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International Research Journal of Engineering and Technology (IRJET) e-ISSN: 2395-0056
Volume: 05 Issue: 04 | Apr42018 www.irjet.net p-ISSN: 2395-0072
© 2018, IRJET | Impact Factor value: 6.171 | ISO 9001:2008 Certified Journal | Page 784
CHANGE DETECTION AND PREDICTION OF LAND USE AND LAND COVER
Ritesh Midha1, Nisha Yadav2, Nishant kumar3, Tej Kumar4
1,2,3,4 B.Tech students, Dept. of Information Technology, IMS Engineering College, Ghaziabad, India
---------------------------------------------------------------------***---------------------------------------------------------------------
ABSTRACT: In remote sensing application, achangemay be
considered to as an alteration of the surface components.
Change detection is used in Forest or
vegetation, landscape and urban change. The process of
identifying differences in the state of anobjectorphenomenon
by observing it at different times. It is useful in many
applications such as land use changes, habitat fragmentation,
rate of deforestation, coastal change, urban sprawl and other
cumulative changes. It involve the application of multi
temporal datasets to quantatively analyze the temporal
effects. Therefore, we have used RS and GIS to study land use
land cover Samastipur district, Samastipur isoneofthethirty-
eight districts of Bihar. Samastipur is a district in Bihar which
is spread over an area of 2904 sq. kms. The people of
Samastipur mainly speak Hindi. According to the2011census,
Population Density in the District is 1465 per sq.km. and the
total population is 4.25 million. The district comprises of 4
sub-divisions, and 20 Blocks. ThelatitudeofSamastipur, Bihar,
India is 25.862968, and the longitude is 85.781029.
Samastipur, Bihar, India is located at India country in the
Cities place category with the gps coordinates of 25°
51’46.6848”N and 85° 46’51.7044”E.
Keywords: GIS, Remote Sensing, LULC, Google Mapper,
Google Earth
1. INTRODUCTION
Land cover changes are driven by natural forces or by
human land uses. Thus, it involves both the natural and the
human dimensions. Land cover affects land use. Locally, the
land cover changes due to environment or climatic factors
determine the vulnerability of people to climatic
perturbations and thus affect the decisions on land use by
people.
1.1 Land Use
Land use is commonly defined as a series of operations on
land, carried out by humans, with the intention to obtain
products and benefits through using land resources. Land
use and land cover have same fundamental difference. Land
use refers to the purpose the land serves, for example-
Recreation, wildlife habitat or agriculture, it does not
describe the surface cover on the ground.
1.2 Land Cover
Land cover is commonly defined as the vegetation (natural
or planted) or man –made constructions (buildings etc.)
which occur on the Earth surface. Water, ice, bare rock, sand
and similar surfaces also count as land cover. Land cover
refers to the surface cover on the ground, whether
vegetation, urban infrastructure, water, bare soil or other, it
does not describe the use of land, and the use of land may be
different for lands with some cover type.
1.3 Change Detection
Change detection for GIS is a process that measures how the
attribute of a particular area have changed between two or
more-time periods. Change detection often involves
comparing aerial photographs or satellite imagery of the
area taken at different times. Change detection has been
widely used to assess shifting cultivation, deforestation,
urban growth, impact of natural disasters like tsunamis,
earthquakes land use and land cover changes etc.
“Change detection is the process of identifying differencesin
the state of an object or phenomenon by observing it at
different times”. Changes in land cover by land use do not
necessarily imply degradation of the land. However due to a
shift in land use patterns, land cover changes that affects
biodiversity, water and other processes that come together
to affect climate and biosphere.
Remote sensing is the science and art of obtaining
information about an object, area, phenomenon through the
analysis of data acquired by a device that is not in contact
with object, area, and phenomenon under investigation.
2. STUDY AREA
2.1 Introduction
Our project study area is Samastipur district. Samastipur is
one of the thirty-eight districts of Bihar. Samastipur is a
district in Bihar which is spread over an area of 2904 sq.
kms. Samastipur is bounded on the north by the Bagmati
River which separates it from Darbhanga district. On the
west it is bordered by Vaishali and some partofMuzaffarpur
district, on the south by the Ganges, while on its east it has
Begusarai and some part of Khagaria district. The district
headquarters is located at Samastipur.
2.2 Location
The latitude of Samastipur, Bihar, India is 25.862968, and
the longitude is 85.781029. Samastipur, Bihar, India is
located at India country in the Cities place category with the
GPS coordinates of 25° 51’46.6848”N and 85° 46’51.7044”E.
International Research Journal of Engineering and Technology (IRJET) e-ISSN: 2395-0056
Volume: 05 Issue: 04 | Apr42018 www.irjet.net p-ISSN: 2395-0072
© 2018, IRJET | Impact Factor value: 6.171 | ISO 9001:2008 Certified Journal | Page 785
Figure-1: Samastipur map
2.3 Climate and Temperature
The climate is warm and temperate in Samastipur.Inwinter,
there is much less rainfall in Samastipur than in summer.
The Köppen-GeigerclimateclassificationisCwa.Theaverage
annual temperature is 25.5 °C in Samastipur. The average
annual rainfall is 1097 mm.
2.4 Population
Samastipur is a Nagar Parishad + Outgrowth city situated in
Samastipur block of Samastipur district.The Samastipur city
is divided into 28 wards for which elections are held every 5
years. As per the Population Census 2011, there are total
13,135 families residing in the Samastipur city. The total
population of Samastipur is 67,925 out of which 35,718 are
males and 32,207 are females thus the Average Sex Ratio of
Samastipur is 902.
The population of Children of age 0-6 years in Samastipur
city is 8683 which is 13% of the total population. There are
4591 male children and 4092 female children between the
ages 0-6 years. Thus as per the Census 2011 the Child Sex
Ratio of Samastipur is 891 which is less than Average Sex
Ratio (902).
2.5 Rivers
Samastipur is traversed by a number of rivers including
Budhi Gandak, Baya, Kosi, Kamla, Kareh and Jhamwari and
Balan, which are both the offshoots of Burhi Gandak. The
Ganges also skirts the district on the south.
2.6. Geography of Samastipur
Samastipur district occupies an area of 2,904 square
kilometers (1,121 sq. mi), [2] comparatively equivalent to
Indonesia's Muna Island.[3] Samastipur is bounded on the
north by the Bagmati River which separates it from
Darbhanga district. On the west it is bordered by Vaishali
and some part of Muzaffarpur district, on the south by the
Ganges, while on its east it has Begusarai and some part of
Khagaria district. The district headquarters is located at
Samastipur.
2.7 Agriculture of Samastipur
Samastipur is rich in agriculture, because of its fertile plain.
Tobacco, maize, rice and wheat are the main crops. Leechi
and mango fruits are grown in abundance. There is a jute
mill in Samastipur at Muktapur Village. This is very famous
jute mill (Rameshwar Jute Mill), employing around 5000
people. Shekhopur is one of the best agricultural villagesand
it also has famous temple, Bhagwatisthan at Manipur.
Samastipur has many a sugar mills which make it
Samastipur is major producer of potatoes. There are more
than 20 cold storages in the district, all storing potatoes and
total capacity is 650000 quintals.
Figure-2: Temperature graph Samastipur
3. MATERIAL AND METHODOLOGY
The satellite data used in the present study includes the
imagery of LANDSAT-5 “TM” AndLANDSAT-8“OLI”&“TIRS”
sensor. Landsat 5 imagery is of February2011andLandsat8
is of February 2017 with resolution of 30m nominal,
panchromatic resolution is 15m. Map projection used is
“UTM” datum used is “WGS84” and UTM zone is 45.
3.1 Software Used
In this study ERDAS IMAGINE is a remote sensing
application with raster graphics editor abilities designed by
ERDAS or geospatial. ERDAS IMAGINE is aimed primarily at
geospatial raster data processing and allows the user to
prepare, display and enhance digital image for mapping use
in GIS or software.
International Research Journal of Engineering and Technology (IRJET) e-ISSN: 2395-0056
Volume: 05 Issue: 04 | Apr42018 www.irjet.net p-ISSN: 2395-0072
© 2018, IRJET | Impact Factor value: 6.171 | ISO 9001:2008 Certified Journal | Page 786
3.2 Data acquisition
This step is dividing into two parts, in which first we have to
download vector file (.shp)formatofthestudyarea.Thenwe
have to download the satellite imagery of the study area
from internet. In this study, we hadtakensatelliteimageryof
Landsat 5 & 8 of year 2011 and 2017. We used “TM” and
“OLI” and “TIRS” sensors respectively.
Satellite Landsat 5 Landsat 8
Sensor’s TM OLI, TIRS
Date February, 2011 February, 2017
Data category NOMINAL NOMINAL
Data type “L1T” “L1T”
Output format GeoTiff GeoTiff
WRS Path 140 140
WRS Row 42 42
Table-1: Sensor’s Details
Operational Land Imager (OLI) it will measure in the
visible, near infrared andshort-waveinfrared portionsof the
spectrum. Its images will have 15 meter panchromatic and
30-meter multi-spectral spatial resolution.
Table-2: OLI
Thematic Mapper (TM) is an advanced, multispectral
scanning, Earth resources sensor designed toachievehigher
image resolution, shaper spectral separation, improved
geometric fidelity and grater radiometric accuracy and
resolution than the MSS sensor. TM data are sensed in seven
spectral bands simultaneously. Band 6 senses thermal
infrared radiation.
Thermal infrared sensor (TIRS) the specification requires
TIRS to collect image data for two thermal infrared spectral
bands with a spatial resolution of 120m across a 185-km
swath from the nominal 705 km Landsat altitude.
Layer Stack, in this part, we have to stack the different
bands of the imagery into a single file (.img) as the Data we
have downloaded present in gz. Format and in this zipped
file each band is present separately. For best outcome, it is
necessary to stack all 7 bands of Landsat5 and all 11 bands
of Landsat8 respectively.
Overlap, in this step, we had to first open the satellite
imagery, then open the shape file on the imagery. If itdid not
work then you have to change the projection of the imagery
or the shape file.
Subset - Subsetting refers to breaking out a portion of a
lager file into one or more smaller file. Often image files
contain areas much larger much larger than a particular
study area. In these cases, it is helpful to reduce the size of
the image file to include only the area of interest (AOL). This
not only eliminates the extraneous data in the file, but it
speeds up processing due to the smaller amount of data to
process. This can be important whendealingwithmultiband
data. In this step, we have to subset the shape file which is
overlapped on the satellite imagery.
Image Classification - Multispectral classification is the
process of sorting pixels into a finite number of individual
classes, or categories of data, based on their data file values.
If a pixel satisfies a certain set of criteria, the pixel is
assigned to the class that corresponds to that criteria. This
process is also referred to as image segmentation.
Depending on the type of information you want to extract
from the origin data, classes may be associated with known
features on the ground or may simply represent areas that
look different to the computer. An example of a classified
image is a land cover map, showing vegetation, bare land,
pasture, urban and so forth. In this study, we are using
supervised image classification maps, one common
application of remotely-sensed images to rangeland
management is the creation of maps, vegetation type, or
other discrete classes by remote sensing software. In
supervised classification, the image processing software is
guided by the user to specify the land cover classes of
interest.
4. RESULT
We have used supervised image classification with
maximum likelihood algorithm,forclassifyingtheimageryof
Samastipur Bihar for years 2011 and 2017. For computing
accuracy assessment, we have used the KHAT statistics
formula to compute the overall accuracy (OA), Producer’s
accuracy (PA) and User accuracy (UA). The study uses
Landsat time series images for showing land use and land
cover change over the period of time in Samastipur Bihar.
The results can be shown in the following tables.
Landsat 5 Landsat 8
Launch date March 1,1984 February 11,2013
Vehicle Delta 3920 Atlas- V rocket
Launched by NASA NASA
Site Vandenberg Air
Force Base
California
Vandenberg Air
Force Base
California
Sensor “TM” “OLI”, “TIRS”
Resolution 30 m. 30m.
International Research Journal of Engineering and Technology (IRJET) e-ISSN: 2395-0056
Volume: 05 Issue: 04 | Apr42018 www.irjet.net p-ISSN: 2395-0072
© 2018, IRJET | Impact Factor value: 6.171 | ISO 9001:2008 Certified Journal | Page 787
CLASS
Area(sq.km)
2011
Area(sq.km)
2017
Overall
Change
in (sq.
km)
OPEN SPACE 185.2 138.254 46.946
SETTLEMENT 1131.25 1272.1 140.85
AGRICULTURE 902.1 872.581 29.519
FOREST 640.38 580.95 59.43
WATERBODY 45.8 40.32 5.48
Total Area 2904 2904
Table-3: Land use Land cover mapping
The table-3 represents the area of each land use land cover
category of three different years.
Table-4: representing the producer’s accuracy, overall
accuracy, user’s accuracy 2011
During the period from 2011 to 2017 the area of settlement,
has increased by 140.85 square kilometer respectively. The
other four feature class namely water body, forest,
agriculture & water body cover of the area has also
decreased in past 6 years.
Figure-3: The land use and land cover map of year 2011S
Figure-4: Land Use Land Cover map 2017 in Area (sq.km)
Table-5: representing the (PA), (UA), and Overall
accuracy 2017.
5. CONCLUSION
The Samastipur district was a chosen as a study area to
monitor land use/land cover dynamics over a period of 6
years. During 2011 to 2017. The study area hasbeendivided
into five categories such as Settlement, Forest, Agriculture,
Water body and Open Space. For remotesensingpropose we
take the help of ERDAS imagine software 2011 softwareand
for GIS purpose we took help of Google earth and Arc map
10.1 software. We have used supervised imageclassification
with Parallelpiped algorithm, for classifying the imagery of
Samastipur Bihar for years 2011 and 2017. For computing
accuracy assessment, we have used the KHAT statistics
formula to compute the overall accuracy (OA), Producer’s
accuracy (PA) and User accuracy (UA). The study uses
Landsat time series images for showing land use and land
cover change over the period of time in Samastipur Bihar.
During the period from 2011 to 2017 the area of settlement,
has increased by 140.85 square kilometer respectively. The
other four feature class namely water body, forest,
agriculture & water body cover of the area has also
decreased in past 6 years. The 2011 map showsthatthearea
was densely covered by agriculture area followed by forest
area, settlement can be seen in near the river bodies and
other areas of the map. The area of water body has lowest
area in 2011 (45.8 sq.km). Land use land cover map of 2017
shows a significant change in area of settlement,agriculture,
International Research Journal of Engineering and Technology (IRJET) e-ISSN: 2395-0056
Volume: 05 Issue: 04 | Apr42018 www.irjet.net p-ISSN: 2395-0072
© 2018, IRJET | Impact Factor value: 6.171 | ISO 9001:2008 Certified Journal | Page 788
forest and other features, showed in the map. The area of
settlement feature is increased by 140.85 sq.km. over the
last 6 years. The area of agriculture is decreased by 29.519
sq. kms over the span of 6 years. Settlement has increased
from 1131.25 to 1272.1 sq. kms, a change of 140.85 sq. kms
is seen in 2011 to 2017. In the Highlight change map red
portion of the map showing decrease area, green portion of
the map showing increase area and whiteportionofthemap
showing no change in the area. Intheimagedifferencemap4
shows there is high change in image and -4 shows there is
low change in image. Error matrix showing user,producer &
overall accuracy as well as overall kappa statistics in the
classified imageries of the two years 2011 and 2017. Overall
output is come from the map, graph and pie diagram for the
year 2011 to 2017, there is decrease in forestry, open space,
agriculture, and water body in between 6 years but
settlements is gradually increasing the main factor behind
the growth of the urban areas in the district could be
development of industries and other amenities.
REFERENCES
[1] G. Sreenivasulu et al. “An Analysis on LandUse/Land
Cover Using Remote Sensing and GIS – A Case Study In
and Around Vempalli, Kadapa District, Andhra Pradesh,
India”, International Journal of Scientific and Research
Publications, Volume 3, Issue 5, May 2013 1 ISSN 2250-
3153.
[2] Madan Mohan, “Urban Land Cover Land Use Change
Detection In National Capital Region (NCR) Delhi: A
Study Of Faridabad District, India”
Http://www.Fig.Net/Pub/Cairo/Papers/Ts_24/Ts24_05
_ Mohan.Pdf.
[3] K.Anitha et al. “Land use Change Detection through
Image Processing and RemoteSensingApproach:ACase
Study of Palladam Taluk, Tamil Nadu”, International
Journal of Engineering Research and Applications
(IJERA) Vol. 2, Issue 4, July-August 2012, ISSN: 2248-
9622
[4] James R. Anderson, Ernest E. Hardy, John T. Roach,
And Richard E, A Land Use And Land Cover
Classification System For Use With RemoteSensorData,
Witmer Geological Survey Professional Paper 964.
[5] Dwivedi, R.S.; Sreenivas K.; Ramana, K.V. Land-
use/land-cover change analysis in partofEthiopia using
Landsat Thematic Mapper data. International Journal of
Remote Sensing 2005, 26 (7), 1285-1287.
[6] Chauthan, T.S., 2003, Geographical Information
system and Remote Sensing for sustainable
Development, Vol, 2, Universal Scientific publishers,
Jaipur.
[7] Sabins F.F., 1997, Remote Sensing Principles and
Interpretation W.H. Freeman and Company, Newyork.
[8] Rajan, K.S. and Shibasaki, R., (2000). A GIS Based
Integrated Land Use/Cover Change Model To Study
HumanLand Interactions. In: International Archives of
Photogrammetry and Remote Sensing, Vol. XXXIII Part
B7 (3), pp.12121219.
[9]Atasoy, M.; Karslı, F.; Bıyık, C.; Demir, O. Determining
Land Use Changes with Digital Photogrammetric
Techniques. Environmental Engineering Science 2006,
23 (4), 712-721.

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LULC Detection

  • 1. International Research Journal of Engineering and Technology (IRJET) e-ISSN: 2395-0056 Volume: 05 Issue: 04 | Apr42018 www.irjet.net p-ISSN: 2395-0072 © 2018, IRJET | Impact Factor value: 6.171 | ISO 9001:2008 Certified Journal | Page 784 CHANGE DETECTION AND PREDICTION OF LAND USE AND LAND COVER Ritesh Midha1, Nisha Yadav2, Nishant kumar3, Tej Kumar4 1,2,3,4 B.Tech students, Dept. of Information Technology, IMS Engineering College, Ghaziabad, India ---------------------------------------------------------------------***--------------------------------------------------------------------- ABSTRACT: In remote sensing application, achangemay be considered to as an alteration of the surface components. Change detection is used in Forest or vegetation, landscape and urban change. The process of identifying differences in the state of anobjectorphenomenon by observing it at different times. It is useful in many applications such as land use changes, habitat fragmentation, rate of deforestation, coastal change, urban sprawl and other cumulative changes. It involve the application of multi temporal datasets to quantatively analyze the temporal effects. Therefore, we have used RS and GIS to study land use land cover Samastipur district, Samastipur isoneofthethirty- eight districts of Bihar. Samastipur is a district in Bihar which is spread over an area of 2904 sq. kms. The people of Samastipur mainly speak Hindi. According to the2011census, Population Density in the District is 1465 per sq.km. and the total population is 4.25 million. The district comprises of 4 sub-divisions, and 20 Blocks. ThelatitudeofSamastipur, Bihar, India is 25.862968, and the longitude is 85.781029. Samastipur, Bihar, India is located at India country in the Cities place category with the gps coordinates of 25° 51’46.6848”N and 85° 46’51.7044”E. Keywords: GIS, Remote Sensing, LULC, Google Mapper, Google Earth 1. INTRODUCTION Land cover changes are driven by natural forces or by human land uses. Thus, it involves both the natural and the human dimensions. Land cover affects land use. Locally, the land cover changes due to environment or climatic factors determine the vulnerability of people to climatic perturbations and thus affect the decisions on land use by people. 1.1 Land Use Land use is commonly defined as a series of operations on land, carried out by humans, with the intention to obtain products and benefits through using land resources. Land use and land cover have same fundamental difference. Land use refers to the purpose the land serves, for example- Recreation, wildlife habitat or agriculture, it does not describe the surface cover on the ground. 1.2 Land Cover Land cover is commonly defined as the vegetation (natural or planted) or man –made constructions (buildings etc.) which occur on the Earth surface. Water, ice, bare rock, sand and similar surfaces also count as land cover. Land cover refers to the surface cover on the ground, whether vegetation, urban infrastructure, water, bare soil or other, it does not describe the use of land, and the use of land may be different for lands with some cover type. 1.3 Change Detection Change detection for GIS is a process that measures how the attribute of a particular area have changed between two or more-time periods. Change detection often involves comparing aerial photographs or satellite imagery of the area taken at different times. Change detection has been widely used to assess shifting cultivation, deforestation, urban growth, impact of natural disasters like tsunamis, earthquakes land use and land cover changes etc. “Change detection is the process of identifying differencesin the state of an object or phenomenon by observing it at different times”. Changes in land cover by land use do not necessarily imply degradation of the land. However due to a shift in land use patterns, land cover changes that affects biodiversity, water and other processes that come together to affect climate and biosphere. Remote sensing is the science and art of obtaining information about an object, area, phenomenon through the analysis of data acquired by a device that is not in contact with object, area, and phenomenon under investigation. 2. STUDY AREA 2.1 Introduction Our project study area is Samastipur district. Samastipur is one of the thirty-eight districts of Bihar. Samastipur is a district in Bihar which is spread over an area of 2904 sq. kms. Samastipur is bounded on the north by the Bagmati River which separates it from Darbhanga district. On the west it is bordered by Vaishali and some partofMuzaffarpur district, on the south by the Ganges, while on its east it has Begusarai and some part of Khagaria district. The district headquarters is located at Samastipur. 2.2 Location The latitude of Samastipur, Bihar, India is 25.862968, and the longitude is 85.781029. Samastipur, Bihar, India is located at India country in the Cities place category with the GPS coordinates of 25° 51’46.6848”N and 85° 46’51.7044”E.
  • 2. International Research Journal of Engineering and Technology (IRJET) e-ISSN: 2395-0056 Volume: 05 Issue: 04 | Apr42018 www.irjet.net p-ISSN: 2395-0072 © 2018, IRJET | Impact Factor value: 6.171 | ISO 9001:2008 Certified Journal | Page 785 Figure-1: Samastipur map 2.3 Climate and Temperature The climate is warm and temperate in Samastipur.Inwinter, there is much less rainfall in Samastipur than in summer. The Köppen-GeigerclimateclassificationisCwa.Theaverage annual temperature is 25.5 °C in Samastipur. The average annual rainfall is 1097 mm. 2.4 Population Samastipur is a Nagar Parishad + Outgrowth city situated in Samastipur block of Samastipur district.The Samastipur city is divided into 28 wards for which elections are held every 5 years. As per the Population Census 2011, there are total 13,135 families residing in the Samastipur city. The total population of Samastipur is 67,925 out of which 35,718 are males and 32,207 are females thus the Average Sex Ratio of Samastipur is 902. The population of Children of age 0-6 years in Samastipur city is 8683 which is 13% of the total population. There are 4591 male children and 4092 female children between the ages 0-6 years. Thus as per the Census 2011 the Child Sex Ratio of Samastipur is 891 which is less than Average Sex Ratio (902). 2.5 Rivers Samastipur is traversed by a number of rivers including Budhi Gandak, Baya, Kosi, Kamla, Kareh and Jhamwari and Balan, which are both the offshoots of Burhi Gandak. The Ganges also skirts the district on the south. 2.6. Geography of Samastipur Samastipur district occupies an area of 2,904 square kilometers (1,121 sq. mi), [2] comparatively equivalent to Indonesia's Muna Island.[3] Samastipur is bounded on the north by the Bagmati River which separates it from Darbhanga district. On the west it is bordered by Vaishali and some part of Muzaffarpur district, on the south by the Ganges, while on its east it has Begusarai and some part of Khagaria district. The district headquarters is located at Samastipur. 2.7 Agriculture of Samastipur Samastipur is rich in agriculture, because of its fertile plain. Tobacco, maize, rice and wheat are the main crops. Leechi and mango fruits are grown in abundance. There is a jute mill in Samastipur at Muktapur Village. This is very famous jute mill (Rameshwar Jute Mill), employing around 5000 people. Shekhopur is one of the best agricultural villagesand it also has famous temple, Bhagwatisthan at Manipur. Samastipur has many a sugar mills which make it Samastipur is major producer of potatoes. There are more than 20 cold storages in the district, all storing potatoes and total capacity is 650000 quintals. Figure-2: Temperature graph Samastipur 3. MATERIAL AND METHODOLOGY The satellite data used in the present study includes the imagery of LANDSAT-5 “TM” AndLANDSAT-8“OLI”&“TIRS” sensor. Landsat 5 imagery is of February2011andLandsat8 is of February 2017 with resolution of 30m nominal, panchromatic resolution is 15m. Map projection used is “UTM” datum used is “WGS84” and UTM zone is 45. 3.1 Software Used In this study ERDAS IMAGINE is a remote sensing application with raster graphics editor abilities designed by ERDAS or geospatial. ERDAS IMAGINE is aimed primarily at geospatial raster data processing and allows the user to prepare, display and enhance digital image for mapping use in GIS or software.
  • 3. International Research Journal of Engineering and Technology (IRJET) e-ISSN: 2395-0056 Volume: 05 Issue: 04 | Apr42018 www.irjet.net p-ISSN: 2395-0072 © 2018, IRJET | Impact Factor value: 6.171 | ISO 9001:2008 Certified Journal | Page 786 3.2 Data acquisition This step is dividing into two parts, in which first we have to download vector file (.shp)formatofthestudyarea.Thenwe have to download the satellite imagery of the study area from internet. In this study, we hadtakensatelliteimageryof Landsat 5 & 8 of year 2011 and 2017. We used “TM” and “OLI” and “TIRS” sensors respectively. Satellite Landsat 5 Landsat 8 Sensor’s TM OLI, TIRS Date February, 2011 February, 2017 Data category NOMINAL NOMINAL Data type “L1T” “L1T” Output format GeoTiff GeoTiff WRS Path 140 140 WRS Row 42 42 Table-1: Sensor’s Details Operational Land Imager (OLI) it will measure in the visible, near infrared andshort-waveinfrared portionsof the spectrum. Its images will have 15 meter panchromatic and 30-meter multi-spectral spatial resolution. Table-2: OLI Thematic Mapper (TM) is an advanced, multispectral scanning, Earth resources sensor designed toachievehigher image resolution, shaper spectral separation, improved geometric fidelity and grater radiometric accuracy and resolution than the MSS sensor. TM data are sensed in seven spectral bands simultaneously. Band 6 senses thermal infrared radiation. Thermal infrared sensor (TIRS) the specification requires TIRS to collect image data for two thermal infrared spectral bands with a spatial resolution of 120m across a 185-km swath from the nominal 705 km Landsat altitude. Layer Stack, in this part, we have to stack the different bands of the imagery into a single file (.img) as the Data we have downloaded present in gz. Format and in this zipped file each band is present separately. For best outcome, it is necessary to stack all 7 bands of Landsat5 and all 11 bands of Landsat8 respectively. Overlap, in this step, we had to first open the satellite imagery, then open the shape file on the imagery. If itdid not work then you have to change the projection of the imagery or the shape file. Subset - Subsetting refers to breaking out a portion of a lager file into one or more smaller file. Often image files contain areas much larger much larger than a particular study area. In these cases, it is helpful to reduce the size of the image file to include only the area of interest (AOL). This not only eliminates the extraneous data in the file, but it speeds up processing due to the smaller amount of data to process. This can be important whendealingwithmultiband data. In this step, we have to subset the shape file which is overlapped on the satellite imagery. Image Classification - Multispectral classification is the process of sorting pixels into a finite number of individual classes, or categories of data, based on their data file values. If a pixel satisfies a certain set of criteria, the pixel is assigned to the class that corresponds to that criteria. This process is also referred to as image segmentation. Depending on the type of information you want to extract from the origin data, classes may be associated with known features on the ground or may simply represent areas that look different to the computer. An example of a classified image is a land cover map, showing vegetation, bare land, pasture, urban and so forth. In this study, we are using supervised image classification maps, one common application of remotely-sensed images to rangeland management is the creation of maps, vegetation type, or other discrete classes by remote sensing software. In supervised classification, the image processing software is guided by the user to specify the land cover classes of interest. 4. RESULT We have used supervised image classification with maximum likelihood algorithm,forclassifyingtheimageryof Samastipur Bihar for years 2011 and 2017. For computing accuracy assessment, we have used the KHAT statistics formula to compute the overall accuracy (OA), Producer’s accuracy (PA) and User accuracy (UA). The study uses Landsat time series images for showing land use and land cover change over the period of time in Samastipur Bihar. The results can be shown in the following tables. Landsat 5 Landsat 8 Launch date March 1,1984 February 11,2013 Vehicle Delta 3920 Atlas- V rocket Launched by NASA NASA Site Vandenberg Air Force Base California Vandenberg Air Force Base California Sensor “TM” “OLI”, “TIRS” Resolution 30 m. 30m.
  • 4. International Research Journal of Engineering and Technology (IRJET) e-ISSN: 2395-0056 Volume: 05 Issue: 04 | Apr42018 www.irjet.net p-ISSN: 2395-0072 © 2018, IRJET | Impact Factor value: 6.171 | ISO 9001:2008 Certified Journal | Page 787 CLASS Area(sq.km) 2011 Area(sq.km) 2017 Overall Change in (sq. km) OPEN SPACE 185.2 138.254 46.946 SETTLEMENT 1131.25 1272.1 140.85 AGRICULTURE 902.1 872.581 29.519 FOREST 640.38 580.95 59.43 WATERBODY 45.8 40.32 5.48 Total Area 2904 2904 Table-3: Land use Land cover mapping The table-3 represents the area of each land use land cover category of three different years. Table-4: representing the producer’s accuracy, overall accuracy, user’s accuracy 2011 During the period from 2011 to 2017 the area of settlement, has increased by 140.85 square kilometer respectively. The other four feature class namely water body, forest, agriculture & water body cover of the area has also decreased in past 6 years. Figure-3: The land use and land cover map of year 2011S Figure-4: Land Use Land Cover map 2017 in Area (sq.km) Table-5: representing the (PA), (UA), and Overall accuracy 2017. 5. CONCLUSION The Samastipur district was a chosen as a study area to monitor land use/land cover dynamics over a period of 6 years. During 2011 to 2017. The study area hasbeendivided into five categories such as Settlement, Forest, Agriculture, Water body and Open Space. For remotesensingpropose we take the help of ERDAS imagine software 2011 softwareand for GIS purpose we took help of Google earth and Arc map 10.1 software. We have used supervised imageclassification with Parallelpiped algorithm, for classifying the imagery of Samastipur Bihar for years 2011 and 2017. For computing accuracy assessment, we have used the KHAT statistics formula to compute the overall accuracy (OA), Producer’s accuracy (PA) and User accuracy (UA). The study uses Landsat time series images for showing land use and land cover change over the period of time in Samastipur Bihar. During the period from 2011 to 2017 the area of settlement, has increased by 140.85 square kilometer respectively. The other four feature class namely water body, forest, agriculture & water body cover of the area has also decreased in past 6 years. The 2011 map showsthatthearea was densely covered by agriculture area followed by forest area, settlement can be seen in near the river bodies and other areas of the map. The area of water body has lowest area in 2011 (45.8 sq.km). Land use land cover map of 2017 shows a significant change in area of settlement,agriculture,
  • 5. International Research Journal of Engineering and Technology (IRJET) e-ISSN: 2395-0056 Volume: 05 Issue: 04 | Apr42018 www.irjet.net p-ISSN: 2395-0072 © 2018, IRJET | Impact Factor value: 6.171 | ISO 9001:2008 Certified Journal | Page 788 forest and other features, showed in the map. The area of settlement feature is increased by 140.85 sq.km. over the last 6 years. The area of agriculture is decreased by 29.519 sq. kms over the span of 6 years. Settlement has increased from 1131.25 to 1272.1 sq. kms, a change of 140.85 sq. kms is seen in 2011 to 2017. In the Highlight change map red portion of the map showing decrease area, green portion of the map showing increase area and whiteportionofthemap showing no change in the area. Intheimagedifferencemap4 shows there is high change in image and -4 shows there is low change in image. Error matrix showing user,producer & overall accuracy as well as overall kappa statistics in the classified imageries of the two years 2011 and 2017. Overall output is come from the map, graph and pie diagram for the year 2011 to 2017, there is decrease in forestry, open space, agriculture, and water body in between 6 years but settlements is gradually increasing the main factor behind the growth of the urban areas in the district could be development of industries and other amenities. REFERENCES [1] G. Sreenivasulu et al. “An Analysis on LandUse/Land Cover Using Remote Sensing and GIS – A Case Study In and Around Vempalli, Kadapa District, Andhra Pradesh, India”, International Journal of Scientific and Research Publications, Volume 3, Issue 5, May 2013 1 ISSN 2250- 3153. [2] Madan Mohan, “Urban Land Cover Land Use Change Detection In National Capital Region (NCR) Delhi: A Study Of Faridabad District, India” Http://www.Fig.Net/Pub/Cairo/Papers/Ts_24/Ts24_05 _ Mohan.Pdf. [3] K.Anitha et al. “Land use Change Detection through Image Processing and RemoteSensingApproach:ACase Study of Palladam Taluk, Tamil Nadu”, International Journal of Engineering Research and Applications (IJERA) Vol. 2, Issue 4, July-August 2012, ISSN: 2248- 9622 [4] James R. Anderson, Ernest E. Hardy, John T. Roach, And Richard E, A Land Use And Land Cover Classification System For Use With RemoteSensorData, Witmer Geological Survey Professional Paper 964. [5] Dwivedi, R.S.; Sreenivas K.; Ramana, K.V. Land- use/land-cover change analysis in partofEthiopia using Landsat Thematic Mapper data. International Journal of Remote Sensing 2005, 26 (7), 1285-1287. [6] Chauthan, T.S., 2003, Geographical Information system and Remote Sensing for sustainable Development, Vol, 2, Universal Scientific publishers, Jaipur. [7] Sabins F.F., 1997, Remote Sensing Principles and Interpretation W.H. Freeman and Company, Newyork. [8] Rajan, K.S. and Shibasaki, R., (2000). A GIS Based Integrated Land Use/Cover Change Model To Study HumanLand Interactions. In: International Archives of Photogrammetry and Remote Sensing, Vol. XXXIII Part B7 (3), pp.12121219. [9]Atasoy, M.; Karslı, F.; Bıyık, C.; Demir, O. Determining Land Use Changes with Digital Photogrammetric Techniques. Environmental Engineering Science 2006, 23 (4), 712-721.