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International Journal of Latest Technology in Engineering, Management & Applied Science (IJLTEMAS)
2nd
Special Issue on Engineering and Technology | Volume VI, Issue VIS, June 2017 | ISSN 2278-2540
www.ijltemas.in Page 29
A New Approach for Multi Index Automatic Change
Detection in HR Remotely Sensed Imagery
Madhukar.B.N1
, Sheshashayana.K.S2
1
Senior Assistant Professor, NHCE, Bengaluru, India,
2
M.Tech Student, NHCE, Bengaluru, India
Abstract— In recent years the technology is growing rapidly and
the development of the country very fast and also due to this the
infrastructures are increasing. Hence the changes could be noted
by using new generation of Earth observation sensors with high
spatial resolution or high resolution (HR) which provide detailed
information for change detection. The widely used methods for
high-resolution image change detection rely on
textural/structural features. In order to get the high resolution
images for viewing the areas in this project we use multi index
automatic change detection method is proposed for the high-
resolution imagery. The advantages are as follows: 1) The
information (images) sent by the satellite would be in very low
size, low pixels so in order to improve the viewing ability we use
high-dimensional but low-level features (e.g., textural and
structural features) i.e. multi index representation method. The
multi index representation refers to the enhanced vegetation
index, the water index, and the recently developed morphological
building index. I am going use this technique for implementing in
military places, which has a very large application. Moreover,
the traditional methods based on the state-of- the-art
textural/morphological features were also implemented for the
purpose of comparison, which further validates the advantages
of my project.
Key words— Building detection, change detection, high
resolution, morphological.
I.INTRODUCTION
ETECTION of land cover/use changes is one of the most
Fundamental and useful tasks for various applications
suchas urban expansion, urban planning, damage assessment,
Convenient to obtain remotely sensed imagery over certain
deforestation, and urban landscape monitoring. With the rapid
development of Earth observation techniques, it becomes area
at different times. Thus, land cover/use changes can be
effectively detected and analyzed by processing the multi
temporal remote sensing images.
In order to timely process the big remote sensing data and
rapidly transfer the data into information and knowledge, it is
necessary to develop automatic techniques for image change
detection. A few studies have recently addressed the
automatic change detection methods, including studies on
multilevel change vector analysis, morphological filters with
change vector analysis, multi temporal morphological
attribute Profiles; pulse coupled neural networks, and
hierarchical spectral change analysis. The basic idea of the
proposed method is to represent complicated high-resolution
scenes by a set of low dimensional semantic indexes that are
used to replace traditional high-dimensional but low-level
features (e.g., textural features and morphological profiles).
Specifically, urban primitives, e.g., buildings, vegetation, and
water, are automatically extracted by the morphological
building index (MBI), the enhanced vegetation index (EVI),
and the normalized difference water index (NDWI),
respectively.
Change detection using high spatial resolution remote sensing
images has received increasing interest since detailed ground
change information is now available. However, a large intra
class variance and a small interclass variance can lead to
inaccuracy for the traditional spectral based and pixel based
image processing framework when high spatial resolution
imagery is used for change detection. In order to deal with this
problem and improve the accuracy of change detection from
high resolution data, researchers have proposed to take spatial
features into consideration for change detection.
The notable characteristics of the multi index method include
the following aspects.1) The complicated urban scenes can be
automatically and effectively represented by a set of low
dimensional information indexes.2) The local histograms of
these indexes are able to describe the frequency and spatial
arrangement of the urban primitives. Consequently, the multi
temporal multi index representations can be used to detect the
structural changes of the urban scenes.The proposed change
detection method is described by the following steps.
1. Calculation of Information Indexes
2. Automatic Change Detection
a) Block based
b) cell based
3. Types of Change
II. MULTIINDEX URBAN REPRESENTATION
In this paper, three urban primitive indexes, i.e., MBI, EVI,
and NDWI, are used to represent a typical urban scene. Please
note that these three indexes provide information not only for
buildings, vegetation, and water but also for nonbuildings,
D
International Journal of Latest Technology in Engineering, Management & Applied Science (IJLTEMAS)
2nd
Special Issue on Engineering and Technology | Volume VI, Issue VIS, June 2017 | ISSN 2278-2540
www.ijltemas.in Page 30
nonvegetation, and nonwater features, which actually
enhances the discrimination ability of distinguishing different
urban structures.
A. MBI
MBI is an effective method for automatic building detection.
It is able to represent spectral–spatial properties of buildings
(e.g., brightness, size, contrast, directionality, and shape) by a
set of morphological operators. It should be noted that
buildings are spectrally similar with the bright soil, and hence,
the original MBI algorithm is improved in this study by
introducing a post processing step, aiming to reduce false
alarms from the urban bright soil. The modified MBI
algorithm is described as follows.
Step 1—Calculation of Brightness: The brightness is the
maximum value of the visible bands for each pixel, which is
used to represent the structures with high reflectance (e.g.,
candidate buildings). The visible bands are considered since
they have the most significant contributions to the spectral
reflectance of buildings.
Step 2—Top-Hat Morphological Profiles: Considering the
fact that buildings and their spatially adjacent shadows lead to
high local contrast, MBI is defined using differential
morphological profiles (DMPs) of the white top-hat by
reconstruction, i.e., DMPWTH, as follows:
DMPWTH = {DMPWTH(s, dir) : smin ≤ s ≤ smax, dir ∈D}
(1)
DMPWTH(s, dir) = |WTH(s+Δs, dir) − WTH(s, dir)| (2)
Where WTH(s, dir) represents the white top-hat of the
brightness image obtained in step 1 by using a linear structural
element (SE), with s and dir being the scale and the direction,
respectively. smin and smax indicate the range of the spatial
size of buildings, and Δs is the interval of the profiles. D is the
set of directions for the linear SE.
Step 3: MBI is calculated by
∑ ( )
(3)
where ND and NS denote the number of directions and scales
for the morphological profiles, respectively. Buildings
correspond to the areas with high MBI values, due to their
large local contrast in various directions and scales.
Step 4—Postprocessing: As aforementioned, in order to refine
the result of the building detection, a post processing step is
proposed to suppress the false alarms of bright soil from the
original MBI. Spectral information plays a key role for
identification of soil. It should be noted that bright soil in an
urban scene often has a yellow tone, corresponding to the
urban construction sites.
Therefore, based on the WorldView-2 images used in this
study, a yellow soil index (YSI) can be defined using the
normalized difference of yellow (Y) and blue (B) channels,
i.e.,
(4)
B. EVI
The vegetation information is automatically extracted by
the EVI. It was developed by enhancing the vegetation signals
through the difference between near-infrared (NIR) and red
(R) bands and, at the same time, reducing the aerosol effects
using blue (B) band. EVI is defined as
(5)
C. NDWI
The NDWI is adopted to detect the water bodies. It high
lights the water areas by maximizing the reflectance in
green(G) band and minimizing the low reflectance in near
infrared (NIR) band, i.e.,
NDWI= (6)
The water information is further refined by imposing an
area based threshold on the NDWI such that small noise and
errors (e.g., shadows) can be removed.
III. CHANGE DETECTION
Based on the previous discussions, it can be stated that
Multiple information indexes have the potential for achieving
automatic change detection from urban areas. Two examples
for the multi index automatic change detection are shown in
Fig. 3, from which it is clearly seen that the structural changes
in high resolution images can be effectively indicated by the
information indexes. Consequently, the multi temporal multi
index representations can be used to detect the structural
changes of the urban scenes. The proposed change detection
method is described by the following steps.
Step 1—Calculation of Information Indexes: Information on
buildings, vegetation, and water is obtained at the pixel level
based on the MBI, the EVI, and the NDWI, respectively;and
the corresponding post processing is then used to suppress the
noise in the initial result, i.e., removing bright soil from
buildings and shadow from water bodies.
Step 2—Automatic Change Detection: The image is first
divided into a series of blocks with the size of N × N (pixels)
for each one, which is viewed as the basic unit for the change
detection. This strategy is called ―hot spot‖ detection, which is
a commonly used approach for change detection from high-
resolution images.
A) Block-based strategy: In this case, the scene is
represented by the frequencies of the primitives in the multi
International Journal of Latest Technology in Engineering, Management & Applied Science (IJLTEMAS)
2nd
Special Issue on Engineering and Technology | Volume VI, Issue VIS, June 2017 | ISSN 2278-2540
www.ijltemas.in Page 31
index histogram of the block. For the block histograms at
times T1 and T2, a weighted distance is used to determine
whether changes occur in this area, i.e.,
∑ ( ( ) ( )) (7)
Dist(i)=|H1(i)-H2(i)| (8)
( )
( )
∑ ( ( )
(9)
where WDist is the weighted distance between the histograms
H 1 and H 2. Dim is the dimension of the histogram. H 1(i) and
H 2(i) represent the frequency of the ith bin in the histograms
H 1 and H 2, respectively. W(i) is expressed as the normalized
distance between H 1(i) and H 2(i), in order to further enlarge
the difference for the dissimilar bins.
B) Cell-based strategy: As shown in Fig. 4, spatial
arrangement of the primitives can be considered by dividing
each block into n × n cells. This way, a cell is viewed as a
basic unit to calculate the frequencies of the information
indexes. A block is then represented by n × n histograms, each
one representing the frequencies of the multiindex features in
each cell. Subsequently, the similarity measure between the
bit temporal histograms is calculated, in order to determine
whether changes occur in this block. In this case, the distance
measure can be extended from , i.e.,
∑ (∑ ( ) ( )) (10)
( )=| (i)- ( ) (11)
( )
( )
∑ ( )
(12)
Step 3—Types of Change: It should be noted that most of
the automatic change detection methods only indicate whether
Changes take place in the block but cannot provide specific
Information related to the types of changes. In this paper,
however, based on the information indexes, it is possible to
further provide the change information corresponding to each
block, by investigating which information index is subject to
significant changes in terms of both frequency and spatial
arrangement in the block. This can be viewed as a by-product
of the proposed change detection method.
IV. DATA SETS AND RESULTS
Fig.1: Image of the Bangalore region 13/Jan/2015.
Fig.1 is the raw image from the satellite of the area of the
Bangalore city taken in 13 Jan 2015 with the co-ordinates lat-
12.921242 and log-77.641255 is the position at the center of
the image with 240 square km distance. It is of pixel size
140x390 feet taken on Jan 13, 2015 from Landsat – 7
satellite.
Fig.2: Image of the Bangalore region 8/Apr/2017
Fig.2 is the raw image from the satellite of the area of the
Bangalore city taken in 8 Apr 2017 with the co-ordinates
lat=12.921242 and log=77.641255 is the position at the center
of the image with 240 square km distance. It is of pixel size
140x390 feet taken on Jan 13, 2015 from Landsat – 7
satellite.
Fig.3: Multi index output 2015(left), 2017 (right)
Fig.3 is the multiuindex output for the change detected in the
image. You can see that the part is the buildings, green is the
vegetation and the blue is the water bodies. The black image
is for soil part or the shadow part which is removed during the
multiindex of the image. Fig.4 is the morphological output
index of the two images which are used as the input the Fig.
6.10 shown explains about the various structures and different
levels of basic things like vegetation, water levels and other
empty land or the shadow.
Fig.4: Final change detection of water, building and vegetation.
International Journal of Latest Technology in Engineering, Management & Applied Science (IJLTEMAS)
2nd
Special Issue on Engineering and Technology | Volume VI, Issue VIS, June 2017 | ISSN 2278-2540
www.ijltemas.in Page 32
We can see there are different colors used to map different
morphological units one such is the buildings water bodies
and vegetation that is the green parts on the earth. I have used
the Bangalore city to explore the change detection that has
happened is the year 2015 and the year 2017.
Fig.5: Change detection using block based (left) and cell based (right).
This change is noted down on the multi index image and the
roc curve which gives the clear change detected in the two
images this change detected can be plotted on the bar graph
for easy understanding and to check the total change with
reference to the pixel of the image using these pixels in
different ratios we can easily calculate the accuracy of the
change detected.
Fig. 6: Graphical Representation Of Block Based.
Fig. 7: Graphical Representation of Cell Based.
Fig.8: ROC Curve for Cell Based.
Fig.9: ROC Curve for Block Based.
V. COMPARISON
The greater part of existing change recognition techniques
could be characterized into three groups, the conventional
pixel0based0change0detection the object0based0change
identification and the hybrid0change0detection. Both PBCD
and OBCD have drawbacks and hence we established HCD
strategies. There is no ideal HCD technique started yet.
Breaking down the complementarities of PBCD and OBCD
strategy, we propose another unsupervised algorithm level
fusion0scheme (UAFS-HCD) which is used in order to
improve the accuracy of the pixel based techniques using
spatial domain approach. This is done by following
approaches.1) Getting the preliminary change with PBCD at
first to estimate few parameters for OBCD.2) Determining the
unaltered territory areas and to wipe out the territories without
changes, which reduces the error amplification phenomenon
of OBCD.3) Acquiring the final change mask by methods for
OBCD technique.
-0.5 0 0.5 1 1.5 2 2.5 3 3.5
2600
2800
3000
3200
3400
3600
3800
4000
4200
False positive rate
Truepoasitiverate
Block based
International Journal of Latest Technology in Engineering, Management & Applied Science (IJLTEMAS)
2nd
Special Issue on Engineering and Technology | Volume VI, Issue VIS, June 2017 | ISSN 2278-2540
www.ijltemas.in Page 33
Fig.10: Block based CD(left), Cell based CD(right) imagery of existing
system.
Fig.11: Block based CD(left), Cell based CD(right) imagery of proposed
system.
VI. CONCLUSION
In this paper, an innovative change area procedure in light of
the multi record picture depiction has been proposed for high
assurance remote distinguishing imagery over urban scenes.
The proposed technique is fit for fulfilling satisfactory change
recognizable proof precision with a game plan of low
dimensional; however semantic information records are saved
in the database. Two specific systems are completed for the
proposed procedure. The first is a block based approach where
the frequencies of the information records are considered for
change area. The other is the cell based one where each block
is moreover scheduled into a movement of cells. Along these
lines, the frequencies as well as the spatial course of action of
the data files in the square can be misused. A near review was
led between the proposed multi record strategy and the
customary multi include technique for programmed change
location. Likewise, the proposed multi list model can
consequently show which class the adjustment in the territory
is identified with. This is a repercussion of the proposed
strategy. Rather, conventional programmed change location
can just decide if changes happen in this district or not.
ACKNOWLEDGMENT
The authors are grateful to Dr. Mohan Manghnani, Chairman,
New Horizon College of Engineering (NHCE) Bengaluru, for
his encouragement for carrying out his work. They are
thankful to Dr. Manjunatha, Principal, New Horizon College
of Engineering (NHCE) Bengaluru, for his encouragement for
this research work. They are also very grateful to Dr. Sanjay
Jain, Professor and HOD, ECE Dept. New Horizon College of
Engineering Bengaluru, for providing necessary backbone
support to proceed on this endeavor. Finally, we are highly
indebted to our parents for encouraging us to excel in our
chose fields.
REFERENCES
[1]. M. Hussain, D. Chen, A. Cheng, H. Wei, and D. Stanley, ―Change
detection from remotely sensed images: From pixel-based to
object-basedapproaches,‖ ISPRS J. Photogramm. Remote Sens.,
vol. 80, pp. 91–106,Jun. 2013.
[2]. P. Coppin, I. Jonckheere, K. Nackaerts, B. Muys, and E. Lambin,
―Digitalchange detection methods in ecosystem monitoring: A
review,‖ Int. J.Remote Sens., vol. 25, no. 9, pp. 1565–1596, May
2004.
[3]. X. Huang and L. Zhang, ―An SVM ensemble approach
combiningspectral, structural, and semantic features for the
classification ofhigh-resolution remotely sensed imagery,‖ IEEE
Trans. Geosci. RemoteSens., vol. 51, no. 1, pp. 257–272, Jan.
2013.
[4]. V. Walter, ―Object-based classification of remote sensing data
forchange detection,‖ ISPRS J. Photogramm. Remote Sens., vol.
58, no. 3/4,pp. 225–238, Jan. 2004.
[5]. T. Celik and K.-K. Ma, ―Multitemporal image change detection
usingundecimated discrete wavelet transform and active
contours,‖ IEEE Trans.Geosci. Remote Sens., vol. 49, no. 2, pp.
706–716, Feb. 2011.
[6]. T. Celik, ―Multiscale change detection in multitemporal satellite
images,‖IEEE Geosci. Remote Sens. Lett., vol. 6, no. 4, pp. 820–
824, Oct. 2009.
[7]. M. Dalla Mura, J. A. Benediktsson, F. Bovolo, and L. Bruzzone,
―An unsupervisedtechnique based on morphological filters for
change detectionin very high resolution images,‖ IEEE Geosci.
Remote Sens. Lett., vol. 5,
no. 3, pp. 433–437, Jul. 2008.
[8]. Z. Lei, T. Fang, H. Huo, and D. Li, ―Bi-temporal texton forest for
landcover transition detection on remotely sensed imagery,‖ IEEE
Trans.Geosci. Remote Sens., vol. 52, no. 2, pp. 1227–1237, Feb.
2014.
[9]. G. Camps-Valls, L. Gómez-Chova, J. Muñoz-Marí, J. L. Rojo-
Álvarez,and M. Martínez-Ramón, ―Kernel-based framework for
multitemporaland multisource remote sensing data classification
and change detection,‖IEEE Trans. Geosci. Remote Sens., vol. 46,
no. 6, pp. 1822–1835,Jun. 2008.
[10]. K. Chen, C. Huo, Z. Zhou, H. Lu, and J. Cheng, ―Semi-
supervisedchange detection via Gaussian processes,‖ in Proc.
IEEE IGARSS, 2009,pp. II-996–II-999.
[11]. M. Roy, S. Ghosh, and A. Ghosh, ―A novel approach for change
detection of remotely sensed images using semi-supervised
multiple classifiersystem,‖ Inf. Sci., vol. 269, pp. 35–47, Jun.
2014.
[12]. U. C. Benz, P. Hofmann, G. Willhauck, I. Lingenfelder, and M.
Heynen,―Multi-resolution, object-oriented fuzzy analysis of
remote sensing datafor GIS-ready information,‖ ISPRS J.
Photogramm. Remote Sens., vol.58, no. 3/4, pp. 239–258, Jan.
2004.
[13]. M. Pesaresi and J. A. Benediktsson, ―A new approach for the
morphologicalsegmentation of high-resolution satellite imagery,‖
IEEE Trans.Geosci. Remote Sens., vol. 39, no. 2, pp. 309–320,
Feb. 2001.

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A New Approach for Multi Index Automatic Change Detection in HR Remotely Sensed Imagery

  • 1. International Journal of Latest Technology in Engineering, Management & Applied Science (IJLTEMAS) 2nd Special Issue on Engineering and Technology | Volume VI, Issue VIS, June 2017 | ISSN 2278-2540 www.ijltemas.in Page 29 A New Approach for Multi Index Automatic Change Detection in HR Remotely Sensed Imagery Madhukar.B.N1 , Sheshashayana.K.S2 1 Senior Assistant Professor, NHCE, Bengaluru, India, 2 M.Tech Student, NHCE, Bengaluru, India Abstract— In recent years the technology is growing rapidly and the development of the country very fast and also due to this the infrastructures are increasing. Hence the changes could be noted by using new generation of Earth observation sensors with high spatial resolution or high resolution (HR) which provide detailed information for change detection. The widely used methods for high-resolution image change detection rely on textural/structural features. In order to get the high resolution images for viewing the areas in this project we use multi index automatic change detection method is proposed for the high- resolution imagery. The advantages are as follows: 1) The information (images) sent by the satellite would be in very low size, low pixels so in order to improve the viewing ability we use high-dimensional but low-level features (e.g., textural and structural features) i.e. multi index representation method. The multi index representation refers to the enhanced vegetation index, the water index, and the recently developed morphological building index. I am going use this technique for implementing in military places, which has a very large application. Moreover, the traditional methods based on the state-of- the-art textural/morphological features were also implemented for the purpose of comparison, which further validates the advantages of my project. Key words— Building detection, change detection, high resolution, morphological. I.INTRODUCTION ETECTION of land cover/use changes is one of the most Fundamental and useful tasks for various applications suchas urban expansion, urban planning, damage assessment, Convenient to obtain remotely sensed imagery over certain deforestation, and urban landscape monitoring. With the rapid development of Earth observation techniques, it becomes area at different times. Thus, land cover/use changes can be effectively detected and analyzed by processing the multi temporal remote sensing images. In order to timely process the big remote sensing data and rapidly transfer the data into information and knowledge, it is necessary to develop automatic techniques for image change detection. A few studies have recently addressed the automatic change detection methods, including studies on multilevel change vector analysis, morphological filters with change vector analysis, multi temporal morphological attribute Profiles; pulse coupled neural networks, and hierarchical spectral change analysis. The basic idea of the proposed method is to represent complicated high-resolution scenes by a set of low dimensional semantic indexes that are used to replace traditional high-dimensional but low-level features (e.g., textural features and morphological profiles). Specifically, urban primitives, e.g., buildings, vegetation, and water, are automatically extracted by the morphological building index (MBI), the enhanced vegetation index (EVI), and the normalized difference water index (NDWI), respectively. Change detection using high spatial resolution remote sensing images has received increasing interest since detailed ground change information is now available. However, a large intra class variance and a small interclass variance can lead to inaccuracy for the traditional spectral based and pixel based image processing framework when high spatial resolution imagery is used for change detection. In order to deal with this problem and improve the accuracy of change detection from high resolution data, researchers have proposed to take spatial features into consideration for change detection. The notable characteristics of the multi index method include the following aspects.1) The complicated urban scenes can be automatically and effectively represented by a set of low dimensional information indexes.2) The local histograms of these indexes are able to describe the frequency and spatial arrangement of the urban primitives. Consequently, the multi temporal multi index representations can be used to detect the structural changes of the urban scenes.The proposed change detection method is described by the following steps. 1. Calculation of Information Indexes 2. Automatic Change Detection a) Block based b) cell based 3. Types of Change II. MULTIINDEX URBAN REPRESENTATION In this paper, three urban primitive indexes, i.e., MBI, EVI, and NDWI, are used to represent a typical urban scene. Please note that these three indexes provide information not only for buildings, vegetation, and water but also for nonbuildings, D
  • 2. International Journal of Latest Technology in Engineering, Management & Applied Science (IJLTEMAS) 2nd Special Issue on Engineering and Technology | Volume VI, Issue VIS, June 2017 | ISSN 2278-2540 www.ijltemas.in Page 30 nonvegetation, and nonwater features, which actually enhances the discrimination ability of distinguishing different urban structures. A. MBI MBI is an effective method for automatic building detection. It is able to represent spectral–spatial properties of buildings (e.g., brightness, size, contrast, directionality, and shape) by a set of morphological operators. It should be noted that buildings are spectrally similar with the bright soil, and hence, the original MBI algorithm is improved in this study by introducing a post processing step, aiming to reduce false alarms from the urban bright soil. The modified MBI algorithm is described as follows. Step 1—Calculation of Brightness: The brightness is the maximum value of the visible bands for each pixel, which is used to represent the structures with high reflectance (e.g., candidate buildings). The visible bands are considered since they have the most significant contributions to the spectral reflectance of buildings. Step 2—Top-Hat Morphological Profiles: Considering the fact that buildings and their spatially adjacent shadows lead to high local contrast, MBI is defined using differential morphological profiles (DMPs) of the white top-hat by reconstruction, i.e., DMPWTH, as follows: DMPWTH = {DMPWTH(s, dir) : smin ≤ s ≤ smax, dir ∈D} (1) DMPWTH(s, dir) = |WTH(s+Δs, dir) − WTH(s, dir)| (2) Where WTH(s, dir) represents the white top-hat of the brightness image obtained in step 1 by using a linear structural element (SE), with s and dir being the scale and the direction, respectively. smin and smax indicate the range of the spatial size of buildings, and Δs is the interval of the profiles. D is the set of directions for the linear SE. Step 3: MBI is calculated by ∑ ( ) (3) where ND and NS denote the number of directions and scales for the morphological profiles, respectively. Buildings correspond to the areas with high MBI values, due to their large local contrast in various directions and scales. Step 4—Postprocessing: As aforementioned, in order to refine the result of the building detection, a post processing step is proposed to suppress the false alarms of bright soil from the original MBI. Spectral information plays a key role for identification of soil. It should be noted that bright soil in an urban scene often has a yellow tone, corresponding to the urban construction sites. Therefore, based on the WorldView-2 images used in this study, a yellow soil index (YSI) can be defined using the normalized difference of yellow (Y) and blue (B) channels, i.e., (4) B. EVI The vegetation information is automatically extracted by the EVI. It was developed by enhancing the vegetation signals through the difference between near-infrared (NIR) and red (R) bands and, at the same time, reducing the aerosol effects using blue (B) band. EVI is defined as (5) C. NDWI The NDWI is adopted to detect the water bodies. It high lights the water areas by maximizing the reflectance in green(G) band and minimizing the low reflectance in near infrared (NIR) band, i.e., NDWI= (6) The water information is further refined by imposing an area based threshold on the NDWI such that small noise and errors (e.g., shadows) can be removed. III. CHANGE DETECTION Based on the previous discussions, it can be stated that Multiple information indexes have the potential for achieving automatic change detection from urban areas. Two examples for the multi index automatic change detection are shown in Fig. 3, from which it is clearly seen that the structural changes in high resolution images can be effectively indicated by the information indexes. Consequently, the multi temporal multi index representations can be used to detect the structural changes of the urban scenes. The proposed change detection method is described by the following steps. Step 1—Calculation of Information Indexes: Information on buildings, vegetation, and water is obtained at the pixel level based on the MBI, the EVI, and the NDWI, respectively;and the corresponding post processing is then used to suppress the noise in the initial result, i.e., removing bright soil from buildings and shadow from water bodies. Step 2—Automatic Change Detection: The image is first divided into a series of blocks with the size of N × N (pixels) for each one, which is viewed as the basic unit for the change detection. This strategy is called ―hot spot‖ detection, which is a commonly used approach for change detection from high- resolution images. A) Block-based strategy: In this case, the scene is represented by the frequencies of the primitives in the multi
  • 3. International Journal of Latest Technology in Engineering, Management & Applied Science (IJLTEMAS) 2nd Special Issue on Engineering and Technology | Volume VI, Issue VIS, June 2017 | ISSN 2278-2540 www.ijltemas.in Page 31 index histogram of the block. For the block histograms at times T1 and T2, a weighted distance is used to determine whether changes occur in this area, i.e., ∑ ( ( ) ( )) (7) Dist(i)=|H1(i)-H2(i)| (8) ( ) ( ) ∑ ( ( ) (9) where WDist is the weighted distance between the histograms H 1 and H 2. Dim is the dimension of the histogram. H 1(i) and H 2(i) represent the frequency of the ith bin in the histograms H 1 and H 2, respectively. W(i) is expressed as the normalized distance between H 1(i) and H 2(i), in order to further enlarge the difference for the dissimilar bins. B) Cell-based strategy: As shown in Fig. 4, spatial arrangement of the primitives can be considered by dividing each block into n × n cells. This way, a cell is viewed as a basic unit to calculate the frequencies of the information indexes. A block is then represented by n × n histograms, each one representing the frequencies of the multiindex features in each cell. Subsequently, the similarity measure between the bit temporal histograms is calculated, in order to determine whether changes occur in this block. In this case, the distance measure can be extended from , i.e., ∑ (∑ ( ) ( )) (10) ( )=| (i)- ( ) (11) ( ) ( ) ∑ ( ) (12) Step 3—Types of Change: It should be noted that most of the automatic change detection methods only indicate whether Changes take place in the block but cannot provide specific Information related to the types of changes. In this paper, however, based on the information indexes, it is possible to further provide the change information corresponding to each block, by investigating which information index is subject to significant changes in terms of both frequency and spatial arrangement in the block. This can be viewed as a by-product of the proposed change detection method. IV. DATA SETS AND RESULTS Fig.1: Image of the Bangalore region 13/Jan/2015. Fig.1 is the raw image from the satellite of the area of the Bangalore city taken in 13 Jan 2015 with the co-ordinates lat- 12.921242 and log-77.641255 is the position at the center of the image with 240 square km distance. It is of pixel size 140x390 feet taken on Jan 13, 2015 from Landsat – 7 satellite. Fig.2: Image of the Bangalore region 8/Apr/2017 Fig.2 is the raw image from the satellite of the area of the Bangalore city taken in 8 Apr 2017 with the co-ordinates lat=12.921242 and log=77.641255 is the position at the center of the image with 240 square km distance. It is of pixel size 140x390 feet taken on Jan 13, 2015 from Landsat – 7 satellite. Fig.3: Multi index output 2015(left), 2017 (right) Fig.3 is the multiuindex output for the change detected in the image. You can see that the part is the buildings, green is the vegetation and the blue is the water bodies. The black image is for soil part or the shadow part which is removed during the multiindex of the image. Fig.4 is the morphological output index of the two images which are used as the input the Fig. 6.10 shown explains about the various structures and different levels of basic things like vegetation, water levels and other empty land or the shadow. Fig.4: Final change detection of water, building and vegetation.
  • 4. International Journal of Latest Technology in Engineering, Management & Applied Science (IJLTEMAS) 2nd Special Issue on Engineering and Technology | Volume VI, Issue VIS, June 2017 | ISSN 2278-2540 www.ijltemas.in Page 32 We can see there are different colors used to map different morphological units one such is the buildings water bodies and vegetation that is the green parts on the earth. I have used the Bangalore city to explore the change detection that has happened is the year 2015 and the year 2017. Fig.5: Change detection using block based (left) and cell based (right). This change is noted down on the multi index image and the roc curve which gives the clear change detected in the two images this change detected can be plotted on the bar graph for easy understanding and to check the total change with reference to the pixel of the image using these pixels in different ratios we can easily calculate the accuracy of the change detected. Fig. 6: Graphical Representation Of Block Based. Fig. 7: Graphical Representation of Cell Based. Fig.8: ROC Curve for Cell Based. Fig.9: ROC Curve for Block Based. V. COMPARISON The greater part of existing change recognition techniques could be characterized into three groups, the conventional pixel0based0change0detection the object0based0change identification and the hybrid0change0detection. Both PBCD and OBCD have drawbacks and hence we established HCD strategies. There is no ideal HCD technique started yet. Breaking down the complementarities of PBCD and OBCD strategy, we propose another unsupervised algorithm level fusion0scheme (UAFS-HCD) which is used in order to improve the accuracy of the pixel based techniques using spatial domain approach. This is done by following approaches.1) Getting the preliminary change with PBCD at first to estimate few parameters for OBCD.2) Determining the unaltered territory areas and to wipe out the territories without changes, which reduces the error amplification phenomenon of OBCD.3) Acquiring the final change mask by methods for OBCD technique. -0.5 0 0.5 1 1.5 2 2.5 3 3.5 2600 2800 3000 3200 3400 3600 3800 4000 4200 False positive rate Truepoasitiverate Block based
  • 5. International Journal of Latest Technology in Engineering, Management & Applied Science (IJLTEMAS) 2nd Special Issue on Engineering and Technology | Volume VI, Issue VIS, June 2017 | ISSN 2278-2540 www.ijltemas.in Page 33 Fig.10: Block based CD(left), Cell based CD(right) imagery of existing system. Fig.11: Block based CD(left), Cell based CD(right) imagery of proposed system. VI. CONCLUSION In this paper, an innovative change area procedure in light of the multi record picture depiction has been proposed for high assurance remote distinguishing imagery over urban scenes. The proposed technique is fit for fulfilling satisfactory change recognizable proof precision with a game plan of low dimensional; however semantic information records are saved in the database. Two specific systems are completed for the proposed procedure. The first is a block based approach where the frequencies of the information records are considered for change area. The other is the cell based one where each block is moreover scheduled into a movement of cells. Along these lines, the frequencies as well as the spatial course of action of the data files in the square can be misused. A near review was led between the proposed multi record strategy and the customary multi include technique for programmed change location. Likewise, the proposed multi list model can consequently show which class the adjustment in the territory is identified with. This is a repercussion of the proposed strategy. Rather, conventional programmed change location can just decide if changes happen in this district or not. ACKNOWLEDGMENT The authors are grateful to Dr. Mohan Manghnani, Chairman, New Horizon College of Engineering (NHCE) Bengaluru, for his encouragement for carrying out his work. They are thankful to Dr. Manjunatha, Principal, New Horizon College of Engineering (NHCE) Bengaluru, for his encouragement for this research work. They are also very grateful to Dr. Sanjay Jain, Professor and HOD, ECE Dept. New Horizon College of Engineering Bengaluru, for providing necessary backbone support to proceed on this endeavor. Finally, we are highly indebted to our parents for encouraging us to excel in our chose fields. REFERENCES [1]. M. Hussain, D. Chen, A. Cheng, H. Wei, and D. Stanley, ―Change detection from remotely sensed images: From pixel-based to object-basedapproaches,‖ ISPRS J. Photogramm. Remote Sens., vol. 80, pp. 91–106,Jun. 2013. [2]. P. Coppin, I. Jonckheere, K. Nackaerts, B. Muys, and E. Lambin, ―Digitalchange detection methods in ecosystem monitoring: A review,‖ Int. J.Remote Sens., vol. 25, no. 9, pp. 1565–1596, May 2004. [3]. X. Huang and L. Zhang, ―An SVM ensemble approach combiningspectral, structural, and semantic features for the classification ofhigh-resolution remotely sensed imagery,‖ IEEE Trans. Geosci. RemoteSens., vol. 51, no. 1, pp. 257–272, Jan. 2013. [4]. V. Walter, ―Object-based classification of remote sensing data forchange detection,‖ ISPRS J. Photogramm. Remote Sens., vol. 58, no. 3/4,pp. 225–238, Jan. 2004. [5]. T. Celik and K.-K. Ma, ―Multitemporal image change detection usingundecimated discrete wavelet transform and active contours,‖ IEEE Trans.Geosci. Remote Sens., vol. 49, no. 2, pp. 706–716, Feb. 2011. [6]. T. Celik, ―Multiscale change detection in multitemporal satellite images,‖IEEE Geosci. Remote Sens. Lett., vol. 6, no. 4, pp. 820– 824, Oct. 2009. [7]. M. Dalla Mura, J. A. Benediktsson, F. Bovolo, and L. Bruzzone, ―An unsupervisedtechnique based on morphological filters for change detectionin very high resolution images,‖ IEEE Geosci. Remote Sens. Lett., vol. 5, no. 3, pp. 433–437, Jul. 2008. [8]. Z. Lei, T. Fang, H. Huo, and D. Li, ―Bi-temporal texton forest for landcover transition detection on remotely sensed imagery,‖ IEEE Trans.Geosci. Remote Sens., vol. 52, no. 2, pp. 1227–1237, Feb. 2014. [9]. G. Camps-Valls, L. Gómez-Chova, J. Muñoz-Marí, J. L. Rojo- Álvarez,and M. Martínez-Ramón, ―Kernel-based framework for multitemporaland multisource remote sensing data classification and change detection,‖IEEE Trans. Geosci. Remote Sens., vol. 46, no. 6, pp. 1822–1835,Jun. 2008. [10]. K. Chen, C. Huo, Z. Zhou, H. Lu, and J. Cheng, ―Semi- supervisedchange detection via Gaussian processes,‖ in Proc. IEEE IGARSS, 2009,pp. II-996–II-999. [11]. M. Roy, S. Ghosh, and A. Ghosh, ―A novel approach for change detection of remotely sensed images using semi-supervised multiple classifiersystem,‖ Inf. Sci., vol. 269, pp. 35–47, Jun. 2014. [12]. U. C. Benz, P. Hofmann, G. Willhauck, I. Lingenfelder, and M. Heynen,―Multi-resolution, object-oriented fuzzy analysis of remote sensing datafor GIS-ready information,‖ ISPRS J. Photogramm. Remote Sens., vol.58, no. 3/4, pp. 239–258, Jan. 2004. [13]. M. Pesaresi and J. A. Benediktsson, ―A new approach for the morphologicalsegmentation of high-resolution satellite imagery,‖ IEEE Trans.Geosci. Remote Sens., vol. 39, no. 2, pp. 309–320, Feb. 2001.