Distribution, Occupancy, and Mercury Load in Texas Alligator Snapping
Distribution, occupancy, and mercury bioaccumulation of alligator snapping turtles in Texas David Rosenbaum1, Christopher M. Schalk1, Daniel Saenz2 1Arthur Temple College of Forestry and Agriculture, Stephen F. Austin State University, Nacogdoches, TX; email: rosenbaudc@jac ks.sfasu.edu 2U.S. Forest Service, Southern Research Station, Nacogdoches, TX Introduction Methods Distribution Increasing anthropogenic habitat alteration and fragmentation in TX During spring and summer 2020-2021, we will Fig. 3: Distribution of M. are expected to further negatively impact freshwater systems. temminckii in TX. Points survey M. temminckii at sites in major river drainages indicate survey sites in of Texas that the species has been reported from the original survey that Animal species in these systems that have low dispersal capabilities, (Fig. 3). At each site,15 fish-baited traps will be set will be resampled from. are long-lived, and are dependent on the adult cohort for population Green-colored counties for 3 consecutive days, for a total of 45 trap nights indicate detection from stability, are vulnerable to anthropogenic factors including habitat per site (sensu Rudolph et al. 2002). 1999-2001, in the original alteration, accumulation of contaminants, and overexploitation. survey, while white Traps will be selectively placed in microhabitats • sizecounties indicate no The alligator snapping turtle (Macrochelys temminckii) exhibits these detection. Blue counties predicted to be favored by M. temminckii (see lower • ageare++ additional potential traits and is in decline throughout its range. Although not federally right quadrant of Fig. 2). survey sites for 2020- protected, it is legally protected as an S2 (imperiled) SGCN in Texas. 2021. Its last statewide distribution study occurred from 1999-2002.
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