Remote sensing and GIS-based Seashore changes of Tuticorin Zone and Punnaikayal Zone in parts of Thoothukudi Coast, Tamil Nadu, India (original) (raw)

Remote sensing and GIS-based Seashore changes of Tuticorin Zone and Punnaikayal Zone in parts of Thoothukudi Coast, Tamil Nadu, India

Sudhakar V 1{ }^{1}, Gurugnanam B 2{ }^{2}, Bairavi S 3{ }^{3},Sorna Chandra Devadass C4\mathrm{C}^{4}
1,2,3{ }^{1,2,3} Centre for Applied Geology, The Gandhigram Rural Institute - Deemed to be University, Dindigul, Tamil Nadu, India
4{ }^{4} Department of Civil Engineering, Samskruti College of Engineering and Technology, Ghatkesar, Hyderabad, India.

Article Info

Volume 82
Page Number: 16844 - 16852 Publication Issue:
January - February 2020

Article History

Article Received: 18 May 2019
Revised: 14 July 2019
Accepted: 22 December 2019
Publication: 29 February 2020

Abstract

Urban coast and Estuary have significant modification as erosion and accretion due to both natural and human intervention. The study was carried out in Tuticorin and Punnaikayal zones in part of Thoothukudi coast from 1968 to 2018. For a detailed study, these zones further divided into three sub-zones, namely as A to F. The SOI Toposheet used for marking the shoreline for the year 1968. The Seashore lines digitised with FCC of Satellite imagery in ArcGIS platform using preprocessed Landsat TM Satellite imagery of 1997 and 2018. Finally, Shoreline changes are measured and analysed by overlay analysis for finding the amount of erosion and accretion between the periods 1968 - 1997 and 1997 - 2018. The findings reveal that in both the zones, more accretion has noticed during the period 1968 1997. However, the accretion process has reduced during the period 1997 - 2018. In Tuticorin zone, the accretion was reduced from 2.40 km22.40 \mathrm{~km}^{2} to 1.14 km21.14 \mathrm{~km}^{2} with the growth rate from 69.63 m2/69.63 \mathrm{~m}^{2} / year to 54,41 m2/54,41 \mathrm{~m}^{2} / year. In Punnaikayal zone, the amount of accretion is reduced from 1.23 km21.23 \mathrm{~km}^{2} to 0.04 km20.04 \mathrm{~km}^{2} with the growth rate decreased from 42,52 m2/42,52 \mathrm{~m}^{2} / year to 1,81 m2/1,81 \mathrm{~m}^{2} / year. The result concludes that an accretion process reduced and in turn erosion process increased in the coastal region.

Keywords-Erosion, Accretion, Net growth, Growth rate

I. INTRODUCTION

Seashore line changes affects the coastal livelihood and economic conditions and land management, and also it controls the environment [1]-[2]. The coastline is one of the most significant straight highlights on the world’s surface, which has a powerful nature [23]. Natural and geological phenomena, sediment transportation and sea-level rise, will cause the seashore line directly [3]. Coastal zones are the world’s most diverse and productive environments. Seaside territories additionally incorporate complex biological systems, for example, coral reefs, mangroves, sandy seashores and ocean grass [22]. One of the essential requirements of coastal protection planning work is
to understand the coastal processes of erosion, deposition and sediment transport, flooding and sealevel changes that continually alter the coastline [23]. The sandy beaches were exposed more for the erosion, and accretion activities. Waves, currents, and tides also contributed to the shoreline erosion and accretion process.

The researchers analyzed the trends in waves with respect to erosion and accretion studies in the Arabian Sea, Bay of Bengal and also in the northern Indian Ocean [4]-[5], using historical satellite databased seashore line measurements [6]- [10], and validated by many scholars [11]-[12]. Shoreline changes are a great concern in the estuaries [13][16]. Sediment transportation through littoral current

is also the cause behind in the beach accretion and erosion. The sediment is more deposited in monsoon season and the same was lower in summer and postmonsoon season The amount of sedimentation accumulation is 1.97mg/cm2/1.97 \mathrm{mg} / \mathrm{cm} 2 / day to 12.31 mg/cm/\mathrm{mg} / \mathrm{cm} / day, in the Gulf of Mannar [20]. Remote sensing plays an important role in spatial data acquisition from an economic perspective [22]. The historical and functional approaches to study shoreline changes along with various landforms help in deciphering the coastal processes operating in an area [22]. Multi-date satellite information has been utilised to analyse about shoreline change and seaside landforms, which gave understanding into huge zone silt transport studies and identifying the long-term change in whole coastline [22]. The Thoothukudi coast has encountered consistent growth from 1969 to 2006 [3]. The present study was carried out in parts of Tuticorin and Punnaikayal areas of part of Thoothukudi from 1968 to 2018.

A. Study Area

The study area forms the part of Thoothukudi coast of Thoothukudi district lies between 8∘36′8^{\circ} 36^{\prime} and 8∘8^{\circ} 47′N47^{\prime} \mathrm{N} latitude and 78∘6′78^{\circ} 6^{\prime} and 78∘17′78^{\circ} 17^{\prime} East longitude. Length of Coastline is is 30 kilometer, and it lies between Threspuram and Kayalpatnam (Fig - 1). The study area dealt with two zones visTuticorin and Punnaikayal. Each zone divided into three subzones, a total of six subzones in order of namely A to F designated for further study. The area of each gird covers 30 km 2 . Geologically, the study area composed of sedimentary rocks of tertiary to recent age. Sandy beaches are the more significant occupant along the coast. Earlier reports reveal that in the study area covers the dominance of sandy beaches and also in few places, estuaries and black sands [16]-[17]-[18]. Mangroves, mudflats, dunes, coral reefs, and van island, also present in the southernmost tip of the Tuticorin coast of the Gulf of Manner. The coast of Tuticorin also supports a number of economic activities such as fisheries, salt
pans, urban settlements and industry. Thamirabarani River has got the number of tributaries in the study area, and it controls the erosion and deposition activities in Thoothukudi coast. District Tuticorin experiences a tropical semi-arid climate. The climate here is usually hot and dry, with the hottest months being May-August, and the coldest months of the year being December-February. It reported a maximum temperature of 29.5−40.5C29.5-40.5 \mathrm{C} and a minimum temperature of 18.4−26.7C18.4-26.7 \mathrm{C}.

II. MATERIALS AND METHODS

The temporal satellite Imageries are highly useful for preparing the shoreline study [19]. In the study, sea shorelines extracted from the Toposheets (1968) and Landsat data sets of TM (1997) and OLI (2018) (Table: I). The Toposheets and Satellite data were re-projected with WGS 1984, Zone of 43 N for further process. The seashore lines were digitised using FCC satellite data (during the years 1997 and 2018) as well as Toposheets for shoreline extraction during the year 1968, in ArcGIS platform. Digitised seashore lines are taken as input data and merged to form an overlay line features. The merged line features were taken as input data to create polygon is generated (Fig- 2). The output feature polygon is used to calculate the amount of erosion and accretion between the periods 1968 - 1997 and 1997 - 2018 (Table: II).

Table: I Landsat Satellite data details

Images Meta data Scene Details
Landsat 5 TM/ 143/54\begin{gathered} \text { TM/ } \\ 143 / 54 \end{gathered} 05/28/1997
Landsat 8 OLI /143/54\begin{gathered} \text { OLI } \\ / 143 / 54 \end{gathered} 04/04/2018

img-0.jpeg

Fig -1: Study Area

III. RESULTS AND DISCUSSION

A. Subzones wise Shoreline Change Analysis

The long-term rate of coastal line changes can be demarcated and calculate the area of erosion and accretion by using satellite imagery [20]. In the present study, historical Satellite images of Tuticorin and Punnaikayal coastal zone’s shorelines were analysed and calculated the shoreline changes during 1968, 1997 and 2018 (Table: 2). Each zone has further divided into three sub-zones viz A - F for a detailed shoreline change study during the periods of 1968, 1997 and 2018 (Fig 2). The results in details discussed for each zone and subzones are detailed below.

  1. Shoreline Change of Tuticorin zone during the period 1968 - 1997.

In sub-zones, A, B, and C, more accretion noticed due to natural and human activities (Fig - 3). Tuticorin zone has a harbour. It is one of the 12 important harbours in India. Tuticorin zone is the main urban area of the thoothukudi district. Moreover, Tuticorin zones have salt pans, fishing harbours, and industries are controlling erosion and accretion activities. Subzone A noticed with more accretion (0.58 km2)\left(0.58 \mathrm{~km}^{2}\right) and less amount of erosion (0.02 km2)\left(0.02 \mathrm{~km}^{2}\right). The overall growth is 0.56 square kilometer with a growth rate of 19.42 meter / year during 1968 - 1997 (Table: II). In Gird B and C also noticed with more accretion. 1.11 km21.11 \mathrm{~km}^{2} of accretion
has observed in gird B due to the human-made activities. In this sub-zones, northern part of the Tuticorin port, significant and minor fishing harbours, salt industries, urban settlements, (Fig - 6 (B)) and Pandian island (now, it is part of Tuticorin port) are the known and famous features in the study area (Fig - 2 (A)), which controls the erosion and deposition of the study area. In this subzone, a small amount of erosion observed (0.65 km2)\left(0.65 \mathrm{~km}^{2}\right), with a overall growth of −0.46 km2-0.46 \mathrm{~km}^{2}, with the growth rate of 15.86 meter / year noticed. It is due to the industrial developments as well as natural activities along the coastal track. Whereas, Subzone C, covered with Harbor Estate and Thermal Quarters camp 2 areas. This coast looks like a curve-shaped structure (Fig 2 (B)). In this sub-zones, more amount of accretion and less amount of erosion observed. It is 0.15 km20.15 \mathrm{~km}^{2} of erosion and 1.53 km21.53 \mathrm{~km}^{2} of accretion (Table: II and Fig - 3). Erosion in this area is due to physical construction and maintenance of the structure. The accretion of this area is due to sediment transport from Thamirabaraniriver and by the current littoral movement in the coastal surf zone. Subzone C has 1.38 km21.38 \mathrm{~km}^{2} net growth of shoreline changes with the growth rate of 4.75 m2/4.75 \mathrm{~m}^{2} / year during the period 1968 1997. It is the high amount of accretion among all girds of Tuticorin Zone. Overall results of Tuticorin zone reveal that this zone exposed to the total amount of erosion is 0.82 km20.82 \mathrm{~km}^{2} and accretion is 3.22 km2\mathrm{km}^{2} during the period 1968 - 1997 (Table: III). Growth rate 82,78 m2/82,78 \mathrm{~m}^{2} / year during 1968−19971968-1997 was noticed (Table: IV and Fig 5).
2) Shoreline Change of Tuticorin zone during the period 1997 - 2018.

During 1997 - 2018, erosion was dominated in the sub-zones A. It is 0.10 km20.10 \mathrm{~km}^{2} erosion, and less amount of accretion (0.03 km2)\left(0.03 \mathrm{~km}^{2}\right) perceived in Threspuram coastal area of subzone A. In this area, Jetties constructed on the sea (Fig - 6(A)). In this jetties, either side erosion observed due to the wave diffraction. The net erosion is −0.029 km2-0.029 \mathrm{~km}^{2} with a

growth rate of −3.26 m2/-3.26 \mathrm{~m}^{2} / year (Table: II) in this subzones. In sub-zone, B, fishing harbours, Thermal plant and Inigo Nagar (Fig - 6(B)) noticed. In Subzone B, more amount of erosion 0.85 km20.85 \mathrm{~km}^{2} and less amount of accretion (0.30 km2)\left(0.30 \mathrm{~km}^{2}\right) observed with a net growth of 0.55 km20.55 \mathrm{~km}^{2} during the period 1997 2018. This subzone growth rate of shoreline changes is 2.62 m2/2.62 \mathrm{~m}^{2} / year (Table: II). In sub zone C, accretion (0.70 km2)\left(0.70 \mathrm{~km}^{2}\right) was noticed. It is due to the accumulation of sediments from Tambraparaniriver. These subzones also under erosion process. It is 0.04 km20.04 \mathrm{~km}^{2} (Table: II and Fig -4 ). The net growth of accretion is 0.66 km20.66 \mathrm{~km}^{2} : with a growth rate of 31.55 m2/31.55 \mathrm{~m}^{2} / year. The overall result reveals that the Tuticorin zone dominates with more accretion during the period 1997 - 2018. The total amount of accretion is 1.58 km2\mathrm{km}^{2}, and erosion is 0.44 km20.44 \mathrm{~km}^{2} (Table: III), and the net growth is 1.15 km21.15 \mathrm{~km}^{2} with a rate 54.51 m2/54.51 \mathrm{~m}^{2} / year, during this period (Table: IV and Fig - 5).
3) Shoreline Change of Punnaikayal zone during the period 1968 - 1997.

The Punnaikayal zone is a delta of Thamirabarani River. The Punnaikayal zone has exposed to accretion due to accumulation of sediments by drift littoral current though the Thamirabaraniriver. Moreover, the predominant wave activities contribute the littoral longshore flows from Southern Tamil Nadu make the seashores as a most potent landform of the territory [25]. The sub-zones D, E, and F show that more accretion has dominated during this period 1968 - 1997. These subzones accretions are 0.43 km2,0.32 km20.43 \mathrm{~km}^{2}, 0.32 \mathrm{~km}^{2}, and 0.49 km20.49 \mathrm{~km}^{2}, respectively (Table: II and Fig - 3). While lesser amounts of erosions observed in gird E and F. The amount of erosions is 0.008 km20.008 \mathrm{~km}^{2} and 0.005 km20.005 \mathrm{~km}^{2}. However, there is no erosion in gird D due to the accumulation of sediment deposition along the
coast. The sub-zones D has 0.43 km20.43 \mathrm{~km}^{2} of net growth accretion. The growth rate of 14.84 m2/14.84 \mathrm{~m}^{2} / year noticed. However, gird E, net growth of accretion is 0.32 km2\mathrm{km}^{2} with a growth rate of 10.88 m2/10.88 \mathrm{~m}^{2} / year between the period 1968 - 1997. In F sub-zones, amount net growth is 0.49 km20.49 \mathrm{~km}^{2} with a growth rate of 16.80 m2/\mathrm{m}^{2} / year during the period 1968 - 1997 (Table: II). Overall girds result reveal that, in Punnaikayal zone, has more amount of accretion and less amount of erosion. This zone’s total amount of accretion is 1.70 km21.70 \mathrm{~km}^{2} and erosion is 0.01 km20.01 \mathrm{~km}^{2} during the period 1968 - 1997 (Table: III). The Zone has accreted by 1.92 km21.92 \mathrm{~km}^{2} of net growth with a rate of 66.27 m2/66.27 \mathrm{~m}^{2} / year during this period (Table: IV and Fig - 5).
4) Shoreline Change of Punnaikayal zone during the period 1997 - 2018.

In sub-zones D, more accretion (0.44 km2)\left(0.44 \mathrm{~km}^{2}\right) observed during 1997 - 2018. D sub-zones covered with Palayakkayal coast area. In sub zone D, erosion (0.13 km2)\left(0.13 \mathrm{~km}^{2}\right) perceive along the coast of this gird (Fig -6 (D)) during the period 1997 - 2018. The net growth of accretion is 0.30 km20.30 \mathrm{~km}^{2}, with a rate of 14.44 m2/\mathrm{m}^{2} / year. The subzone E noticed with the erosion of 0.47 km20.47 \mathrm{~km}^{2}, net growth of erosion is −0.47 km2-0.47 \mathrm{~km}^{2} during the period 1977 - 2018. The growth rates are -22.20 m2/\mathrm{m}^{2} / year. In sub-zones F , the accretion (0.004 km2)\left(0.004 \mathrm{~km}^{2}\right) has noticed, and 0.205 km20.205 \mathrm{~km}^{2} of erosion was observed (Table: II and Fig - 4). Subzone F has 0.20 km20.20 \mathrm{~km}^{2} of net growth of accretion with a growth rate of 9.56 m2/\mathrm{m}^{2} / year during the period 1997 - 2018 (Table: II). Overall results of these subzones reveal that the zone has shown both an erosion and accretion during the period 1997 - 2018. The total amount of Punnaikayal zone’s erosion is 0.61 km20.61 \mathrm{~km}^{2} and accretion is 0.64 km20.64 \mathrm{~km}^{2} (Table: III). The zone has a net growth of 0.04 km20.04 \mathrm{~km}^{2} with a rate of 1,81 m2/1,81 \mathrm{~m}^{2} / year during this period (Table: IV and Fig - 5).

Gird wise Shoreline Change Analysis

Tuticorin and Punnaikayal Zone Erosion and Accretion
Periods Sub zones Erosion (km2)\left(\mathbf{k m}^{2}\right) Accretion (km2)\left(\mathbf{k m}^{2}\right) Net growth (km2)\left(\mathbf{k m}^{2}\right) Growth rate (m2/year)\left(\mathbf{m}^{2} / \mathbf{y e a r}\right)
1968−1997\mathbf{1 9 6 8} \mathbf{- 1 9 9 7} A 0.020 0.584 0.563 19.424
B 0.650 1.110 0.460 15.865
C 0.149 1.526 1.377 47.490
D - 0.430 0.430 14.835
E 0.008 0.324 0.315 10.877
F 0.005 0.493 0.487 16.804
1997- 2018 A 0.097 0.029 −0.068-0.068 −3.258-3.258
B 0.298 0.848 0.550 26.213
C 0.042 0.704 0.663 31.551
D 0.131 0.435 0.303 14.444
E 0.466 - −0.466-0.466 −22.197-22.197
F 0.004 0.205 0.201 9.560

img-1.jpeg

img-2.jpeg

Fig - 2: Sub zones A - F, Shoreline Change Analysis maps

B. Shoreline changes for a period of 1968-1997 and 1997-2018

The shoreline changes in increasing and decreasing trend of sand supply study to be done over a long period. Geologically, Thoothukudi coast comes under from Pleistocene_new age [19]. He has also pointed out that the beach materials of sand, gravel are deposited along this coast due to wave action and currents of backshore [19]. The sea level has to lie down in Thoothukudi coast, because of the seafloor developing by the neo-tectonic activity [20]. The study concludes that accretion dominated between the period 1968 - 1997. While, during period 1997 - 2018, an accretion process decreased in both the zones. In Tuticorin zone, the net accretion is reduced from 2.40 km 2 to 1.15 km 2 with a decreasing rate of 69.63 m2/69.63 \mathrm{~m} 2 / year to 54.41 m2/\mathrm{m} 2 / year. Whereas, in Punnaikayal zone, net accretion is diminished from 1.23 km 2 to 0.04 km 2 with a growth rate of reduced from 42.52 m2/42.52 \mathrm{~m} 2 / year to 1.81 m2/1.81 \mathrm{~m} 2 / year (Table: IV and Fig 5). These results
indicate that Tuticorin and Punnaikayala zones are under the reduced accretion process.
img-3.jpeg

Fig - 3 Shoreline Change During 1968 - 1997

img-4.jpeg

Fig - 4 Shoreline Change During 1997 - 2018
Table: III
Zone wise Shoreline Change Analysis

Erosion and Accretion between Tuticorin and Punnaikayal zone
Period s Zones Erosio n\mathbf{n} (km2)\left(\mathbf{k m}^{2}\right) Accretio n(km2)\mathbf{n}\left(\mathbf{k m}^{2}\right) Net growt h (km2)\left(\mathbf{k m}^{2}\right) Growth rate (m2/ yea \left(\mathrm{m}^{2} / \text { yea }\right. r)
1968−1997\begin{gathered} 1968- \\ 1997 \end{gathered} Tuticorin 0.819 3.220 2.401 82.779
Punnaikay al 0.014 1.247 1.233 42.515
1997−2018\begin{gathered} 1997- \\ 2018 \end{gathered} Tuticorin 0.436 1.581 1.145 54.506
Punnaikay al 0.601 0.639 0.038 1.807

Table: IV
Shoreline change Growth Rate BetweenTuticorin and Punnaikayal

Zone During 1968 - 1997 During 1997 - 2018
Net growth (km2)\left(\mathbf{k m}^{2}\right) Growth rate (m2/ year )\left(\mathrm{m}^{2} / \text { year }\right) Net growth (km2)\left(\mathbf{k m}^{2}\right) Growth rate (m2/ year )\left(\mathrm{m}^{2} / \text { year }\right)
Tuticorin 2.401 82.779 1.145 54.506
Punnaikayal 1.233 42.515 0.038 1.807

img-5.jpeg

Fig - 5 variations of Net growth Rate between the periods 1968 - 1997 and 1997 - 2018
img-6.jpeg
(A)Jetties Constructed along the Threspuram Coast
img-7.jpeg
(B) InigoNager Developed along the Tuticorin coast

img-8.jpeg
© Curve Shape of Coast in Thermal Quarters Camp 2
img-9.jpeg
(D) Erosion in Palayakkayal Coast

Fig - 6 (A-D) Erosion and deposition between the Tuticorin and Punnaikayal zones

IV. CONCLUSION

The study carried out to assess the coast zone changes between Tuticorin and Punnaikayal zones in part of Thoothukudi coast. The study concludes that the Urban area of Tuticorin zone has noticed with accretion results and Punnaikayal zone also noticed with accretion results due to both natural and human interventions during the period 1968 1997. In 1997 -2018, the accretion results indicate that it is in reducing condition. It indicates that these zones continuously reducing their accretion process. It indicates the erosion activity started in this zone. The study concludes that these zones to be protected from erosion activities.

ACKNOWLEDGEMENT

We thank Centre for Applied Geology for providing facilities; the authors are also thankful to the USGS for providing Satellite data.

REFERENCES

[1] R. Welch, M. Remillard, J. Alberts, “Integration of GPS, remote sensing, and GIS techniques for coastal resource management,” Photogrammetric Engineering Remote Sensing, Vol.58, no. 11, pp.1571-1578, 1992
[2] H. VanStokkom, G. Stokman and J. HOVENIER, “Quantitative use of passive optical remote sensing over coastal and inland water bodies,” International Journal of Remote Sensing, vol. 14, no. 3, pp. 541-563, 1993. Available: 10.1080/01431169308904356.
[3] P. Mujabar and N. Chandrasekar, “Shoreline change analysis along the coast between Kanyakumari and Tuticorin of India using remote sensing and GIS,” Arabian Journal of Geosciences, vol. 6, no. 3, pp. 647-664, 2011. Available: 10.1007/s12517-011-0394-4.
[4] M. Hemer, X. Wang, J. Church and V. Swail, “MODELING PROPOSAL: Coordinating Global Ocean Wave Climate Projections”, Bulletin of the American Meteorological Society, vol.91, no. 4, pp. 451 - 454, 2010. Available: 10.1175/2009bams2951.1.
[5] M. Dobrynin, J. Murawsky and S. Yang, “Evolution of the global wind wave climate in CMIP5 experiments,” Geophysical Research Letters, vol. 39, no. 18, pp.L18606, 2012. Available: 10.1029/2012gl052843.
[6] P. K. Bhaskaran, N. Gupta, and M. K. Dash, “Wind-wave Climate Projections for the Indian Ocean from Satellite Observations,” Journal of Marine Science: Research & Development, Vol.1, no.11, pp.S11:005. Mar 2014. doi:10.4172/2155-9910.S11-005.
[7] A. Patra and P. K. Bhaskaran, “Trends in wind-wave climate over the head Bay of Bengal region,” International Journal of Climatology,

Vol.36, no.36, pp.4222-4240, 2016. Available: 10.1002 /joc. 4627.
[8] P. R. Shanas, and V. Sanil Kumar, “Temporal variations in the wind and wave climate at a location in the eastern Arabian Sea based on ERA-Interim reanalysis data,” Natural Hazards and Earth System Sciences, Vol.14, no.5, pp.1371-1381, 2014.
[9] Wu. Lingli, Qin. Jie, Wu. Teng, and Li. Xing, “Trends in global ocean surface wave characteristics as represented in the ERA-Interim wave reanalysis for 1979-2010,” Journal of Marine Science and Technology, Vol.23, no.1, pp.2-9, 2017. Doi: 10.1007/s00773-017-0450-1.
[10] A. S. Genz, C. H. Fletcher, R. A. Dunn, L. N. Frazer, J. J. Rooney, “The predictive accuracy of shoreline change rate methods and along shore beach variation on Maui, Hawaii,” Journal of Coastal Research. Vol.23, no.1, pp.87-105, 2007. http://dx.doi.org/10.2112/05-0521.1.
[11] M. Ford, “Shoreline changes on an urban atoll in the central pacific ocean: majuro atoll, Marshall Islands,” Journal of Coastal Research, Vol.28, no.1, pp.11-22, 2012. http://dx.doi.org/10.2112/JCOASTRES-D-1100008.1.
[12] M. Ford, “Shoreline changes interpreted from multi-temporal aerial photographs and highresolution satellite images: Wotje Atoll, Marshall Islands,” Remote Sensing of Environment. Vol.135, pp. 130 - 140, 2013. http://dx.doi.org/10.1016/j.rse.2013.03.027.
[13] K. Jacob, “Ilmenite and garnet sands of the Chowghat (west coast), Tinnevelly, Ramnad and Tanjore coasts (East coast),” Roc GeolSurvInd, Vol.82, no. 4 pp.567-602, 1956.
[14] T. M Rao, “Rec. of Geological Survey of India,” General Report, Vol.92, pp.39-40, 1957.
[15] H. N. Siddique, G. V. Rajamanickam, “Surficial mineral deposits of the continental shelf of India,” Seminar on Offshore mineral resources, Orleans France, 23 - 27th Oct 1978, pp.233-254.
[16] M. Chockalingam, “Coastal geomorphological studies of the region subtended
between Mandapam and Devipattinam, TamilNadu,” Ph.D., Thesis report, Tamil University, Thanjavur, 1993, pp. 117.
[17] D. O. Eulie, D. R. Corbett, & J. P. Walsh, “Shoreline erosion and decadal sediment accumulation The Estuaries contain emulation in the Tar-Pamlico estuary, North Carolina, USA: A source-to-sink analysis,” Estuarine, Coastal and Shelf Science, Vol.202, pp.246-258, 2018. https://doi.org/10.1016/j.ecss.2017.10.011
[18] T. H. van Andel, K. O. Emery & D. G. Aubrey 1991. “Sea Levels, Land Levels, and Tide Gauges. Xiv 237 pp. Berlin, Heidelberg, New York, Paris, London, Tokyo, Hong Kong: Springer-Verlag. Price DM 118.00 (hardcovers). ISBN 354097449 0.,” Geological Magazine, vol.129, no.6, pp. 796797, Nov 1992.
[19] K. Dharanirajan, M. Thanikachalam, B. Gurugnanam, “Remote Sensing and GIS for the study of Coastal Ecosystem changes and its conservation,” International Journal of Earth Science and Engineering, Vol.3, no.4, pp.512-524, 2010.
[20] S. Kumaravel, T. Ramkumar, B. Gurugnanam, M. Suresh, “Quantitative estimation of shoreline changes using remote sensing and GIS: A case study in the parts of Cuddalore district, East coast of Tamil Nadu, India,” International Journal of Environmental Sciences, Vol.2, no.4, pp.2482-2490, 2012.
[21] G. Winarso, S. Budhiman, “The potential application of remote sensing data for coastal study,” Proc. 22nd, Asian conference on remote sensing, Singapore, May 2012.
[22] M.G. Shaikh, S. R. Nayak, P. N. Shah, and B. B. Jambusaria, “Coastal landform mapping around the Gulf of Khambhat using Landsat TM data,” Journal of Indian Society of Remote Sensing, Vol.17, no.1, pp.41-48, 1989a.