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International Research Journal of Engineering and Technology (IRJET) e-ISSN: 2395-0056
Volume: 07 Issue: 02 | Feb 2020 www.irjet.net p-ISSN: 2395-0072
© 2020, IRJET | Impact Factor value: 7.34 | ISO 9001:2008 Certified Journal | Page 491
MAPPING CHANGE IN WATER SPREAD AREA OF HIMAYATSAGAR USING
REMOTE SENSING AND GIS
K. NAVATHA1 and C. SUDHAKAR REDDY2
1Department of Environmental Science, Osmania University, Hyderabad 5000007, Telangana, India
2National Remote Sensing Centre, ISRO
------------------------------------------------------------------------***-----------------------------------------------------------------------
ABTRACT- The present study is to analyse the spatio-temporal changes in wetland of Himayatsagar during 2001 and 2011.
Reference map Landsat ETM image of 29th October 2001 and IRS P6 AWIFS image of 11th November 2011 was used. It is aimed
to reveal the qualitative and quantitative changes in wetland during the past ten years and for analyzing the primary causes.
Key Words: Remote sensing, GIS, Himayatsagar, Water spread area, Wetland.
1. INTRODUCTION
Mapping and monitoring of land use and wetlands are the foremost requirements for planning, management and
conservation. Remote Sensing, GIS and GPS play vital role in mapping of existing land resources information at a particular
period. The multi-spectral data obtained from remote sensing satellites like Landsat, IRS, SPOT, IKONOS have been used to
study features either by visual interpretation or by processing digital data using digital computers. It provides excellent
capability to monitor composition of ecosystem and impact of management and degradation processes. Remote sensing (RS),
with its utility for surveying large areas in a time and cost-effective manner, offers a solution to difficulties of this type as
illustrated by its successful application to wetland ecosystem mapping (Bancroft and Bowman 1994). Classification is a
fundamental task for RS applications (Hay et al. 1996; Li and Xiao 2007). However, classification accuracy needs to be
considered to satisfy the requirements of desired baseline data applications (Zhang et al. 2013). Mostly, wetlands
classifications have been done at broad scale, using satellite imagery that covers large extents such as Landsat (Frohn et al.
2009; Frohn et al. 2012) but with coarse spatial resolution. Visual interpretation is a commonly used method for classification
and band selection in wetlands (Hung andWu 2005; Sridhar et al., 2008).
2. STUDY AREA
The present study Himayatsagar is one among the beautiful lakes located about 20 km from Hyderabad in Telangana, India.
The storage capacity of the reservoir is about 3.0 TMC. The construction of reservoir on Esi a tributary of Musi River was
completed in 1927, for providing drinking water source for Hyderabad, and also saving the city from floods, which
Hyderabad suffered in 1908. The Himayatsagar was the source of water supply for drinking and irrigation to the twin cities of
Secunderabad and Hyderabad, but due to the growth in population and increase in the need of peoples it was finally decided
by the state government to make it as a point of interest. The Engineer at the time of construction was Late Khaja Mohinuddin.
The Himayatsagar spread over 500 sq. miles covers Pargi, Venkatapuram, Shamshabad and other areas. The maximum
capacity of 1.60 lakh cusecs. In Himayatsagar, the water level in June (2012) was 1743.3 feet and on October 1(2012), it was
1,747.4 feet, an increase of about 4 feet. Similarly, In October 2011, the water levels at Himayatsagar were 1754.9 feet
respectively. There are few studies on wetlands using satellite remote sensing in India i.e. Pant et al., 1992; Pattanaik & Reddy,
2007; Reddy et al. 2007; Reddy and Roy, 2008; Reddy et al., 2008 a,b,c,d,e,f; Navatha et al., 2011 a and Romshoo and Rashid,
2012. The main aim of the present study is to analyse the spatio-temporal changes in wetlands of Himayatsagar during 2001
and 2011. It is also aimed to reveals the qualitative and quantitative changes in wetlands during the past ten years and for
analyzing the primary causes. In this study change refers to increases or decreases in extent of water spread of wetlands due
to natural and anthropogenic influences.
3. MATERIAL METHODS
Data used in the study of Himayat sagar lake, image of, ETM 29th October 2001 and 11th November 2011. Band 1, 2, 3 was used
for image classification. All three reflective bands were used in image classification. Images represent wet season as they were
captured in the month of October and November on different images. It was assumed that temporal changes of water body
remained insignificant over the period of months, at least for city wide change analysis. The study has been carried out under
International Research Journal of Engineering and Technology (IRJET) e-ISSN: 2395-0056
Volume: 07 Issue: 02 | Feb 2020 www.irjet.net p-ISSN: 2395-0072
© 2020, IRJET | Impact Factor value: 7.34 | ISO 9001:2008 Certified Journal | Page 492
the frame work of Geographic Information System (GIS) and Remote Sensing. Most case studies were conducted using GIS
techniques to explore environmental impacts of growing urbanization based on the analysis of spatial and temporal
relationships between various land use classes (Xiao et al. 2013; Hegazy and Kaloop 2015; Song et al. 2015; Abdulkareem et al.
2018; Nautiyal et al. 2017; Zadbagher et al. 2018; Gashaw et al. 2018). The image processing task has been carried out using
(Earth Resource Data Analysis System) ERDAS 9.2 image processing software (Leica Geosytems Geo- spatial Imaging, LCC).
Data on wetland features has been extracted by ERDAS Imagine 9.2 software. However, GIS task has been carried out using
ArcGIS 9.3.1 version. SOI maps served purpose of delineating the basin boundary and stream networks and authentication of
various features on the satellite image. Several variations of these methods exist, each process uses multiple bands of the
images to isolate unique spectral classes. No definite advice can be made about which classifier is best in all circumstances
(Townshend, 1992). The digital image classification as such seems to be simple process but in reality there are complications
that limit the accuracy of land cover classification (Mather 1991). In the unsupervised approach, pixels are grouped into
different spectral classes by clustering algorithms without using prior information (Jensen 1996). ISODATA, an unsupervised
classification technique was used in order to group the pixels into clusters. 100 spectral clusters with 95% convergence value
were selected with the aim of performing unsupervised classification. Unsupervised classification examines the spectral
characteristics of each pixel and statistically groups similar pixels into classes. User further aggregates the spectral classes into
information classes. In unsupervised classification any individual pixel is compared to each discrete cluster to see which one it
is closest to. A map of all pixels in the image, classified as to which cluster each pixel is most likely to belong, is produced (in
black and white or more commonly in colours assigned to each cluster). This then must be interpreted by the user as to what
the colour pattern may mean in terms of classes, etc. that are actually present in the real world scene.
4. Result
In the beginning of 2001 to 2011 the total extent area of Himayatsagar wetland of Hyderabad as a whole is estimated to be
13,879 Ha (Table-1). The land use/cover classes classified into 5 categories and area of each class has been calculated. There is
a depiction between 2001 and 2011 of Himayatsagar of total geographical area most of the land use is under agriculture
(10737.3 Ha of area 77.4%), as this is main occupation of people, scrub is a vegetative cover predominantly occupied by
shrubs with crown density 10.4%. It is the vegetative class covering an area of 1.7% in Himayatsagar. Water land occupies
significant area, which is about 14.6% which second dominant class covering an area of 2022.2 Ha. Built up area which
includes urban/ rural settlements represents an area of 1427.2 Ha, it third dominant class of an 5.8%. Orchids land
contributes significantly to the land cover with Himayatsagar 0.5%. (Fig -1a,1b). In the lake the total extent of water occupy is
about 2022.2 Ha.
TABLE: 1 Status Of Wetland And Other Land Use Of Himayatsagar LakeAnd Surroundings (Area In Ha.)
S.No Class 2001 2011
1 Water 1924 2120
2 Scrub 244 241
3 Built up area 587 1023
4 Agriculture 11051 10423
5 Orchards 72 72
Total 13879 13879
1924
244
587
11051
72
Fig: 1a Wetland and Other Land Use of HimayatsagaLake
(Area In Ha) 2001
2120 241
1023
10423
72
Water Scrub Built up area
Fig: 1b Wetland and Other Land Use of HimayatsagarLake
(Area In Ha) 2001
International Research Journal of Engineering and Technology (IRJET) e-ISSN: 2395-0056
Volume: 07 Issue: 02 | Feb 2020 www.irjet.net p-ISSN: 2395-0072
© 2020, IRJET | Impact Factor value: 7.34 | ISO 9001:2008 Certified Journal | Page 493
5. Discussion
The change matrix analyses allowed mapping of the abrupt changes in wetland. The results confirm that land cover has
changed significantly since 2001 with agriculture land being transformed to wetland. From analysis it is observed that an area
195 Ha of water was increased by 2001. Built up area was increased twice by 2011 were 43 Ha of agriculture land have been
converted. Changes that have occurred from the period 2001-2011 were presented in (Fig – 2) and (Table- 2). The time series
wetland mapping demonstrated the existence of water spread area of the lake. Comparisons between 2001- 2011 indicated
that changes in overall wetland areas were significant over the ten years. (Fig – 3 to 6). From the study it is evident that area of
drinking water bodies of Hyderabad city found to be increased. Significant correlation of gain of wetland are also found with
in-creasing water spread area and urban population and build-up area showed wide expansion, where as agriculture land
reduced from 2001 to 2011 (Table-1). Human induced activities are also now becoming important factors for change of
wetland after 2015. Climate change may increase, causing threat to natural environment.
TABLE : 2 Change Area Matrix of Wetland and Land Use of Himayatsagar Lake (2001 To 2011)
S.No 2001/2011 Water Scrub
Built up
area
Agriculture Orchards 2001
1 Water 1924 0 0 0 0 1924
2 Scrub 0 241 3 0 0 244
3 Built up area 0 0 587 0 0 587
4 Agriculture 195 0 433 10423 0 11051
5 Orchards 0 0 0 0 72 72
2011 2120 241 1023 10423 72 13879
Fig : 2 Dynamics In Extent of Water in Himyatsagar Lake (2001-2011)
1800
1850
1900
1950
2000
2050
2100
2150
2001 2011
International Research Journal of Engineering and Technology (IRJET) e-ISSN: 2395-0056
Volume: 07 Issue: 02 | Feb 2020 www.irjet.net p-ISSN: 2395-0072
© 2020, IRJET | Impact Factor value: 7.34 | ISO 9001:2008 Certified Journal | Page 494
FIG: 3 LANDSAT ETM FCC Image of Himayatsagar
Lake and its Surroundigs (October 2001)
FIG: 4. Wetland Map of Himayatsagar Lake and
its Surroundings (October, 2001)
FIG: 5 IRS P6 AWIFS FCC Image of Himayatsagar
Lake and its surroundings (November 2011)
FIG: 6 Wetland Map of Himayatsagar Lake
and its Surroundigs (November, 2011)
International Research Journal of Engineering and Technology (IRJET) e-ISSN: 2395-0056
Volume: 07 Issue: 02 | Feb 2020 www.irjet.net p-ISSN: 2395-0072
© 2020, IRJET | Impact Factor value: 7.34 | ISO 9001:2008 Certified Journal | Page 495
6. CONCLUSION
The total extent area of Himayat sagar as a whole is estimated to be 13,879 Ha. In the lake the total extent of water is about
2022.2 Ha. From the study it is evident that water spread area is increased and built up area showed wide expansion, where as
agriculture land decreased from 2001 to 2011. It is clearly evident from remote sensing data an increase in built up area at
present scenario in Hyderabad. In view of ecological significance of wetlands and long term conservation, mapping and
monitoring is needed for sustainable management of natural resources.
7. REFERENCES
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Remote Sensing Of Environment 55:108–122.
6. Hegazy IR, Kaloop MR (2015) Monitoring urban growth and land use change detection with GIS and remote sensing
techniques in Daqahlia governorate Egypt. Int J Sustain Built Environ 4(1):117–124
7. Hung MC, Wu YH, 2005. Mapping and Visualizing the Great Salthung MC, Wu YH Mapping and Visualizing the Great Salt
Lake Landscape Dynamics Using Multi-Temporal Satellite Images, 1972–1996. International Journal of Remote Sensing
26:1815–1834.
8. Li P, Xiao X., 2007. Multispectral Image Segmentation by a Multichannel Watershed-Based Approach. International
Journal of Remote Sensing 28:4429–4452.
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(Orissa, India) Using Remote Sensing Based Data. The National Academy Science Letters: Vol.30: 5 & 6. 161-164.
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in Indian Himalayas. Arab J. Geosci. DOI 10.1007/S12517-012-0761-9.
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Using Multi-Temporal Satellite Data and GIS. Research Journal of Environmental Sciences 2(2): 108-115.
14. Reddy, C.S., Pattanaik, C. and Murthy, M.S.R. 2007a. Assessment and Monitoring Of Mangroves of Bhitarkanika Wildlife
Sanctuary, Orissa, India Using Remote Sensing & GIS. Current Science 92(10): 1409-1415.
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International Research Journal of Engineering and Technology (IRJET) e-ISSN: 2395-0056
Volume: 07 Issue: 02 | Feb 2020 www.irjet.net p-ISSN: 2395-0072
© 2020, IRJET | Impact Factor value: 7.34 | ISO 9001:2008 Certified Journal | Page 496
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Aquaculture Plots Using Satellite Data. International Journal of Remote Sensing 29:313–323.
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IRJET- Mapping Change in Water Spread Area of Himayatsagar using Remote Sensing and GIS

  • 1. International Research Journal of Engineering and Technology (IRJET) e-ISSN: 2395-0056 Volume: 07 Issue: 02 | Feb 2020 www.irjet.net p-ISSN: 2395-0072 © 2020, IRJET | Impact Factor value: 7.34 | ISO 9001:2008 Certified Journal | Page 491 MAPPING CHANGE IN WATER SPREAD AREA OF HIMAYATSAGAR USING REMOTE SENSING AND GIS K. NAVATHA1 and C. SUDHAKAR REDDY2 1Department of Environmental Science, Osmania University, Hyderabad 5000007, Telangana, India 2National Remote Sensing Centre, ISRO ------------------------------------------------------------------------***----------------------------------------------------------------------- ABTRACT- The present study is to analyse the spatio-temporal changes in wetland of Himayatsagar during 2001 and 2011. Reference map Landsat ETM image of 29th October 2001 and IRS P6 AWIFS image of 11th November 2011 was used. It is aimed to reveal the qualitative and quantitative changes in wetland during the past ten years and for analyzing the primary causes. Key Words: Remote sensing, GIS, Himayatsagar, Water spread area, Wetland. 1. INTRODUCTION Mapping and monitoring of land use and wetlands are the foremost requirements for planning, management and conservation. Remote Sensing, GIS and GPS play vital role in mapping of existing land resources information at a particular period. The multi-spectral data obtained from remote sensing satellites like Landsat, IRS, SPOT, IKONOS have been used to study features either by visual interpretation or by processing digital data using digital computers. It provides excellent capability to monitor composition of ecosystem and impact of management and degradation processes. Remote sensing (RS), with its utility for surveying large areas in a time and cost-effective manner, offers a solution to difficulties of this type as illustrated by its successful application to wetland ecosystem mapping (Bancroft and Bowman 1994). Classification is a fundamental task for RS applications (Hay et al. 1996; Li and Xiao 2007). However, classification accuracy needs to be considered to satisfy the requirements of desired baseline data applications (Zhang et al. 2013). Mostly, wetlands classifications have been done at broad scale, using satellite imagery that covers large extents such as Landsat (Frohn et al. 2009; Frohn et al. 2012) but with coarse spatial resolution. Visual interpretation is a commonly used method for classification and band selection in wetlands (Hung andWu 2005; Sridhar et al., 2008). 2. STUDY AREA The present study Himayatsagar is one among the beautiful lakes located about 20 km from Hyderabad in Telangana, India. The storage capacity of the reservoir is about 3.0 TMC. The construction of reservoir on Esi a tributary of Musi River was completed in 1927, for providing drinking water source for Hyderabad, and also saving the city from floods, which Hyderabad suffered in 1908. The Himayatsagar was the source of water supply for drinking and irrigation to the twin cities of Secunderabad and Hyderabad, but due to the growth in population and increase in the need of peoples it was finally decided by the state government to make it as a point of interest. The Engineer at the time of construction was Late Khaja Mohinuddin. The Himayatsagar spread over 500 sq. miles covers Pargi, Venkatapuram, Shamshabad and other areas. The maximum capacity of 1.60 lakh cusecs. In Himayatsagar, the water level in June (2012) was 1743.3 feet and on October 1(2012), it was 1,747.4 feet, an increase of about 4 feet. Similarly, In October 2011, the water levels at Himayatsagar were 1754.9 feet respectively. There are few studies on wetlands using satellite remote sensing in India i.e. Pant et al., 1992; Pattanaik & Reddy, 2007; Reddy et al. 2007; Reddy and Roy, 2008; Reddy et al., 2008 a,b,c,d,e,f; Navatha et al., 2011 a and Romshoo and Rashid, 2012. The main aim of the present study is to analyse the spatio-temporal changes in wetlands of Himayatsagar during 2001 and 2011. It is also aimed to reveals the qualitative and quantitative changes in wetlands during the past ten years and for analyzing the primary causes. In this study change refers to increases or decreases in extent of water spread of wetlands due to natural and anthropogenic influences. 3. MATERIAL METHODS Data used in the study of Himayat sagar lake, image of, ETM 29th October 2001 and 11th November 2011. Band 1, 2, 3 was used for image classification. All three reflective bands were used in image classification. Images represent wet season as they were captured in the month of October and November on different images. It was assumed that temporal changes of water body remained insignificant over the period of months, at least for city wide change analysis. The study has been carried out under
  • 2. International Research Journal of Engineering and Technology (IRJET) e-ISSN: 2395-0056 Volume: 07 Issue: 02 | Feb 2020 www.irjet.net p-ISSN: 2395-0072 © 2020, IRJET | Impact Factor value: 7.34 | ISO 9001:2008 Certified Journal | Page 492 the frame work of Geographic Information System (GIS) and Remote Sensing. Most case studies were conducted using GIS techniques to explore environmental impacts of growing urbanization based on the analysis of spatial and temporal relationships between various land use classes (Xiao et al. 2013; Hegazy and Kaloop 2015; Song et al. 2015; Abdulkareem et al. 2018; Nautiyal et al. 2017; Zadbagher et al. 2018; Gashaw et al. 2018). The image processing task has been carried out using (Earth Resource Data Analysis System) ERDAS 9.2 image processing software (Leica Geosytems Geo- spatial Imaging, LCC). Data on wetland features has been extracted by ERDAS Imagine 9.2 software. However, GIS task has been carried out using ArcGIS 9.3.1 version. SOI maps served purpose of delineating the basin boundary and stream networks and authentication of various features on the satellite image. Several variations of these methods exist, each process uses multiple bands of the images to isolate unique spectral classes. No definite advice can be made about which classifier is best in all circumstances (Townshend, 1992). The digital image classification as such seems to be simple process but in reality there are complications that limit the accuracy of land cover classification (Mather 1991). In the unsupervised approach, pixels are grouped into different spectral classes by clustering algorithms without using prior information (Jensen 1996). ISODATA, an unsupervised classification technique was used in order to group the pixels into clusters. 100 spectral clusters with 95% convergence value were selected with the aim of performing unsupervised classification. Unsupervised classification examines the spectral characteristics of each pixel and statistically groups similar pixels into classes. User further aggregates the spectral classes into information classes. In unsupervised classification any individual pixel is compared to each discrete cluster to see which one it is closest to. A map of all pixels in the image, classified as to which cluster each pixel is most likely to belong, is produced (in black and white or more commonly in colours assigned to each cluster). This then must be interpreted by the user as to what the colour pattern may mean in terms of classes, etc. that are actually present in the real world scene. 4. Result In the beginning of 2001 to 2011 the total extent area of Himayatsagar wetland of Hyderabad as a whole is estimated to be 13,879 Ha (Table-1). The land use/cover classes classified into 5 categories and area of each class has been calculated. There is a depiction between 2001 and 2011 of Himayatsagar of total geographical area most of the land use is under agriculture (10737.3 Ha of area 77.4%), as this is main occupation of people, scrub is a vegetative cover predominantly occupied by shrubs with crown density 10.4%. It is the vegetative class covering an area of 1.7% in Himayatsagar. Water land occupies significant area, which is about 14.6% which second dominant class covering an area of 2022.2 Ha. Built up area which includes urban/ rural settlements represents an area of 1427.2 Ha, it third dominant class of an 5.8%. Orchids land contributes significantly to the land cover with Himayatsagar 0.5%. (Fig -1a,1b). In the lake the total extent of water occupy is about 2022.2 Ha. TABLE: 1 Status Of Wetland And Other Land Use Of Himayatsagar LakeAnd Surroundings (Area In Ha.) S.No Class 2001 2011 1 Water 1924 2120 2 Scrub 244 241 3 Built up area 587 1023 4 Agriculture 11051 10423 5 Orchards 72 72 Total 13879 13879 1924 244 587 11051 72 Fig: 1a Wetland and Other Land Use of HimayatsagaLake (Area In Ha) 2001 2120 241 1023 10423 72 Water Scrub Built up area Fig: 1b Wetland and Other Land Use of HimayatsagarLake (Area In Ha) 2001
  • 3. International Research Journal of Engineering and Technology (IRJET) e-ISSN: 2395-0056 Volume: 07 Issue: 02 | Feb 2020 www.irjet.net p-ISSN: 2395-0072 © 2020, IRJET | Impact Factor value: 7.34 | ISO 9001:2008 Certified Journal | Page 493 5. Discussion The change matrix analyses allowed mapping of the abrupt changes in wetland. The results confirm that land cover has changed significantly since 2001 with agriculture land being transformed to wetland. From analysis it is observed that an area 195 Ha of water was increased by 2001. Built up area was increased twice by 2011 were 43 Ha of agriculture land have been converted. Changes that have occurred from the period 2001-2011 were presented in (Fig – 2) and (Table- 2). The time series wetland mapping demonstrated the existence of water spread area of the lake. Comparisons between 2001- 2011 indicated that changes in overall wetland areas were significant over the ten years. (Fig – 3 to 6). From the study it is evident that area of drinking water bodies of Hyderabad city found to be increased. Significant correlation of gain of wetland are also found with in-creasing water spread area and urban population and build-up area showed wide expansion, where as agriculture land reduced from 2001 to 2011 (Table-1). Human induced activities are also now becoming important factors for change of wetland after 2015. Climate change may increase, causing threat to natural environment. TABLE : 2 Change Area Matrix of Wetland and Land Use of Himayatsagar Lake (2001 To 2011) S.No 2001/2011 Water Scrub Built up area Agriculture Orchards 2001 1 Water 1924 0 0 0 0 1924 2 Scrub 0 241 3 0 0 244 3 Built up area 0 0 587 0 0 587 4 Agriculture 195 0 433 10423 0 11051 5 Orchards 0 0 0 0 72 72 2011 2120 241 1023 10423 72 13879 Fig : 2 Dynamics In Extent of Water in Himyatsagar Lake (2001-2011) 1800 1850 1900 1950 2000 2050 2100 2150 2001 2011
  • 4. International Research Journal of Engineering and Technology (IRJET) e-ISSN: 2395-0056 Volume: 07 Issue: 02 | Feb 2020 www.irjet.net p-ISSN: 2395-0072 © 2020, IRJET | Impact Factor value: 7.34 | ISO 9001:2008 Certified Journal | Page 494 FIG: 3 LANDSAT ETM FCC Image of Himayatsagar Lake and its Surroundigs (October 2001) FIG: 4. Wetland Map of Himayatsagar Lake and its Surroundings (October, 2001) FIG: 5 IRS P6 AWIFS FCC Image of Himayatsagar Lake and its surroundings (November 2011) FIG: 6 Wetland Map of Himayatsagar Lake and its Surroundigs (November, 2011)
  • 5. International Research Journal of Engineering and Technology (IRJET) e-ISSN: 2395-0056 Volume: 07 Issue: 02 | Feb 2020 www.irjet.net p-ISSN: 2395-0072 © 2020, IRJET | Impact Factor value: 7.34 | ISO 9001:2008 Certified Journal | Page 495 6. CONCLUSION The total extent area of Himayat sagar as a whole is estimated to be 13,879 Ha. In the lake the total extent of water is about 2022.2 Ha. From the study it is evident that water spread area is increased and built up area showed wide expansion, where as agriculture land decreased from 2001 to 2011. It is clearly evident from remote sensing data an increase in built up area at present scenario in Hyderabad. In view of ecological significance of wetlands and long term conservation, mapping and monitoring is needed for sustainable management of natural resources. 7. REFERENCES 1. Abdulkareem JH, Sulaiman WNA, Pradhan B, Jamil NR (2018) Long term hydrologic impact assessment of non-point source pollution measured through land use/land cover (LULC) changes in a tropical complex catchment. Earth Syst Environ 2:1–18. 2. Frohn RC, Reif M, Lane C, Autrey B, 2009. Satellite Remote Sensing of Isolated Wetlands Using Object-Oriented Classification of Landsat-7 Data. Wetlands 29:931–941. 3. Frohn RC, D’Amico E, Lane C, Autrey B, Rhodus J, Liu HX, 2012. Multi-Temporal Sub-Pixel Landsat ETM Plus Classification of Isolated Wetlands in Cuyahoga County, Ohio, USA. Wetlands 32:289–299. 4. Gashaw T, Tulu T, Argaw M, Worqlul AW (2018) Modeling the hydrological impacts of land use/land cover changes in the Andassa watershed, Blue Nile Basin, Ethiopia. Sci Total Environ 619:1394–1408. 5. Hay GJ, Niemann KO, Mclean GF, 1996. An Object-Specific Image Texture Analysis Of H-Resolution Forest Imagery. Remote Sensing Of Environment 55:108–122. 6. Hegazy IR, Kaloop MR (2015) Monitoring urban growth and land use change detection with GIS and remote sensing techniques in Daqahlia governorate Egypt. Int J Sustain Built Environ 4(1):117–124 7. Hung MC, Wu YH, 2005. Mapping and Visualizing the Great Salthung MC, Wu YH Mapping and Visualizing the Great Salt Lake Landscape Dynamics Using Multi-Temporal Satellite Images, 1972–1996. International Journal of Remote Sensing 26:1815–1834. 8. Li P, Xiao X., 2007. Multispectral Image Segmentation by a Multichannel Watershed-Based Approach. International Journal of Remote Sensing 28:4429–4452. 9. Nautiyal S, Kaechele H, Tikhile P, Subbanna S, Baksi S (2017) Study on land use dynamics: appropriate methods for change estimation in social science research. ESE 1(2):27. 10. Pant, D.N., Das, K.K and Roy, P.S., 1992. Mapping of Tropical Dry Deciduous Forest and Land Use In Part of Vindyan Range Using Satellite Remote Sensing. Photonirvachak, Journal of the Indian Society of Remote Sensing 20: 9-20. 11. Pattanaik, C. and Reddy, C.S. 2007. Need for the Conservation of Wetland Ecosystems: A Case Study of Ansupa Lake (Orissa, India) Using Remote Sensing Based Data. The National Academy Science Letters: Vol.30: 5 & 6. 161-164. 12. Romshoo, SA and Rashid, I., 2012. Assessing the Impacts of Changing Land Cover and Climate on Hokersar Wetland in Indian Himalayas. Arab J. Geosci. DOI 10.1007/S12517-012-0761-9. 13. Reddy, C.S. and Roy, A., 2008. Assessment of Three Decade Vegetation Dynamics in Mangroves of Godavari Delta, India Using Multi-Temporal Satellite Data and GIS. Research Journal of Environmental Sciences 2(2): 108-115. 14. Reddy, C.S., Pattanaik, C. and Murthy, M.S.R. 2007a. Assessment and Monitoring Of Mangroves of Bhitarkanika Wildlife Sanctuary, Orissa, India Using Remote Sensing & GIS. Current Science 92(10): 1409-1415. 15. Reddy, C.S., Rangaswamy, M. and Jha, C.S. 2008b. Monitoring Of Spatio-Temporal Changes In Part of Kosi River Basin, Bihar, India Using Remote Sensing And Geographical Information System. Research Journal of Environmental Sciences 2(1): 58-62. 16. Reddy, C.S., Shilpa, B., Sudha, K., Sudhakar, S. and Raju, V.S. 2008c. Vegetation Cover Mapping and Landscape Level Disturbance Gradient Analysis In Warangal District, Andhra Pradesh, India Using Satellite Remote Sensing And GIS. Space Research Journal 1: 29-38. 17. Reddy, C.S., Pattanaik, C., Murthy, E.N. and Raju, V.S. 2008d. Mapping and Monitoring Of Calamus Rotang L. In The Adjoining Areas Of Ramappa Lake, Andhra Pradesh Using Remote Sensing And GIS. Current Science: 94(5). 575-577. 18. Reddy, C.S., Navatha, K., Shivakala, T., Rachel, B. and Manikya Reddy, P. 2008e. Mapping Wetlands of Warangal District, Andhra Pradesh, India Using IRS P6 LISS III Data. Sarovar Saurabh, SACON-ENVIS (1): 6-8. 19. Reddy, C.S., Pujar, G.S., Sudhakar, S., Shilpa, B., Sudha, K., Trivedi, S., Gharai, B. and Murthy, M.S.R., 2008f. Mapping the Vegetation Types of Andhra Pradesh, India Using Remote Sensing. Proc. A.P. Akademi Of Sciences 12(1&2): 14-23. 20. Song W, Pijanowski BC, Tayyebi A (2015) Urban expansion and its consumption of high-quality farmland in Beijing, China. Ecol Indic 54:60–70
  • 6. International Research Journal of Engineering and Technology (IRJET) e-ISSN: 2395-0056 Volume: 07 Issue: 02 | Feb 2020 www.irjet.net p-ISSN: 2395-0072 © 2020, IRJET | Impact Factor value: 7.34 | ISO 9001:2008 Certified Journal | Page 496 21. Sridhar PN, Surendran A, Ramana, 2008. Auto-Extraction Techniquebased Digital Classification of Saltpans And Aquaculture Plots Using Satellite Data. International Journal of Remote Sensing 29:313–323. 22. Xiao R, Su S, Zhang Z, Qi J, Jiang D, Wu J (2013) Dynamics of soil sealing and soil landscape patterns under rapid urbanization. CATENA 109:1–12 23. Zadbagher E, Becek K, Berberoglu S (2018) Modeling land use/land cover change using remote sensing and geographic information systems: case study of the Seyhan Basin, Turkey. Environ Monit Assess 190:494