Spatial GIS Database for Adaptive Grassland Management in Dudhwa National Park, India

Spatial GIS Database for Adaptive Grassland Management in Dudhwa National Park, India

University of Kentucky UKnowledge International Grassland Congress Proceedings XXII International Grassland Congress Spatial GIS Database for Adaptive Grassland Management in Dudhwa National Park, India Neha Midha WWF-India, India Pradeep K. Mathur Wildlife Institute of India, India Follow this and additional works at: https://uknowledge.uky.edu/igc Part of the Plant Sciences Commons, and the Soil Science Commons This document is available at https://uknowledge.uky.edu/igc/22/1-13/6 The XXII International Grassland Congress (Revitalising Grasslands to Sustain Our Communities) took place in Sydney, Australia from September 15 through September 19, 2013. Proceedings Editors: David L. Michalk, Geoffrey D. Millar, Warwick B. Badgery, and Kim M. Broadfoot Publisher: New South Wales Department of Primary Industry, Kite St., Orange New South Wales, Australia This Event is brought to you for free and open access by the Plant and Soil Sciences at UKnowledge. It has been accepted for inclusion in International Grassland Congress Proceedings by an authorized administrator of UKnowledge. For more information, please contact [email protected]. Monitoring and managing grass and forage biomass resources at the landscape level Spatial GIS database for adaptive grassland management in Dudhwa National Park, India Neha Midha A and Pradeep K.Mathur B A WWF-India, Secretariat, 172 B, Lodi Road, New Delhi, - 110 003, India B Wildlife Institute of India, P Box # 18, Chandrabani, Dehra Dun – 248 001 (Uttarakhand), India Contact email: [email protected] Keywords: GIS database, grassland management. Introduction park (680 sq km). The overall accuracy computed for the land use map was found to be 91.3 % and overall Kappa Ecologically important tall grasslands of Dudhwa National statistics was 0.9. Park (DNP) in Northern India are being threatened by various natural and biotic factors including varying Extents and distribution of grassland types grassland burning regimes viz. cut and burn, harrowed and One thirty seven sq km extent of grasslands was identified burn, or only burn adopted by management for their through land use mapping within DNP. The analysis maintenance (De 2001). Uncertainty regarding resultant identified two types of grasslands. This included Upland grassland composition and disturbance to grassland grasslands (grassy blanks on well drained soils within the obligate species prompted the management and scientific Sal forest; dominant grasses included Cyrtococcum patens, communities concerned to develop an adaptive manage- Desmostachya bipinnata, Imperata cylindrica, and ment strategy for long term conservation goals (Chadden et Cymbopogon jwarancusa; 6.1 % of area) and Lowland al. 2004). In view of this, the present study attempted to grasslands (found in low lying areas or water logged develop comprehensive GIS (Geographic Information depressions; prominent grass species were Phragmites System) spatial database and associated hard copy maps of karka, Saccharum narenga, Saccharum spontaneum, and park at the scale of 1:25,000, to support field practitioners Schlerostachya fusca; 13.9 % of area). for successful implementation of proposed Adaptive Grassland Management. Definition of other attributes Methodology The land use classes found within grasslands or adjacent are: Sal (Shorea robusta) forests (predominant; covered Development of land use maps 56.4 % of area); Mixed deciduous forest (common We visually interpreted IRS P6 LISSIV (spatial resolution associates were: Mallotus philippensis, Bombax ceiba, of 5.8 m) satellite data after radiometric and geometric Syzygium cumini, and Acacia catechu; 8.3 %); Tropical corrections. The ground validation information was semi - evergreen forest (characterized by presence Calamus collected in March, 2005 and working scale was set at the tenuis, Lygodium flexuosum and climbers. Prominent tree scale of 1: 12,500 to allow a finer presentation at 1: 25,000. species: Trewia nudiflora, Mallotus philippensis, Syzygium Overall accuracy and kappa statistics were also calculated. cumini, and Ficus hispida; 2.1 %); Tropical seasonal swamp forest (found in swampy depressions. Syzygium Development of infrastructure maps cumini formed the main constituent with Trewia nudiflora, We extracted the data relevant from the developed spatial Ficus racemosa, Mallotus philippensis, and Acacia catechu layers (Mathur and Midha 2008): railway network; ; 3.9 %); Teak plantation (5.0 %); Other plantations (Eucalyptus citriodora, Acacia catechu, Dalbergia sissoo, power lines; buildings (residential colonies and perman- and Terminalia arjuna; 0.1 %); Swamp, water bodies and ent huts); road network (forest and metalled road); scrub (1.1 %) and River (1.2 %). topography (contour, slope, aspect, and elevation map); To present how the database would look like, a sample drainage network (primary, secondary, and tertiary site; Sathiana range on south-western boundary of the park drainage lines). Each layer had a description of the was chosen (Fig. 1). For better visualization, we presented geographical coverage; data attributes and was at the the database on digital image. scale of 1:25,000. Discussion and Conclusions Boundaries Spatial database and large scale maps could act as a The boundaries of the administrative units (forest range, decision making tool for identification of grassland patches block, beat and compartment) were manually digitized which would ultimately be subjected to specific treatment from paper source followed by re-projection and re-scaling. and will also help in assessing vegetation patterns related to particular management activities. This will make the Results management decision planned, formal and more Land use theme consists of 10 classes identified within the scientifically rigorous than the existing one. Further © 2013 Proceedings of the 22nd International Grassland Congress 871 Midha et al. Figure 1. (a) Location of the study area; (b) Land use map of DNP; (c) Sample site to present the database (d) Sample site enlarged. adaptive management typically has a modeling (Bunch References 2000, Chadden et al. 2004) component (dynamic simulation modeling of hydrology and fire fuel), the Bunch MJ (2000) An adaptive management approach for database could make a contribution to this component by rehabilitation and management of the Cooum River Environmental System in Chennai, India. Ph.D. Thesis. facilitating the baseline information as model input. Faculty of Environmental Studies, University of Waterloo, Moreover, it can support spatially-explicit studies including Waterloo, Ontario, Canada. pp. xviii and 404. identification of conservation-priority habitat core areas; habitat restoration initiatives; and ecological implications Chadden A, Dowskza E, Turner L (2004) Adaptive Management of land use planning alternatives. It is envisioned that this for Southern California Grassland. M.Sc. Thesis (Group project). Donald Bren School of Environmental Science and database will be the foundation of adaptive grassland Management. University of California. pp. 241. management strategy efforts and other informed management decision. De R (2001) Management Plan of Dudwa Tiger Reserve. 2000- 2001 to 2009-2010, Wildlife Preservation Organization, Acknowledgments Forest Department, Uttar Pradesh. The authors acknowledge financial and logistic support from the Mathur PK , Midha N (2008) Mapping of National Parks and Wildlife Institute of India, WII-MoEF-NNRMS Project of Wildlife Sanctuaries, Dudhwa Tiger Reserve, WII-NNRMS- Ministry of Environment and Forests, Government of India and MoEF Project, Final Technical Report, Wildlife Institute of Uttar Pradesh Forest Department. India, Dehradun, India. pp. 216. © 2013 Proceedings of the 22nd International Grassland Congress 872 .

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