1 Centre for Ecological Sciences (CES), Energy & Wetlands Research Group, Indian Institute of Science (IISc),
Bangalore 560012, India;
2 Centre for Sustainable Technologies (ASTRA), Indian Institute of Science (IISc), Bangalore 560012, India
3 Centre for Infrastructure, Sustainable Transportation and Urban Planning (CiSTUP), Indian Institute of
Science (IISc), Bangalore 560012, India
4 Ranbir and Chitra Gupta School of Infrastructure Design and Management (RCG SIDM), IIT-Kharagpur,
Kharagpur 721302, India
5 Department of Civil Engineering, SR University, Warangal 506371, India
*Corresponding author:
trv@iisc.ac.in
Introduction
The aquatic ecosystem plays a vital role in sustaining ecological processes and the basic needs of society. Ecosystem
quality varies due to natural processes (such as climatic factors, precipitation, soil erosion, weathering of rocks,
soil quality, and watershed characteristics) and anthropogenic factors such as land-use changes, overexploitation of
water resources, and agricultural practices [1,2]. During the twenty-first century, the planning, development, and
management of aquatic resources relied on human-centric factors such as population, per capita water demand,
agriculture production, and socio-economic activities [3]. Developing countries in the tropics have been facing
water stress due to large-scale land cover changes from deforestation [4,5], unplanned developmental activities, and
unprecedented and unscientific agriculture practices with extensive water abstraction [6–9]. The overexploitation of
freshwater resources to cater to burgeoning societal needs has compromised the health and sustainability of
resources in India and across the globe [10,11]. Anthropogenic activities coupled with skewed policies have resulted
in the disappearance of pristine forests [12–14] in the catchment, affecting biogeochemical dynamics [4,15–17]. The
structural changes in the catchment (landscape) have affected the functional aspects of ecosystems, thereby
impairing the assimilative and supportive capacity [18,19] of fragile ecosystems. The impacts are evident with the
recurring instances of droughts and floods and with the shortages of quality water affecting the regional economy
and people’s livelihoods [20]. The conservation of forests with native species in the catchment has helped sustain
the hydrological regime and maintain biodiversity [21].
The integrity of the catchment of aquatic ecosystems decides water sustenance, as vegetation helps in retarding the
velocity of water by allowing impoundment and groundwater recharge through infiltration. At the same time, another
fraction returns to the atmosphere through evapotranspiration. Forests with native species of plants would aid as
sponges, retaining and regulating the transfer of water between land and atmosphere [21]. The mechanism by which
vegetation controls the flow regime is dependent on various bio-physiographic characteristics, namely, the type of
vegetation, the species composition, maturity, density, structure, aerodynamic and surface resistance, root density
and depth, and the hydro-climatic conditions [22]. The roots of diverse terrestrial vegetation provide habitats for
diverse microflora and fauna, and with microbial actions, the soil has higher porosity or permeability, thereby
enabling efficient infiltration. These functions depend on the diversity and maturity of the forests, and the
density of plant species. This necessitates safeguarding and maintaining the existing native forest patches to
sustain the hydrological regime, which caters to biotic (ecological and societal) demands. An undisturbed native
forest has a consistent hydrologic regime with sustained flows during lean seasons [21,22].
Generally, ecosystems permit complex interactions among abiotic and biotic entities to recover from minor
perturbations [21–23]. It is necessary to maintain the quantity, quality, and timing of flow [23,24], which is also
known as ecological flow [25–27] across all segments of the riverine systems for the sustainable functioning of
freshwater resources. This emphasizes understanding the hydrologic regime and the consumption behavior and
transactions of resources among/between ecological and societal activities [28]. The hydrological regime sustaining
the biotic components is referred to as an eco-hydrological footprint.
The physical, chemical, and biological characteristics of aquatic ecosystems are determined by water quality
assessments [29]. The long-term and continuous monitoring of surface water bodies provides insights into the spatial
and temporal variability in water quality [30,31]. Alterations in water quantity and quality govern the species
composition, ecosystem productivity, and physiological conditions of aquatic organisms. Altered flows due to changes
in ecosystem conditions influence the fish population, bringing about changes in habitat, food availability,
community structure, composition, and behavior [32]. Pollutants such as heavy metals cause a severe threat to living
organisms and humans as they are toxic and persist for a more extended period in nature, resulting in their
bioaccumulation in the food chain [33,34].
Various statistical approaches have been adapted for interpreting water quality variables [35,36]. Furthermore, the
computation of water quality indices (WQI) aid in understanding the suitability of water for anthropogenic purposes.
Multivariate analysis such as cluster analysis (CA) and principal component analysis (PCA) aid in understanding
spatial-temporal variations, a grouping of monitored stations, and identification of important factors that
influences the quality of streams [37–40].
The Aghanashini River in the central
Western Ghats is a free-flowing river that supports rich biodiversity and sustains people’s livelihoods. The
catchment of this river is witnessing land cover changes due to increasing societal demands. This necessitates
understanding landscape dynamics with biodiversity, hydrologic regime, and water quality characteristics for the
prudent management of fragile aquatic ecosystems.
The eco-hydrological footprint assessment of a river considers water availability, water quality characteristics, and
water demand for the sustenance of biotic components. The objective of the current research
is to assess the eco-hydrological footprint of the Aghanashini River basin at the sub-catchment level, considering
various societal demands, ecological needs, and water availability. This entailed land use analysis; spatio-temporal
analyses of annual rainfall data, hydrological and ecological footprint, the computation of eco-hydrological indices
(EHI), eco-hydrological footprint, and water quality indices (through water quality assessment).