Purpose of Review
The science of landscape connectivity is widely applied to identify corridors for wildlife movement through unprotected areas. Where corridors coincide with forested or vegetated headwater catchments, they can contribute to blue water security for downstream users and recycle precipitation through green water flux to the larger region. This review examines the extent to which hydrology is recognized within studies on wildlife corridors. We illustrate the synergy between wildlife corridors and water security in the Central Indian Highlands, a globally important region for tiger (Panthera tigris) conservation and the water tower for five major rivers.
We find that a growing but still minor component of the literature on landscape connectivity addresses hydrology. Out of 127 publications on landscape connectivity that address both hydrology and wildlife, 50% were published after 2015 and hydrology-related words appear more frequently in abstracts over time (27% in 1993–2003 and 45% in 2014–2023 of most frequently used words) The case study illustrates potential synergies for water security and conservation, with areas for wildlife connectivity twice as rugged, three times more forested, and about 1.8 times denser with small streams than other areas in the landscape. About half of the area identified for landscape connectivity overlaps with catchment areas for five major dams.
Freshwater resources and water security are vital in human-dominated landscapes such as central India. A holistic view of landscape connectivity beyond wildlife provides practitioners with additional rationale for conserving these areas to maintain water resources that are directly relevant to people living in the landscape.
Connectivity arose as a key concept in landscape ecology in the 1990s, originally defined as “the degree to which the landscape facilitates or impedes movement among resource patches” . The concept is now embedded in conservation practice to counterbalance negative effects of habitat fragmentation as people convert land for agriculture, urban areas, mines, and other uses, leaving higher quality patches within a matrix of lower quality habitat. Wildlife corridors are an established approach to maintain movement of plants and animals between patches. Corridors, such as Yellowstone to Yukon and the Terai Arc, facilitate movement of grizzly bears (Ursus arctos horribilis) and tigers (Panthera tigris), respectively, enable gene flow to retain health of populations and provide migration options in the face of climate change (see  for many examples of corridors).
In addition to the importance of landscape connectivity for wildlife, corridors also control many other types of biotic and abiotic flows including seed dispersal, fire spread, water flows, pests, and diseases. Some of these flows can be harmful for people such as the spread of fires and disease, while some are beneficial such as surface and groundwater for downstream irrigation, urban water supplies, and other uses. Landscapes that protect high-quality wildlife habitat also protect streams in the watershed against high sediment loads from erosion, contamination from intensive human use, flooding due to rapid runoff from impervious surfaces, and impeded hydrological connectivity [3, 4]. Large forest patches in corridors also recycle evapotranspiration (green water flux) that contributes to precipitation over large regions [5,6,7,8,9].
Water security, particularly in light of increasingly variable and extreme precipitation and unsustainable water withdrawals, is a critical problem in many parts of the world . The Ministerial Conference at the Second World Water Forum, held at The Hague in 2000, defined water security as “ensuring…that every person has access to enough safe water at an affordable cost to lead a healthy and productive life and that the vulnerable are protected from the risks of water-related hazards” . The 2023 Global Commission on the Economics of Water notes that the adequate water provides a “stable foundation for human well-being and ecosystem health, and hence is a necessity for socio-economic and ecological prosperity” . Although economic and political forces are critical to achieve all aspects of water security, healthy vegetation in headwater catchments contributes to water security by promoting hydrologic connectivity, maintaining water quality, reducing sediment generation, cycling precipitation, and enhancing infiltration. In this paper, we adopt the definition of hydrologic connectivity as “the internal linkages between runoff and sediment generation in upper parts of the catchments and the receiving waters” including two types of connectivity: “direct connectivity via new channels or gullies, and diffuse connectivity as surface runoff reaches the stream network via overland flow .”
“Water towers”—a symbolic term that underscores the importance of mountain regions in providing freshwater for adjacent areas downstream —are particularly critical in Asia to provide water for lowland agriculture and major population centers . Headwater streams constitute a large proportion of overall stream length in a hydrologic system and can act as the conduit for water flows to lowlands. Vegetation in catchment areas for small streams can curtail soil erosion and provide many other ecosystem services that maintain water supply, aquatic biodiversity, and water quality [16, 17]. Protection of watersheds in the Catskills region, for example, provides clean, unfiltered water for millions of downstream consumers in New York City . In Kenya, the government established the Waters Towers Agency in 2012 to oversee sustainable management of the country’s critical water towers in the face of rampant deforestation and declining water resources . In Mumbai, the forests of the Borivali in the Sanjay Gandhi National Park protect water catchments and reservoirs that supply clean drinking water to the mega-city .
Wildlife corridors are located where land cover and low human population densities offer low resistance to animal movements. Many wildlife corridors are located in remaining forested areas, which in turn tend to be located in hilly areas, particularly in India (the focus of this special issue) . These upper reaches also serve as water towers that are vital for water security. Consequently, headwaters and wildlife corridors potentially overlap to provide critical services to society.
In this paper, we address the confluence of these two aspects of landscape connectivity—conservation of iconic wildlife and water security. Both relate to the management of landscapes to provide societal needs into the future. If such a synergy holds up to scientific scrutiny, a holistic view of corridors provides policy makers additional rationale for conserving and managing wildlife corridors as hydrologically and hydro-climatologically important for downstream water users.
First, we assess the literature to determine the degree to which hydrologic function is incorporated into research and practice related to wildlife corridors. We then provide a case study from the Central Indian Highlands to assess the utility of wildlife corridors for protecting headwaters for critical rivers and catchment areas for major dams. The Central Indian Highlands and their forests serve as the water tower for five major rivers and 268 reservoirs  and recycle moisture to delay the withdrawal of the summer monsoon as well as to support precipitation regionally . The region is also a globally recognized area for tiger conservation .
Data and Methods
We used the Biblioshiny web interface version 4.0.0 of the bibiometrix library in R  to analyze the extent to which the literature addresses overlaps between landscape connectivity for wildlife corridors and for watershed protection. The bibliometrix analysis is used in many publications to assess trends in research fields, e.g., [25, 26] for sustainability-related topics. We accessed the ISI Web of Science database on February 7, 2023 to retrieve metadata for publications in all possible years (1990–2023) for search terms in the category “abstract” . Search terms were “(landscape connectivity OR corridor) AND (wildlife OR biodiversity),” and “(“landscape connectivity” OR corridor) AND (hydrology OR watershed)”. To identify the publications that address both wildlife/biodiversity and hydrology/watershed we conducted a search on the term “(“landscape connectivity” OR corridor) AND (wildlife OR biodiversity) AND (hydrology OR watershed).” We also checked results from a search with the same criteria in SCOPUS, which produced similar results but fewer and overlapping papers as Web of Science.
For the publications identified through the search that pertain to both wildlife/biodiversity and hydrology/watershed, we utilized Biblioshiny to calculate annual scientific production and to track the focus of these papers over time based on frequency of words in the abstracts. We used Biblioshiny software to identify the top ten words based on frequency in abstracts, then grouped these words depending on whether they pertain to wildlife/biodiversity conservation or watersheds. We report the frequency of these words by decade beginning with the earliest paper identified in the search.
Case Study of Landscape Connectivity in Central Indian Highlands
The Central Indian Highlands exemplifies multiple potential benefits from landscape connectivity for water security and wildlife conservation. As in other parts of India, tiger populations have increased with improved protection over the last decade , but mines, roads, urbanization, and other development activities are advancing at a rapid pace to impede connectivity . With the small size of India’s protected areas relative to home range sizes of many wildlife species, the habitat matrix outside protected areas plays a major role in the ability of animals to disperse . Wildlife corridors are paramount to the health of the endangered tiger (Panthera tigris) and other iconic wildlife populations.
Central India includes the Central Indian Highlands and spans multiple states without a clearly defined boundary, is a globally designated tiger conservation landscape (defined as “areas where there is sufficient habitat for at least five tigers, and tigers have been confirmed in the last ten years”) . Central India, which houses approximately 30% of India’s tigers, contains four out of seventeen class 1 highest priority tiger conservation landscapes globally . An estimated one-third of wild tigers in central India live outside protected areas  within a matrix of forest patches, small-scale farms, villages, and cities. Local livelihoods depend on small-scale agriculture, cattle rearing, and collection of forest products for people living near forested areas .
Schoen et al.  identified “consensus connectivity areas” in the Central Indian Highlands based on five independent, published studies that mapped corridors in central India based on varying data inputs and model parameters. Competition for land use is acute in the consensus connectivity areas (CCAs). Approximately 70% of the CCAs fall within village administrative boundaries, 16% within 1 km of linear infrastructure, and 78% of forest land diversions for infrastructure and mining in the state comprising the majority of the area (Madhya Pradesh) occurred in districts containing CCAs. All of the land in the CCAs fall within forest department management boundaries .
The Central Indian Highlands also serve as the water tower for five of India’s major rivers (Ganga, Narmada, Godavari, Mahanadi, and Tapti). Average precipitation is 987 mm per year with nearly all precipitation falling within the monsoon season. Agriculture is the dominant land use and accounts for 95% of total water demand (Fig. 1). There are 17 urban centers with populations greater than 100,000 within the landscape, all of which experience water stress (demand greater than supply) at some time during the year . As irrigation and urban water demand continue to increase, managing land use to maintain flows to reservoirs and to recharge groundwater is critical for water security.
The vegetation of the central Indian region plays an important role in regulating and supplying rainfall to ecosystems and people due to the monsoon wind circulation patterns and through recycling of evapotranspiration or green-water. In the central Indian region, precipitation is a factor of at least two greater in air parcels with exposure to large vegetation patches than in air parcels with small exposure . Precipitation from recycled evapotranspiration varies from approximately 20 to more than 200 mm per day during the southwest monsoon. The recycling delays the end or withdrawal of the summer monsoon in September [5,6,7, 9, 22].
Analysis of Overlap Between Wildlife Corridors and Headwaters in Central India Highlands
For the case study, we overlaid the wildlife corridors with topographic data and the stream network. The wildlife corridors, denoted as consensus connectivity areas (CCAs), were obtained from . We further identified the domain for the case study by drawing a convex hull around the CCAs within the area covered by all five studies. The convex hull excludes parts of the landscapes around the edges that potentially are important for connectivity but are not within the CCAs merely because the studies did not include nodes beyond the boundaries of their study regions. We further clipped the case study domain to include entire watersheds to constrain the comparison of areas within and outside CCAs, using level 12 (highest available) watershed boundaries from HydroBASIN .
Ruggedness was determined by R package for terrain ruggedness index based on 30-m resolution elevation data from the ALOS global digital surface model . The stream network was obtained from . Stream order represents Strahler orders in the HydroRivers data set. Land cover data at 10-m resolution was obtained from . Major dams were located from data used in .
For this study, we follow  to define “headwater streams” as 1st order streams, i.e., the smallest streams with a defined channel. We define “small streams” as 1st and 2nd order streams together, with 2nd order streams resulting from the confluence of two 1st order streams. We assessed the number of headwater and small streams that overlap the consensus connectivity areas relative to the total number of stream reaches in the domain. For the five largest dams in the case study domain based on surface area, we identify the catchment area by using the HydroSheds raster Layers “HSdrainageUTM” and “HSstreamUTM.” We then determined the outlet point of a dam that coincided with the stream layer and noted its coordinates. We used the ‘r.water.outlet’ tool and loaded HSdrainageUTM as input along with the coordinates of the identified outlet point to generate the catchment area for each dam. For each catchment area, we determine the proportion of the catchment that overlaps CCAs. The density of streams is the number of stream reaches per unit area within CCAs or in the case study domain.
3608 publications on landscape connectivity (78% of all publications identified in the three searches) pertain specifically to wildlife and biodiversity, while 856 (19%) publications pertain to hydrology and watersheds. Far fewer papers address the synergy between the two functions of landscape connectivity, with 127 (3%) publications identified when using all the search terms (Fig. 2). The search revealed that 3% and 13% of wildlife and hydrology-related publications on landscape connectivity, respectively, address synergies between the two landscape functions.
The number of publications per year that address this synergy has increased in recent years, from 1 in 1993 to 15 in 2022. Approximately 50% of all publications on landscape connectivity that address both wildlife/biodiversity and hydrology/watershed were published after 2015 (Fig. 3).
The frequency of words in the abstracts per decade revealed growing attention to water-related issues in the connectivity literature that addresses both wildlife and watersheds (Fig. 4). The top ten words with highest frequency in the abstracts (from greatest to least) were water, species, biodiversity, riparian, landscape, ecological, habitat, connectivity, conservation, and river. The words related to water (“water,” “riparian,” and “river”) are less frequent (27%) in the early decades compared to words related to wildlife (“species,” “biodiversity,” “habitat,” and “conservation”). In later decades, frequencies of water-related words (45%) increase relative to wildlife-related words. This trend indicates increasing attention to water in the connectivity literature. Notably, words related to landscape connectivity for water security and water supply to downstream users, such as “agriculture,” “cities,” “dams,” or “reservoirs,” do not appear in the words that are used most frequently.
Within the 127 papers, the most highly cited papers focus on hydrologic connectivity in wetland, riparian, and river systems and the implications for aquatic ecosystems and biodiversity [39,40,41,42] and biosphere reserves . Within these most five highly cited papers, none focused on potential synergies between landscape connectivity for wildlife and downstream water flows and green water flux.
Synergies Between Consensus Connectivity Areas For Tigers and Hydrologic Function in Central India Highlands
The connectivity consensus areas (CCAs) cover approximately 13% of the total area of the case study domain (study extent clipped to the convex hull around the CCAs and watershed boundaries). The CCAs are approximately twice as rugged and have three times more forest cover and five times less cropland than the areas outside of the CCAs. Although the CCAs contain only approximately 25% of headwater and small streams in the total case study domain, the density of these streams in the CCAs is almost twice the density outside the CCAs for both headwater and small streams (Table 1).
The total catchment area for the five largest dams in the case study domain comprises 46% (79,320 km2 out of 171,649 km2) of the total case study domain (Fig. 5). The proportion of catchment areas that overlap CCAs range from 2 for Pench Totladoh to 20% for Bargi, with 15% for the total catchment areas for the five dams (Table 2). Protected areas cover between 3 (Bansagar) and 24% (Tawa) of the catchment areas, which by definition are not included in CCAs and provide additional protection of the catchment areas. Relative to total CCA area, over 50% (11,748 km2 out of 23,134 km2) of CCA overlaps the catchment areas of these five major dams.
The number of headwater streams (first order) and small streams (first and second order) in these catchment areas is disproportionately high in the CCAs relative to the proportion of total catchment area (Fig. 6). CCAs in the catchment areas for the five dams combined contain 27% of all first-order streams and 19% of small streams compared with 15% of total area in CCAs. The disproportionately high representation of headwater and small streams in CCAs varies among the catchment areas, with Bargi containing 32% and 23% of headwater and small streams, respectively, compared with 20% of area. At 8% and 6%, respectively, the disproportionately high representation in the number of streams occurs for Pench Totladoh as well, which only has 2% of the catchment area as CCA. The high relative number of headwater and small streams suggests that maintaining CCAs with vegetation cover and free from disturbances, such as large mines and transport infrastructure, would contribute to hydrologic function and sediment control as well as landscape connectivity for wildlife.
Discussion and Conclusions
The bibliometric analysis of literature on landscape connectivity/corridors, wildlife/biodiversity, and hydrology/watershed indicates that the research field of landscape connectivity for wildlife movement is well-established. On the other hand, literature on landscape connectivity that incorporates hydrologic function and water security is an emerging but less mature research area. Within the papers produced from the search on the overlap between landscape connectivity for wildlife and water security, there is a paucity of papers that examine the potential for corridors to maintain landscape connectivity to address these two objectives. In general, these results indicate a need for the scientific community to examine possible synergies that landscape connectivity can provide for water security and wildlife conservation.
The case study in the Central Indian Highlands, where areas of importance for wildlife movement also serve as headwaters for multiple rivers that provide essential water to downstream users, illustrates the potential for increased synergy to address multiple goals through management of these headwaters. The CCAs comprise 13% of the total land area but contain approximately 25% of headwater and small streams in the case study domain. Forest cover in the CCAs (approximately three times the forest cover outside of CCAs) reduces soil erosion through maintaining vegetative cover, slowing runoff, and enhancing infiltration. The ruggedness of the CCAs (approximately twice as rugged as areas outside the CCAs) makes conservation of forests within CCAs particularly crucial to control soil erosion and downstream water quality flowing from these headwater and small streams.
The extensive overlap between the CCAs and the catchment areas for the five largest dams (more than 50% overlap of all CCAs and 15% overlap of total catchment area) in the case study area illustrate the potential relevance of management of the CCAs to downstream water quality and flow. CCAs in the catchment areas contain 27% of the headwater and 19% of small streams on 15% of the total area. Consequently, management of the CCAs to maintain healthy vegetation cover and pervious surfaces contributes disproportionately to the water security for downstream users. The degree of potential co-benefit between water security and landscape connectivity for wildlife depends on the amount of overlap in land area between the catchment area and wildlife corridor for any particular dam. In the case study, this overlap ranges from 2 to 20% across the five largest dams.
Despite the potential for synergies between management for wildlife movement and watershed protection, the practicality of management for multiple objectives is limited. The mandate for wildlife managers is to manage habitat for wildlife, the mandate for water managers is to manage water flows, and the mandate of the development sector is to expand infrastructure, mines, and other activities. Increased attention from the research community on the potential for landscape connectivity to synergistically contribute to hydrologic function as well as wildlife movement could help foster a useful dialogue. Such a dialogue could nudge managers and decision-makers towards overcoming silo-ed management and achieving more holistic management of these critical parts of the landscape. For example, efforts that protect both wildlife corridors and watersheds such as reducing pressure on forests for construction, fuelwood, and other forest products would address both objectives .
The imperative to holistically manage remaining semi-wild areas for landscape connectivity is particularly acute in India. Water security is a primary concern in its own right for over a billion people. While tiger conservation is highly valued by many and a success story in the country, water is a daily, immediate need recognized by every citizen and manager. Headwaters with healthy vegetation to reduce sedimentation, filter contaminants, recharge groundwater, maintain streamflow into the dry season, and recycle and redistribute precipitation through green water flux potentially serve a dual purpose of wildlife corridors—for tigers and for reducing water stress for people and ecosystems across the landscape. This aspect of landscape connectivity has been underappreciated in the literature.
The scarcity of land for multiple uses leads to competition between agriculture, commercial forestry, habitations, energy and transport infrastructure, and other human uses in the region. Most often, forest lands are diverted for infrastructure and mining in the region . In central India, conserving remaining semi-wild areas for hydrologic function can add much-needed rationale to the conservationists’ calls for landscape connectivity for wildlife movement. Similar situations are likely to exist around the world, particularly in areas facing water insecurity from overuse and climate change. Our results conclude that research into the synergies between landscape connectivity and ecosystem services, in specific hydrologic function that contributes to water security, can lead to less-silo-ed management decisions to meet multiple wildlife and human development goals.
Shape files with consensus connectivity areas for tigers for the case study region are publicly available at https://www.centralindia-datacollab.org/. All other data sets used in this analysis are publicly available.
Taylor PD, Fahrig L, Henein K, Merriam G. Connectivity is a vital element of landscape structure. Oikos. 1993:571–3.
Hilty J, Worboys GL, Keeley A, Woodley S, Lausche B, Locke H, et al. Guidelines for conserving connectivity through ecological networks and corridors. Best practice protected area Guidelines Series. 30th ed. 2020. p. 122.
Zhang Y, Huang C, Zhang W, Chen J, Wang L. The concept, approach, and future research of hydrological connectivity and its assessment at multiscales. Environ Sci Pollut Res. 2021;28(38):52724–43.
Dosskey MG, Vidon P, Gurwick NP, Allan CJ, Duval TP, Lowrance R. The role of riparian vegetation in protecting and improving chemical water quality in streams 1. J Am Water Resour Assoc. 2010;46(2):261–77.
Spracklen DV, Arnold SR, Taylor C. Observations of increased tropical rainfall preceded by air passage over forests. Nature. 2012;489(7415):282–5.
Spracklen D, Baker J, Garcia-Carreras L, Marsham J. The effects of tropical vegetation on rainfall. Annu Rev Environ Resour. 2018;43:193–218.
Budakoti S, Chauhan T, Murtugudde R, Karmakar S, Ghosh S. Feedback from vegetation to interannual variations of indian summer monsoon rainfall. Water Resour Res. 2021;57(5):e2020WR028750.
Paul S, Ghosh S, Rajendran K, Murtugudde R. Moisture supply from the western ghats forests to water deficit east coast of India. Geophys Res Lett. 2018;45(9):4337–44.
Sujith K, Saha SK, Pokhrel S, Hazra A, Chaudhari HS. The dominant modes of recycled monsoon rainfall over India. J Hydrometeorol. 2017;18(10):2647–57.
Jain SK. Water resources management in India-challenges and the way forward. Curr Sci. 2019;117(4).
Calaguas BU. Water security in the 21st century: report from the Second World Water Forum & Ministerial Conference. Waterlines. 2000;20–3.
Global Commission on the Economics and Water. The what, why and how of the world water crisis: Global Commission on the Economics of ater Phase 1 review and findings. Paris: France; 2023.
Croke J, Mockler S, Fogarty P, Takken I. Sediment concentration changes in runoff pathways from a forest road network and the resultant spatial pattern of catchment connectivity. Geomorphology. 2005;68(3–4):257–68.
Viviroli D, Dürr HH, Messerli B, Meybeck M, Weingartner R. Mountains of the world, water towers for humanity: typology, mapping, and global significance. Water Resour Res. 2007;43(7).
Viviroli D, Kummu M, Meybeck M, Kallio M, Wada Y. Increasing dependence of lowland populations on mountain water resources. Nat Sustain. 2020;3(11):917–28.
Lowe WH, Likens GE. Moving headwater streams to the head of the class. Bioscience. 2005;55(3):196–7.
Ferreira V, Albariño R, Larrañaga A, LeRoy CJ, Masese FO, Moretti MS. Ecosystem services provided by small streams: an overview. Hydrobiologia. 2022;1–35.
Appleton AF. How New York City used an ecosystem services strategy carried out through an urban-rural partnership to preserve the pristine quality of its drinking water and save billions of dollars and what lessons it teaches about using ecosystem services. 2002.
Rodary E, Bruno-Lézy L, Landy F, Morokawa M, Swanepoel J. The history of the four parks: favouring or protecting from urban growth, different successive conservation policies. From Urban National Parks to Natured Cities in the Global South: The Quest for Naturbanity. 2018. p. 35–62.
Qureshi Q, Saini S, Basu P, Gopal R, Raza R, Jhala Y. Connecting tiger populations for long-term conservation. National Tiger Conservation Authority & Wildlife Institute of India, Dehradun. Dehradun TR2014–02. 2014.
Clark B, DeFries R, Krishnaswamy J. India's commitment to increase tree and forest cover: consequences for water supply and agriculture production within the Central Indian landscape. Water 2021;13(959).
Pathak A, Ghosh S, Kumar P. Precipitation recycling in the Indian subcontinent during summer monsoon. J Hydrometeorol. 2014;15(5):2050–66.
Schoen J, Neelakantan A, Cushman S, Dutta T, Habib B, Jhala Y, et al. Synthesizing connectivity analyses for co-management of a globally important human-dominated tiger (Panthera tigris) conservation landscape. Conserv Biol. 2022;36(4).
Aria M, Cuccurullo C. Bibliometrix: an R-tool for comprehensive science mapping analysis. J Informetr. 2017;11(4):959–75.
Dhyani S, Murthy IK, Kadaverugu R, Dasgupta R, Kumar M, Adesh GK. Agroforestry to achieve global climate adaptation and mitigation targets: are South Asian countries sufficiently prepared? Forests. 2021;12(3):303.
Abafe EA, Bahta YT, Jordaan H. Exploring biblioshiny for historical assessment of global research on sustainable use of water in agriculture. Sustainability. 2022;14(17):10651.
Garfield E, Sher IH. Key words plus [TM]-algorithmic derivative indexing. J Am Soc Inf Sci. 1993;44:298.
Jhala Y, Gopal R, Mathur V, Ghosh P, Negi HS, Narain S, et al. Recovery of tigers in India: critical introspection and potential lessons. People Nat. 2021;3(2):281–93.
Nayak R, Karanth K, Dutta T, DeFries R, Karanth UK, Vaidyanathan S. Bits and pieces: impact of linear institutions on forest structural connectivity in India. Land Use Policy. 2020.
Jayadevan A, Nayak R, Karanth K, Krishnaswamy J, DeFries R, Karanth UK, et al. Navigating paved paradise: evaluating landscape permeability to movement for large mammals in two conservation priority landscapes in India. Biol Conserv. 2020;247:1908613.
Dinerstein E, Loucks C, Heydlauff A, Wikramanayake E, Bryja G, Forrest J, et al. Setting priorities for the conservation and recovery of wild tigers: 2005–2015. A User’s Guide. 2006. p. 1–50.
Sanderson EW, Forrest J, Louckes CJ, Ginsberg JR, Dinerstein E, Seidensticker J, et al. Setting priorities for conservation and recovery of wild tigers: 2005–2015. In: Tilson R, Nyhus PJ, editors., et al., Tigers of the world: the science, politics and conservation of Panthera tigris. London: Academic Press; 2010. p. 143–61.
Jhala Y, Qureshi Q, Gopal R. The status of tigers in India 2014. National Tiger Conservation Authority, New Delhi and Wildlife Institute of India. Dehradun. 2015. p. 28.
DeFries R, Sharma S, Dutta T. A landscape approach to conservation and development in the Central Indian Highlands: introduction to the special issue. Reg Environ Change. 2016.
Clark B, DeFries R, Krishnaswamy J. Water stress trends in the Central Indian landscape from 2002–2012. Reg Environ Change. 2016;16(5).
Lehner B, Grill G. Global river hydrography and network routing: baseline data and new approaches to study the world’s large river systems. Hydrol Process. 2013;27(15):2171–86.
Tadono T, Nagai H, Ishida H, Oda F, Naito S, Minakawa K, et al. Generation of the 30 M-mesh global digital surface model by ALOS PRISM. Int Arch Photogramm, Remote Sens Spat Inf Sci. 2016;41.
Karra K, Kontgis C, Statman-Weil Z, Mazzariello JC, Mathis M, Brumby SP. Global land use/land cover with Sentinel 2 and deep learning. In: 2021 IEEE international geoscience and remote sensing symposium IGARSS. IEEE; 2021.
Blann KL, Anderson JL, Sands GR, Vondracek B. Effects of agricultural drainage on aquatic ecosystems: a review. Crit Rev Environ Sci Technol. 2009;39(11):909–1001.
Nilsson C, Svedmark M. Basic principles and ecological consequences of changing water regimes: riparian plant communities. Environ Manage. 2002;30:468–80.
Harvey J, Gooseff M. River corridor science: hydrologic exchange and ecological consequences from bedforms to basins. Water Resour Res. 2015;51(9):6893–922.
Tonkin JD, Altermatt F, Finn DS, Heino J, Olden JD, Pauls SU, et al. The role of dispersal in river network metacommunities: patterns, processes, and pathways. Freshw Biol. 2018;63(1):141–63.
Pringle CM. Hydrologic connectivity and the management of biological reserves: a global perspective. Ecol Appl. 2001;11(4):981–98.
DeFries R, Agarwala M, Baquie S, Choksi P, Khanwilkar S, Mondal P, et al. Improved household living standards can restore dry tropical forests. Biotropica. 2022;54(6):1480–90.
Funds from the DeFries Bajpai Foundation for the Network for Conserving Central India supported Amrita Neelakantan and Satvik Parashar for this analysis.
Conflict of Interest
Ruth DeFries, Satvik Parashar, Amrita Neelakantan, Benjamin Clark, and Jagdish Krishnaswamy have no conflicts of interests to declare.
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DeFries, R., Parashar, S., Neelakantan, A. et al. Landscape Connectivity For Wildlife and Water: The State of the Literature. Curr Landscape Ecol Rep (2023). https://doi.org/10.1007/s40823-023-00091-0
- Central India
- Wildlife corridors
- Landscape connectivity
- Water security
- Hydrologic connectivity
- Human-dominated landscape