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Kori Bustards (Ardeotis kori) respond to vegetation density and elevation in the Northern Tuli Game Reserve, Botswana

机译:Kori Bustards(Ardeotis kori)对博茨瓦纳北部图里野生动物保护区的植被密度和海拔高度做出反应

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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.
机译:有关物种的保护规划和决策需要有关丰度和栖息地关联的准确信息。我们在2014年6月至7月和2015年5月至2015年7月对博茨瓦纳北部图里野生动植物保护区进行了横断面调查,以估算科里Bu鸟(Ardeotis kori)的占有率和丰度。与树冠覆盖率> 50%(ψ2014= 0.00)相比,树冠覆盖率≤50%(ψ2014= 0.37,SE±0.09;ψ2015= 0.39,SE±0.06)的地区,Kori Bustards的居住概率更高。 ,SE±0.00;ψ2015= 0.00,SE±0.00)。在我们的研究地点,Kori Bustards的密度范围为0.03-5.02个/km²。它们显示出年度变化,并且在植被被分类为稀疏或裸露土壤的地区密度最高。在我们的研究地点,低海拔(≤海拔540 m)和高海拔(≥海拔540 m)区域也表现出Kori Bustards密度的差异,但海拔差异随年份而变化。 2014年,植被稀疏和海拔较高的地区估计密度最高,为5.02个人/平方公里。 2015年,被归类为稀疏植被和低海拔地区的密度最高,为2.20个人/平方公里。我们的研究表明,稀疏的植被和开放的树冠区域对于Kori Bustards很重要。但是,随着人口和对食物的需求增加,保护区以外的开放林冠区域可能有转换为大田作物和其他农业形式的风险。与生境有关的信息对于将来的研究将很有用,以便确定在Kori Bustard范围内进行景观保护规划期间的风险。

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