Monitoring Shoreline Changes in the Gulf of Khambhat, India During
Transcription
Monitoring Shoreline Changes in the Gulf of Khambhat, India During
OPEN JOURNAL OF REMOTE SENSING AND POSITIONING VOLUME 1, NUMBER 1, JUNE 2014 OPEN JOURNAL OF REMOTE SENSING AND POSITIONING Monitoring Shoreline Changes in the Gulf of Khambhat, India During 1966-2004 Using RESOURCESAT-1 LISS-III Mukesh Gupta1,2 * 1 4141, Earth Sciences and Hydrology Division, Marine and Earth Sciences Group, Remote Sensing Applications and Image Processing Area, Space Applications Centre, Indian Space Research Organisation, Ahmedabad 380 015, Gujarat, India. 2 463, Wallace Building, Centre for Earth Observation Science, Department of Environment and Geography, Clayton H. Riddell Faculty of Environment, Earth, and Resources, University of Manitoba, Winnipeg R3T 2N2, Manitoba, Canada. *Corresponding author: [email protected] Abstract: This paper provides an assessment of the shoreline changes, which occurred during 1966 2004 in the coastal regions of the Gulf of Khambhat using RESOURCESAT-1 LISS-III (Linear Imaging Self Scanner) data. The remote sensing observations of the Gulf show a large area facing a serious threat due to dramatically changing shorelines. The entire coast around the Gulf has undergone accretion except some parts of the northern region and a few areas near the Mahi and Dhadhar estuaries where erosion is observed. These significant landform changes have occurred in four decades. The study has also shown the potential of the enhanced radiometric resolution satellite remote sensing data to be utilized for preparing good quality cartographic maps with improved shorelines leaving behind old maps prepared using conventional geodetic/ground surveys. The detection/quantification of shoreline change in the Gulf of Khambhat using advanced/latest models is proposed as an avenue of further research. Keywords: Coastal processes; Erosion; Gulf of Khambhat; Remote sensing; RESOURCESAT-1 LISS-III; Shoreline change 1. INTRODUCTION Shoreline change subsequent to global warming of the planet and tidal forcing is a serious concern for the security of life and property around the world. Several natural and human-induced coastal hazards affect the Indian coast, modify the coastal processes operating in the region, and need to be monitored regularly. The Gulf of Khambhat (earlier known as Gulf of Cambay) in the Indian subcontinent has been an ancient center for trade with the maritime routes to Arabian Sea and Indian Ocean and has notably undergone tremendous industrial developments after the colonial independence in 1947. Major ports of Bharuch, Bhavnagar, Daman, Khambhat, and Surat lie in this region. The erosion/accretion along the coastline of the Gulf is predominant due to semi-diurnal tidal effects [1–3], which make the shoreline in this region vulnerable to changes. It is also one of the major fishing areas along the Gujarat coast. Several inlets and creeks formed by the confluence of Mahi, Narmada, and Shetrunji Rivers characterize the Gulf 27 OPEN JOURNAL OF REMOTE SENSING AND POSITIONING [4]. A full understanding of shoreline changes requires understanding of the regional coastal processes, tidal inputs in the region, recognizing coastal hazards, identifying vulnerability, mapping zones of risks, developing site specific mitigation techniques including preservation, augmentation, and restoration of natural environment, and monitoring implementation of mitigation recommendations [5]. Integrated coastal zone management and regulation of activities in the coastal zone have been adopted for the Indian coast [6, 7]. The coastal region of Gulf of Khambhat and Gujarat state as a whole have undergone dramatic geomorphological changes due to changing shorelines since ancient times. These changes have impacted many civilizations in the last 10,000 years, and are also evidenced through archaeological findings [8]. The shoreline of Gulf of Khambhat area is predominantly a low lying flat, land packed with river mouths, creeks, estuaries, backwaters, mangroves, deltas, swales, mudflats, saltpans, etc. The anticipated sea-level rise due to global warming is expected to flood these coastal zones [9]. Many geological and geomorphic evidences show that the changes in sea-level lead to significant physical changes to shorelines particularly softer sandy shores as the coast adjusts to changing water levels. These physical changes including shoreline erosion and increased flooding may expose coastal buildings, roads, and other infrastructure to damage; hence, there is a need to identify coastal areas vulnerable to such changes to be able to effectively plan coastal developments [5]. Changes in the mean sea-level relative to the land are prone to the initiation or acceleration of significant landform changes in the Gulf of Khambhat region. The shoreline of the Gulf of Khambhat is a part of the dynamic coastal zone that experiences opposing winds and the associated onshore coastal currents during July, which traps the freshwater in the Gulf region. Low-salinity plumes emerging from Gulf of Khambhat during post-monsoon have been discovered, though, there is no river discharge during this period [10]. Besides, sediment dynamics and geomorphological changes occurring in the Gulf of Khambhat, the eutrophication and biological productivity are also dramatically affected by the discharge brought by the three estuaries; i.e. Mahi, Narmada, and Sabarmati [11]. Since the advent of satellite remote sensing, coastal monitoring has become much simpler and efficient. Remote sensing and geo-information techniques for the Indian coast have proven to be one of the extremely useful tools for understanding coastal processes and hazards [12–14]. Satellite data have also proved to be useful in creating baseline inventory of the entire Indian coastline at 1:250,000, 1:50,000, and 1:25,000 scales [15–17]. Previous studies show wetland features between high and low water lines and land use features of the adjoining shore (up to 1.5 km from high water line). Researchers [15–17] carried out the shoreline change mapping (1967 1968, 1985 1989, 1990 1992 periods) for the entire Indian coast using Landsat MSS/TM and IRS LISS II (7-bit quantization) data on 1:250,000 and 1:50,000 scale. In this paper, the shoreline changes for a period 1966 2004 are reported with an objective to infer geomorphological evolution of shoreline in the Gulf of Khambhat to facilitate adequate coastal management plans in the region, and to demonstrate the improved radiometric resolution (10-bit) capability of RESOURCESAT-1 LISS-III to delineate shoreline around the Gulf of Khambhat. 2. MATERIALS AND METHODS 2.1 Study Area The Gulf of Khambhat, Gujarat, lies in the west coast of India and north of Arabian Sea between 20 000 N 22 300 N, and longitude 71 000 E 73 000 E (Figure 1). It is about 80 km wide at the mouth and less than 25 km in the interior. The longitudinal stretch of the Gulf is about 140 km. The tidal flats and tidal creeks cover this entire coastal region. Major rivers of Mahi, Narmada, and Sabarmati, and many 28 Monitoring Shoreline Changes in the Gulf of Khambhat, India During 1966-2004 Using RESOURCESAT-1 LISS-III Table 1. Major specifications of RESOURCESAT-1 LISS-III. System Parameter Value Spectral bands 0.52–0.59 µ 0.62–0.68 µ 0.77–0.86 µ 1.55–1.70 µ (SWIRa ) Spatial resolution 23.5 m Swath 141 km Band2: 28–31 Saturation radiance Band3: 26–28 (mw/cm2 /sr/µ) Band4: 27–30 Band5: 7.5 Integration time 3.32 ms Quantization 7-bit; 10-bit (SWIR) a SWIR: Shortwave infrared. other rivulets are the sources of freshwater to the Gulf. The Gulf is shallow with depths up to 30 m in the middle. The seawater is highly turbid containing very high concentrations of suspended sediments due to strong tidal mixing and re-suspension of sediments. 2.2 Data Used The imagery used in the study is a cloud- and haze-free RESOURCESAT-1 LISS-III imagery of 27 March 2004 from different regions of the Gulf. The Indian satellite, RESOURCESAT-1 [also known as IRS (Indian Remote Sensing Satellite)-P6], launched on 17 October 2003 carried LISS-III (Linear Imaging Self Scanner) among various other sensors (Table 1). The satellite was launched by PSLV (Polar Satellite Launch Vehicle)-C5 rocket into a Sun-synchronous orbit at an altitude of 817 km and the equatorial crossing time is 10:30 am (Indian Standard Time). The atmospheric correction of the images is not considered as it is assumed that the changes in the top of atmosphere remained uniform over the whole study area and are not a major consideration for shoreline mapping. Old topographical maps prepared by Survey of India (SOI) and RESOURCESAT-1 LISS-III ‘precision geocoded’ (Level 3 accuracy 100 m) satellite data products are used to interpret shoreline at 150 ⇥ 150 (28 km ⇥ 28 km) grid and to prepare a mosaic image afterwards. The SOI prepares maps based on intensive geodetic, geological, geophysical, photogrammetric, topographical, and aerial surveys. The satellite products are geocoded by the National Remote Sensing Centre (NRSC), Hyderabad, India using SOI maps and a large number of precision ground control points (GCP) as reference. These products are carefully generated after applying radiometric and geometric corrections, orthorectification, orienting the image to true north and generating the product with an output resolution, suitable to the map scale (1:50,000). The digital elevation model (DEM) used in orthorectification are derived from digitizing topographic sheets and GCPs with locational (horizontal) accuracy 25±15 m [18, 19]. For orthorectification, the locational (horizontal) accuracy according to Moorthi et al. [19] is 25 m considering 11 or more GCPs. This accuracy of 25 m is the best available for 150 ⇥ 150 coverage for this product. A maximum error of ±15 m is expected for the same. This implies that most points are centered around 25 m with a maximum deviation (if any) of 15 m on either side of mean. Precision geocoded products at 100 m accuracy are generated from these orthorectified images. This is an additional step beyond the systematic corrections. The aim of precision correction is to improve the location accuracy of the data product, i.e. latitude, longitude knowledge or the map projection coordinates of the image features in the final product [19]. The precision 29 OPEN JOURNAL OF REMOTE SENSING AND POSITIONING Khambhat Bhavnagar Dahej Gujarat Aliabet Hazira Gulf of Khambhat India Figure 1. A geographic map of the study area. geocoded products are value-added products that are thoroughly checked for misregistration, mosaicking problems, noise-related artifacts, and area coverage aside from other quality assurance such as removal of vertical striping and geometric quality. The products are available in Geographic Latitude/Longitude coordinate system with the Polyconic projection and WGS (World Geodetic System)-84 datum. Standard geocoded products have 5–6 pixel internal distortion, which is not compatible to mapping standards of 1:50,000 scale, so precision geocoded products are used for shoreline mapping. The NRSC provides an accuracy of 100 m in its precision geocoded products. The GCPs used for orthorectification (before the precision geocoded image is prepared) have an accuracy of 25 m. The precision geocoded products at 100 m accuracy are generated using these orthorectified images and supplied to users for intended applications. Thus, the final image has an accuracy of 100 m, which is also the accuracy of shoreline detection. Therefore, the accuracy of shoreline detection based on the location of GCP is 100 m; however, the pixel size in the image (spatial resolution of LISS-III) is 23.5 m. 2.3 Shoreline Extraction Technique The shoreline in the topographic sheets of 1966 1977 is extracted from the marked high water line, and the shoreline from the imagery is extracted from Band5 [shortwave infrared (SWIR-with 10-bit quantization)] of LISS-III (Table 1), because the water absorption is strongest in this region of electromagnetic spectrum rendering negligible water-leaving radiance in this band. LISS-III Band5 (1.55–1.70 µ) has an improved radiometric resolution (10-bit quantization) over previous sensors (6 or 30 Monitoring Shoreline Changes in the Gulf of Khambhat, India During 1966-2004 Using RESOURCESAT-1 LISS-III Table 2. Survey of India (SOI) topographic sheet number and the year of survey. SOI topographic Year of survey sheet number 46 B7 1966 1967 46 B8 1977 46 B11 1971 1972 46 B12 1971 1972 46 C1 1966 1967 46 C9 1971 1972 46 C10 1971 1972 46 C11 1970 1972 46 C14 1972 1973 7-bit). Due to its enhanced radiometric resolution at 23.5 m spatial resolution, Band5 can be a good discriminator of land and turbid seawater boundary. A complete post-launch data quality evaluation (DQE) (radiometric and geometric) was performed during calibration mode of acquisition (commissioning). Inflight LED (light emitting diode)-based calibration was programmed during night pass in real-time. Onboard calibration data are compared with the ground reference data to perform radiometric calibration. The digitization (on-screen drawing of the shoreline) was carried out to retrieve shoreline from the imagery. An aggregate of 10 satellite images of the same date were used that corresponded with SOI map numbering scheme. These maps/images were 46 (B7, B8, B11, B12), C1, C9, C12, (C10, C11, and C14) (Table 2). The NRSC provided satellite imageries (only the shoreline area) for each identified SOI map section. Each section image, e.g. C10, C14, etc. is exactly the same size of the corresponding SOI topographic sheet. Some of the images were mosaicked according to the map sections grouped in brackets above. No inconsistency was observed in the borders of mosaicked images. A broad approach followed includes, a) Creation of digital shoreline maps (using the existing coastal thematic maps prepared at 1:50,000 scale from SOI topographic sheets 1966 1977 and satellite image); and b) Overlaying of high water shoreline onto the shoreline derived from the satellite images. The shoreline extracted from topographic sheets is also overlaid onto the false color composite (FCC) (R4:G3:B2) images of the corresponding map sections and is visually inspected for comparison. 3. RESULTS During 1966 2004, most areas along the coastline of the Gulf have undergone accretion including coastal region around Tapi and Mindhola estuaries, and Hazira port (Figure 2). The main reasons behind this accretion are attributed to the strong tidal currents and a large load of sediments brought through the major rivers; i.e. Dhadhar, Mahi, Narmada, and Sabarmati Rivers. Figure 3 provides a mosaic of all the segments of topographic sheets (in blue) overlaid by the shoreline derived from the satellite data of 27 March 2004 (in red) showing accretion in most areas except some parts of the northern Gulf. Rajawat et al. [14] utilized the IRS-P4 OCM (Ocean Color Monitor) data with temporal resolution of two days and 360 m spatial resolution to understand regional sediment dynamics according to the flooding and ebbing tides. They observed that the sediments as well as pollutants under the influence of strong tidal currents underwent dispersion and settled within the Gulf of Khambhat resulting in siltation at a rapid rate. It is evident from LISS-III data that the entire coast around the Gulf of Khambhat shows accretion except the northern region and a few areas near northern parts of the Mahi and Narmada estuaries (Figure 31 OPEN JOURNAL OF REMOTE SENSING AND POSITIONING Gulf of Khambhat Hazira Tapi estuary Mindhola estuary 46 C12 High Water Line 10 km 0 Figure 2. RESOURCESAT-1 LISS-III (false color composite, R4:G3:B2) image of a section of Gulf of Khambhat overlaid by high water line (in yellow) derived from topographic sheets of 1970 1972 (map section 46 C12). Also shown are the locations of Hazira port, Mindhola, and Tapi estuaries. 73ºE 72ºE B7 B B11 Khambhat B12 B1 Mahi estuary B8 22ºN Dhadhar estuary C9 C1 Bhavnagar Dahej Narmada estuary Aliabett C10 C14 C11 Hazira C12 Tapi estuary 21ºN Figure 3. Shoreline changes derived from RESOURCESAT-1 LISS-III (27 March 2004) and SOI topographic sheets during 1966 1977. Each grid has the same size as that of a precision geocoded image. Accretion is observed in almost entire coastline of the Gulf of Khambhat. The SOI topographic map sections are also shown. Bolded line segments are the edges of mosaics of the corresponding images. 32 20 km 0 B7 B11 B8 B12 46 Sa ba rm ati R. Monitoring Shoreline Changes in the Gulf of Khambhat, India During 1966-2004 Using RESOURCESAT-1 LISS-III Khambhat Mahi estuary High Water Line Gulf of Khambhat Figure 4. RESOURCESAT-1 LISS-III (false color composite, R4:G3:B2) image of a section of Gulf of Khambhat overlaid by high water line (in yellow) derived from topographic sheets of 1966 1977 (map sections 46 B7, B8, B11, and B12). Also shown are the locations of Khambhat city, Mahi estuary, and Sabarmati River. A large area of land has eroded. 4). Figure 5 shows that a large area of land is vulnerable to flooding as depicted by high water line drawn from topographic sheets of 1966 1977. This accretion area, formed in about 40 years, now includes several saltpans around the outer limits of Bhavnagar city. A large area, which is unoccupied by industrial developmental activities and human settlement around Dhadhar estuary, is under heavy siltation evident from LISS-III observations. A large accretion around north of Dhadhar estuary is also observed (Figure 6). This accretion, which has now made the Aliabet Island accessible via land route, has occurred in four decades in the areas around Narmada estuary, and new vegetation has grown in the region (Figure 7). 4. DISCUSSION The case studies from the tide-dominated Gulf of Khambhat, Gujarat along the west coast of India are discussed. The shoreline change in the Gulf is grouped into five regions. Figures 2 7 show in details, the erosion/accretion that has occurred in each of the regions. It may be understood that even without substantial sea-level rise and climate change, coasts can undergo significant geomorphological changes over relatively short periods of time. Such changes may be continuous and progressive (e.g., the long term physical adjustment of shorelines to the last-glacial sea-level that stabilized at roughly its present level around 6,500 years ago), or it may be episodic and non-linear (e.g., repeated major adjustments of sandy shores to occasional periods of more frequent than usual storm activity). Human modification of shores and coastal processes, through construction of sea walls, groynes, breakwaters, jetties, and in many other ways also cause physical changes to shorelines often in ways that are not expected and many modified shorelines are continuing to adjust in response to such disturbances. Hence, a wide range of coastal hazards including flooding and coastal erosion have posed risks to human coastal infrastructure and other assets throughout history, often for reasons unrelated to shoreline change. 33 OPEN JOURNAL OF REMOTE SENSING AND POSITIONING High Water Line 46 C1 Bhavnagar 10 km 0 Figure 5. RESOURCESAT-1 LISS-III (false color composite, R4:G3:B2) image of a section of Gulf of Khambhat overlaid by high water line (in yellow) derived from topographic sheets of 1966 1967 (map section 46 C1). Also shown is the location of Bhavnagar city. Devajagan Dhadhar estuary Gulf of Khambhat 46 C9 10 km 0 Figure 6. RESOURCESAT-1 LISS-III (false color composite, R4:G3:B2) image of a section of Gulf of Khambhat overlaid by high water line (in yellow) derived from topographic sheets of 1971 1972 (map section 46 C9). Also shown is the location of Dhadhar estuary. 34 Monitoring Shoreline Changes in the Gulf of Khambhat, India During 1966-2004 Using RESOURCESAT-1 LISS-III Dahej Narmada estuary Aliabet island High Water Line 20 km Gulf of Khambhat 0 C10 C14 46 C11 Figure 7. RESOURCESAT-1 LISS-III (false color composite, R4:G3:B2) image of a section of Gulf of Khambhat overlaid by high water line (in yellow) derived from topographic sheets of 1970 1973 (map sections 46 C10, C11, and C14). Also shown are the locations of Aliabet Island, Dahej port, and Narmada estuary. It is important to circumspect that shoreline change and climate change are not the only causes of coastal hazards; however, the anthropogenic shoreline change (including agricultural growth, ports and harbor development) that accelerated during the past century or so has added a major new factor into the complexity of natural processes determining coastal landform changes. Coastal flooding and erosion hazards are likely to increase due to the shoreline change and climate change. The Gulf of Khambhat is a part of the widest continental shelf on the west coast of India. Mumbai is located in the southeastern and Veraval in the southwestern corner of the region and the entire coastline around the Gulf has undergone large industrial and urban growth. The proposed developmental activities such as the Kalpasar project which aim to create a freshwater reservoir by closing off the Gulf itself and use the large tidal range to generate power add to the importance of the region. The Gulf is a strongly converging channel experiencing tides with large amplitudes. The tide amplitude range in this region is 8–11 m with tidal current velocities as high as 10 m/s. The large tidal ranges give rise to strong tidal currents and provide a mechanism for transport of suspended sediments in the Gulf of Khambhat. The net transport of sediments is toward land as evidenced by extensive mudflats [15, 16]. Though, during 2000 2010, the understanding of the impacts of sea-level rise on the shorelines has advanced greatly, the linkages between sea-level rise and the shoreline response still lack a thorough understanding. The Gulf of Khambhat exemplifies significant erosion/accretion due to causes including sea-level changes and tidal forcing in this region. The changes that occurred in four-decade period, as shown in this paper, produce an evidence of this fact. A shoreline retreat model that considers tidal forcing as main constituent can further help quantify the erosion/accretion. The Bruun Rule [20], a two-dimensional model of shoreline response to sea-level rise, is not applicable in the Gulf of Khambhat. This Rule is abandoned because it ignores various important geological and oceanographic principles [21]; e.g., tidal forcing, which dominate in the Gulf. The model-based analysis and computation of shoreline change, however, is outside the focus of this paper. 35 OPEN JOURNAL OF REMOTE SENSING AND POSITIONING The sharp delineation capability of RESOURCESAT-1 LISS-III Band5, having an improved radiometric resolution of 10-bit, provided a much better data source over previous satellite data (7-bit) for shoreline delineation studies [12]. Such type of high radiometric and spatial resolution data make a promising candidate for preparing satellite-based cartographic digital maps with much better accuracy than that achieved through conventional ground surveys. It is also a prerequisite in studies such as shoreline change detection at high temporal and spatial scales. 5. CONCLUSION The present work included an assessment of the geomorphological changes that occurred during 1966 2004 in the coastal regions of the Gulf of Khambhat using satellite remote sensing techniques. It is alarming that the entire coast around the Gulf of Khambhat has undergone accretion except some parts of northern region and few areas near the Mahi and Dhadhar estuaries where erosion has occurred. These significant geomorphological and landform changes have merely occurred in past four decades (1966 2004). In the current context, the model-based analysis, and quantification of the eroded/accreted areas is not provided; which can be a topic of future work for micro planning of the industrial infrastructure and coastal tourism development. Quantified information (mainly restricted to Government of India use) of the areas of vulnerability with a timeline is a requirement for integrated coastal zone management, inundation measures and its impact on human settlement and crops. The detection/quantification of shoreline change in the Gulf of Khambhat using advanced/improved models is proposed as an avenue of further research. This study has also shown a potential of the enhanced radiometric resolution satellite remote sensing data to be utilized for preparing better cartographic maps with improved shorelines leaving behind conventional geodetic/ground surveys. With the NRSC having started producing ‘precision geocoded’ products for coastal regions, India is prepared to venture into the enhanced resolution digital cartography era. ACKNOWLEDGEMENTS The author expresses gratitude to the Director, Space Applications Centre (Indian Space Research Organisation, Department of Space, Government of India), Ahmedabad, India for providing necessary data and facilities. Many thanks are due to Dr. Shailesh R. Nayak, SAC (now at Ministry of Earth Sciences, Government of India) for his leadership during this project. References [1] A. S. Unnikrishnan, S. R. Shetye, and G. S. 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