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IOSR Journal of Applied Geology and Geophysics (IOSR-JAGG)
e-ISSN: 2321–0990, p-ISSN: 2321–0982.Volume 3, Issue 6 Ver. II (Nov. - Dec. 2015), PP 55-60
www.iosrjournals.org
DOI: 10.9790/0990-03625560 www.iosrjournals.org 55 | Page
Application of Remote Sensing Techniques for Change Detection
in Land Use/ Land Cover of Ratnagiri District, Maharashtra
Balu L. Rathod 1
, Jagdish B. Sapkale 2
1
Assistant Professor, Department of Geography, Kankavli College, Kankavli, District- Sindhudurg,
Maharashtra, India (Ph.D. Scholar, Department of Geography, Shivaji University, Kolhapur)
2
Assistant Professor, Department of Geography, Shivaji University, Kolhapur, Maharashtra, India.
Abstract: Remote sensing data and imageries have been used for the assessment and monitoring of land use
and land cover changes, so that available resources of any region may be used properly. In the coastal areas of
Maharashtra, catastrophic and human interventions are highly influencing on coastal resources. Now there is
an urgent need to use the sustainable resources by reducing the rate of degradation. The present study is an
attempt to analysis the change detection in the major aspects of land use and land cover in the Ratnagiri district
of Maharashtra. Satellite images of the years 1989, 1999 and 2009 have been obtained from Global Land Cover
Facility (GLCF) & NRSC and used for the analysis of periodic changes in LULC of Ratnagiri.
Keywords: LISS-III, LULC, GLCF, Change detection, Degradation,
I. Introduction
The Ratnagiri district covers 8,16,433 hectares of the total area of the district having nine tehsils
(fig 1). Most of the part is covered by forest with undulating landscape. Various resources are available in the
district, but needs proper management. Therefore remote sensing techniques for monitoring the natural
resources is the proper way that can also give the information about the vulnerable sites of degradation from
time to time.
In the past three decades, there has been a growing trend in the development of the change detection
techniques using remote sensing data. Remote Sensing (RS) and Geographical Information System (GIS) are
now providing new tools for ecosystem management. The data is collected by remote sensing enables the
synoptic analysis of earth system functions; also change at local, regional and global scale over times. Such data
also provides an important link between intensive, localized ecological research and regional, national and
international conservation and management of biological diversity (Wilkie and Finn, 1996 ; Lillesand et al.,
2008). Land use is defined as the use of land for economic purpose by human beings. The land use includes
agricultural land, built-up land, recreational area, wildlife management area etc. Land cover refers to the
physical characteristics of earth‟s surface, distribution of vegetation, water, soil and other physical features of
the land including those created solely by human activities, e.g. settlement. (Anderson, 1976).
Figure : 1 Tehsil wise Area of Ratnagiri district
Application of Remote Sensing Techniques for Change Detection in Land Use/ Land Cover…
DOI: 10.9790/0990-03625560 www.iosrjournals.org 56 | Page
Land use refers to the purpose of land reserves, for example, recreation, wildlife habitat or agriculture.
Land use applications involve both baseline mapping and subsequent monitoring, since timely information is
required to know the current quantity of land and the type of its usage and to identify the land use changes from
year to year. Satellite remote sensing data i.e. images and soft data is the most common data source for change
detection, quantification, and mapping of LULC patterns and variations can be easily detected due to its
repetitive data acquisition, digital format suitable for computer processing, and accurate georeferencing
procedures (Anderson, 1976; Chen, Vierling, & Deering, 2005; Jensen, 2005; ). Change detection is the process
of identifying differences in the state of an object or phenomenon by observing it at different times. Essentially,
it involves the ability to quantify temporal effects using multi-temporal data sets. One of the major applications
of remotely-sensed data obtained from Earth-orbiting satellites is change detection because of repetitive
coverage at short intervals and consistent image quality (Anderson, 1976). Amount of degradation can be easily
accessed using these advances tools and techniques ( Sapkale & Rathod, 2014; 2015).
II. Data And Methods
Land use and land cover classification through supervised classification methods by using LANDSAT,
TM , Satellite image of Ratnagiri Coastal Resource for the years 1989 has been performed/ done. LANDSAT,
ETM, Satellite image of Ratnagiri Coastal Resource 1999 and LISS-III Satellite image of Ratnagiri Coastal
Resource 2009 were also used to carry out change detection analysis. Satellite images of the years 1989, 1999
and 2009 have been obtained from Global Land Cover Facility (GLCF) & NRSC. The resolution was 30 meters
for Landsat data and 23.5 m. LISS III image. The Land Use/ Land Cover classification has been performed
through supervised classification method using Digital Image Processing software. Erdas Imagine and ArcGIS
software are powerful tools for extracting the land use and land cover layers from Ratnagiri Coastal Resource.
III. Discussions And Results
LAND USE / LAND COVER MAPPING AND CHANGE ANALYSIS: The land use and land cover
classes includes agricultural land, vegetation, built up area, water bodies and fallow land. It is the broad
classification of the land use and land cover of study area.
CROPPED AREA: The cropped land may be defined broadly as land that is used primarily for
production of food and fodder. Cropped land occupies sizeable area. Rice, Vegetables are the major crops in this
region. In the year 1989 the cropped land is covered by 7.21% of the total area under these categories. In 1999
about 11.65% of the total area is under cropped in this region. In 2009 about 13.47% of the total area is under
cropped in this region. In Ratnagiri district the cropped area has increased by 1.82% in 20 years from 1989 to
2009. There is a positive change in agricultural land in these 20 years (table no. 1 to 5).
BUILTUP AREA :The built-up land cover is reported from Ratnagiri district in the year of 1989 is
0.10%. The total area covered by built-up land in the years 1999 and 2009 is 0.59% and 2.46% respectively. It
can be observed that in these 20 years, from 1989 to 2009 the builtup area has increased by 1.87%. There is a
positive change in builtup land in these 20 years.
Table No. 1
LAND USE / LAND COVER CLASSIFICATION IMAGE-YEAR-1989
Sr. No Class Name Area in Hectare Area in Percentage%
1 Built-up 10623 0.10
2 Cropped 757809 7.21
3 Open land 2128305 20.26
4 Dense forest 339202 3.22
5 Sparse forest 6671676 63.52
6 Water body 218784 2.08
7 Barren land 375732 3.57
Total Area 10502131 100
Application of Remote Sensing Techniques for Change Detection in Land Use/ Land Cover…
DOI: 10.9790/0990-03625560 www.iosrjournals.org 57 | Page
Source:- Based on Global Land Cover Facility (GLCF)
Application of Remote Sensing Techniques for Change Detection in Land Use/ Land Cover…
DOI: 10.9790/0990-03625560 www.iosrjournals.org 58 | Page
Application of Remote Sensing Techniques for Change Detection in Land Use/ Land Cover…
DOI: 10.9790/0990-03625560 www.iosrjournals.org 59 | Page
OPEN LAND AREA : In the Ratnagiri district some area covered with open land. The open land refers
the land may be uncultivated and unused land. In the year of 1989, the open land has occupied 22.92% of total
area of region. From 1999 to 2009, it is 22.92% and 11.17% respectively. In Ratnagiri district the open land
area has decreased by -11.75% in 20 years from 1989 to 2009. There is a negative change in open land area in
these 20 years.
DENSE FOREST AREA : The area under forest includes the land classified as forest under any legal
enactment dealing with forest or administrated for forest, whether state-owned or private, and whether wooded
or maintained as potential forest land. The areas where crops are raised in the forests and grazing lands or areas
open for grazing within the forests are included under forest area (National Commission on Agriculture, 1976).
The present Ratnagiri district is located in coastal and hilly region with uneven topography covered by dense
vegetation. Most of the area is under dense forests.
Table No. 2
LAND USE / LAND COVER CLASSIFICATION IMAGE-YEAR-1999
Sr. No Class Name Area in Hectare Area in Percentage%
1 Builtup 59722 0.59
2 Cropped 1171164 11.65
3 Open land 2302773 22.92
4 Dense forest 826064 8.22
5 Sparse forest 5337999 53.13
6 Water body 159428 1.58
7 Barren land 188264 1.87
Total Area 10045414 100
Table No. 3
LAND USE / LAND COVER CLASSIFICATION IMAGE-YEAR-2009
Sr. No Class Name Area in Hectare Area in Percentage%
1 Builtup 237421 2.45
2 Cropped 1298500 13.44
3 Open land 1077218 11.15
4 Dense forest 601475 6.22
5 Sparse forest 6008559 62.20
6 Water body 125540 1.29
7 Barren land 310192 3.21
Total Area 9658905 100
Table No. 4
LAND USE/ LAND COVER CHANGE FROM 1989 TO 1999
Year-1989 Year-1999 Difference Change
(1989 to
1999)
Sr.
No
Class Name Area in
Hectare
Area in % Area in
Hectare
Area in % Area in
Hectare
Area in %
1 Builtup 10623 0.10 59722 0.59 49099 0.49
2 Cropped 757809 7.21 1171164 11.65 413355 4.44
3 Open land 2128305 20.26 2302773 22.92 174468 2.66
4 Dense forest 339202 3.22 826064 8.22 486862 5.00
5 Sparse forest 6671676 63.52 5337999 53.13 -1333677 -10.39
6 Water body 218784 2.08 159428 1.58 -59356 -0.5
7 Barren land 375732 3.57 188264 1.87 -187468 -1.7
Total Area 10502131 100 10045414 100
Application of Remote Sensing Techniques for Change Detection in Land Use/ Land Cover…
DOI: 10.9790/0990-03625560 www.iosrjournals.org 60 | Page
In 1989, the dense forest area cover was 3.22% of the total area in study region. In 1999 and 2009 the
area of Ratnagiri district under dense forest area cover was 8.22% and 6.23% respectively. It can be observed
that in these 20 years, almost -1.99% dense forest area cover has decreased in the study region. There is a
negative change in dense forest area in these 20 years.
SPARSE FOREST AREA: The present Ratnagiri district is located in coastal and hilly region with
uneven topography covered by sparse vegetation. Most of the area is under sparse forests. In 1989, the sparse
forests cover was 63.52% of the total area in the study region. In 1999 and 2009 the area of Ratnagiri district
under sparse forests cover was 53.13% and 62.13% respectively. It can be observed that in these 20 years,
almost 9.00% sparse forests area cover has increased in the study region. There is a positive change in sparse
forests area cover in these 20 years.
WATER BODY: Water bodied includes estuary, wells, lakes, ponds, river and stream. The percentage
of water bodies in the region is 2.08% of the total area in the year 1989. The total area covered by water bodies
in the years 1999 and 2009 was 1.58% and 1.50% respectively. The area under water bodies in Ratnagiti district
has decreased increased from 1989 to 2009 by -0.08%. There is a negative change in dense forest area in these
20 years.
BARREN LAND: The Barren land cover is reported from Ratnagiri district in the year of 1989 is
3.57%. The total area covered by barren land in the years 1999 and 2009 is 1.87% and 3.01% respectively. In
Ratnagiri district the barren land area has increased by 1.14% in 20 years from 1989 to 2009. There is a positive
change in barren land area in these 20 years.
IV. Conclusion
Updated information about land use and land cover of the present study area will help to overcome the
problems in connection with the agricultural systems, forest cover, various infrastructures etc. Therefore it has
suggested that, Remote sensing, GIS, GPS techniques should be used continuously for the management and
development in the study area.
References
[1] Anderson, James Richard. A land use and land cover classification system for use with remote sensor data. Vol. 964. US
Government Printing Office, 1976.
[2] Chen, X., Vierling, L., & Deering, D., A simple and effective radiometric correction method to improve landscape change detection
across sensors and across time. Remote Sensing of Environment, 98(1), 63-79, 2005.
[3] Jensen, J. R. (2005). Introductorydigitalimageprocessing:Aremotesensingperspective (3rd Edn). Upper SaddleRiver, NJ:Prentice-Hall,2005.
[4] Lillesand, M.T., KIefer, W. R. andChipman, N, J. (2008). :Remotesensingand image interpretation (6th ed). JohnWileyand Sons, Inc, NewYork..
[5] Rathod, B.L, (2015) , “ Coastal Resource Management Using Remote Sensing and GIS Techniques: A Case Study of Ratnagiri
District, Maharashtra, (2015), Unpublished Ph.D. Dissertation.
[6] Rathod, B. L., Sapkale, J.B., Status ofAgriculture in Coastal Villages of Ratnagiri, Maharashtra.,. ,International Journal of Scientific and Engineering
Research, (IJSER), 6(9),1556-15592015.
[7] Sapkale, J.B., Rathod, B. L., “Kharlands-An Agrarian Disaster in CoastalAreas of Southern Ratnagiri, Maharashtra:AStudy Using Remote Sensing
and GIS”, InternationalRefereedJournalofEngineeringand Science (IRJES),3(6),71-78, 2014.
[8] Socio-economic Review and Statistical Abstract Ratnagiri District 1980-2013.
[9] Wilkie, D.S. and Finn, J.T. : „Remote Sensing Imagery for Natural Resources Monitoring‟. Columbia University Press, New York.,
P.P.- 295. 1996.
Table No. 5
LAND USE/ LAND COVER CHANGE FROM 1999 TO 2009
Year-1999 Year-2009 Difference Change (1999
to 2009)
Sr.
No
Class Name Area in
Hectare
Area in % Area in
Hectare
Area in
%
Area in
Hectare
Area in %
1 Builtup 59722 0.59 237421 2.46 177699 1.87
2 Cropped 1171164 11.65 1298500 13.47 127336 1.82
3 Open land 2302773 22.92 1077218 11.17 -1225555 -11.75
4 Dense forest 826064 8.22 601475 6.23 -224589 -1.99
5 Sparse forest 5337999 53.13 5989325 62.13 651326 9.00
6 Water body 159428 1.58 144776 1.50 -14652 -0.08
7 Barren land 188264 1.87 290864 3.01 102600 1.14
Total Area 10045414 100 9639579 100

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Application of Remote Sensing Techniques for Change Detection in Land Use/ Land Cover of Ratnagiri District, Maharashtra

  • 1. IOSR Journal of Applied Geology and Geophysics (IOSR-JAGG) e-ISSN: 2321–0990, p-ISSN: 2321–0982.Volume 3, Issue 6 Ver. II (Nov. - Dec. 2015), PP 55-60 www.iosrjournals.org DOI: 10.9790/0990-03625560 www.iosrjournals.org 55 | Page Application of Remote Sensing Techniques for Change Detection in Land Use/ Land Cover of Ratnagiri District, Maharashtra Balu L. Rathod 1 , Jagdish B. Sapkale 2 1 Assistant Professor, Department of Geography, Kankavli College, Kankavli, District- Sindhudurg, Maharashtra, India (Ph.D. Scholar, Department of Geography, Shivaji University, Kolhapur) 2 Assistant Professor, Department of Geography, Shivaji University, Kolhapur, Maharashtra, India. Abstract: Remote sensing data and imageries have been used for the assessment and monitoring of land use and land cover changes, so that available resources of any region may be used properly. In the coastal areas of Maharashtra, catastrophic and human interventions are highly influencing on coastal resources. Now there is an urgent need to use the sustainable resources by reducing the rate of degradation. The present study is an attempt to analysis the change detection in the major aspects of land use and land cover in the Ratnagiri district of Maharashtra. Satellite images of the years 1989, 1999 and 2009 have been obtained from Global Land Cover Facility (GLCF) & NRSC and used for the analysis of periodic changes in LULC of Ratnagiri. Keywords: LISS-III, LULC, GLCF, Change detection, Degradation, I. Introduction The Ratnagiri district covers 8,16,433 hectares of the total area of the district having nine tehsils (fig 1). Most of the part is covered by forest with undulating landscape. Various resources are available in the district, but needs proper management. Therefore remote sensing techniques for monitoring the natural resources is the proper way that can also give the information about the vulnerable sites of degradation from time to time. In the past three decades, there has been a growing trend in the development of the change detection techniques using remote sensing data. Remote Sensing (RS) and Geographical Information System (GIS) are now providing new tools for ecosystem management. The data is collected by remote sensing enables the synoptic analysis of earth system functions; also change at local, regional and global scale over times. Such data also provides an important link between intensive, localized ecological research and regional, national and international conservation and management of biological diversity (Wilkie and Finn, 1996 ; Lillesand et al., 2008). Land use is defined as the use of land for economic purpose by human beings. The land use includes agricultural land, built-up land, recreational area, wildlife management area etc. Land cover refers to the physical characteristics of earth‟s surface, distribution of vegetation, water, soil and other physical features of the land including those created solely by human activities, e.g. settlement. (Anderson, 1976). Figure : 1 Tehsil wise Area of Ratnagiri district
  • 2. Application of Remote Sensing Techniques for Change Detection in Land Use/ Land Cover… DOI: 10.9790/0990-03625560 www.iosrjournals.org 56 | Page Land use refers to the purpose of land reserves, for example, recreation, wildlife habitat or agriculture. Land use applications involve both baseline mapping and subsequent monitoring, since timely information is required to know the current quantity of land and the type of its usage and to identify the land use changes from year to year. Satellite remote sensing data i.e. images and soft data is the most common data source for change detection, quantification, and mapping of LULC patterns and variations can be easily detected due to its repetitive data acquisition, digital format suitable for computer processing, and accurate georeferencing procedures (Anderson, 1976; Chen, Vierling, & Deering, 2005; Jensen, 2005; ). Change detection is the process of identifying differences in the state of an object or phenomenon by observing it at different times. Essentially, it involves the ability to quantify temporal effects using multi-temporal data sets. One of the major applications of remotely-sensed data obtained from Earth-orbiting satellites is change detection because of repetitive coverage at short intervals and consistent image quality (Anderson, 1976). Amount of degradation can be easily accessed using these advances tools and techniques ( Sapkale & Rathod, 2014; 2015). II. Data And Methods Land use and land cover classification through supervised classification methods by using LANDSAT, TM , Satellite image of Ratnagiri Coastal Resource for the years 1989 has been performed/ done. LANDSAT, ETM, Satellite image of Ratnagiri Coastal Resource 1999 and LISS-III Satellite image of Ratnagiri Coastal Resource 2009 were also used to carry out change detection analysis. Satellite images of the years 1989, 1999 and 2009 have been obtained from Global Land Cover Facility (GLCF) & NRSC. The resolution was 30 meters for Landsat data and 23.5 m. LISS III image. The Land Use/ Land Cover classification has been performed through supervised classification method using Digital Image Processing software. Erdas Imagine and ArcGIS software are powerful tools for extracting the land use and land cover layers from Ratnagiri Coastal Resource. III. Discussions And Results LAND USE / LAND COVER MAPPING AND CHANGE ANALYSIS: The land use and land cover classes includes agricultural land, vegetation, built up area, water bodies and fallow land. It is the broad classification of the land use and land cover of study area. CROPPED AREA: The cropped land may be defined broadly as land that is used primarily for production of food and fodder. Cropped land occupies sizeable area. Rice, Vegetables are the major crops in this region. In the year 1989 the cropped land is covered by 7.21% of the total area under these categories. In 1999 about 11.65% of the total area is under cropped in this region. In 2009 about 13.47% of the total area is under cropped in this region. In Ratnagiri district the cropped area has increased by 1.82% in 20 years from 1989 to 2009. There is a positive change in agricultural land in these 20 years (table no. 1 to 5). BUILTUP AREA :The built-up land cover is reported from Ratnagiri district in the year of 1989 is 0.10%. The total area covered by built-up land in the years 1999 and 2009 is 0.59% and 2.46% respectively. It can be observed that in these 20 years, from 1989 to 2009 the builtup area has increased by 1.87%. There is a positive change in builtup land in these 20 years. Table No. 1 LAND USE / LAND COVER CLASSIFICATION IMAGE-YEAR-1989 Sr. No Class Name Area in Hectare Area in Percentage% 1 Built-up 10623 0.10 2 Cropped 757809 7.21 3 Open land 2128305 20.26 4 Dense forest 339202 3.22 5 Sparse forest 6671676 63.52 6 Water body 218784 2.08 7 Barren land 375732 3.57 Total Area 10502131 100
  • 3. Application of Remote Sensing Techniques for Change Detection in Land Use/ Land Cover… DOI: 10.9790/0990-03625560 www.iosrjournals.org 57 | Page Source:- Based on Global Land Cover Facility (GLCF)
  • 4. Application of Remote Sensing Techniques for Change Detection in Land Use/ Land Cover… DOI: 10.9790/0990-03625560 www.iosrjournals.org 58 | Page
  • 5. Application of Remote Sensing Techniques for Change Detection in Land Use/ Land Cover… DOI: 10.9790/0990-03625560 www.iosrjournals.org 59 | Page OPEN LAND AREA : In the Ratnagiri district some area covered with open land. The open land refers the land may be uncultivated and unused land. In the year of 1989, the open land has occupied 22.92% of total area of region. From 1999 to 2009, it is 22.92% and 11.17% respectively. In Ratnagiri district the open land area has decreased by -11.75% in 20 years from 1989 to 2009. There is a negative change in open land area in these 20 years. DENSE FOREST AREA : The area under forest includes the land classified as forest under any legal enactment dealing with forest or administrated for forest, whether state-owned or private, and whether wooded or maintained as potential forest land. The areas where crops are raised in the forests and grazing lands or areas open for grazing within the forests are included under forest area (National Commission on Agriculture, 1976). The present Ratnagiri district is located in coastal and hilly region with uneven topography covered by dense vegetation. Most of the area is under dense forests. Table No. 2 LAND USE / LAND COVER CLASSIFICATION IMAGE-YEAR-1999 Sr. No Class Name Area in Hectare Area in Percentage% 1 Builtup 59722 0.59 2 Cropped 1171164 11.65 3 Open land 2302773 22.92 4 Dense forest 826064 8.22 5 Sparse forest 5337999 53.13 6 Water body 159428 1.58 7 Barren land 188264 1.87 Total Area 10045414 100 Table No. 3 LAND USE / LAND COVER CLASSIFICATION IMAGE-YEAR-2009 Sr. No Class Name Area in Hectare Area in Percentage% 1 Builtup 237421 2.45 2 Cropped 1298500 13.44 3 Open land 1077218 11.15 4 Dense forest 601475 6.22 5 Sparse forest 6008559 62.20 6 Water body 125540 1.29 7 Barren land 310192 3.21 Total Area 9658905 100 Table No. 4 LAND USE/ LAND COVER CHANGE FROM 1989 TO 1999 Year-1989 Year-1999 Difference Change (1989 to 1999) Sr. No Class Name Area in Hectare Area in % Area in Hectare Area in % Area in Hectare Area in % 1 Builtup 10623 0.10 59722 0.59 49099 0.49 2 Cropped 757809 7.21 1171164 11.65 413355 4.44 3 Open land 2128305 20.26 2302773 22.92 174468 2.66 4 Dense forest 339202 3.22 826064 8.22 486862 5.00 5 Sparse forest 6671676 63.52 5337999 53.13 -1333677 -10.39 6 Water body 218784 2.08 159428 1.58 -59356 -0.5 7 Barren land 375732 3.57 188264 1.87 -187468 -1.7 Total Area 10502131 100 10045414 100
  • 6. Application of Remote Sensing Techniques for Change Detection in Land Use/ Land Cover… DOI: 10.9790/0990-03625560 www.iosrjournals.org 60 | Page In 1989, the dense forest area cover was 3.22% of the total area in study region. In 1999 and 2009 the area of Ratnagiri district under dense forest area cover was 8.22% and 6.23% respectively. It can be observed that in these 20 years, almost -1.99% dense forest area cover has decreased in the study region. There is a negative change in dense forest area in these 20 years. SPARSE FOREST AREA: The present Ratnagiri district is located in coastal and hilly region with uneven topography covered by sparse vegetation. Most of the area is under sparse forests. In 1989, the sparse forests cover was 63.52% of the total area in the study region. In 1999 and 2009 the area of Ratnagiri district under sparse forests cover was 53.13% and 62.13% respectively. It can be observed that in these 20 years, almost 9.00% sparse forests area cover has increased in the study region. There is a positive change in sparse forests area cover in these 20 years. WATER BODY: Water bodied includes estuary, wells, lakes, ponds, river and stream. The percentage of water bodies in the region is 2.08% of the total area in the year 1989. The total area covered by water bodies in the years 1999 and 2009 was 1.58% and 1.50% respectively. The area under water bodies in Ratnagiti district has decreased increased from 1989 to 2009 by -0.08%. There is a negative change in dense forest area in these 20 years. BARREN LAND: The Barren land cover is reported from Ratnagiri district in the year of 1989 is 3.57%. The total area covered by barren land in the years 1999 and 2009 is 1.87% and 3.01% respectively. In Ratnagiri district the barren land area has increased by 1.14% in 20 years from 1989 to 2009. There is a positive change in barren land area in these 20 years. IV. Conclusion Updated information about land use and land cover of the present study area will help to overcome the problems in connection with the agricultural systems, forest cover, various infrastructures etc. Therefore it has suggested that, Remote sensing, GIS, GPS techniques should be used continuously for the management and development in the study area. References [1] Anderson, James Richard. A land use and land cover classification system for use with remote sensor data. Vol. 964. US Government Printing Office, 1976. [2] Chen, X., Vierling, L., & Deering, D., A simple and effective radiometric correction method to improve landscape change detection across sensors and across time. Remote Sensing of Environment, 98(1), 63-79, 2005. [3] Jensen, J. R. (2005). Introductorydigitalimageprocessing:Aremotesensingperspective (3rd Edn). Upper SaddleRiver, NJ:Prentice-Hall,2005. [4] Lillesand, M.T., KIefer, W. R. andChipman, N, J. (2008). :Remotesensingand image interpretation (6th ed). JohnWileyand Sons, Inc, NewYork.. [5] Rathod, B.L, (2015) , “ Coastal Resource Management Using Remote Sensing and GIS Techniques: A Case Study of Ratnagiri District, Maharashtra, (2015), Unpublished Ph.D. Dissertation. [6] Rathod, B. L., Sapkale, J.B., Status ofAgriculture in Coastal Villages of Ratnagiri, Maharashtra.,. ,International Journal of Scientific and Engineering Research, (IJSER), 6(9),1556-15592015. [7] Sapkale, J.B., Rathod, B. L., “Kharlands-An Agrarian Disaster in CoastalAreas of Southern Ratnagiri, Maharashtra:AStudy Using Remote Sensing and GIS”, InternationalRefereedJournalofEngineeringand Science (IRJES),3(6),71-78, 2014. [8] Socio-economic Review and Statistical Abstract Ratnagiri District 1980-2013. [9] Wilkie, D.S. and Finn, J.T. : „Remote Sensing Imagery for Natural Resources Monitoring‟. Columbia University Press, New York., P.P.- 295. 1996. Table No. 5 LAND USE/ LAND COVER CHANGE FROM 1999 TO 2009 Year-1999 Year-2009 Difference Change (1999 to 2009) Sr. No Class Name Area in Hectare Area in % Area in Hectare Area in % Area in Hectare Area in % 1 Builtup 59722 0.59 237421 2.46 177699 1.87 2 Cropped 1171164 11.65 1298500 13.47 127336 1.82 3 Open land 2302773 22.92 1077218 11.17 -1225555 -11.75 4 Dense forest 826064 8.22 601475 6.23 -224589 -1.99 5 Sparse forest 5337999 53.13 5989325 62.13 651326 9.00 6 Water body 159428 1.58 144776 1.50 -14652 -0.08 7 Barren land 188264 1.87 290864 3.01 102600 1.14 Total Area 10045414 100 9639579 100