CN106126909A - PM2.5 concentration prediction method based on Unscented kalman neutral net - Google Patents

PM2.5 concentration prediction method based on Unscented kalman neutral net Download PDF

Info

Publication number
CN106126909A
CN106126909A CN201610457234.8A CN201610457234A CN106126909A CN 106126909 A CN106126909 A CN 106126909A CN 201610457234 A CN201610457234 A CN 201610457234A CN 106126909 A CN106126909 A CN 106126909A
Authority
CN
China
Prior art keywords
concentration
time
neural network
prediction
unscented kalman
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
Application number
CN201610457234.8A
Other languages
Chinese (zh)
Inventor
苏盈盈
王晓峰
贾威
贾瑞楠
Current Assignee (The listed assignees may be inaccurate. Google has not performed a legal analysis and makes no representation or warranty as to the accuracy of the list.)
Chongqing University of Science and Technology
Original Assignee
Chongqing University of Science and Technology
Priority date (The priority date 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 date listed.)
Filing date
Publication date
Application filed by Chongqing University of Science and Technology filed Critical Chongqing University of Science and Technology
Priority to CN201610457234.8A priority Critical patent/CN106126909A/en
Publication of CN106126909A publication Critical patent/CN106126909A/en
Pending legal-status Critical Current

Links

Classifications

    • GPHYSICS
    • G06COMPUTING; CALCULATING OR COUNTING
    • G06NCOMPUTING ARRANGEMENTS BASED ON SPECIFIC COMPUTATIONAL MODELS
    • G06N3/00Computing arrangements based on biological models
    • G06N3/02Neural networks
    • G06N3/04Architecture, e.g. interconnection topology
    • GPHYSICS
    • G16INFORMATION AND COMMUNICATION TECHNOLOGY [ICT] SPECIALLY ADAPTED FOR SPECIFIC APPLICATION FIELDS
    • G16ZINFORMATION AND COMMUNICATION TECHNOLOGY [ICT] SPECIALLY ADAPTED FOR SPECIFIC APPLICATION FIELDS, NOT OTHERWISE PROVIDED FOR
    • G16Z99/00Subject matter not provided for in other main groups of this subclass

Landscapes

  • Engineering & Computer Science (AREA)
  • Theoretical Computer Science (AREA)
  • Physics & Mathematics (AREA)
  • Data Mining & Analysis (AREA)
  • General Health & Medical Sciences (AREA)
  • Biomedical Technology (AREA)
  • Biophysics (AREA)
  • Computational Linguistics (AREA)
  • Life Sciences & Earth Sciences (AREA)
  • Evolutionary Computation (AREA)
  • Artificial Intelligence (AREA)
  • Molecular Biology (AREA)
  • Computing Systems (AREA)
  • General Engineering & Computer Science (AREA)
  • General Physics & Mathematics (AREA)
  • Mathematical Physics (AREA)
  • Software Systems (AREA)
  • Health & Medical Sciences (AREA)
  • Management, Administration, Business Operations System, And Electronic Commerce (AREA)

Abstract

The invention provides a kind of PM2.5 concentration prediction method based on Unscented kalman neutral net, comprise the steps: to obtain the historical data of PM2.5 concentration, recurrence calculation is carried out based on Unscented kalman neutral net, MATLAB simulation software is utilized to program, constantly carry out on-line prediction, constantly revise weights and threshold value, set up the Dynamic Evolution Model of PM2.5 concentration prediction, on the basis of obtaining Dynamic Evolution Model and prediction data, set up figure and regard change early warning, to reach the forewarning function after data prediction.For based on BP neural net model establishing, based on Unscented kalman neural net model establishing on predicting the outcome more accurate, error is less.

Description

PM2.5 concentration prediction method based on unscented Kalman neural network
Technical Field
The invention relates to the technical field of air quality prediction, in particular to a PM2.5 concentration prediction method based on an unscented Kalman neural network (UKFNN for short).
Background
PM2.5, fine particulate matter, is particulate matter having an aerodynamic equivalent diameter of less than or equal to 2.5 microns in ambient air, also known as respirable lung particulate matter. It can be suspended in air for a long time, and the higher its concentration in air, the more serious the air pollution. Compared with the atmospheric particulate matters with larger diameters, PM2.5 has small particle size, large surface area, strong activity, easy attachment of toxic and harmful substances, longer retention time in the atmosphere, long conveying distance and larger influence on human health and atmospheric environment. It can cause diseases of bronchus, cardiovascular and respiratory tract, damage the oxygen conveying capacity of hemoglobin, even cause pathological changes in human body and induce cancer. Simultaneously, because the particulate matter in the atmosphere is to the scattering and the absorption of light, can show to weaken light signal, reduce effective stadia by a wide margin to make visibility in the air reduce, produce haze weather, bring inconvenience and harm to people's daily life. Therefore, monitoring of PM2.5 and studying of the concentration change thereof are important.
Disclosure of Invention
The application provides a PM2.5 concentration prediction method based on an unscented Kalman neural network, so as to solve the technical problems of inaccurate PM2.5 concentration prediction and large error in the prior art.
In order to solve the technical problems, the application adopts the following technical scheme:
a PM2.5 concentration prediction method based on an unscented Kalman neural network comprises the following steps:
s1: acquiring historical data of PM2.5 concentration;
s2: carrying out recursion operation by using an unscented Kalman neural network, and circularly correcting the weight and the threshold of the neural network by continuously carrying out online prediction to realize prediction of the PM2.5 concentration chaotic time sequence so as to establish a dynamic evolution model for predicting the PM2.5 concentration:
is provided with an N-layer forward neural network, and the number of neurons in each layer is Sk(k is 1,2, …, N), the input layer is the first layer, the output layer is the nth layer, and the connection weights for the k layer neurons are(i=1,2,…,Sk-1,j=1,2,…,Sk) Taking the weight w and the threshold b of the neural network as state variables of unscented kalman filtering, taking the output of the neural network as a measurement variable of the unscented kalman filtering, and forming a state vector by all the weights and the thresholds in the neural network:
X = [ w 11 1 ... w s 1 s 2 1 w 11 2 ... w s 1 s 2 2 b 11 1 w 11 N - 1 ... w s 1 s 2 N - 1 b 1 1 ... . b s 1 1 b 1 2 ... . b s 2 2 b 1 N - 1 ... . b s n - 1 N - 1 ] T ,
the state equation and observation equation for the system can be expressed as:
X k = X k - 1 Y e k = h ( W k , X k ) + V k = F N ( W k N , F N - 1 ( W k N - 1 ... F 2 ( W k 2 , X k ) ) ) + V k
in the formula, h (-) is a nonlinear transformation, FNIs the N layer transfer function of the neural network, YekTo desired output, XkAs an input vector, VkTo observe noise, it is random white noise, set to 0 in unscented kalman neural network;
the time is updated as: predicted state variable X from time k-1 to time kk/k-1=AXkATPrediction error covariance matrix P from time k-1 to time kk/k-1=APkATWherein A is [1 ]],PkThe covariance matrix at the k moment;
the measurement is updated as: computing kalman filter gainIn the formula, KkA filter gain matrix for time k, Pk/k-1Is a prediction error mean square error matrix from time k-1 to time k, HkIs the observation matrix at time k, RkVariance matrix of the measured noise sequence at time k, Rk=[0.01];
Updating state variable X with measured valuesk=Xk/k-1+Kk(y(k)T-Hk) In the formula, y (k)TTo the desired output, HkOutputting for network training;
updating an error covariance matrix Pk=(I-KkHk)Pk/k-1Wherein, the identity matrix I ═ diag (1);
s3: and predicting the concentration of the PM2.5 by using a dynamic evolution model of the concentration value of the PM 2.5.
In order to clearly and vividly display the predicted PM2.5 concentration value, as a preferred technical solution, the present invention further includes step S4: the PM2.5 concentration predicted in step S3 is displayed by a table and/or a map visualization warning map.
Compared with the prior art, the technical scheme that this application provided, the technological effect or advantage that have are: the method predicts the concentration of the PM2.5 particles, enables people to know the distribution of the PM2.5 particles in advance, brings convenience to travel and life of people, and has extremely important significance in preventing and treating air pollution and preventing diseases of people.
Drawings
FIG. 1 is a comparative graph of the actual value of a PM2.5 concentration prediction dynamic evolution model based on UKFNN and a training value;
FIG. 2 is an error curve diagram of prediction of a UKFNN-based PM2.5 concentration prediction dynamic evolution model;
FIG. 3 is a graph of the error percentage predicted by a UKFNN-based PM2.5 concentration prediction dynamic evolution model;
FIG. 4 is a graph showing the comparison between the true values and the training values of the UKFNN model and the BPNN model;
FIG. 5 is a graph of the comparison of training errors in the UKFNN model and the BPNN model;
fig. 6 is a PM2.5 concentration warning diagram.
Detailed Description
The embodiment of the application provides a PM2.5 concentration prediction method based on an unscented Kalman neural network, so as to solve the technical problems of inaccuracy in PM2.5 concentration prediction and large error in the prior art.
In order to better understand the technical solutions, the technical solutions will be described in detail below with reference to the drawings and specific embodiments.
Examples
A PM2.5 concentration prediction method based on an unscented Kalman neural network comprises the following steps:
s1: acquiring historical data of PM2.5 concentration;
s2: carrying out recursion operation by using an unscented Kalman neural network, and circularly correcting the weight and the threshold of the neural network by continuously carrying out online prediction to realize prediction of the PM2.5 concentration chaotic time sequence so as to establish a dynamic evolution model for predicting the PM2.5 concentration:
is provided with an N-layer forward neural network, and the number of neurons in each layer is Sk(k is 1,2, …, N), the input layer is the first layer, the output layer is the nth layer, and the connection weights for the k layer neurons are(i=1,2,…,Sk-1,j=1,2,…,Sk) Taking the weight w and the threshold b of the neural network as state variables of unscented kalman filtering, taking the output of the neural network as a measurement variable of the unscented kalman filtering, and forming a state vector by all the weights and the thresholds in the neural network:
X = [ w 11 1 ... w s 1 s 2 1 w 11 2 ... w s 1 s 2 2 b 11 1 w 11 N - 1 ... w s 1 s 2 N - 1 b 1 1 ... . b s 1 1 b 1 2 ... . b s 2 2 b 1 N - 1 ... . b s n - 1 N - 1 ] T ,
the state equation and observation equation for the system can be expressed as:
X k = X k - 1 Y e k = h ( W k , X k ) + V k = F N ( W k N , F N - 1 ( W k N - 1 ... F 2 ( W k 2 , X k ) ) ) + V k
in the formula, h (-) is a nonlinear transformation, FNIs the N layer transfer function of the neural network, YekTo desired output, XkAs an input vector, VkTo observe noise, it is random white noise, set to 0 in unscented kalman neural network;
the time is updated as: predicted state variable X from time k-1 to time kk/k-1=AXkATPrediction error covariance matrix P from time k-1 to time kk/k-1=APkATWherein A is [1 ]],PkThe covariance matrix at the k moment;
the measurement is updated as: computing kalman filter gainIn the formula, KkA filter gain matrix for time k, Pk/k-1Is a prediction error mean square error matrix from time k-1 to time k, HkIs the observation matrix at time k, RkVariance matrix of the measured noise sequence at time k, Rk=[0.01];
Updating state variable X with measured valuesk=Xk/k-1+Kk(y(k)T-Hk) In the formula, y (k)TTo the desired output, HkOutputting for network training;
updating an error covariance matrix Pk=(I-KkHk)Pk/k-1Wherein, the identity matrix I ═ diag (1);
s3: and predicting the concentration of the PM2.5 by using a dynamic evolution model of the concentration value of the PM 2.5.
In order to clearly and vividly display the predicted PM2.5 concentration value, as a preferred technical solution, the present invention further includes step S4: the PM2.5 concentration predicted in step S3 is displayed by a table and/or a map visualization warning map.
In this embodiment, training models of PM2.5 concentration values of 13 regions, west ampere city between 14 days 1 month and 3 months 11 days 3 months 2013 are established, and a learning training process and a simulation result are described by taking a grassland region as an example.
1) PM2.5 concentration prediction based on unscented Kalman neural network
And taking the weight value and the threshold value of the neural network as state variables of the UKF, and taking the output of the neural network as measurement variables of the UKF. And (3) forming a state vector by all weights and thresholds in the neural network:
X = [ w 1 s 1 1 ... w 1 s 1 s 2 b 1 1 s 1 w 2 s 1 1 b 2 11 ] T , ( s 1 = 6 , s 2 = 1 ) - - - ( 1 )
wherein,
w 1 = - 1.6810 - 0.2834 0.4875 1.6035 - 0.3082 1.5307 2.1457 - 0.8814 0.2406 - 2.3426 - 0.7667 - 1.1243 2.8476 - 0.3048 0.5918 0.8294 - 0.6096 - 0.2993 , w 2 = - 0.9656 0.8364 0.2417 - 0.3390 0.4409 0.1224
b1=[-1.1071 -0.3188 -0.7754 -1.6647 1.1671 -1.8766]T,b2=[-0.6239]
the state equation and observation equation for the system can be expressed as:
X k = X k - 1 Y e k = h ( W k , X k ) + V k = F N ( W k N , F N - 1 ( W k N - 1 ... F 2 ( W k 2 , X k ) ) ) + V k - - - ( 2 )
in the formula, FNIs the N layer transfer function of the neural network, YekTo desired output, XkAs an input vector, VkTo observe noise, it is random white noise, set to 0 in unscented kalman neural network;
the Kalman algorithm operates as follows:
the time is updated as: predicted state variable X from time k-1 to time kk/k-1=AXkATPrediction error covariance matrix P from time k-1 to time kk/k-1=APkATWherein A is [1 ]],PkThe covariance matrix at the k moment;
X=[-1.6810 1.6035 2.1457 -2.3426 2.8476 0.8294 -0.2834 -0.3082 -0.8814 -0.7667 -0.3048 -0.6096 0.4875 1.5307 0.2406 -1.1243 0.5918 -0.2993 -1.1071 -0.3188 -0.7754 -1.6647 1.1671 -1.8766 -0.9656 0.8364 0.2417 -0.33900.4409 0.1224 -0.6239]T
the measurement is updated as: computing kalman filter gainIn the formula, KkA filter gain matrix for time k, Pk/k-1Is a prediction error mean square error matrix from time k-1 to time k, HkIs the observation matrix at time k, RkVariance matrix of the measured noise sequence at time k, Rk=[0.01];
K=[-0.1424 0.1184 0.2102 -0.1627 0.5129 0.1188 -0.6120 0.5076 1.0498-0.8239 1.2770 0.4568 -0.1038 0.1177 0.1747 -0.1864 0.3739 0.0877 -0.15040.1165 0.3069 -0.5505 0.5667 0.3761 0.1098 0.0274 0.0347 0.1938 0.0229 0.07660.2119]T
Updating state variable X with measured valuesk=Xk/k-1+Kk(y(k)T-Hk) In the formula, y (k)TTo the desired output, y (k)T=[0.038],HkFor network training output, Hk=[0.2419];
Updating an error covariance matrix Pk=(I-KkHk)Pk/k-1In the formula, the identity matrix I is diag (1)
H=[-0.0320 0.0444 0.0121 -0.0044 0.0115 0.0028 -0.0489 0.0678 0.0185-0.0067 0.0175 0.0044 -0.0334 0.0463 0.0127 -0.0046 0.0120 0.0030 -0.14820.2053。0.0561 -0.0204 0.0531 0.0132 0.1894 0.5674 0.36630.0643 0.8600 0.12280.10]
After the program is operated, an output result of a dynamic evolution model for predicting the PM2.5 concentration is obtained, and a comparison curve graph of an actual value and a training value of a beach zone is obtained and is shown in figure 1, figure 2 is an error curve graph, and figure 3 is an error percentage curve graph.
2) PM2.5 concentration prediction based on unscented Kalman neural network (AFNN) and PM2.5 concentration prediction based on BP neural network (BPNN) are compared
For clearer comparison of the PM2.5 concentration training results of the UKFNN and the BPNN on the beach area, respectively, fig. 4 is a comparison graph of the true value and the training value of the dynamic PM2.5 concentration evolution model based on the UKFNN and the BPNN, and fig. 5 is an error comparison graph of the dynamic PM2.5 concentration evolution model based on the UKFNN and the BPNN. As can be seen from fig. 4 and 5, the training values of UKFNN are closer to the true values and generate smaller errors than BPNN. In order to compare the training effects of the two models more conveniently, a part of data in the output values of the training of the concentration of PM2.5 in the beach area is selected to be compared with the real values, and a data table is listed, as shown in the table 1.
TABLE 1 comparison table of training output values and true values of two models in grassland and beach area
In order to make people know the concentration of PM2.5 in the next few days more directly and clearly so that people can take corresponding preventive measures in life and production, the embodiment predicts the concentration of PM2.5 in the next seven days of 13 regions in the city of sienna based on UKFNN, obtains corresponding predicted values as shown in table 2, and performs graphical early warning on the predicted concentration. The graph visualization early warning has the main function that after the concentration predicted value of PM2.5 is obtained, the obtained data is displayed on the corresponding area graph, so that the effect of simply and conveniently forecasting and reminding residents in each area is achieved. Fig. 6 shows a PM2.5 concentration warning map of 13 regions in west ampere city, 24 days 4 and 24 months in 2013, and table 3 shows an environmental quality grade table of 13 regions. As can be seen from fig. 6 and table 3: 2013-4-24, wherein the environmental quality grade of a high and new area, a city sports office, a Hades area and a poling area is good; the Xingqing district, the Changan district, the Yangjiang culture group, the textile city and the Jingkai district belong to light pollution; the small village and the wide Tan belong to moderate pollution; high-pressure plant switching and the grass beach are serious pollution.
Seven days PM2.5 concentrations (μ g/m) in 213 regions in Table3) Prediction value
Table 32013-4-2413 area PM2.5 environmental quality grade table
In the foregoing embodiment of the present application, a PM2.5 concentration prediction method based on an unscented kalman neural network is provided, including the following steps: acquiring historical data of PM2.5 concentration, carrying out recursive calculation based on an unscented Kalman neural network, programming by using MATLAB simulation software, continuously carrying out online prediction, continuously correcting weight and threshold, establishing a dynamic evolution model for predicting PM2.5 concentration, and establishing visualization early warning on the basis of obtaining the dynamic evolution model and prediction data so as to achieve the early warning effect after data prediction. Compared with the modeling based on the BP neural network, the modeling based on the unscented Kalman neural network is more accurate in prediction result and has smaller error.
It should be noted that the above description is not intended to limit the present invention, and the present invention is not limited to the above examples, and those skilled in the art may make variations, modifications, additions or substitutions within the spirit and scope of the present invention.

Claims (2)

1. A PM2.5 concentration prediction method based on an unscented Kalman neural network is characterized by comprising the following steps:
s1: acquiring historical data of PM2.5 concentration;
s2: carrying out recursion operation by using an unscented Kalman neural network, and circularly correcting the weight and the threshold of the neural network by continuously carrying out online prediction to realize prediction of the PM2.5 concentration chaotic time sequence so as to establish a dynamic evolution model for predicting the PM2.5 concentration:
is provided with an N layers of forward neural networks, each layer of neuronsNumber Sk(k is 1,2, …, N), the input layer is the first layer, the output layer is the nth layer, and the connection weights for the k layer neurons are(i=1,2,…,Sk-1,j=1,2,…,Sk) Taking the weight w and the threshold b of the neural network as state variables of unscented kalman filtering, taking the output of the neural network as a measurement variable of the unscented kalman filtering, and forming a state vector by all the weights and the thresholds in the neural network:
X = [ w 11 1 ... w s 1 s 2 1 w 11 2 ... w s 1 s 2 2 b 11 1 w 11 N - 1 ... w s 1 s 2 N - 1 b 1 1 .... b s 1 1 b 1 2 .... b s 2 2 b 1 N - 1 .... b s k - 1 N - 1 ] T ,
the state equation and observation equation for the system can be expressed as:
X k = X k - 1 Y e k = h ( W k , X k ) + V k = F N ( W k N , F N - 1 ( W k N - 1 ... F 2 ( W k 2 , X k ) ) ) + V k
in the formula, h (-) is a nonlinear transformation, FNIs the N layer transfer function of the neural network, YekTo desired output, XkAs an input vector, VkTo observe noise, it is random white noise, set to 0 in unscented kalman neural network;
the time is updated as: predicted state variable X from time k-1 to time kk/k-1=AXkATPrediction error covariance matrix P from time k-1 to time kk/k-1=APkATWherein A is [1 ]],PkThe covariance matrix at the k moment;
the measurement is updated as: computing kalman filter gainIn the formula, KkA filter gain matrix for time k, Pk/k-1Is a prediction error mean square error matrix from time k-1 to time k, HkIs the observation matrix at time k, RkVariance matrix of the measured noise sequence at time k, Rk=[0.01];
Updating state variable X with measured valuesk=Xk/k-1+Kk(y(k)T-Hk) In the formula, y (k)TTo the desired output, HkOutputting for network training;
updating an error covariance matrix Pk=(I-KkHk)Pk/k-1Wherein, the identity matrix I ═ diag (1);
s3: and predicting the concentration of the PM2.5 by using a dynamic evolution model of the concentration value of the PM 2.5.
2. The method for predicting the concentration of PM2.5 based on the unscented kalman network according to claim 1, further comprising the step S4: the PM2.5 concentration predicted in step S3 is displayed by a table and/or a map visualization warning map.
CN201610457234.8A 2016-06-22 2016-06-22 PM2.5 concentration prediction method based on Unscented kalman neutral net Pending CN106126909A (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
CN201610457234.8A CN106126909A (en) 2016-06-22 2016-06-22 PM2.5 concentration prediction method based on Unscented kalman neutral net

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
CN201610457234.8A CN106126909A (en) 2016-06-22 2016-06-22 PM2.5 concentration prediction method based on Unscented kalman neutral net

Publications (1)

Publication Number Publication Date
CN106126909A true CN106126909A (en) 2016-11-16

Family

ID=57269256

Family Applications (1)

Application Number Title Priority Date Filing Date
CN201610457234.8A Pending CN106126909A (en) 2016-06-22 2016-06-22 PM2.5 concentration prediction method based on Unscented kalman neutral net

Country Status (1)

Country Link
CN (1) CN106126909A (en)

Cited By (6)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN109063938A (en) * 2018-10-30 2018-12-21 浙江工商大学 Air Quality Forecast method based on PSODE-BP neural network
CN109061506A (en) * 2018-08-29 2018-12-21 河海大学常州校区 Lithium-ion-power cell SOC estimation method based on Neural Network Optimization EKF
CN111289414A (en) * 2020-03-12 2020-06-16 徐州工业职业技术学院 PM2.5 pollution monitoring and predicting method
CN112649337A (en) * 2020-12-21 2021-04-13 张家口市杰星电子科技有限公司 Oil smoke online monitoring method and device
CN113654959A (en) * 2021-07-29 2021-11-16 中国科学院合肥物质科学研究院 Rapid inversion method and system for time-space distribution of smoke cloud concentration
WO2023044770A1 (en) * 2021-09-24 2023-03-30 京东方科技集团股份有限公司 Dry pump downtime early warning method and apparatus, electronic device, storage medium, and program

Cited By (7)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN109061506A (en) * 2018-08-29 2018-12-21 河海大学常州校区 Lithium-ion-power cell SOC estimation method based on Neural Network Optimization EKF
CN109063938A (en) * 2018-10-30 2018-12-21 浙江工商大学 Air Quality Forecast method based on PSODE-BP neural network
CN111289414A (en) * 2020-03-12 2020-06-16 徐州工业职业技术学院 PM2.5 pollution monitoring and predicting method
CN112649337A (en) * 2020-12-21 2021-04-13 张家口市杰星电子科技有限公司 Oil smoke online monitoring method and device
CN113654959A (en) * 2021-07-29 2021-11-16 中国科学院合肥物质科学研究院 Rapid inversion method and system for time-space distribution of smoke cloud concentration
CN113654959B (en) * 2021-07-29 2023-11-17 中国科学院合肥物质科学研究院 Rapid inversion method and system for smoke cloud concentration space-time distribution
WO2023044770A1 (en) * 2021-09-24 2023-03-30 京东方科技集团股份有限公司 Dry pump downtime early warning method and apparatus, electronic device, storage medium, and program

Similar Documents

Publication Publication Date Title
CN106126909A (en) PM2.5 concentration prediction method based on Unscented kalman neutral net
Rao et al. A survey on air quality forecasting techniques
Jalalkamali Using of hybrid fuzzy models to predict spatiotemporal groundwater quality parameters
CN105784556B (en) A kind of air fine particles PM based on Self-organized Fuzzy Neural Network2.5Flexible measurement method
Fu et al. A novel integrated method based on a machine learning model for estimating evapotranspiration in dryland
Ebrahimi-Khusfi et al. Accuracy, uncertainty, and interpretability assessments of ANFIS models to predict dust concentration in semi-arid regions
CN109308544B (en) Blue algae bloom prediction method based on contrast divergence-long and short term memory network
Memarianfard et al. Artificial neural network forecast application for fine particulate matter concentration using meteorological data
CN113011455B (en) Air quality prediction SVM model construction method
Ayturan et al. Short-term prediction of PM2. 5 pollution with deep learning methods
CN114004163A (en) PM2.5 inversion method based on MODIS and long-and-short-term memory network model
CN108805253B (en) PM2.5 concentration prediction method
Wang et al. Weather condition-based hybrid models for multiple air pollutants forecasting and minimisation
Akkoyunlu et al. A neural network-based approach for the prediction of urban SO2 concentrations in the Istanbul metropolitan area
Zerouali et al. Artificial intelligent systems optimized by metaheuristic algorithms and teleconnection indices for rainfall modeling: The case of a humid region in the mediterranean basin
Mirzania et al. Hybrid COOT-ANN: a novel optimization algorithm for prediction of daily crop reference evapotranspiration in Australia
Lu et al. Remote sensing-based house value estimation using an optimized regional regression model
Khan et al. An outlook of ozone air pollution through comparative analysis of artificial neural network, regression, and sensitivity models
Zhang et al. LSTM-based air quality predicted model for large cities in China
Tasdemır et al. The effect on the wind power performance of different normalization methods by using multilayer feed-forward backpropagation neural network
Lu et al. A deep belief network based model for urban haze prediction
Valencia et al. A general regression neural network for modeling the behavior of PM10 concentration level in Santa Marta, Colombia
Xie et al. Multi-sensor data fusion based on fuzzy neural network and its application in piggery environmental control strategies
CN107545121A (en) A kind of Soil Temperature And Moisture data assimilation method based on EnPF
Wang et al. Estimation of urban AQI based on interpretable machine learning

Legal Events

Date Code Title Description
C06 Publication
PB01 Publication
C10 Entry into substantive examination
SE01 Entry into force of request for substantive examination
RJ01 Rejection of invention patent application after publication
RJ01 Rejection of invention patent application after publication

Application publication date: 20161116