Boa Constrictor at the Charles Deering Estate at Cutler

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Presentation transcript:

Boa Constrictor at the Charles Deering Estate at Cutler Jessica Fiallo, Dallas Hazelton, Elias Horna, Frank Ridgley DVM, Karen Solms, Dustin Smith, Carolina Segarra

History Snow reported in 2007 that likely present since the 1970’s Juveniles and adults found in 1990 after a burn Reported possibly breeding in 1992 164 removed since 1989 – 58 (35%) of which were YOY

History Adjacent resident’s cat killed by boa Outcry and website resulted FWC surveyed area 12 times with no captures Captures appear to be random and by chance Guests, employees, NAM plant crews

Objectives Determine the potential impact on the ecosystems Use radiotelemetry and visual surveys to determine habitat preference (2.2.2) Suggest a management strategy for this species Collect genetic samples to potentially determine the origin for the introduced population Develop a reference genetic profile for the population that will allow identification of individuals found outside the site as dispersers or unrelated releases. Analyze gut contents and fecal samples to learn about its prey base, possible impacts on the local wildlife populations, and possible implications if the population were to ever disperse to other natural areas. Discover any pathology, viruses or parasites that are endemic in the population that may pose a risk to native wildlife.

Slide text 444 acres

Slide text 104 Pine Rockland 116 Hammock 160 Coastal 33Wetland

DB-1, 3, 8, 10, & 12 DB1 DB8 DB10 DB12 SV/ST - 223.4/244.5 8.61 kg

DB1 MCP Slide text Area = 104,135 m2 25.7 acres

DB1 Kernal - female Slide text 157,901/24,631 m2 39/6 acres SF = 100

DB8 MCP Slide text Area = 388,317 m2 96.0 acres

DB8 Kernal - male Slide text 256,431/ 20,014 m2 63.3/4.9 acres SF = 100

DB10 MCP Slide text Area = 44,551 m2 11.0 acres

DB 10 Kernal - female Slide text 62,859 / 9,662 m2 15.5/2.4 acres SF = 100

DB12 MCP Slide text Area = 288,092 m2 71.2 acres

DB12 Kernal - male Slide text 413,028 / 66,731 m2 102/16.5 acres SF = 100

Combined Kernals Slide text

Capture Points

Site Fidelity Slide text

Timeframe and Points DB1- Dec 10, 2012 to Nov 13, 2013 – 102 points DB3- Aug 28, 2013 to Nov 1, 2013 – 18 points DB8- Oct 28, 2013 – still tracking – 53 points DB10- Nov 12, 2013 – still tracking – 58 points DB12- Nov 26, 2013 – still tracking – 49 points DB13 & 17 juveniles currently tracking

Macrohabitat Usage Pine Rockland – 62.5% Rockland Hammock – 35.7% Mangroves – 1.8%

Microhabitat Underground – 59.6% Filtering Canopy – 18.2% Under cover – 9.6% Fully exposed – 4.6% Tree – 2.9% Water – 1.8% Unknown – 3.2%

Histopathology Evidence of parasite migration in tissues but no actual parasites have been seen in slide sections Some parasites found in the lungs but have not been submitted yet for identification No evidence of IBD Most were remarked to be in good health and physical condition based on tissue samples

Diet Virginia Opossum Grey Squirrel Feral Cat Rat Otter?

Management Suggestions Still preliminary results small sample size Map out burrows/solution holes in pine rockland and monitor Maintain adults with transmitters near breeding season and monitor closely ~Oct-Nov November 1st Search areas immediately around where neonates are found – May-Sept