Earth and Planetary Sciences » Oceanography and Atmospheric Sciences » "Advanced Air Pollution", book edited by Farhad Nejadkoorki, ISBN 978-953-307-511-2, Published: August 17, 2011 under CC BY-NC-SA 3.0 license. © The Author(s).

Chapter 25

Artificial Neural Networks - a Useful Tool in Air Pollution and Meteorological Modelling

By Primož Mlakar and Marija Zlata Božnar
DOI: 10.5772/20824

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Artificial Neural Networks - a Useful Tool in Air Pollution and Meteorological Modelling

Primož Mlakar and Marija Zlata Božnar

1. Introduction

Artificial neural networks have become a widely used tool in several air pollution and meteorological applications. Yi and Prybutok (1996) used MPNN for surface ozone predictions, as well as Comrie (1997). Several prediction models were also made for other pollutants; for instance for SO2 (Božnar et al., 1993) and for CO (Moseholm et al., 1996). Marzban & Stumpf (1996) used MPNN for predicting the existence of tornadoes.

A review article by Gardner (1998) described a variety of applications, mainly in the field of air pollution forecasting and pattern classification. Though the number of applications is growing, especially in recent years, no special attention has been paid to the principles of artificial neural network usage in environmental applications.

Our group first established a method for short term forecasting of SO2 concentrations on the basis of a multilayer perceptron neural network (Božnar et al, 1993), but in the following years we use an artificial neural networks in several other applications that differ very much each another.

In this article we intend to show examples of a variety of applications of artificial neural networks in air pollution and the meteorological field. Examples are taken from our past experience, extending over a decade.

Several applications in this field start from fundamentals and too much attention is paid to optimization and speeding up of the learning algorithms. From our experience this should be a minor problem for an environmental modeller and does not significantly affect the final model quality if modern tools are used. In the process of model construction other factors are much more crucial – such as feature determination, pattern selection, and learning process optimization. These are the methods that are derived from the basic principle of artificial neural networks – that is the ability to learn information from given examples.

In this article we intend to show some solutions for the effective transformation of measured information into air pollution and meteorological models. We hope that the variety of examples will inspire new applications and methods that will serve the air pollution modelling community. The mystique of artificial neural networks, derived directly from their name, prevents many modellers from using them. It is the purpose of this article to demystify this useful mathematical tool and in this way encourage its usage.

2. Artificial neural networks – several types for different purposes

Artificial neural networks can be divided into several groups according to their topology. The tool was firstly widely used in the pattern recognition field. The topologies vary from feed forward neural networks with several hidden layers, to topologies with backward loops that make the result sequence dependent, to fuzzy logic and several automatic sorting tools. A detailed explanation of this groups is far beyond the scope of this article. The reader interested in this issue can get information from several books (Lawrence, 1991).

In this article we focus on two main “species” of artificial neural networks that can cover a huge variety of air pollution and meteorological modelling applications. The two selected are the Multilayer Perceptron artificial Neural Network (MPNN) and the Kohonen neural network (KNN). Both can be replaced by other artificial neural networks for the same purpose, but this does not change the method of using these tools. In this article MPNN and KNN can both be treated as one of the best possible solutions. The authors of this article have no intention to argue about the qualifications of other topologies.

In this article it will be shown what the most suitable applications of MPNN and KNN are. The latter is not so widely used although it has great potential in environmental problems.

MPNN is mathematically speaking a universal approximator (Hornik, 1991; Kurkova, 1992). It can reconstruct arbitrary multivariable and highly non-linear functions. Therefore it is a suitable tool for modelling atmospheric phenomena whose behaviour has not yet been described by formulas but is only known from measured examples.

KNN, on the other hand, is a structure capable of sorting a multitude of multivariable samples or patterns into groups of similar ones. It is important that it can find these groups without a teacher – so-called unsupervised learning. This ability becomes extremely important when dealing with multivariable patterns where similarity rules are not obvious.

3. Multilayer perceptron artificial neural network (MPNN)

The structure of MPNN was introduced by Rumelhart (1986). It is one of the basic neural network structures from which several others were derived.

The basic element of the MPNN is a neuron. Several neurons are organized into layers – input, hidden (one or more) and output layer. Each neuron has a simple structure that mimics the functionality of the neuron found in animals and the whole structure of layers mimics the brain structure. This similarity gives rise to the name. Each neuron firstly summarizes the weighted input values and then passes the sum through the transfer function. If the transfer function is nonlinear, such as a basic sigmoid function or hyperbolic tangent, then the whole structure acquires its great ability as an universal approximator.

The neurons in the input layer take the values from the model input variables and pass the values to the neurons in the hidden layer, the hidden layer neurons pass the values to the higher hidden layers and finally to the output layer that gives the model output value. The output of each neuron is passed to the input of all neurons in the next higher layer. All the connections between neurons are weighted. These interconnection weights are the basic parameters of the model that are adjusted during the learning process.

Model inputs take their values from the input features – measured parameters that determine the output of the model. Model output(s) represents the phenomenon that is being reconstructed (approximated). Outputs are called output features.

The values of one particular realization of all inputs is called the input vector, and the model outputs values form the output vector. Both vectors together form a pattern. A pattern is therefore like one dot in the multivariable space lying on the surface of the function the model is approximating.

The whole idea of constructing a model to approximate a multivariable function is the following: Firstly enough patterns should be available (for instance from the measurements) with known input and output features. These patterns should be uniformly spread over the whole investigated domain. Then the model topology is designed according to the number of input and output features. The model learning stage consists of several adjustments of model interconnection weights – in order to minimize the average error between the actual measured output values and the output values that are produced by the neural network. One of the algorithms that can be used for this purpose is the backpropagation algorithm. In the process of learning the MPNN takes the information (about phenomenon under investigation) that is available in the learning patterns and when learning is completed (the model constructed) it can give the results for previously unknown patterns – where only input values are presented to the network. This is possible if there were similar patterns (to the unknown pattern) in the learning set. This is the so-called generalizing capability of the MPNN. The similarity is mathematically speaking the distance between two patterns.

The basic rule of MPNN model construction is therefore to provide information rich learning patterns.

There are some basic steps and methods that should be used in the model construction process to obtain effective models. These steps will be summarized in the following paragraphs and their practical use is shown in the exemplary applications that follow this section.

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Figure 1.

The structure of a feedforward multilayer perceprtron neural network

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Figure 2.

Node (artificial neuron or perceptron)

3.1. Feature determination

Feature determination should be done in order to properly define the modelled domain (independent variables), to enable all important information to be captured, to simplify MPNN and therefore achieve more effective learning, to reduce the number of learning patterns needed and to increase the probability of finding the global minimum of the error function during learning.

Firstly the modeller should determine what the desired output of the model is. This can be one or several parameters that can be measured or calculated. These are the output features. For several output features it is usually more effective to establish one model for each feature than one model for all. Then the input features should be determined from several other measured parameters that represent the possible variables that cause or influence the output parameter. Input features are the ones that have significant influence on the outputs. Feature determination can be done heuristically (using expert knowledge about the phenomenon under investigation) or using other methods (feature reduction that can be extraction or selection (Devijver, 1982); examples of selection are contribution factors or Saliency metrics techniques). In both the latter methods basically the model is firstly trained with all available features and the higher absolute values of interconnection weights reveal the more important input features.

It is extremely important that the feature determination process should not be based on a linear method. Most of the processes in the atmosphere over complex terrain are not linearly dependent on each other. Therefore if the input features are chosen from the possible input measurements by a linear criterion (for instance calculation of the linear correlation factor between the examined input measurement and output modelled parameter), then most probably the important ones are rejected. An MPNN has the very important ability of being able to simulate highly non-linear dependencies and the modeller should obtain the most advantage out of this. The above mentioned contribution factors and Saliency metrics techniques both allow highly-nonlinear relationships to be found.

3.2. Model construction

The data base of the measurements (values of input and output features for several situations – for instance for several measuring intervals) form the data base of patterns. It should be divided into several sets (training, testing, production, on-line, remaining). The training set is used to adjust the interconnection weights of the MPNN model. The testing set is used periodically during the learning process to test the model’s generalizing capabilities – this is optimization during learning. The final model is the one that gives the best results on the testing set. In this way we prevent the model from becoming too dependent on known patterns and therefore losing the generalizing capabilities. The training and testing sets together form the learning set. A third set different from the previous ones is the production set. This set is used for model verification to determine its expected error. All three sets should have known input and output vectors. When the model has been tained, it can be used on patterns with unknown output values. This set of patterns is the on-line set – when a newly measured situation arises, the model gives us an answer.

3.3. Pattern selection

Only patterns with valuable information should be put into the learning set, while others are rejected and form the remaining set. The pattern selection can be done either heuristically or a Kohonen neural network can be used to sort patterns into groups and in this way the KNN shows which ones are more important. The main goal of pattern selection techniques is to select patterns over the whole of the modelled domain. These patterns should contain all the information about the studied phenomenon. Patterns selected for the training and testing set should represent all important but usually rare situations that may appear during the further use of the model. Just having a lot of patterns that are the most common, but do not represent the rare complicated situations, is certainly not enough for an effective model.

3.4. Network topology determination

The topology (number of neurons in the input, hidden and output layers) is determined from the number of features and the number of patterns. Input and output features determine the number of neurons in the input and output layers. The number of neurons in the hidden layer(s) is usually determined as the number of inputs divided by two plus the square root of the number of patterns. There is no rule for a perfect solution – the user should acquire some experience.

3.5. Training and testing process

After the topology has been determined and the patterns prepared, a training algorithm (for instance a backpropagation algorithm) should be used to determine the model’s interconnection weights. Basically the algorithms have parameters that determine the speed of learning. Learning is a process of finding the global minimum of the error function. If during the learning process we move in big steps, the model cannot reach the bottom of the minimum function, but escapes quickly to other local minima. If the steps are too small, the model can be stuck in a local minimum far from the global one. During the learning process, the network should be periodically tested on the testing set (not included in the training set) to prevent overtraining. At the end the model is the network giving the best results on the optimization – testing set. This is an optimizing process that finds the network with best generalizing capabilities instead of the best memorizing capabilities. Learning speed determination and optimization are usually far more important for successful learning than having a slightly better or worse algorithm.

3.6. Model verification

When the model is trained, it should always be validated on the production set to determine the expected error in further on-line use. To obtain a fair judgement of the model’s abilities, the patterns that form the production set for validation should not be presented to the model in the training or testing set at all.

The training, testing and production sets should reflect all the situations that can arise in the on-line use of the model.

Feature determination and pattern selection are therefore the most crucial steps in model construction and usually determine the model’s abilities.

4. Short term forecasting of ambient SO2 concentrations using MPNN

First let us use the MPNN as a basis for short term ambient SO2 concentration forecasting. As an example for study the area around the Šoštanj Thermal Power Plant in Slovenia was used. The studied domain of 30 by 30 km with the TPP in the centre lies in very complex terrain – a basin surrounded by several hills that are cut by valleys. The area is characterized by very low wind speeds, frequent calm situations and thermal inversions in winter that cause severe air pollution. The whole of the studied area is covered by 6 ambient automatic measuring stations (measuring basic meteorological parameters like wind, air temperature, relative humidity and precipitation and pollutant concentrations) and emission stations in the TPP. All the stations collect data every half hour.

The idea was to test the forecasting abilities of the new MPNN tool. Low winds and quick wind changes in the area cause severe air pollution peaks of very short duration (only a few intervals). We tried to establish a model that would forecast the SO2 concentration for the following half hour from the data available for present or past intervals (air pollution and meteorological measurements). The task was a difficult one, because the work was concentrated on rapid warning of short but severe SO2 peaks and on not causing false alarms.

The data base of measurements was huge in all dimensions. There were over 50 parameters that were measured every half hour and several years of data were available for analysis (one year consists of over 17000 half hour intervals). It is obvious that all the data could not be simply used together because of the computational space and time problems (this was at the beginning of the PC era) and more importantly because the patterns with less information would prevail over the sparse patterns carrying crucial information. The same is valid for the different measured parameters that are the possible inputs to the model. This huge data base forced us to establish methods for feature determination and pattern selection. The idea was to find patterns that carry most of the available information and to determine which measurements influence the modeled ambient SO2 concentration at a chosen station. It is very important to stress that we were seeking for highly non-linear dependencies that the MPNN is able to model.

The whole procedure of feature determination and pattern selection techniques is explained in detail in several our publications (Božnar, 1997; Mlakar, 1997; Mlakar & Božnar, 1996; Božnar et. al, 1993; Božnar & Mlakar, 2001).

This approach resulted in a model for a chosen station that used around 15 input measurements from that and other stations to forecast the local SO2 air pollution. The model was trained with small (in comparison to the huge data base available) data sets of chosen patterns. This resulted in a significant improvement of model forecasting ability.

It is also important that the usual cost functions (linear correlation coefficient, mean square error, …) are not suitable for forecasting problems where most of the time nothing out of the ordinary is happening, but when the peak of concentration comes, it is severe and short. It was very easy to obtain very good values of the above mentioned cost functions – but this does not tell anything about the real model capabilities (if it really correctly and on-time predicts the coming SO2 peak). Therefore we defined a new cost function termed p6 (Mlakar, 1997). This is the probability of successful forecasting of a high concentration without causing false alarms. It is a very sharp cost function that clearly distinguishes good models from the ones that are in the range of naive predictors.

In the process of SO2 modelling it was clearly proven that feature determination and pattern selection techniques influence the final model performance much more than the training algorithms and other details of the establishment of the model. This is caused by the fact that the information carried in the features and patterns of the available data set should be presented to the model in the learning phase in a “model understandable” way. To generalize this principle it can be stated that an understandable way is similar to a humanly understandable way. People also cannot learn effectively if the informative and key examples are hidden in large quantity of useless examples.

5. Daily ozone peak forecasting for a semi-urban area

A model for ozone forecasting was established for the city of Nova Gorica in Slovenia close to the Adriatic sea (Grašič, 2006). During the hot summer period high ozone episodes are often recorded. The idea of constructing the model is to have information about the ozone pollution peak of the following day already available in the evening of the day before 19:00. That would allow the population sensitive to ozone to plan their activities for the following day.

Slovene legislation defines warning values for a one hour average ozone concentration and for eight hour moving average values. We concentrated our research on determination of the maximum hourly value of ozone concentration of the following day. Ozone peaks usually occur during the midday period, therefore the task deals with forecasting cca 17 hours in advance.

The available data were measurements from a local air pollution measuring station (SO2, O3, NO, NO2, CO, VOC) that also measures ground level meteorological parameters (wind, air temperature, relative humidity, air pressure and global solar radiation). In principle in the evening meteorological forcasts are available for the city of Nova Gorica. Of these values two are more reliable – the maximum daily air temperature and the average wind speed and direction for the following midday. For the purpose of establishing the model from the historical data base, actual measurements of these two parameters on the following days were taken instead of prognostic values.

A two year data base was available for model construction and verification. In this case only one pattern per day is available. Therefore two years data give cca 700 patterns only. Out of this data base one winter and one summer month were excluded (were not used in the learning process at all) for independent model verification.

Because of the small data base available for learning it was only divided into a randomly taken group of 10% for testing (optimising) and the remaining 90% used for adjustment of the model's weights (training). No other pattern selection was performed.

Feature selection was done in two steps. Firstly a wide selection of possible input features was made using chemical knowledge about ozone formation and other related processes. Then this wide range was narrowed using contribution factors. The finally selected input features were air temperature, global solar radiation, NO, NO2, NOx, CO, O3 all as 24h average values calculated at 19:00 on the previous day, prognostic vector wind speed, sine of wind direction and maximal hourly air temperature for the day of prediction (all three prognostic values were taken from the available measured data base).

The verification of the model for approximately two months not used in the learning process showed that the model has a good performance. For final judgement, a longer verification period would be necessary. It is also expected that its performace would be slightly worse if actual meteorological prognostic model predictions were taken instead of real measurements (for the last three features).

6. Ground level wind reconstruction over complex terrain

Air pollution prediction was the first but not the only field where we successfully constructed MPNN based models.

Recently we encountered the problem of missing ground level wind data on the location of a planned industrial plant. The time available for the task was short and therefore it was not possible to perform one year of measurements, and only 6 weeks of measurements were available. The location was again in the complex terrain of Zasavje, Slovenia. Study of the winds in the area clearly show that ground level wind reconstruction from global prognostic meteorological models would not be useful because of the orographic complexity of the area.

But there are six existing meteorological stations in the area on sited from 2 to 10 km from the planned location. None of these locations has the same characteristics as the new location, so their data could not be used directly.

Our idea was to reconstruct one year of ground level wind data on the new location from one year of wind data at the old station locations. This is a very suitable task for a MPNN based model. The six weeks data base when wind measurements were available at both old and new locations was used to train and verify the model.

In contrast to the SO2 forecasting problem, this problem again has a small data base consisting of 6 weeks of half hour average values of wind speed and direction measurements at 7 locations. Therefore only the last week of measurements was reserved for final model verification and was not used for model learning. The remaining five week data base was again divided into a randomly taken 10% test set for optimization and 90% for training.

For every station vector and scalar half hour average values and maximum values of wind speed were available, as well as wind direction. The vectors were also decomposed into cosine and sine components. The decomposition into cosine and sine components is a trick that should be used whenever we have a measurement of circular nature (such as azimuth angle or hour within a day). All these measurements and their combination at the old stations locations are candidates for model input features.

Firstly a heuristic feature selection was performed by simply comparing the similarity of wind roses for the new and old locations. Then the final feature selection was repeated using the contribution factors technique.

The results of the model verification show better results than expected, considering the high complexity of the area studied.

The reconstructed wind speed mean absolute error at the new location was less than0.4 m/s, the mean squared error 0.45 m/s and the linear correlation coefficient 0.84. The average absolute error for the wind direction was 35 degrees over the whole verification data set (which contains a lot of very low wind speeds and calms) and as little as15.5 degrees if only cases with a wind speed over 3 m/s were examined.

7. Other meteorological applications of MPNN

We successfully applied MPNN in the following meteorological problems that will be only shortly explained:

  • reconstruction of SODAR measurements,

  • short term forecasting of ground level wind,

  • reconstruction of diffuse solar radiation,

  • correction of long wave solar radiation measurements.

7.1. Reconstruction of SODAR measurements

SODAR measurements are crucial for modern numerical Lagrangean particle models used for short scale air pollution reconstruction over complex terrain. But SODAR measurements are not always available. SO2 air pollution was studied in detail (fourth chapter of this article) in the Šoštanj area of Slovenia. In the Šoštanj basin SODAR measurements were available only for an aproximately two month period during a measuring campaign (Elisei et. al, 1992). The area of the basin and surrounding hills is well covered with ground level wind measuring stations.

We made a MPNN based model to see whether it was possible to reconstruct SODAR upper layer (not ground level) measurements from the measurements at other stations. A test model was made for the level 50m above the ground. The results were quite good (comparable to the Trbovlje wind reconstruction). Some details can be found in paper by Božnar and Mlakar (1995).

7.2. Short term forecasting of ground level wind

In the same area around Šoštanj short term ground level wind forecasts would also be very useful as an input to an SO2 concentration forecasting model. Forecasts of wind changes for the next few half hour intervals are more dependent on local thermal and solar radiation changes than on the movement of global fronts. Due to terrain complexity again such forecasts cannot be derived from regional prognostic meteorological models, because they operate in too sparse (time and space) coordinates.

We constructed a model for ground level wind forecasting for one of the stations in the Šoštanj region. The forecast was made for one averaging interval in advance. The input features were ground level wind measurements from the studied station and from two other stations for the current time interval. For wind speed one interval in the past was also used. The results were very good for wind speed and acceptable for wind direction prediction. Some details can be found in paper by Božnar and Mlakar (1995).

7.3. Reconstruction of diffuse solar radiation measurements and correction of long wave solar radiation measurements

Our colleagues from Sao Paulo, Brazil made extensive research on the measurement of and construction of correlation based models for diffuse solar radiation in the Sao Paulo urban area (Oliveira et. al, 2002). The diffuse solar radiation component requires expensive measuring procedures in comparison to other basic meteorological measurements, including global and long wave solar radiation. Therefore it would be useful for many purposes if the diffuse solar radiation component could be reconstructed from other simpler meteorological measurements. An MPNN-based model was constructed for this purpose that gives significantly better results than previously available models. Details can be found in paper by Soares et. al, (2004).

Another problem arose from this work – correction of long wave measurements according to the Fairall formula (Fairall et al, 1998). This correction requires additional measurements of the temperature of the long wave sensor’s dome and base. There exist several years of long wave solar radiation measurements for Sao Paulo but without the required additional measurements for correction. We solved the problem by several months measurements of the missing parameters and then establishing a MPNN-based model for reconstruction of the Fairall correction from the basic meteorological measurements that are available for several years (Oliveira, 2006). The model again gave very good results.

In both the above explained models, feature determination and pattern selection techniques were applied in the model construction phase.

8. Kohonen neural network (KNN)

The Kohonen neural network (KNN) (Kohonen, 1995) differs significantly from the MPNN. The main purpose of KNN is to sort multivariable patterns into groups (clusters) of similar ones. It is important that the grouping criteria need not be known – therefore this is unsupervised learning.

KNN is a very practical and effective tool for finding groups of similar patterns in data sets where it is not known in advance (through some other available knowledge) what their natural division into groups of similar patterns is.

The sorting principle is as follows: firstly the user prepares a data set of multivariable patterns that should be searched for groups of similar ones. The pattern consists of input features (the same definition as in MPNN). The output feature is the number of the cluster that the pattern belongs to. The quantity of clusters should be determined by the user. The natural number of clusters (the number of clusters that best fits the examined problem) cannot be determined automatically. But there is a relatively simple way of finding it. The process of dividing data set into groups is repeated for several different quantities of groups. For each division the average standard deviation of the distance of all patterns from the corresponding centre of the group should be calculated. On increasing the number of groups, the standard deviation decreases rapidly until the natural number of groups is reached. After that, if we divide these groups into more groups, the standard deviation decreases significantly slower than before. Using this rule, the “natural” number of groups can be easily derived from a graph of the average standard deviation of the distance versus the number of groups.

The crucial part of sorting is selection of the measure of distance appropriate to the problem examined. In most cases the Euclidean distance between two vectors can be used. But it should be noted that if the components of the vector represent measurements of different natural processes, then each process should be normalized. If this is not done, some components may prevail over others. Beside Euclidean distance, many other distance measures that are known from pattern recognition theory can also be used.

In the iterative process when KNN sorts the available data set of patterns into a chosen number of groups, it actually puts together patterns that are close one to another in terms of the distance function used. The algorithm is again an iterative one and the user can stop the process of division when the groups become stable.

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Figure 3.

Presentation of wind roses for all clusters for the division into 10 clusters

Feature determination is also an important process when using KNN. In this case feature selection means that the user should find the inputs that can provide some information about how a particular pattern differs from other ones. With KNN, feature determination is mostly done heuristically according to the user’s knowledge about the examined phenomenon.

KNN is an extremely useful sorting tool for problems dealing with huge data bases and multivariable patterns.

In the following paragraphs two successful problems that we solved using KNN will be presented.

9. Sorting of ground level wind fields using KNN

The Šoštanj area (a basin in complex terrain, explained in previous sections) has very colorful ground level wind field patterns due to the fact that the very low winds that prevail there meander in the basin and follow the shape of nearby lying valleys and become stronger over the hills and passes. Hence the wind roses of six ambient automatic measuring stations (that were examined for SO2 forecasting) look totally different, in spite of the fact that they are only a few kilometers away one from another. This fact illustrates the complexity of the ground level winds in the area.

We examined the following problem (Mlakar & Božnar, 1996): is it possible to find groups of similar wind fields (a wind field in this case is represented by a packet of simultaneously measured wind data at all stations) occurring in this area, or is the problem too stochastic to be grouped? If there are groups, what is the “natural” number of groups there?

To answer these questions we examined the wind data for five stations. One station was excluded because its location was inappropriate for representative wind measurements.

The data base of over 26000 half hour intervals was examined when wind measurements were available for all five stations. Due to the complexity of the wind roses for the whole data set it was expected that the natural number of groups would be very large. Several divisions from 10 to 100 groups were tested. As a measure of division quality a special index was defined – the weighted sum of the standard deviation of wind speed and the standard deviation of wind direction within the obtained groups. The natural number of groups was found to be around 32.

The quality of the division of the 26000 wind patterns into 32 groups was easily controlled by plotting wind roses for the new groups for each station. The new wind roses were not similar to the wind roses composed of the whole data set for each station. And also the wind roses of different groups (and the pattern for five stations) were different one from another. The pictures of the wind roses for 32 groups at five stations proved very obviously that the sorting process was done in a very effective and successful way.

This example of wind data sorting is a very persuasive one to convince the user about the effectiveness of KNN. This is due to the fact that wind roses are a graphical presentation that can be easily comprehended and the differences or similarities visualized. And on the other hand, there is no way (because of the area complexity) to do this sorting manually - only on the basis of some meteorological knowledge.

10. KNN as a tool for pattern selection techniques for MPNN based models

Another very successful application where we used KNN was as a pattern selection technique. When establishing methods for pattern selection that would not need user knowledge about meteorological phenomenon, we used KNN to sort a huge data base of air pollution patterns into natural groups of patterns. When the groups are obtained it is easy to construct a training and testing set to effectively train the MPNN.

The method was developed for the case of SO2 prediction in the Šoštanj area (Božnar, 1997).

The method of pattern selection using KNN showed the same improvement in the MPNN model effectiveness as the method of using all the available detailed expert knowledge about air pollution in the area. Therefore KNN pattern selection techniques are particularly suitable for problems where detailed expert knowledge is not available.

11. Conclusion

Two types of artificial neural networks were shown to be useful tools for environmental modelling: the multilayer perceptron neural network MPNN and the Kohonen neural network KNN. MPNN is an universal approximator. Therefore it can be used for modeling phenomena where reconstruction or prediction of one (or several) parameters is required on the basis of other measured parameters. In the model construction phase there are two important steps that are often neglected. These are feature determination and pattern selection techniques. The methods that we suggest can be used in very different applications. They contribute much to the final model performance. Their contribution can be described as extraction of useful information from the available data base of measurements and presentation of this information to the neural network during the learning process in the most plausible way. The variety of presented examples from air pollution prediction to meteorological applications shows how flexible MPNN models can be. Meteorological applications especially demonstrate that MPNN models can be a useful additional tool in the field of meteorological preprocessors for modern air pollution models. The variety of examples presented also proves that feature determination and pattern selection techniques are more or less universal.

KNN is not used so widely as MPNN in atmospheric research. The examples presented here prove that KNN is a very effective tool for sorting problems. It actually performs very well also in cases where there is no a priori knowledge about similarities at all.

We hope that the given examples of successful use of artificial neural networks will inspire other applications in atmospheric research.

Acknowledgements

The study was partially financed by the Slovenian Research Agency, Project No. L1-2082.

References

1 - M. Božnar, 1997Pattern selection strategies for a neural network- based short term air pollution prediction model. Adeli, H. (ed.). Intelligent Information Systems IIS’97, Grand Bahama Island, Bahamas, December 8-10, Proceedings. Los Alamitos, California[etc.]: IEEE Computer Society, 340 344
2 - M. Božnar, P. Mlakar, 1995Neural networks- a new mathematical tool for air pollution modelling., Editors: Power, H., Moussiopoulos, N., Brebbia, C. A. Air pollution III. 1Air pollution theory and simulation. Southampton; Boston: Computational Publications, 259 266
3 - A. C. Comrie, 1997Comparing neural networks and resression models for ozone forecasting. Journal of Air and Waste Management 47, 653 663
4 - J. Soares, A. P. Oliveira, M. Z. Božnar, P. Mlakar, J. F. Escobedo, A. J. Machado, 2004Modeling hurly diffuse solar-radiation in the city of São Paulo using a neural’network technique. Applied Energy 79(1), 201 214
5 - J. Yi, R. Prybutok, 1996A neural network model forecasting for prediction of daily maximum ozone concentration in an industrialised urban area. Environmental Pollution 92 (3), 349 357
6 - D. E. Rumelhart, G. E. Hilton, R. J. Williams, 1986Learning internal representation by error propagation, in Parallel Distributed Processing: Explorations in the Nicrostructure of Cognition. eds. DE Rumelhart and JL McClelland, 1MIT Press, Cambridge, MA
7 - M. Božnar, M. Lesjak, P. Mlakar, 1993A neural network-based method for short-term predictions of ambient SO2 concentrations in highly polluted industrial areas of complex terrain. Atmospheric Environment, B 27(2), 221 230
8 - M. Božnar, P. Mlakar, 2001Artificial neural network-based environmental models. Air pollution modeling and its application XIV, Kluwer Academic: Plenum Publishers, New York, 483 490
9 - J. K. Devijver, 1982 Pattern recognition: A statistical Approach. Englewood Cliffs, Prentice-Hall, Inc.
10 - Elisei et. al 1992 Experimental Campaign for the Environmental Impact Evaluation of Sostanj Thermal Power Plant, Progress Report, CISE, Milano
11 - C. W. Fairall, P. O. G. Persson, E. F. Bradley, R. E. Payne, S. P. Anderson, 1998A New Look at Calibration and Use of Eppley Precision Infrared Radiometers. Part I: Theory and Application. Journal of Atmospheric and Oceanic Technology; 15, 1229 1242
12 - M. W. Gardner, S. R. Dorling, 1998Artificial neural networks (the multilayer perceptron)- a review of applications in the atmospheric sciences. Atmospheric Environment 32 (14/15), 2627 2636
13 - B. Grašič, P. Mlakar, M. Z. Božnar, 2006Ozone prediction based on neural networks and Gaussian processes. Il Nuovo Cimento C, 29 6 651 661
14 - K. Hornik, 1991Approximation capabilities of multilayer feedforward networks. Neural Networks 4, 251 257
15 - T. Kohonen, 1995 Self-organizing maps. Springer, Berlin
16 - V. Kurkova, 1992Kolmogorov’s Theorem and Multilayer Neural Networks, Neural Networks, 5, 501 506
17 - J. Lawrence, 1991 Introduction to Neural Networks, California Scientific Software, Grass Valley
18 - C. Marzban, G. J. Strumpf, 1996A neural network for tornado prediction based on doppler radar derivd attributes. Journal of Applied Meteorology 35, 617 626
19 - P. Mlakar, 1997 Determination of features for air pollution forecasting models. Adeli, H. (ed.). Intelligent Information Systems IIS’97, Grand Bahama Island, Bahamas, December-10, Proceedings. Los Alamitos, California, USA: IEEE Computer Society 1997, pp. 350-354
20 - P. Mlakar, M. Božnar, 1996Analysis Of Winds And SO2 Concentrations In Complex Terrain. Editors: Caussade, B., Power, H., Brebbia, C.A.. Air Pollution IV: Monitoring, Simulation And Control. Southampton; Boston: Computational Mechanics Publications, Cop., 455 464
21 - L. Moseholm, J. Silva, T. Larson, 1996Forecasting carbon monoxide concentrations near a sheltered intersection using video traffic surveillance and neural networks. Transport Research 1D (1), 15 28
22 - A. P. Oliveira, J. F. Escobedo, A. J. Machado, J. Soares, 2002Correlation models of diffuse solar radiation applied to the City of São Paulo (Brazil). Applied Energy 71(1), 59 73
23 - A. P. Oliveira, J. R. De Soares, M. Božnar, P. Mlakar, J. F. Escobedo, 2006An application of neural network technology to corrent the dome temperature effects on pyrgeometer measurements. Journal of Atmospheric and Oceanic Technolog, 23 80 89