium
CN117290639B (en) * 2023-11-24 2024-02-27 深圳大学 Method and system for positioning and detecting material leakage in phase-change energy storage tank
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Citations (2)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
EP2317311A2 (en) * 2009-09-11 2011-05-04 SELEX Galileo Ltd Sensing network and method
CN102313793A (en) * 2011-09-07 2012-01-11 中国环境科学研究院 Monitoring system of multi-component gas pollutants in air of chemical industrial park

Patent Citations (2)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
EP2317311A2 (en) * 2009-09-11 2011-05-04 SELEX Galileo Ltd Sensing network and method
CN102313793A (en) * 2011-09-07 2012-01-11 中国环境科学研究院 Monitoring system of multi-component gas pollutants in air of chemical industrial park

Non-Patent Citations (2)

* Cited by examiner, † Cited by third party
Title
工业园区事故风险评价研究;孙爱军;《http://wenku.baidu.com/view/e6e7bcf1551810a6f4248600.html?from=search》;20130724;第36-53页 *
翟卓韬等.基于MapX的泄露事故救援决策系统.《计算机与应用化学》.2007,第24卷(第4期),第498-502页. *

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