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Ms. Neha Bhatt, Mr. IndrJeet Rajput, Mr. Vinitkumar Gupta / International Journal of
Engineering Research and Applications (IJERA) ISSN: 2248-9622 www.ijera.com
Vol. 3, Issue 3, May-Jun 2013, pp.174-179
174 | P a g e
Classification of Multi-date, Tempo-Spectral data using NDVI
values
1
Ms. Neha Bhatt, 2
Mr. IndrJeet Rajput, 3
Mr. Vinitkumar Gupta
1
Department of Computer EngineeringGTU UniversityIndia
2,3
Department of Computer EngineeringHGCEIndia
Abstract— NASA launched the Earth
Observing System's flagship satellite "Terra,"
named for Earth, on December 18, 1999. Terra
has been collecting data about Earth's changing
climate Normalized Difference Vegetation
Index (NDVI) is a simple graphical indicator that
can be used to analyze remote sensing
measurements. These indexes can be used to
prediction of classes of Remote Sensing (RS)
images. In this paper, we will classify the Terra
image on NDVI values of 5 different date’s
images (Captured by Terra satellite). For
classifying images, we will use formulae, which is
based on similarity measure. It will compare the
clustered image with the Reference image based
on the equation, it will classify the image. It is
simple process, which can classify much faster.
Keywords-Terra, Normalized Difference Vegetation
Index (NDVI), Remote Sensing, Multi date.
I. INTRODUCTION
The evaluation of the tempo -spectral data is very
useful in environment field [1]. In this paper, we
propose the technique for finding similarity based on
reference images. The Vegetation Index (VI) based
on the image taken through Remote Sensing can be
used to identify the objects [1]. Normalized
Difference Vegetation Index (NDVI) is one of the
popular Vegetation Index. In this paper, we are using
Terradata to compute the similarity.
Terra carries five state-of-the-art sensors that
have been studying the interactions among the Earth's
atmosphere, lands, oceans, and radiant energy. Each
sensor has unique design features that will enable
scientists to meet a wide range of science objectives.
The five Terra onboard sensors are:
 ASTER, or Advanced Spaceborne Thermal
Emission and Reflection Radiometer
 CERES, or Clouds and Earth's Radiant
Energy System
 MISR, or Multi-angle Imaging
Spectroradiometer
 MODIS, or Moderate-resolution Imaging
Spectroradiometer
 MOPITT, or Measurements of Pollution in
the Troposphere
Because Terra's five sensors share a platform,
they collect complimentary observations of Earth's
surface and atmosphere. These varying perspectives
of the same event can yield unique insights into the
processes that connect Earth's systems.
Figure1: Terra Sensor
NDVI value of an image can be calculated based
upon the following formulae.
REDIR
REDIR
NDVI



Where IR (Infra-Red) denotes the value in the
Infra-Red band and RED denotes the value in Red
band. As image consist of many bands, NDVI uses
these 2 bands for its calculation.
Template matching is one of the simple
techniques used from past many decades. It is a basic
technique for image as it can answer too many
questions related to image [2]. We give the faster
algorithm Sum of Squared Difference on NDVI
values of Remote Sensing data. Also the intention of
this paper is not to say that this measure opposes the
other measures.
II. RELATED WORK
Integration of different and complementary
sensor images such as optical and radar remotely-
sensed images has been widely used for cloud cover
removal [1] and achieving better scene interpretation
accuracy [2, 3]. The integration may be done by
image mosaicking or data fusion which are
accomplished either at the preprocessing stage [4] or
the postprocessing stage [2]. Sensor-specific
classifiers are commonly used. For example,
classifiers based on image tonal or spectral features
are used to classify optical images [2]. In other
cases, classifiers based on texture features are used
for recognizing cloud types [5] and improving the
urban area classification result for optical images.
For radar image interpretation, classifiers based on
various texture models were used [6, 7, 8], but
problems may arise if homogeneous-region land
cover objects exist in the radar image [9].
Ms. Neha Bhatt, Mr. IndrJeet Rajput, Mr. Vinitkumar Gupta / International Journal of
Engineering Research and Applications (IJERA) ISSN: 2248-9622 www.ijera.com
Vol. 3, Issue 3, May-Jun 2013, pp.174-179
175 | P a g e
We have observed that both optical and
radar images consist of homogeneous and textured
regions. Aregion is considered as homogeneous if
the local variance of gray level distribution is
relatively low, and a region is considered as textured
if the local variance is high. Our further
investigations found that land-cover objects can also
be grouped into homogeneous and textured land
cover objects which offer better discrimination in
each group. Based on these findings we have
proposed an integrated multi-sensor classification
scheme [1]. The same procedure can be used for
classifying optical or radar input images. We use the
multivariate Gaussian distribution to model the
homogeneous part of an image, and use the
multinomial distribution to model the gray level co-
occurrences of the textured part [9]. We apply a
spectral-based classifier to the homogeneous part
anda texture-based classifier to the textured part of
an image. These classifiers use maximum-likelihood
decision rule which work concurrently on an input
image.
Low-level data fusion may be done to
improve radar image classification accuracy or to
exploit the synergy of multi-sensor information. The
data fusion method may include algebraic
operations, the principal component transformation
or the Karhunen-Loeve transform, FCC or IHS
tranformation, augmented vector classification, and
hierarchical data fusion. We have utilized the
intensity transformation based on the Karhunen-
Loeve transform [11] and hierarchical data fusion
[4]
The classification scheme was discussed in
[1]. Basically, there are three parameters that control
the proposed classifier:
(a) A threshold value that decides if a pixel belongs
to either the homogeneous or the textured region,
(b) Type of each land cover object (homogeneous,
textured, or both), and
(c) The window size over which the texture meaures
are computed.
The threshold value can be tuned so that we
can even have a fully spectralbased classifier or a
fully texture-based classifier if it is necessary. The
type of each land cover object can be determined
based on the labeled training samples. We can use a
window size as small as 3x3 if there are roads or
other line-shaped objects, or a window size of 9x9 if
larger objects are contained in the image.
Several studies have found that the
temporal variations of MODIS vegetation index
(NDVI/EVI) values are related to climatic conditions
such as temperature and precipitation [12-15]. The
authors discovered that the interannual variation in
Normalized Difference Vegetation Index (NDVI)
and Enhanced vegetation index (EVI) values for
specific eight-day periods was correlated with the
phenological indicators [12].It has been
demonstrated that vegetation covers of different
moisture conditions or different species
compositions have different variation patterns in the
time series of the MODIS Enhanced Vegetation
Index (EVI) values[16]. Template matching isa
fundamental method of detecting the presence or
theabsence of objects and identifying them in an
image. Atemplate isitself an image that contains a
feature or an object or a part ofa bigger image, and
isused to search a given image for the presence or
the absence of the contents ofthe template. This
search iscarried out by translating the template
systematically pixel - by-pixel all over the image,
and at each position ofthe template the closeness of
the template to the area covered by it ismeasured.
The locationat which the maximum degree of
closeness isachieved isdeclared to be the location of
the object detected [17].Template matching is one of
the simple techniques used from past many decades.
It is a basic technique for image as it can answer too
many questions related to image [27]. We give the
faster algorithm Sum of Squared Difference on
NDVI values of Remote Sensing data. Also the
intention of this paper is not to say that this measure
opposes the other measures.
While vegetation is the concern, there
should be accuracy in classifying the image based on
proper criteria which must leads to a valid
conclusion. Existing models of the vegetation
dynamic are typically ignores the spatial correlations
[19]. There are many numbers of techniques which
are used for the template matching. It includes
template matching strategy using template trees
growth [20], Comparison based template matching
[21], Digital Image processing [22], Correlation
techniques in Image processing [23]. Multi-date
sequence of the data can be used to quantifying the
time-space structure of vegetation [24]. As an
example, remotely sensed image series of NDVI [25]
and Enhanced VI (EVI) gathered from the different
sensors can be directly used in analysis of the
structural and functional characteristics of land
covers [26]. For the short lead-time applications in
agricultural water management and forest-fire
assessment, a spatiotemporal model that captures
spatial variation patterns in vegetation conditions and
phenology is required. In this paper, we propose a
predictive multidimensional model of vegetation
anomalies that overcomes the limitations of existing
approaches. The model is based on a two-step
process. The first step describes the deterministic
component of vegetation dynamics through an
additive model, including seasonal components,
interannual trends, and jumps. The spatial
dependences are neglected in the first step. The
deterministic model (DM) represents a filtering
procedure able to generate a new stationary time
series of anomalies (residuals). The second step
assumes that the residual component of the DM is a
Ms. Neha Bhatt, Mr. IndrJeet Rajput, Mr. Vinitkumar Gupta / International Journal of
Engineering Research and Applications (IJERA) ISSN: 2248-9622 www.ijera.com
Vol. 3, Issue 3, May-Jun 2013, pp.174-179
176 | P a g e
stochastic process which exhibits systematic
autoregressive (AR) and spatial dependences. Then,
the dynamics of the anomalies are analyzed through a
multidimensional model (space-time AR (STAR)
model), which accounts for the AR characteristics
and the spatial correlations of the remotely sensed
image sequences [18].
III. APPROACH
There are many approaches to classify the
image sensed using Remote Sensing Satellites.
A. Classical Approach
There are many techniques available for
classifying an image. Some of them are listed
below.
• Comparison based template matching
• Digital Image Processing
• Correlation techniques
• Pattern matching
• Time-space structure of vegetation
B. Our Approach
NDVI values can be calculated using the
following algorithm.
For each i in range
ndvi_lower_part = (nir_value[i] + red_value[i])
ndvi_upper_part = (nir_value[i] - red_value[i])
ndvi = ndvi_upper_part/ndvi_lower_part
Algorithm1: Calculate NDVI values
Similarity
Measure
Formula
Sum of
Squared
Difference
(SSD)


Wji
jyixIjiI
),(
2
21 )),(),((
Sum of
Absolute
Difference
(SAD)


Wji
jyixIjiI
),(
21 |),(),(|
Zero-mean
Sum of
Absolute
Difference
(ZSAD)


Wji
jyixIjyixIjiIjiI
),(
2211 |),(),(),(),(|
Locally
scaled
Sum of
Absolute
Difference
(LSAD)




Wji
jyixI
jyixI
jiI
jiI
),(
2
2
1
1 |),(
),(
),(
),(|
Table1: Similarity Measures
Table 1shows some of the similarity measures
available which can be applicable to image data. This
type of similarity measure we called it as correlation
based similarity measure. In this technique, we are
taking window of a small size and the pixels in that
region are compared with the reference of that type
of image and small window of that region. This
method checks the similarity pixel by pixel.
There are many other similarity measures like
Sum of the Squared Difference (SSD), Zero-mean
Sum of the Squared Difference (ZSSD), Locally
Scaled Sum of the Squared Difference (LSSD),
Normalized Cross Correlation (NCC), Zero mean
Normalized Cross Correlation (ZNCC) and Sum of
Hamming Distance (SHD).
Consider the equation shown below:
 

),(2),(1
)),(2),(1(
jyixIjiI
jyixIjiIAbs
Equation [1]
Above formulae is a proposed formula to measure
similarity. It is based on Sum of Absolute Difference
and it can provide nearer result to the Sum of
Absolute Difference. Now apply above formulae to
Unknown image with Reference image. Images used
for applying above algorithm is as shown below.
Figure 2: 18 Feb 2013, 15 Jan 2013, 10 Dec 2012,
8 Nov 2012, 2 Oct 2012 Respectively
Ms. Neha Bhatt, Mr. IndrJeet Rajput, Mr. Vinitkumar Gupta / International Journal of
Engineering Research and Applications (IJERA) ISSN: 2248-9622 www.ijera.com
Vol. 3, Issue 3, May-Jun 2013, pp.174-179
177 | P a g e
Below is the file used for Reference classes
2/10/12 8/11/12 10/12/12 15/01/13 18/02/13
Ref-
Class
137.89 103.56 102.22 132.44 165.11 1
157.56 106 92.33 127.33 168 2
115.56 93.67 113.89 147.22 155.44 3
133.56 97 105.67 129.44 156.44 4
142.33 96.67 104.78 117.11 162.22 5
96.22 116.44 153.89 158 131.89 6
103.56 108.44 141 156.78 141.11 7
102.56 111.33 161 156.11 129.78 8
100.44 123.11 156.44 154.33 105.78 9
97.56 113.89 167 157 131 10
116.11 111.89 156.89 126.67 136.78 11
71.44 66.22 53 60.33 82.67 12
78.78 76.44 72.67 81.11 72.33 13
79.22 71.67 61 60.89 83.11 14
74.11 75 74.33 77 83.44 15
115.78 102.44 107 115.44 101.33 16
106.33 101.11 100.22 99.56 96.67 17
142.89 120.44 114.56 124.44 104.11 18
160.78 127.44 140 125.89 110.89 19
156.22 119.89 136.78 126.56 107.11 20
Table2: Reference File
Below is the file used to compare unknown class.
2/10/12 8/11/12
10/12/
12
15/01/
13
18/02/
13
Cluster
No
101.58 4.7 119.21 0 111.11 1
1.01 90.72 0 114.33 0 2
70.25 73.96 66.27 78.99 91.33 3
101.08 97.52 99.38 99.32 96.68 4
98.02 98.76 107.31 114.17 114 5
Table3: Cluster File
Proposed Work:
1. Take 5 different dates Reference and
Unknown cluster images.
2. Calculate NDVI images for all 5 images
using algorithm 1 as shown above.
3. Get the Unknown interested regions from
the image and collect the NDVI values into
1 file.
4. Normalize NDVI values of -1 to 1 into 0 to
200 by
using formulae:
ndvi_new = ndvi_old x 100 + 100
5. Make the Reference file and Unknown
cluster file as shown above in Table 2 and
Table 3.
6. Apply Equation [1] given above for these 2
files and get the class label.
7. Get the output as shown in Table4. It will
contain the class in which unknown class is
classified.
IV. IMPLEMENTATION
To calculate NDVI values, we can use
GDAL library. GDAL is one type of Translator
library, generally used for raster Geospatial data
format and which is open source. We will use
Python language for programming and we can use
Eclipse IDE. We can implement the functionality
shown in Algorithm1 in Python after embedding
GDAL library into it. After calculating NDVI
values, we can use this NDVI data to apply
Equation [1]. Here, we will use .Net technology
with C# as programming language to implement
Equation1. Fig. 4 shows the design of the
implementation of algorithm. It will take input as
Reference File and Cluster File and it will produce
Output file which will contain classification
details.
159.74 130.6 147.48 136.85 120.94 19
1.01 90.72 0 114.33 0 1
70.25 73.96 66.27 78.99 91.33 15
101.08 97.52 99.38 99.32 96.68 17
98.02 98.76 107.31 114.17 114 16
Table4: Output File
After classification process when we can
compare the resulted Reference and unknown
cluster it can be shown as a graph.
Figure 3: Analysis
90
92
94
96
98
100
102
104
106
108
Cluster
Reference
Ms. Neha Bhatt, Mr. IndrJeet Rajput, Mr. Vinitkumar Gupta / International Journal of
Engineering Research and Applications (IJERA) ISSN: 2248-9622 www.ijera.com
Vol. 3, Issue 3, May-Jun 2013, pp.174-179
178 | P a g e
V. CONCLUSION
From above implementation results, we can
conclude that this algorithm is much faster
compared to other approaches as it includes small
mathematical calculation and it take O (n) time to
compute the result. The „n‟ value depends upon
number of clusters that needs to classify.
VI. FUTURE WORK
This algorithm can also used to enhance the
perfection by including Standard deviation. Also it
can‟t be used for needs where some dates are having
more importance and need to give more preference to
that particular date. In that case, we need to modify
this algorithm to some point. This feature can also be
implemented using Sum of Absolute Difference. In
that case, we can get similar value to that of Sum of
Squared Difference.
ACKNOWLEDGMENT
We would like to thank the School of Computer
Science and Engineering, GTU, for giving us such an
opportunity to carry out this research work and also
for providing us the requisite resources and
infrastructure for carrying out the research.
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Ms. Neha Bhatt, Mr. IndrJeet Rajput, Mr. Vinitkumar Gupta / International Journal of
Engineering Research and Applications (IJERA) ISSN: 2248-9622 www.ijera.com
Vol. 3, Issue 3, May-Jun 2013, pp.174-179
179 | P a g e
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Af33174179

  • 1. Ms. Neha Bhatt, Mr. IndrJeet Rajput, Mr. Vinitkumar Gupta / International Journal of Engineering Research and Applications (IJERA) ISSN: 2248-9622 www.ijera.com Vol. 3, Issue 3, May-Jun 2013, pp.174-179 174 | P a g e Classification of Multi-date, Tempo-Spectral data using NDVI values 1 Ms. Neha Bhatt, 2 Mr. IndrJeet Rajput, 3 Mr. Vinitkumar Gupta 1 Department of Computer EngineeringGTU UniversityIndia 2,3 Department of Computer EngineeringHGCEIndia Abstract— NASA launched the Earth Observing System's flagship satellite "Terra," named for Earth, on December 18, 1999. Terra has been collecting data about Earth's changing climate Normalized Difference Vegetation Index (NDVI) is a simple graphical indicator that can be used to analyze remote sensing measurements. These indexes can be used to prediction of classes of Remote Sensing (RS) images. In this paper, we will classify the Terra image on NDVI values of 5 different date’s images (Captured by Terra satellite). For classifying images, we will use formulae, which is based on similarity measure. It will compare the clustered image with the Reference image based on the equation, it will classify the image. It is simple process, which can classify much faster. Keywords-Terra, Normalized Difference Vegetation Index (NDVI), Remote Sensing, Multi date. I. INTRODUCTION The evaluation of the tempo -spectral data is very useful in environment field [1]. In this paper, we propose the technique for finding similarity based on reference images. The Vegetation Index (VI) based on the image taken through Remote Sensing can be used to identify the objects [1]. Normalized Difference Vegetation Index (NDVI) is one of the popular Vegetation Index. In this paper, we are using Terradata to compute the similarity. Terra carries five state-of-the-art sensors that have been studying the interactions among the Earth's atmosphere, lands, oceans, and radiant energy. Each sensor has unique design features that will enable scientists to meet a wide range of science objectives. The five Terra onboard sensors are:  ASTER, or Advanced Spaceborne Thermal Emission and Reflection Radiometer  CERES, or Clouds and Earth's Radiant Energy System  MISR, or Multi-angle Imaging Spectroradiometer  MODIS, or Moderate-resolution Imaging Spectroradiometer  MOPITT, or Measurements of Pollution in the Troposphere Because Terra's five sensors share a platform, they collect complimentary observations of Earth's surface and atmosphere. These varying perspectives of the same event can yield unique insights into the processes that connect Earth's systems. Figure1: Terra Sensor NDVI value of an image can be calculated based upon the following formulae. REDIR REDIR NDVI    Where IR (Infra-Red) denotes the value in the Infra-Red band and RED denotes the value in Red band. As image consist of many bands, NDVI uses these 2 bands for its calculation. Template matching is one of the simple techniques used from past many decades. It is a basic technique for image as it can answer too many questions related to image [2]. We give the faster algorithm Sum of Squared Difference on NDVI values of Remote Sensing data. Also the intention of this paper is not to say that this measure opposes the other measures. II. RELATED WORK Integration of different and complementary sensor images such as optical and radar remotely- sensed images has been widely used for cloud cover removal [1] and achieving better scene interpretation accuracy [2, 3]. The integration may be done by image mosaicking or data fusion which are accomplished either at the preprocessing stage [4] or the postprocessing stage [2]. Sensor-specific classifiers are commonly used. For example, classifiers based on image tonal or spectral features are used to classify optical images [2]. In other cases, classifiers based on texture features are used for recognizing cloud types [5] and improving the urban area classification result for optical images. For radar image interpretation, classifiers based on various texture models were used [6, 7, 8], but problems may arise if homogeneous-region land cover objects exist in the radar image [9].
  • 2. Ms. Neha Bhatt, Mr. IndrJeet Rajput, Mr. Vinitkumar Gupta / International Journal of Engineering Research and Applications (IJERA) ISSN: 2248-9622 www.ijera.com Vol. 3, Issue 3, May-Jun 2013, pp.174-179 175 | P a g e We have observed that both optical and radar images consist of homogeneous and textured regions. Aregion is considered as homogeneous if the local variance of gray level distribution is relatively low, and a region is considered as textured if the local variance is high. Our further investigations found that land-cover objects can also be grouped into homogeneous and textured land cover objects which offer better discrimination in each group. Based on these findings we have proposed an integrated multi-sensor classification scheme [1]. The same procedure can be used for classifying optical or radar input images. We use the multivariate Gaussian distribution to model the homogeneous part of an image, and use the multinomial distribution to model the gray level co- occurrences of the textured part [9]. We apply a spectral-based classifier to the homogeneous part anda texture-based classifier to the textured part of an image. These classifiers use maximum-likelihood decision rule which work concurrently on an input image. Low-level data fusion may be done to improve radar image classification accuracy or to exploit the synergy of multi-sensor information. The data fusion method may include algebraic operations, the principal component transformation or the Karhunen-Loeve transform, FCC or IHS tranformation, augmented vector classification, and hierarchical data fusion. We have utilized the intensity transformation based on the Karhunen- Loeve transform [11] and hierarchical data fusion [4] The classification scheme was discussed in [1]. Basically, there are three parameters that control the proposed classifier: (a) A threshold value that decides if a pixel belongs to either the homogeneous or the textured region, (b) Type of each land cover object (homogeneous, textured, or both), and (c) The window size over which the texture meaures are computed. The threshold value can be tuned so that we can even have a fully spectralbased classifier or a fully texture-based classifier if it is necessary. The type of each land cover object can be determined based on the labeled training samples. We can use a window size as small as 3x3 if there are roads or other line-shaped objects, or a window size of 9x9 if larger objects are contained in the image. Several studies have found that the temporal variations of MODIS vegetation index (NDVI/EVI) values are related to climatic conditions such as temperature and precipitation [12-15]. The authors discovered that the interannual variation in Normalized Difference Vegetation Index (NDVI) and Enhanced vegetation index (EVI) values for specific eight-day periods was correlated with the phenological indicators [12].It has been demonstrated that vegetation covers of different moisture conditions or different species compositions have different variation patterns in the time series of the MODIS Enhanced Vegetation Index (EVI) values[16]. Template matching isa fundamental method of detecting the presence or theabsence of objects and identifying them in an image. Atemplate isitself an image that contains a feature or an object or a part ofa bigger image, and isused to search a given image for the presence or the absence of the contents ofthe template. This search iscarried out by translating the template systematically pixel - by-pixel all over the image, and at each position ofthe template the closeness of the template to the area covered by it ismeasured. The locationat which the maximum degree of closeness isachieved isdeclared to be the location of the object detected [17].Template matching is one of the simple techniques used from past many decades. It is a basic technique for image as it can answer too many questions related to image [27]. We give the faster algorithm Sum of Squared Difference on NDVI values of Remote Sensing data. Also the intention of this paper is not to say that this measure opposes the other measures. While vegetation is the concern, there should be accuracy in classifying the image based on proper criteria which must leads to a valid conclusion. Existing models of the vegetation dynamic are typically ignores the spatial correlations [19]. There are many numbers of techniques which are used for the template matching. It includes template matching strategy using template trees growth [20], Comparison based template matching [21], Digital Image processing [22], Correlation techniques in Image processing [23]. Multi-date sequence of the data can be used to quantifying the time-space structure of vegetation [24]. As an example, remotely sensed image series of NDVI [25] and Enhanced VI (EVI) gathered from the different sensors can be directly used in analysis of the structural and functional characteristics of land covers [26]. For the short lead-time applications in agricultural water management and forest-fire assessment, a spatiotemporal model that captures spatial variation patterns in vegetation conditions and phenology is required. In this paper, we propose a predictive multidimensional model of vegetation anomalies that overcomes the limitations of existing approaches. The model is based on a two-step process. The first step describes the deterministic component of vegetation dynamics through an additive model, including seasonal components, interannual trends, and jumps. The spatial dependences are neglected in the first step. The deterministic model (DM) represents a filtering procedure able to generate a new stationary time series of anomalies (residuals). The second step assumes that the residual component of the DM is a
  • 3. Ms. Neha Bhatt, Mr. IndrJeet Rajput, Mr. Vinitkumar Gupta / International Journal of Engineering Research and Applications (IJERA) ISSN: 2248-9622 www.ijera.com Vol. 3, Issue 3, May-Jun 2013, pp.174-179 176 | P a g e stochastic process which exhibits systematic autoregressive (AR) and spatial dependences. Then, the dynamics of the anomalies are analyzed through a multidimensional model (space-time AR (STAR) model), which accounts for the AR characteristics and the spatial correlations of the remotely sensed image sequences [18]. III. APPROACH There are many approaches to classify the image sensed using Remote Sensing Satellites. A. Classical Approach There are many techniques available for classifying an image. Some of them are listed below. • Comparison based template matching • Digital Image Processing • Correlation techniques • Pattern matching • Time-space structure of vegetation B. Our Approach NDVI values can be calculated using the following algorithm. For each i in range ndvi_lower_part = (nir_value[i] + red_value[i]) ndvi_upper_part = (nir_value[i] - red_value[i]) ndvi = ndvi_upper_part/ndvi_lower_part Algorithm1: Calculate NDVI values Similarity Measure Formula Sum of Squared Difference (SSD)   Wji jyixIjiI ),( 2 21 )),(),(( Sum of Absolute Difference (SAD)   Wji jyixIjiI ),( 21 |),(),(| Zero-mean Sum of Absolute Difference (ZSAD)   Wji jyixIjyixIjiIjiI ),( 2211 |),(),(),(),(| Locally scaled Sum of Absolute Difference (LSAD)     Wji jyixI jyixI jiI jiI ),( 2 2 1 1 |),( ),( ),( ),(| Table1: Similarity Measures Table 1shows some of the similarity measures available which can be applicable to image data. This type of similarity measure we called it as correlation based similarity measure. In this technique, we are taking window of a small size and the pixels in that region are compared with the reference of that type of image and small window of that region. This method checks the similarity pixel by pixel. There are many other similarity measures like Sum of the Squared Difference (SSD), Zero-mean Sum of the Squared Difference (ZSSD), Locally Scaled Sum of the Squared Difference (LSSD), Normalized Cross Correlation (NCC), Zero mean Normalized Cross Correlation (ZNCC) and Sum of Hamming Distance (SHD). Consider the equation shown below:    ),(2),(1 )),(2),(1( jyixIjiI jyixIjiIAbs Equation [1] Above formulae is a proposed formula to measure similarity. It is based on Sum of Absolute Difference and it can provide nearer result to the Sum of Absolute Difference. Now apply above formulae to Unknown image with Reference image. Images used for applying above algorithm is as shown below. Figure 2: 18 Feb 2013, 15 Jan 2013, 10 Dec 2012, 8 Nov 2012, 2 Oct 2012 Respectively
  • 4. Ms. Neha Bhatt, Mr. IndrJeet Rajput, Mr. Vinitkumar Gupta / International Journal of Engineering Research and Applications (IJERA) ISSN: 2248-9622 www.ijera.com Vol. 3, Issue 3, May-Jun 2013, pp.174-179 177 | P a g e Below is the file used for Reference classes 2/10/12 8/11/12 10/12/12 15/01/13 18/02/13 Ref- Class 137.89 103.56 102.22 132.44 165.11 1 157.56 106 92.33 127.33 168 2 115.56 93.67 113.89 147.22 155.44 3 133.56 97 105.67 129.44 156.44 4 142.33 96.67 104.78 117.11 162.22 5 96.22 116.44 153.89 158 131.89 6 103.56 108.44 141 156.78 141.11 7 102.56 111.33 161 156.11 129.78 8 100.44 123.11 156.44 154.33 105.78 9 97.56 113.89 167 157 131 10 116.11 111.89 156.89 126.67 136.78 11 71.44 66.22 53 60.33 82.67 12 78.78 76.44 72.67 81.11 72.33 13 79.22 71.67 61 60.89 83.11 14 74.11 75 74.33 77 83.44 15 115.78 102.44 107 115.44 101.33 16 106.33 101.11 100.22 99.56 96.67 17 142.89 120.44 114.56 124.44 104.11 18 160.78 127.44 140 125.89 110.89 19 156.22 119.89 136.78 126.56 107.11 20 Table2: Reference File Below is the file used to compare unknown class. 2/10/12 8/11/12 10/12/ 12 15/01/ 13 18/02/ 13 Cluster No 101.58 4.7 119.21 0 111.11 1 1.01 90.72 0 114.33 0 2 70.25 73.96 66.27 78.99 91.33 3 101.08 97.52 99.38 99.32 96.68 4 98.02 98.76 107.31 114.17 114 5 Table3: Cluster File Proposed Work: 1. Take 5 different dates Reference and Unknown cluster images. 2. Calculate NDVI images for all 5 images using algorithm 1 as shown above. 3. Get the Unknown interested regions from the image and collect the NDVI values into 1 file. 4. Normalize NDVI values of -1 to 1 into 0 to 200 by using formulae: ndvi_new = ndvi_old x 100 + 100 5. Make the Reference file and Unknown cluster file as shown above in Table 2 and Table 3. 6. Apply Equation [1] given above for these 2 files and get the class label. 7. Get the output as shown in Table4. It will contain the class in which unknown class is classified. IV. IMPLEMENTATION To calculate NDVI values, we can use GDAL library. GDAL is one type of Translator library, generally used for raster Geospatial data format and which is open source. We will use Python language for programming and we can use Eclipse IDE. We can implement the functionality shown in Algorithm1 in Python after embedding GDAL library into it. After calculating NDVI values, we can use this NDVI data to apply Equation [1]. Here, we will use .Net technology with C# as programming language to implement Equation1. Fig. 4 shows the design of the implementation of algorithm. It will take input as Reference File and Cluster File and it will produce Output file which will contain classification details. 159.74 130.6 147.48 136.85 120.94 19 1.01 90.72 0 114.33 0 1 70.25 73.96 66.27 78.99 91.33 15 101.08 97.52 99.38 99.32 96.68 17 98.02 98.76 107.31 114.17 114 16 Table4: Output File After classification process when we can compare the resulted Reference and unknown cluster it can be shown as a graph. Figure 3: Analysis 90 92 94 96 98 100 102 104 106 108 Cluster Reference
  • 5. Ms. Neha Bhatt, Mr. IndrJeet Rajput, Mr. Vinitkumar Gupta / International Journal of Engineering Research and Applications (IJERA) ISSN: 2248-9622 www.ijera.com Vol. 3, Issue 3, May-Jun 2013, pp.174-179 178 | P a g e V. CONCLUSION From above implementation results, we can conclude that this algorithm is much faster compared to other approaches as it includes small mathematical calculation and it take O (n) time to compute the result. The „n‟ value depends upon number of clusters that needs to classify. VI. FUTURE WORK This algorithm can also used to enhance the perfection by including Standard deviation. Also it can‟t be used for needs where some dates are having more importance and need to give more preference to that particular date. In that case, we need to modify this algorithm to some point. This feature can also be implemented using Sum of Absolute Difference. In that case, we can get similar value to that of Sum of Squared Difference. ACKNOWLEDGMENT We would like to thank the School of Computer Science and Engineering, GTU, for giving us such an opportunity to carry out this research work and also for providing us the requisite resources and infrastructure for carrying out the research. REFERENCES [1] A. Murni, A.K. Jain, and J. Rais.An Integrated Multisensor Image Classification Scheme for Landcover Mapping.In Proc. 2nd Asian Conference onComputer Vzsion, pages 111-92 - 111-96, December 1995. [2] A.H. Schistad Solberg, T. T a t , and A.K. Jain. A Markov Random Field Model for Classification of Multisource Satellite Imagery.IEEE Transactionson Geoscience and Remote Sensing, 34(1):100-113, 1996. [3] R. Loizzo, G. SylosLabini, M. Pappalepore, P. Pieri, G. Pasquariello, and M. Antoninetti.Multitemporal and Multisensor Signatures Evaluation for LithologicClassification. In Proc. International Geoscience and Remote Sensing Symposium, pages 2209-221 1,1995. [4] Y.T. Zhou. Multi-sensor image fusion. In Proc.12th Int. Conference on Pattern Recognition, Jerusalem, pages 193-197, October 1994. [5] J.L. Lee, R.C. Weger, S.K. Sengupta, and R.M. Welch. A Neural Network Approach to Cloud Classification.IEEE Transactions on Geoscience and RemoteSensing, 28(5):846- 855, September 1990. [6] A.H. Schistad and A.K. Jain.Texture analysis in the presence of speckle noise. In Proc. International Geoscience and Remote Sensing Symposium, pages884-886, May 1992 [7] A. Murni, N. Darwis, M. Mastur, and D. Hardianto.A texture classification experiment for SAR radar images. In Pattern Recognition in Practice IV,E.S. Gelsema and L.N. Kana1 (eds), North Holland, pages 213-225, 1994 [8] D.R. Peddle and S.E. Franklin. Image Texture Processing and Data Integration for Surface Pattern Discrimination.Photogrammetric Engineering and RemoteSensing, 57(4):413- 420, April 1991. [9] G. Lohmann. Co-occurrence-based Analysis and Synthesis of Textures. In Proc.12th Int. Conference on Pattern Recognition, Jerusalem, pages 449-453,0ct.ober 1994. [10] K.A. Soofi, R.S.U.S mith, and R. Siregar.A Planimetrically Accurate SPOT Image Mosaic of Buton Island, Sulawesi, Indonesia.PhotogrammetricEngineering and Remote Sensing, 57(9):1217-1220, September 1991. [11] R.Y. Wong. Sensor transformations.IEEE Transactions on Systems, Man, and Cybernetics, SMC- 7(12):836-841, December 1977 [12] P. R. Bajgiran, Y. Shimizu, F. Hosoi, and K. Omasa, “MODIS vegetation and water indices for drought assessment in semi-arid ecosystems of Iran,” Journal of Agricultural Meteorology, vol. 65, pp. 349-355, 2009 [13] A. R. Huete, and G. Ponce, “Satellite observed shifts in seasonality and vegetation – rainfall relationships in the southwest USA,” International Archives of the Photogrammetry, Remote Sensing and Spatial Information Science, vol. 38, pp. 775-777, 2010. [14] D. Song, P. Guo, and H. Sheng, “Spatial distribution pattern of MODISNDVI and correlation between NDVI and meteorology factors in Shandong province in China,” Piers Online, vol. 4, pp 191-196, 2008. [15] A. Yuhas, and L. A. Scuderi, “MODIS- derived NDVI characterization of drought-
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