jane12306-sup-0001

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Stomach content analysis
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Number of individual prey items (i.e., numerical counts) was assigned based on the
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presence of species-specific body parts known to represent one individual for a particular taxon.
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All prey taxa were first identified to the lowest taxonomic subdivision possible, in most cases
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genus or species, and then categorized into resource groups according to the prey species’ known
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habitat use patterns and presence in specific habitats during stable isotope sampling. Prey were
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classified into either marine/estuarine (species which inhabit marine/estuarine habitats as well as
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those that are known to consume resources from both marine/estuarine and freshwater/upland
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habitats) or freshwater/upland (species which inhabit freshwater wetlands or terrestrial upland
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habitats) resource categories. Cross-ecosystem foragers, Procyon lotor Linnaeus 1758
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(Procyonidae, raccoon) for example, were classified as marine/estuarine since these species often
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obtain a large portion of their dietary resources from marine/estuarine ecosystems (Fleming,
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Palisano & Joanen 1969).
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Stable isotope sample collection and analysis
Crocodilian scutes (superficial scale-like structures of the skin) are chiefly composed of
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two biological materials, keratinous epidermal layer and cartilaginous dermal layer comprised of
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dense collagen fibers (Alibardi & Thompson 2000; Alibardi & Toni 2007). Frozen whole caudal
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scute samples were thawed, cleaned with deionized water and gently hand washed to remove
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foreign debris (i.e., epiphytic algae and detritus). After cleaning, the keratinous epidermal layer
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of the scutes was separated from dermal collagen layer using NaOH digestion (Radloff, Hobson
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& Leslie 2012) or mechanically using a sterile scalpel. Isolated keratin samples were dried for
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48 hours at 60 °C and ground. Alligator mississippiensis scute tissue has a slow rate of turnover
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(590 days for δ13C and 414 days for δ15N, Rosenblatt and Heithaus 2013), thus stable isotope
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signatures of scute keratin represent incorporation of long-term dietary patterns (> 1 year).
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Representative primary producer and potential prey species were sampled
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opportunistically from fall 2007 to summer 2009 at five sites within upland freshwater habitats
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and five sites within marine/estuarine habitats (Fig. 1). If samples could not be collected, values
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were obtained from literature sources. For primary producers, aggregate samples consisted of
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live green leaves collected from 10 to 15 individual plants or live clumps in the case of
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macroalgae species. All samples were placed on ice at the time of collection and frozen at -10
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°C until further processing. Samples were washed with deionized water, gently rubbed free of
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debris, dried at 60 °C for 48 hours, and ground.
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Representative prey items and food web constituents were sampled using dip-nets,
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minnow traps, seine nets, single-line sampling, collected from roadkill, and harvested by local
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recreational hunters and fishermen. Smaller organisms (< 1cm) were aggregate samples
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consisting of 10-15 whole individuals. For larger animals, 1 to 3 g of bulk muscle tissue was
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taken from a single specimen. Animal samples were cleaned with deionized water, indigestible
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body portions removed (i.e., carbonate shell, scales, hair), dried at 60 °C for 48 hours or until
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completely dehydrated and ground.
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Approximately 500 to 800 µg of homogenized animal tissues or 1 to 3 mg of plant tissues
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was weighed and loaded into 9 × 5 mm tin capsules for stable isotope analysis at the University
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of Florida Geology Stable Isotope Laboratory, Gainesville, Florida. Analyses were performed
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using one of two systems: either a Finnigan DeltaPlus XL isotope mass spectrometer with
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ConFlo III interface linked to a Costech ECS 4010 Elemental Combustion System (elemental
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analyzer) or Finnigan-MAT 252 isotope ratio mass spectrometer coupled with a ConFlo II
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interface linked to a Carlo Erba NA 1500 CNS Elemental Analyzer. Stable isotope values are
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expressed in standard per mil notation δX (‰): δX (‰) = [Rsample⁄Rstandard -1 ]×1000, where X is
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the element of interest and R is the ratio of heavy to light isotopes (13C/12C or 15N/14N) of the
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sample and standard (Vienna Pee Dee Belemnite used for δ13C and Atmospheric Nitrogen-AIR
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for δ15N). Machine accuracy was measured and corrected for during each sample run, using four
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measures of in-lab standard USGS-40 (l-glutamic acid, δ13C = -26.39 and δ15N = −4.52) with
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analytical machine error for USGS-40 was 0.12‰ ± 0.04 for δ15N and 0.1‰ ± 0.05 δ13C (mean ±
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SD).
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References
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Alibardi, L. & Thompson, M.B. (2000) Scale morphogenesis and ultrastructure of
dermis during embryonic development in the alligator (Alligator
mississippiensis, Crocodilia, Reptilia). Acta Zoologica, 81, 325–338.
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Alibardi, L. & Toni, M. (2007) Characterization of keratins and associated proteins
involved in the corneification of crocodilian epidermis. Tissue and Cell, 39,
311–323.
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Fleming, D.M., Palisano, A.W. & Joanen, T. (1969) Food Habits of Coastal Marsh
Raccoons with Observations of Alligator Nest Predation. Wildlife Session pp.
348–357. U.S. Fish and Wildlife Service.
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Radloff, F.G.T., Hobson, K.A. & Leslie, A.J. (2012) Characterising ontogenetic
niche shifts in Nile crocodile using stable isotope (δ13C, δ15N) analyses of
scute keratin. Isotopes in Environmental and Health Studies, 48, 439–56.
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