TY - JOUR
T1 - L’abondance de l’outarde kori (Ardeotis kori) varie selon la végétation et l’élévation dans la réserve de chasse de northern tuli, Dotswana
AU - McCollum, Kathryn R.
AU - Powell, Larkin A.
AU - Snyman, Andrei
AU - Brown, Mary Bomberger
AU - Carroll, John P.
N1 - Funding Information:
Funding was provided by The Wilson Ornithological Society, The Cooper Ornithological Society, the University of Nebraska-Lincoln’s School of Natural Resources’ Graduate Student Association Travel Grant, the Irvin A. and Agnes E. Nelson fellowship, and crowd-sourced donations. We would like to thank the landowners and board of the Mashatu Game Reserve and the Northern Tuli Game Reserve for their support, the Republic of Botswana’s Ministry of Environment, Wildlife and Tourism, and the Department of Wildlife and National Parks for their permission to work in Botswana. We also thank EcoTraining, Inc. for their care and support throughout this project. Finally, we would like to acknowledge the hard work of our field assistants including the University of Georgia and University of Nebraska-Lincoln study abroad courses from 2014 and 2015, as well as all of the EcoTraining volunteers, students, staff, guides, and instructors throughout both of the field seasons.
Publisher Copyright:
© 2018 by the author(s).
PY - 2018/6
Y1 - 2018/6
N2 - Conservation planning and decision making for species of concern requires precise information on abundance and habitat associations. We conducted transect surveys throughout the Northern Tuli Game Reserve, Botswana during June–July 2014 and May– July 2015 to estimate the occupancy and abundance of Kori Bustards (Ardeotis kori). The probability of occupancy of Kori Bustards was greater in areas with tree canopy cover ≤ 50% (ψ2014 = 0.37, SE ± 0.09; ψ2015 = 0.39, SE ± 0.06) when compared with areas with tree canopy cover > 50% (ψ2014 = 0.00, SE ± 0.00; ψ2015 = 0.00, SE ± 0.00). Densities of Kori Bustards ranged from 0.03–5.02 individuals/km² at our study sites. They showed annual variation, and densities were highest in areas where vegetation was classified as sparse or bare soil. Areas at low (≤ 540 m above sea level) and high (≥ 540 m above sea level) elevations at our study sites also exhibited differences in density of Kori Bustards but elevational differences varied among years. Areas categorized as both sparse vegetation and higher elevation had the highest estimated densities in 2014 with 5.02 individuals/km². Areas categorized as sparse vegetation and lower elevation had the highest densities in 2015 with 2.20 individuals/km². Our study demonstrates that areas of sparse vegetation and open canopy areas are important to Kori Bustards. However, open canopy areas outside of reserves may be at risk of conversion to row crop and other forms of agriculture as human populations and demands for food increase. Habitat-specific information will be useful for future studies to identify risks during landscape conservation planning within the range of the Kori Bustard.
AB - Conservation planning and decision making for species of concern requires precise information on abundance and habitat associations. We conducted transect surveys throughout the Northern Tuli Game Reserve, Botswana during June–July 2014 and May– July 2015 to estimate the occupancy and abundance of Kori Bustards (Ardeotis kori). The probability of occupancy of Kori Bustards was greater in areas with tree canopy cover ≤ 50% (ψ2014 = 0.37, SE ± 0.09; ψ2015 = 0.39, SE ± 0.06) when compared with areas with tree canopy cover > 50% (ψ2014 = 0.00, SE ± 0.00; ψ2015 = 0.00, SE ± 0.00). Densities of Kori Bustards ranged from 0.03–5.02 individuals/km² at our study sites. They showed annual variation, and densities were highest in areas where vegetation was classified as sparse or bare soil. Areas at low (≤ 540 m above sea level) and high (≥ 540 m above sea level) elevations at our study sites also exhibited differences in density of Kori Bustards but elevational differences varied among years. Areas categorized as both sparse vegetation and higher elevation had the highest estimated densities in 2014 with 5.02 individuals/km². Areas categorized as sparse vegetation and lower elevation had the highest densities in 2015 with 2.20 individuals/km². Our study demonstrates that areas of sparse vegetation and open canopy areas are important to Kori Bustards. However, open canopy areas outside of reserves may be at risk of conversion to row crop and other forms of agriculture as human populations and demands for food increase. Habitat-specific information will be useful for future studies to identify risks during landscape conservation planning within the range of the Kori Bustard.
KW - Conservation
KW - Density estimation
KW - Distance sampling
KW - Occupancy analysis
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U2 - 10.5751/ACE-01191-130113
DO - 10.5751/ACE-01191-130113
M3 - Article
AN - SCOPUS:85049196623
SN - 1712-6568
VL - 13
JO - Avian Conservation and Ecology
JF - Avian Conservation and Ecology
IS - 1
M1 - 13
ER -