Shuvankar Ghosh

Dr. Shuvankar Ghosh

Iora Ecological Solutions, New Delhi, Delhi, International
orcid

Research Focus & Metrics

Academic Career Length

15Years (2012-Present)

(Calculated once Scilit publication data is synced: current year − year of first publication + 1)

Representative Publications

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1 February 2016 in Remote Sensing of Environment
Verified
Journal Article
Closed access
SGShuvankar Ghosh
Shuvankar Ghosh
Deepak MishraDeepak Mishra
Deepak Mishra
AGAnatoly A. Gitelson
Anatoly A. Gitelson

1 March 2012 in Remote Sensing of Environment
Verified
Journal Article
Closed access
Deepak MishraDeepak Mishra
Deepak Mishra
HCHyun J. Cho
Hyun J. Cho
SGShuvankar Ghosh
Shuvankar Ghosh
AFAmelia Fox
Amelia Fox
CDChristopher Downs
Christopher Downs
SMSachidananda Mishra
Sachidananda Mishra

20 December 2017 in Remote Sensing
Verified
Journal Article
Open access
PDF file
SGShuvankar Ghosh
Shuvankar Ghosh
Deepak MishraDeepak Mishra
Deepak Mishra
In this study, we examined the phenology of the salt marsh ecosystem across coastal Louisiana (LA) for a 16-year time period (2000–2015) using NASA’s Moderate Resolution Imaging Spectroradiometer’s (MODIS) eight-day average surface reflectance images (500 m). We compared the performances of least squares fitted asymmetric Gaussian (AG) and double logistic (DL) smoothing functions in terms of increasing the signal-to-noise ratio from the raw phenology derived from the time-series composites. We performed derivative analysis to determine the appropriate start of season (SOS) and end of season (EOS) thresholds. After that, we extracted the seasonality parameters in TIMESAT, and studied the effect of environmental disturbances/anomalies on the seasonality parameters. Finally, we performed trend analysis using the derived seasonality parameters such as base green biomass (GBM) value, maximum GBM value, seasonal amplitude, and small seasonal integral. Based on root mean square error (RMSE) values and residual plots, we selected the best thresholds for SOS (5% of amplitude) and EOS (20% of amplitude), along with the best smoothing function. The selected SOS and EOS thresholds were able to capture the environmental disturbances that have affected the salt marsh ecosystem during the 16-year time period. Our trend analysis results indicate positive trends in the base GBM values in the salt marshes of LA. However, we did not notice as much of a positive trend in the maximum GBM levels. Hence, we observed mostly negative changes in the GBM amplitude and small seasonal integral values. These negative changes indicated the overall progressive decline in the rates of photosynthesis and biomass allocation in the LA salt marsh ecosystem, which is most likely due to elevated atmospheric carbon dioxide levels and sea level rise. The results illustrate both the relative efficiency of MODIS-based biophysical models for analyzing salt marsh phenology, and performances of the smoothing techniques in terms of improving the signal-to-noise ratio of the MODIS-derived phenology.

1 May 2020 in Science of The Total Environment
Verified
Journal Article
Closed access
WWWei Wu
Wei Wu
PBPatrick Biber
Patrick Biber
Deepak MishraDeepak Mishra
Deepak Mishra
SGShuvankar Ghosh
Shuvankar Ghosh

11 May 2022 in Remote Sensing
Verified
Journal Article
Open access
PDF file
SGShuvankar Ghosh
Shuvankar Ghosh
CPChristophe Proisy
Christophe Proisy
MGMuthusankar GOWRAPPAN
Muthusankar GOWRAPPAN
CHChristiane Hassenrück
Christiane Hassenrück
HVHelfer Véronique
Helfer Véronique
RNRajendran Narendran
Rajendran Narendran
Highlighting spatiotemporal changes occurring within mangrove habitats at the finest possible scale could contribute fundamental knowledge and data for local sustainable management. This study presents the current situation of the Pichavaram mangrove area, a coastal region of Southeast India prone to both cyclones and reduced freshwater inflow. Based on the supervised classification and visual inspection of very high spatial resolution (VHSR) satellite images provided with a pixel size of 85%), which confirmed the potential of classification techniques applied to VHSR images in capturing changes in mangroves on a very fine scale. Our diagnosis reveals variable expansion rates in plantations made by the local authorities. We also report an ongoing mangrove dieback and confirm progressive shoreline erosion along the coastline. Despite a lack of field data, VHSR images allowed for the multiscale diagnosis of the ecosystem situation, thus constituting the first fine-scale assessment of the fragile Pichavaram mangrove area upon which the coastal community is dependent.

16 May 2019 in Weed Technology
Verified
Journal Article
Closed access
PDF file
AKAbhishek Kumar
Abhishek Kumar
CCChristopher Cooper
Christopher Cooper
CRCaren M. Remillard
Caren M. Remillard
SGShuvankar Ghosh
Shuvankar Ghosh
AHAustin Haney
Austin Haney
Deepak MishraDeepak Mishra
Deepak Mishra
Hydrilla is an invasive aquatic plant that has rapidly spread through many inland water bodies across the globe by outcompeting native aquatic plants. The negative impacts of hydrilla invasion have become a concern for water resource management authorities, power companies, and environmental scientists. The early detection of hydrilla infestation is very important to reduce the costs associated with control and removal efforts of this invasive species. Therefore, in this study, we aimed to develop a tool for rapid, frequent, and large-scale monitoring and predicting spatial extent of hydrilla habitat. This was achieved by integrating in situ and Landsat 8 Operational Land Imager satellite data for Lake J. Strom Thurmond, the largest US Army Corps of Engineers lake east of the Mississippi River, located on the border of Georgia and South Carolina border. The predictive model for presence of hydrilla incorporated radiometric and physical measurements, including remote-sensing reflectance, Secchi disk depth (SDD), light-attenuation coefficient (Kd), maximum depth of colonization (Zc), and percentage of light available through the water column (PLW). The model-predicted ideal habitat for hydrilla featured high SDD, Zc, and PLW values, low values of Kd. Monthly analyses based on satellite images showed that hydrilla starts growing in April, reaches peak coverage around October, begins retreating in the following months, and disappears in February. Analysis of physical and meteorological factors (i.e., water temperature, surface runoff, net inflow, precipitation) revealed that these parameters are closely associated with hydrilla extent. Management agencies can use these results not only to plan removal efforts but also to evaluate and adapt their current mitigation efforts.