Abstract
Water is an essential resource for sustaining human life. The ever-increasing demand for clean water from the
growing human population and other anthropogenic needs have pushed several regions into highly water-
stressed areas. Diminishing freshwater resources and high amounts of water contamination are increasing the
threat of severe water scarcity even further. Since the total available freshwater resources cannot be modified,
the options are to maintain and/or improve water quality in water bodies and increase the reusability of the
water. The former can be achieved by continuous monitoring of the water quality in the water bodies and
identifying and regulating the source of contaminations that pollute these water bodies. So, water quality in
rivers and large inland water bodies are being measured occasionally through in-situ approaches. While these
do provide valuable inputs, they are not sufficient to understand the underlying causes for such changes in
water quality, including the seasonal and other drivers of contamination. Hence, there is a need to monitor
water bodies, especially the lakes and reservoirs, regularly. Constant inflows and long storage time of water
with limited or no proper outflow make these water bodies much more susceptible to the adverse effects of
contaminants than rivers.
This study takes a three-pronged approach to study and understand the water quality in inland water bodies –
first, by developing and evaluating a methodology for monitoring nutrient contamination and its changes in
inland water bodies using remote sensing satellite data; second, to hypothesize and study the probable source
of the contamination as land use and its practices; and three, to understand, analyze and model the interactions
between the land use changes in the contributing watershed and the water quality to help improve the regional-
scale decision making capabilities. The case study area is Nagarjuna Sagar (NS) reservoir in the Krishna River
basin, one of the largest inland water bodies in India. NS is a multipurpose dam and inland water body (reservoir)
with a spatial spread of 285 Km2 and a catchment area of 215,000 Km 2 . In addition to Irrigation and Power
generation, it is also a primary source of drinking water to Hyderabad, a large metropolis in India with nearly
10million population. All these make it essential to study and maintain the water quality of the NS water body.
While the literature suggests that the remote sensing approach can help monitor the nutrient content in the water
body, most studies and analyses have been done for oceans, seas, and enormous water bodies. Their application
to inland water bodies is still a challenge due to the spatial and spectral limitations of the remote sensing sensors.
Hence, the study explored the effectiveness of the remote sensing data in studying the inland water body
nutrient contamination. Here, the presence and spatial spread of Chl-a, a remote sensing detectable agent,
present in the photosynthetic organisms such as algae, phytoplankton, and cyanobacteria (AP) was used as a
proxy for monitoring nutrient contamination in water bodies. The unique spectral signature of Chl-a was used
to detect and identify its spatial spread across the water body. For this process, a decision-tree-based
classification technique was developed that exploits the spectral response peaks within the region of 705nm to
860nm for each pixel to detect and classify them into No to Low contamination, Moderate and High Chl-a
levels. The spatial spread of moderate and high Chl-a areas was used to understand the severity of the
contamination in the water body. Further, through meta-analysis and comparative study, it was found that
MODIS and Sentinel satellite data are best suited for the detection of Chl-a content in the water body using the
spectral signature-based method. While various works have well-studied MODIS data, Sentinel data is
relatively recent and needs to be tested for its sensitivity towards Chl-a across various concentrations of Chl-a
in water bodies situated in different environments. Since the NS water quality data is not available, it is prudent
to use the water quality data from earlier published studies to evaluate the method. As part of this, Lake Taihu
(TL, with an area of 2250 Km 2 ) and Lake Bebe (LB, with an area of 24 Km 2 ) with different concentrations of
Chl-a were used to test the sensitivity of the method. The Manasarovar Lake (ML) (area of 411 Km 2 ) was used
as a zero baseline case as it is free of any Chl-a contamination to check if the method was working without any
false positives. The results from TL showed that more than 50% of the water body indicates the presence of
Chl-a content which matched with the data given in the literature.
Similarly, the method could not detect any Chl-a content in the ML, which agrees with the literature but showed
some limitations in the case of LB. On applying