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Demographic population structure of European rabbits at Turretfield, South Australia, 1998–2013, shown as a frequency distribution of posterior modes of estimated longevity in days (d) or years (yr). Numbers at the right of each bar represent the average posterior range of individual birth date (BD) and longevity (L) estimates for each age class using credible intervals. Individuals with uncertainty in BD >100 days have been excluded from the plot (i.e., those mainly with age estimates of 7–8 years).  

Demographic population structure of European rabbits at Turretfield, South Australia, 1998–2013, shown as a frequency distribution of posterior modes of estimated longevity in days (d) or years (yr). Numbers at the right of each bar represent the average posterior range of individual birth date (BD) and longevity (L) estimates for each age class using credible intervals. Individuals with uncertainty in BD >100 days have been excluded from the plot (i.e., those mainly with age estimates of 7–8 years).  

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The effectiveness of invasive species control can be influenced by seasonal fluctuations in reproduction in response to environmental conditions. However, it is difficult to determine how demography and environmental conditions affect the efficacy of different control efforts from field trials alone. We incorporated an ontogenetic growth model into...

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... with only 463 out of 3,736 estimates (12%) having credible intervals of 100 days uncertainty. Because of this uncertainty, longevity was deemed to be unrealistically high, 7-8 years for 31% of individuals. The overall demographic structure of the rabbit population was characterized by up to 60% of recorded individuals dying before 1 year of age (Fig. 2). Capture probabilities varied over seasons and time periods between 0.07 (CI ¼ 0.07-0.08) and 0.37 (CI ¼ 0.35-0.38), being highest in spring (Sep-Nov) and increasing towards the end of the study ...

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