Share This Article:

ART Based Reliable Method for Prediction of Agricultural Land Changes Using Remote Sensing

Abstract Full-Text HTML XML Download Download as PDF (Size:5970KB) PP. 1051-1067
DOI: 10.4236/cs.2016.76089    1,157 Downloads   1,545 Views  

ABSTRACT

This paper focuses on prediction of change in agricultural lands by using ART2 algorithm. The existing method used ENVI and ARCGIS software to predict the changes in land, which showed less accuracy due to human errors. To overcome this user friendly GUI based ART2 algorithm has been developed in java to obtain more accuracy in prediction of changes in land. The input is satellite temporal images of the years 1990 and 2014. By using the ART2 algorithm, the input images of the years 1990 and 2014 are classified, where the features are identified to form cluster. The clustered image is given as input and pixel to pixel comparison method in ART2 is implemented in java, for detecting the changes in agricultural lands. The comparison results of ENVI and ARCGIS and GUI based ART2 with in situ data show that the prediction of changes in agricultural land is more accurate in the case of GUI based ART2 implementation.

Received 23 March 2016; accepted 24 May 2016; published 27 May 2016

1. Introduction

1.1. General

Agriculture plays a vital role in the district’s economy. Agriculture land change detection is an inevitable one. Most of the people in Tirunelveli are mainly depending on income from agriculture. Proper land use planning is essential for a sustainable development of agriculture. Due to the extensive changes in the land use land cover, there is a fall in natural vegetation cover and decrease in area under wetland agriculture. Due to population pressure, land degradation results mainly lead to intense land use without proper management practices [1] - [3] . By the human activities, there is an increase of built up land area and decrease agricultural land. Recent functioning of the real estate people and property promoters are bringing a serious disaster to forest area and agricultural land. Changes of agricultural land detection are essential to understand the existing situation and plan for the future. The aim is to analyze the agricultural land use/land cover pattern of Tirunelveli city and estimate the change of agricultural land over the period 1990 to 2014 and then to develop the model for agricultural land use change detection using adaptive resonance theory.

Artificial neural networks have more general and flexible functional forms than the traditional statistical methods and can effectively deal with supervised and unsupervised learning methods and address problems such as pattern recognition and prediction [4] . Adaptive resonance theory is used to process the human cognitive information [5] . ART can be used as a real time neural network model which performs supervised and unsupervised learning. It also performs pattern recognition and prediction [6] [7] . Most of the applications in ART, uses fast learning, for each input vector pattern, the updation of weights converge to equilibrium. Fast learning creates memories that depend upon the order of output presentation. ART applications exploit this feature to improve accuracy by voting across several trained networks, with voters providing a measure of confidence in each prediction. ART is a part of a growing family of self organizing network models that feature attentional feedback and stable code learning. ART systems can be used to classify the databases and produce validated classification results, and to focus attention upon those featural groupings. ART2 network extends between capabilities to support continuous inputs [(Grossberg and Carpenter, 1987].

ART1 was designed for clustering binary vectors. ART2 for clustering continuous or real valued vectors. The learning laws of ART2 are simple though the network is complicated. The F1 field in ART2 includes a combination of normalization and noise suppression in addition to the comparison of the bottom up and top down signals needed for the reset mechanism. The orienting subsystem can also to accommodate real valued data [3] [8] - [13] .

1.2. Related Study

Masroor Hussain, depicts that the there are two artificial neural network algorithms applied such as multi layer perceptron and maximum likelihood and then compared. These methods are implemented for classification and change detection processes. Here SOM produced high accurate results [1] . The author developed a automated land cover change detection system using back propagation network algorithm. This system is compared with maximum likelihood classification method. Using post classification method in ENVI, change detection process is done. The artificial neural method in change detection process produced high accuracy [2] . The author has introduced eleven change detection techniques the post classification and PCA, image differencing and image ratio methods were implemented and compared. Here PCA produced high accuracy results and at last artificial neural network was implemented which produced higher accuracy result than other techniques [3] . Nitton Corredia da Silva has developed automated system software for classification and change detection process in C++ language [4] . This author tells that the neural network based change detection system is implemented using back propagation neural network. It identified changed and non changed area [5] . [6] , denotes that the classification of images is performed using multilayer peceptron which uses supervised learning method. The artificial neural network classification method is implemented in ENVI 4.7 software. The change detection process is done using post classification method which is a familiar method. [7] , compares the result of artificial neural network technique with maximum likelihood result in the classification process. It is proved that artificial neural network algorithm produced higher accuracy than maximum likelihood. Conventional algorithms such as Hopfield, back propagation algorithms were used. In this paper, ART2 algorithm being used to give more stability and plasticity. Thus making this system fully automated [3] [8] - [13] .

2. Study Area and Data Used

2.1. Study Area

The area chosen for this study is Tirunelveli district, Tamilnadu and it lies between 8˚05' and 9˚30' of the Northern latitude and 77˚05' and 78˚25' of Eastern longitude. The total geo graphical area coverage is 6759 sq・kms and total agricultural area coverage is 183,319 Ha. The district had a population of 3,077,233. The total cropped area is 171,155 hectares, which worked out 25.32% of the total area of 675,850. The important food crops are Paddy, Cholam, Ragi, Cumbu Maize and other minor millets. The commercial crops are Cotton, Chillies, Sugarcane and Groundnut.

2.2. Data Used

For this research work, IRS P6 LISS III satellite images for the years of 1990 and 2014 were acquired with resolution 23.6 m for determining agriculture changes between these years in Tirunelveli region, Tamiladu from NRSC, Hydrabad. The statistical data about population, rain fall data, area coverage of Crop, built-up, forest, waste land and water bodies for 1990 and 2014 were collected from statistical office, Tirunelveli for verification purpose.

2.3. Software Used

a) ARCGIS―This has been also used to compliment the display and processing of the data and subsequently for change detection analysis of the study area.

b) ENVI 4.7―This is used for the development of land use land cover classes and determine the statistics of change detection

c) JAVA AND APPLET―This is used for modeling of agricultural land change detection.

3. Methodology

3.1. General

The procedure adopted in this research work forms the basis for deriving statistics of agriculture land changes between the years of 1990 and 2014. The methodology has been developed and tested for detecting agricultural land changes in Tirunelveli city. The overview of the study is given in Figure 1.

Figure 1. Flow chart for change detection of agricultural land.

3.2. Methods of Data Analysis

The flowchart as shown in Figure 1, Image registration and Enhancement processes are implemented before the classification in ENVI. The required area is masked from the input images. The images are classified using maximum likelihood supervised classification. With help of post classification method, the change detection statistics are determined and the accuracy of classification is obtained. In ARCGIS, first the study area from the images is extracted and digitized using tools. Through overlay operations, with help of SQL, the agriculture area is selected using select command. Using clip operation, agriculture area of 1990 and 2014 are given as input and the changed area is found. At last the result of all the software is analyzed.

3.3. Image Pre Processing

Two clear, cloud free IRS P6 LISS III images were selected to classify the study area for 1990 and 2014 years. The Tiunelveli city area is entirely contained within IRS P6 images path: 101 and Row 67, 68. The two images were geo referenced using well distributed ground control points and convolution resampling method. The noises of images spatially and spectrally were rectified by using high and low pass filters. After preprocessing, the root mean square errors were less than.25 pixels for each of the two images. Image processing was performed using ENVI 4.7. Land use/land cover mapping is achieved through interpretation of IRS P6 LISS III images of 1990 and 2014.

3.4. Image Classification

Based on Anderson land use/ land cover classification system, the images are classified as forest land, water bodies, agriculture land, waste land and settlement area. Before implementing the classification, the region of interests is created using ground truth data. The field work was carried out to collect the ground truth data for training purpose in the input satellite images. After collecting the ground truth data, the points are inserted into images through software as shown in Figure 2. In order to create ROI, the set of points are selected randomly and then mapped. The image classification was carried out in ENVI 4.7 software. A supervised classification technique with Maximum Likelihood Algorithm was applied. The classification was done based on training samples for the images of 1990 and 2014.The classified images of 1990 and 2014 were produced by using supervised image classification technique based on the Maximum Likelihood Classifier(MLC). Based on Anderson land use/land cover classification system, the images are classified as forest land, water bodies, agriculture land, waste land and settlement area. Before implementing the classification, the region of interests is created using ground truth data. The field work was carried out to collect the ground truth data for training purpose in the input satellite images. After collecting the ground truth data, the points are inserted into images through software. In order to create ROI, the set of points are selected randomly and then mapped. The image classification was carried out in ENVI 4.7 software. A supervised classification technique with Maximum Likelihood

Figure 2. ART2 training algorithm.

Algorithm was applied. The classification was done based on training samples for the images of 1990 and 2014. The classified images of 1990 and 2014 were produced by using supervised image classification technique based on the Maximum Likelihood Classifier (MLC).

3.5. Testing

The accuracy of classification is assessed using ENVI 4.7 software. The confusion matrix in post classification is selected as error matrix. Error matrix is mapped between class and reference class (ROI) to assess accuracy. In the assessment, overall accuracy, users, producer’s accuracies and Kappa coefficient were derived from error matrices. Here overall accuracy is calculated from diagonal elements and off diagonal elements of matrix.

3.6. Change Detection

The classified images of 1990 and 2014 were given as input to the change detection statistics. Following the classification of imagery from the individual years, a multi date post-classification comparison change detection statistics was used to determine changes in land cover in intervals, 1990-2014. The post classification approach provides information about the changes and land transformations occurred which can be easily calculated and mapped.

3.7. Methodology in ARCGIS

The overall process involved in methodology of ARGGIS software as shown Figure 3. In preprocessing, the images of 1990 and 2014 are enhanced by using contrast manipulation, edge enhancement, and spatial filter techniques. The first stage of process is to collect the toposheet from survey of India at 1:50,000. The toposheet is scanned and digitized and this is used as base map. With this base map, the study area of tirunelveli is extracted from the input image. The second stage is to classify the images in different category of land use. The input images of Tirunelveli region are classified into 7 classes such as paddy, vegetation, water, forest, barren and urban. From classified images of 1990 and 2014, with the help of key interpretation, the agriculture land area is digitized. Many polygons are created and it shows the shape of the area in the attribute table. Then sum of shape area is calculated for year of 1990 and 2014 separately. The difference is calculated between years of agriculture land maps. This gives the details of the changes of agriculture land value.

3.8. Modeling in Artificial Neural Network

3.8.1. Adaptive Resonance Theory

Images of 1990 and 2014 are classified using artificial neural network. In this paper, the images are classified using adaptive resonance theory. ART is an unsupervised classification algorithm which accepts number of bands present in the input images. ART differs from conventional artificial neural network. It solves the problem

Figure 3. Flow chart representing the change detection method.

of stability-plasticity dilemma which means ART maintains stored pattern whenever new patterns are created. ART is an evolving self organizing model. There are two types network available in ART family namely ART1 and ART2. For the classification, pixels are clustered based on the band values. In change detection, the classified image pixels are stored into databases separately for the year of images 1990 and 2014 then the pixel comparison is done using ART algorithm.

3.8.2. Image Classification

The enhanced images of 1990 and 2014 are the inputs to ART algorithm. Here the bands are accepted as inputs. Each band value is one neuron. For this study 3 bands of the IRS P6 LISS III satellite images of 1990 and 2014 are chosen as input images. So there are 3 neurons as input for ART neural network. The process of classification is performed in two layers (F1, F2) of ART. The F1 layer accepts the band values and normalization process is done for suppressing the noise. The product of sum is calculated between input values and weights which produce high value neuron and this neuron is considered as winning neuron. In F2 layer, the winning neuron is matched with stored pattern or prototype and if it is matches, the cluster is to be formed as separate one otherwise winning neuron is created as new pattern. Then the cluster is formed separately. The coding has implemented in java language.

3.8.3. Change Detection

The classified images of 1990 and 2014 are the input images for change detection process. Using ART algorithm, pixels of the classified images 1990 and 2014 are stored into data bases. With the help of cross tabulation method, the change detected image is determined. The change detection process is implemented in java language.

4. Results and Discussions

4.1. Base Maps

The base map for Tirunelveli district was obtained from IRS P6 LISS III satellite images by using ARCGIS software. The image is geo referenced and digitized by using ARCGIS tools. Finally the layout of the base map is created. The base map as shown in Figure 4 consists of important location, tourist places, and railway lines, national and state highways.

The block map represents area of taluks in Tirunelveli district as shown in Figure 5. Based upon geo referenced map, the boundary of Tirunelveli district and boundary of the all taluks in Tirunelveli district is digitized. From this the layout of the block map is obtained. All the process is done by using ARCGIS software. The Figure 5 shows location of all taluks in Tirunelveli district.

Figure 6 represents drainage network map which shows canals, streams, thamirabarani river, Manimuthar reservoir. All the draining networks are digitized by using ARCGIS software.

4.2. Results in ENVI 4.7

The input images for 1990 and 2014 are obtained from IRS P6 LISS III satellite images as shown Figure 7 and Figure 8. By using ARCGIS software, the Tirunelveli taluk area is extracted with help of geo referenced data.

The classified images of 1990 and 2014 are segmented into agriculture, water, barren, settlement, shrub and forest lands as shown in Figure 9 and Figure 10. The white pixels represent agriculture area, magenta pixels

Figure 4. Land change detection process.

Figure 5. Block map for Tirunelveli district.

represent settlement area, green pixels denote water bodies, Sea green pixels show shrub, coral pixels indicate forest and red pixel represents barren land.

The accuracy assessment for the classified image of 1990 is 93.6054% and Kappa coefficient is 0.8884. All of the pixels are classified fully in the agriculture area and the pixels are misclassified only in the settlement area as shown Table 1. This method has produced high accuracy result in classification.

Here only few pixels are misclassified into water and settlement area so there is no severe changes in accuracy results. The overall accuracy of the classification is 88.66 and Kappa coefficient is 0.8694 as shown Table 2.

Figure 6. Drainage network map.

The result of agriculture land change detection using ENVI 4.7 software is 266.95 sq・km of area. The decreased agricultural land has changed to urban areas as shown in Table 3. This difference is shown between the years of 1990 and 2014. If agriculture land changes continuously, it can further shrink to 1067 sq・km in 2020.

Figure 7. Input image for 1990.

Figure 8. Input image for 2014.

Figure 9. Classified image for 1990.

Figure 10. Classified image for 2014.

Table 1. Accuracy assessment for classified image of 1990.

Table 2. Accuracy assessment for classified image of 2014.

Table 3. Statistics of change detection in ENVI 4.7.

4.3. Results in ARCGIS

Figure 11 and Figure 12 depict agricultural land use maps for the year of 1990 and 2014. The extracted IRS P6 LISS III images of 1990 and 2014 for Tirunelveli taluk as input for creation ofagriculture land use map. First Tirunelveli taluk boundary is obtained by digitization then also agriculture areas are digitized thus generating the agriculture land use map. Here red color represents the agriculture area as shown in Figure 10 and Figure 11. Then calculated the change detected rate between the years of 1990 and 2014. The change detected rate is obtained from difference between sum of shape area in 1990 and 2014 agriculture land use maps. The calculated change detection between the years is 42,340 sq・m.

4.4. Results in Modeling

The input images are obtained from the satellite images of IRS P6 LISS III for 1990 and 2014. By using GUI based software model, the classified images, graph1 and graph2 are created automatically for both years separately. The classified images of 1990 and 2014 represents paddy, vegetation, water bodies, urban and unclassified features as shown Figure 13 and Figure 14. Here red color pixels indicates paddy and vegetation areas in both classified images.

Figure 15 depicts change detected image between 1990 and 2014. The image shows the changes of the land with different features such as urban, barren, vegetation, paddy, forest, water and classified. It depicts change detected image between 1990 and 2014.

Figure 16 represents the change detected graph1, x axis represents number of features and y axis represents number of pixels. The first bar represents paddy feature with 3600 pixels, second bar denotes vegetation with 1700, third bar shows water feature with 2000 pixels, the fourth bar shows forest feature with 2800 pixels, the fifth bar shows barren feature 1800 pixels, the sixth bar shows urban feature with 4000 pixels.

Figure 11. Agriculture land map for 1990.

Figure 17 shows that first bar has 1100 pixels with paddy feature, the second bar shows that there are 1000 pixels with vegetation feature, the third bar shows that there are 3000 pixels with water feature, the fourth bar shows that there are 3700 pixels forest feature, the fifth bar shows that there are 2100 pixels barren feature, the sixth bar shows that there are 2700 pixels with urban feature.

Figure 18 denotes the paddy area has decreased up to 58,750 sq・m. and the vegetation has decreased up to 16,450 sq・m. There is no change in the water catchment area but changes occurred in forest and barren lands.

Figure 19 shows the analysis graph of the three software ENVI, ARCGIS and GUI based software model. The results from ENVI show that the agriculture land has changed by 29,965 sq・m. ARCGIS denotes that the agriculture land has changed by 42,340 sq・m then GUI based model shows that there is 58,750 sq・m changed in agriculture land. The GUI based model shows more accuracy when compared to other accuracy methods. The validation was done by using the in situ data.

Figure 12. Agriculture land map for 2014.

Figure 13. Classified image of 1990.

Figure 14. Classified image of 2014.

Figure 15. Change detected image.

Number of features

Figure 16. Change detected graph 1.

Number of features

Figure 17. Change detected graph 2.

Number of features

Figure 18. Change detected graph.

Figure 19. Analysis graph.

5. Conclusion

This research work demonstrates the ability of GIS and Remote Sensing in capturing spatial-temporal data. The agricultural land changes are found by implementing 3 techniques. Remote sensing and GIS are providing many tools for analysis of the satellite images. Using the tools, change detection is found in 3 ways. First the statistics value of agriculture land change between the year 1990 to 2014 is found using ENVI 4.7 software. The statistics shows that the agricultural land has decreased to 26,695 sq・m. The second way was done using ARCGIS software. The calculated change detection between the years is 42,340 sq・m. In this research, the automatic software is developed by using adaptive resonance theory algorithm. This is a fully automatic ad unsupervised learning method. This software is worked similar to ENVI 4.7 and ARCGIS software but produce high accuracy level and also the graphs are differently created for the year of 1990 and 2014. The software has focused that the statistics value of agriculture land change is 58,750 sq・m. The value is compared with field data for the verification. Approximately the software has produced high accurate results. If the changes are continued in future, 70% people may be affected and pulled down to poverty level. This software can be used in future to predict the changes that have occurred due to the urbanization and reduction of ground water level.

Conflicts of Interest

The authors declare no conflicts of interest.

Cite this paper

Malini, M. , Kumar, M. and Sakthieswaran, N. (2016) ART Based Reliable Method for Prediction of Agricultural Land Changes Using Remote Sensing. Circuits and Systems, 7, 1051-1067. doi: 10.4236/cs.2016.76089.

References

[1] Hussain, M. (2013) Change Detection from Remotely Sensed Images: From Pixel-Based to Object-Based Approaches. ISPRS Journal of Photogrammetry and Remote Sensing, 80, 91-106.
http://dx.doi.org/10.1016/j.isprsjprs.2013.03.006
[2] Fkirin, M.A. (2009) Change Detection Using Neural Network with Improvement Factor in Satellite Images. American Journal of Environmental Sciences, 5, 706-713.
[3] Haykin, S. (1994) Neural Networks, Comprehensive Foundation. College Publishing Company, New York.
[4] da Silva, N.C. (2012) Change Detection Software Using Self-Organizing Feature Maps. Brazilian Journal of Geophysics, 30, 505-518.
[5] Heerman, P.D. (1991) Classification of Multi-Spectral Remote Sensing Data Using Back-Propagation Neural Network. IEEE Transactions on Geoscience and Remote Sensing, 30, 81-88.
http://dx.doi.org/10.1109/36.124218
[6] Ahmadizadeh, S. (2014) Land Use Change Detection Using Remote Sensing and Artificial Neural Network: Application to Birjand, Iran. Computational Ecology and Software, 4, 276-288.
[7] Deilmai, B.R. (2014) Comparison of Pixel-Based and Artificial Neural Networks Classification Methods for Detecting Forest Cover Changes in Malaysia, Earth and Environmental Science. 8th International Symposium of the Digital Earth (ISDE8).
[8] Pijanowski (2002) Using Neural Networks and GIS to Forecast Land Use Changes: A Land Transformation Model. Computers, Environment and Urban Systems, 26, 553-575.
[9] Abdullah, F. (2013) Investigating the Use of Remote Sensing and GIS Techniques to Detect Land Use and Land Cover Change: A Review. Advances in Remote Sensing, 193-204.
[10] Dam, H. (2008) Neural-Based Learning Classifier Systems. IEEE Transactions on Knowledge and Data Engineering, 20, 26-39.
http://dx.doi.org/10.1109/TKDE.2007.190671
[11] Long Dal, X. (1999) Remotely Sensed Change Detection Based on Artificial Neural Networks. Photogrammetric Engineering & Remote Sensing, 65, 1187-1194.
[12] Mas, J.F. (2008) The Application of Artificial Neural Networks to the Analysis of Remotely Sensed Data. International Journal of Remote Sensing, 29, 617-663.
http://dx.doi.org/10.1080/01431160701352154
[13] Pajares, G. (2012) A Hopfield Neural Network for Image Change Detection. IEEE Transactions on Neural Networks, 17, 1250-1264.

  
comments powered by Disqus

Copyright © 2019 by authors and Scientific Research Publishing Inc.

Creative Commons License

This work and the related PDF file are licensed under a Creative Commons Attribution 4.0 International License.