Editorial Type:
Article Category: Research Article
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Online Publication Date: 26 Sept 2022

Range-Wide Population Projections for Northern Red-Bellied Cooters (Pseudemys rubriventris)

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Page Range: 362 – 369
DOI: 10.1670/21-065
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ABSTRACT

Northern Red-Bellied Cooters (Pseudemys rubriventris) have a disjunct distribution with a relictual population in southeastern Massachusetts and a larger range across the mid-Atlantic United States. The relictual population is currently listed with protections under the U.S. Endangered Species Act but the status of the population in the remainder of the species' range has not been assessed, and there is concern that it may be at risk of extinction without protection. The U.S. Fish and Wildlife Service requires scientific information of the species' status to inform conservation decisions. There is little empirical information available from P. rubriventris populations and, furthermore, the majority of what exists comes from the disjunct northern subpopulation. To fill data gaps in the species' life history and reduce geographic bias, we supplement available data from P. rubriventris with demographic rate estimates from other Pseudemys species to parameterize an age-structured population projection model. Our estimate of mean population growth rate was 0.987 (0.92–1.04), indicating that P. rubriventris populations may be in decline. However, there was considerable uncertainty in our results, with 35% of projections resulting in stable or increasing populations. Additional uncertainty about parameter values, geographic variation, and current threats limit the assessment. We discuss the merits and limitations of our population projection modeling (PPM) approach where other analytical methods are precluded by lack of available data.

Copyright: Copyright 2022 Society for the Study of Amphibians and Reptiles 2022
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Fig. 1.
Fig. 1.

The full range of Pseudemys rubriventris (in dark gray), which consists of a disjunct population in Massachusetts and a larger mid-Atlantic range (USGS GAP, 2018).


Fig. 2.
Fig. 2.

Pseudemys life history matrix diagram with parameters; hatchling survival (SH), years 1–2 survival (S1), years 2–3 survival (S2), years 3–13 survival (S3), adult survival (SA), and adult fecundity (FA). FA represents a product of egg survival (SE), S1, proportion of adults that reproduce annually (R), and clutch size (C) in this figure.


Fig. 3.
Fig. 3.

Phylogenetic tree showing the relationship of Pseudemys rubriventris to other species within the genus (Spinks et al., 2013). Means of the parameter estimates found in the literature for each species are next to species names. Note that many other taxonomic hypotheses exist (e.g., Guillon et al., 2012, Spinks et al., 2016).


Fig. 4.
Fig. 4.

Probability density of finite population growth rate (λ) in a hypothetical Pseudemys population. Here, λ has a mean of 0.987 (dotted line) and a 95% confidence interval of 0.91–1.04 (shaded area).


Fig. 5.
Fig. 5.

Population trajectories over 20 yr with an initial population of 134 individuals (constant abundance shown in red) given a random 50 of the simulated population matrices. Mean population size at the end of 20 yr across all 50,000 simulated matrices was 121.9 (95% CI: 28.7–302.7).


Contributor Notes

2 Corresponding author. Email: jefleming@usgs.gov
Accepted: 12 Apr 2022
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