Editorial Type: Articles
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Online Publication Date: 18 Dec 2018

Comparisons of Summer and Winter Patterns in Ovarian Development, Plasma Vitellogenin, and Sex Steroids in Female Diamondback Terrapins (Malaclemys terrapin) in Southern Florida

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Article Category: Research Article
Page Range: 227 – 235
DOI: 10.2744/CCB-1310.1
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Abstract.

The reproductive cycles of turtles are linked to environmental factors, such as photoperiod and temperature. Currently, the reproductive physiology of diamondback terrapins (Malaclemys terrapin) is poorly understood, especially in Gulf of Mexico. The reproductive cycles of terrapins are thought to follow typical seasonal patterns. However, latitudinal variations in temperature regimens lead to longer-lasting warm periods, which can facilitate extended reproductive periods in some turtle species. This suggests that terrapins may show a similar change in the southern parts of their range. To elucidate aspects of the terrapin reproductive cycle, we sampled during the known reproductive season of a southern population of terrapins (May–July), as well as during the winter in late December and early January. We used enzyme-linked immunosorbent assays to quantify concentrations of the plasma sex hormones estradiol and testosterone, and the egg yolk protein precursor vitellogenin. Additionally, we used radiography and ultrasonography to monitor the ovarian status and egg development in females. Follicles showed no significant difference in average diameter across sampling periods with preovulatory class follicles existing in both summer and winter. Eggs were only detected from May to July, with radiographic data showing second clutches in 4 individuals. Testosterone and estradiol showed elevated concentrations throughout the nesting season, coinciding with multiple clutches of eggs, before both showed a significant decrease in winter. Vitellogenin showed peak concentrations in June with other months showing lower but detectable concentrations. Our results suggest that in southwestern Florida, terrapins may have extended reproductive potential and continuous vitellogenic cycles given the presence of preovulatory follicles and high quantities of vitellogenin found in summer and winter. However, true continuous reproduction was not detected in this study.

The diamondback terrapin (Malaclemys terrapin) is the only obligate estuarine chelonian species in the United States ranging from the Texas Gulf of Mexico coast up the eastern seaboard to Cape Cod (Carr 1952; Gibbons et al. 2001). Terrapins use many forms of coastal habitat and may serve as keystone species in coastal ecosystems (Levesque 2000; Cole and Hesler 2001). Terrapins have a history of exploitation by the food trade (Schaffer et al. 2008), with more recent threats such as habitat fragmentation, incidental drowning as bycatch, and collection for the pet trade negatively influencing populations (Bishop 1983; Wood and Herlands 1997; Cheung and Dudgeon 2006; Coleman et al. 2014; Crawford et al. 2014). These pressures and declines in populations have led to terrapins being listed as imperiled or vulnerable in several states (Hackney 2010), while also leading to additional population assessments in both government-based and independent studies (Mitro 2003; Butler et al. 2006; Hart and McIvor 2008; Boykin 2011; Selman et al. 2014). Many facets of terrapin life history have been studied; however, our understanding of their reproductive endocrinology, particularly with respect to the Gulf of Mexico populations, is lacking. Further understanding the reproductive cycles of this species throughout its range could lead to better understanding of reproductive seasons, and in turn allow for additional and more appropriate conservation practices to be employed.

Currently, our knowledge of diamondback terrapin reproductive cycles largely comes from populations in more northern latitudes along the eastern seaboard. In these populations, terrapins show a peak nesting period ranging from April to July, before slowing down in August and becoming inactive in the late fall or winter (Seigel 1980; Lazell and Auger 1981; Roosenburg 1994; Wood and Herlands 1997). Terrapin reproductive cycles are likely linked to temperature and photoperiods, as is the case in other species (Ganzhorn and Licht 1983; Mendonca 1987). However, some species with ranges extending into southern latitudes with mild winter temperatures show extended reproductive potential compared to northern conspecifics (Iverson 1977; McPherson and Marion 1981; Kuchling 1999b).

Many species also show variation of clutch size and egg size across latitudes, including M. terrapin (Tinkle 1961; Greaves and Litzgus 2009; Allman et al. 2012). It is possible that terrapin endocrine cycles might show similar variation across latitudinal gradients, with the potential for continuous reproductive cycles in more southern regions with less intense winters (Licht 1984).

Further, most studies of M. terrapin have rarely investigated ovarian progression and hormonal production and have almost solely relied on nesting females to assess reproductive activity with the exceptions of thesis studies by Lee (2003) and Wolf (2014), which used hormones, ultrasound data, or proteins to determine reproductive status. Nesting females offer important information into the reproductive activity of these animals but may not tell the full story of reproductive cycles, as differences in hormonal concentrations due to the stress and rigor of nesting may obscure the actual status of reproductive cycles (Winters et al. 2016).

Reproductive cycles in most nonavian reptile species can be described as a derivative of 1 of 2 major categories: prenuptial cycles, in which gametes are produced rapidly just prior to reproductive activities (e.g., mating, nesting), or postnuptial cycles, in which gametes begin developing shortly after the reproductive seasons have ceased (Gorman et al. 1981; Licht et al. 1982; van Wyk 1995). Often, cycles can be diagnosed via the proliferation of ovarian follicles in the case of females, and the growth of testes and production of sperm in males (Gibbons 1968; Georges 1983; Iverson and Moler 1997; Meylan et al. 2002). Steroid hormones such as testosterone (T) and estradiol (E2) can also serve as key indicators of reproductive cycles, often showing increases that correspond to seasonal reproductive activity and gonadal development (Amey and Whittier 2000; Edwards and Jones 2001; Hamann et al. 2002; Huot-Daubremont et al. 2003). The egg yolk protein precursor vitellogenin (Vtg) is regulated by E2, and is deposited into developing ovarian follicles to serve as nourishment for developing embryos once eggs are laid (Cree et al. 1991; Kuchling 1999a). Like steroid hormones, Vtg can be used to monitor the reproductive status of females in oviparous species (Ho et al. 1982; Heck et al. 1990).

The purpose of this study was to elucidate the reproductive cycles of M. terrapin in south Florida, using the gonadal steroids T and E2, along with Vtg and radiographs and ultrasound imaging of the ovaries. We hypothesized that terrapins in southern Florida would exhibit the ability to reproduce in an extended fashion, similar to other species with ranges extending across diverse latitudes (Iverson 1977; McPherson and Marion 1981; Moll and Moll 1990; Kuchling 1999b).

METHODS

Study Site

We sampled terrapins in a single mangrove estuary, predominantly composed of red mangrove (Rhizophora mangle) and black mangrove (Avicennia germinans), with intersecting tidal creeks that emptied into the Pine Island Sound of Lee County, Florida. Terrapins were sampled in collaboration with an ongoing mark–recapture study with the Sanibel Captiva Conservation Foundation.

Sample Collection

During the spring and summer of 2014, we sampled for terrapins across 8 d in May (∼ 60 survey hours), 7 d in June (∼ 50 survey hours), 5 d in July (∼ 40 survey hours), and 3 d (∼ 25 survey hours) in December and January of 2014–2015. Gravid females were previously documented in this population, between late April and late July (C. Lechowicz, unpubl. data, 2013). Terrapins were sampled exclusively through opportunistic hand capture, taking advantage of inflow and outflow of water from tidal creeks as has been documented in other populations (Tucker et al. 1995). Upon capture terrapins were sexed by external dimorphic characters, such as tail length and head width (Gibbons and Lovich 1990).

Upon first handling, between 0.5 and 2.0 ml of blood was collected from the subcarapacial sinus via a syringe with a heparinized 25-gauge needle. Blood was drawn within 5–10 min of capture. This time frame reduces the potential for stress-induced artefacts as documented in other species (Mahmoud et al. 1989; Owens 1997). Whole blood was put into 1.5-ml Eppendorf tubes and stored on ice immediately after collection. Samples were centrifuged within 3 hrs of collection to separate plasma, which was then stored on dry ice before transport to a −80°C freezer. Animals were measured, tagged with passive integrated transponders, and marked on the external marginal scutes via the Cagle (1939) method before release.

Ultrasound/Radiographic Imaging

From May to July 2014, female terrapins were transported to the Clinic for the Rehabilitation of Wildlife, Sanibel, Florida, for ultrasound and radiographic examination in order to determine ovarian status and clutch size. During the December−January sampling a portable ultrasound (TITAN, Sonosite Inc, Bothell, WA) was used to inspect ovarian development in the field. Egg and ovarian follicle diameters were measured to the nearest 0.1 cm using built-in caliper tools in Sonosite software or post hoc using ImageJ (Schneider et al. 2012) owing to a limit on the number of measurements in the active Sonosite software. Follicles were assigned to 1 of 4 size classes (C) as described by Lahanas (1982) and Mitchell (1985) (C1, < 0.6 cm; C2, 0.6–1.1 cm; C3, 1.1–1.6 cm; C4, > 1.6 cm). Both ultrasounds used convex-type probes (3.5–6.8 MHz), with the portable Sonosite machine using a slightly smaller microconvex probe.

Hormone and Vtg Assays

We used commercial enzyme-linked immunosorbent assay (ELISA) kits (Enzo Life Sciences, Farmingdale, NY) for measuring both E2 and T. High-sensitivity kits (products ADI-901-176 and ADI-900-174) were used to quantify the hormones. Hormone kits were validated for this species via parallelism tests of M. terrapin plasma to the standard curve of the assay. Hormone extractions were performed using 150–400 μl of plasma using the methods described by Myre et al. (2016) and Smelker et al. (2014). Predicted hormone concentrations were corrected for the amount of buffer used for reconstitution prior to analysis. Animals with concentrations of hormones below detectable limits were assigned a concentration of 0 pg/ml.

For Vtg measurement, we used an in-house ELISA similar to that described by Smelker et al. (2014), using Trachemys scripta anti-Vtg antibodies, which have shown excellent cross-reactivity among turtles of the Emydidae family, including M. terrapin (Wolfe 2014). Briefly, diluted purified Vtg standards and samples using phosphate-buffered saline (PBS) were set up at dilutions ranging from pure plasma to 1:7500. We placed these standards and samples on 96-well microplates and incubated microplates at 4°C overnight. The following day, plates were washed with PBS–Tween 20 solution (100 μl of Tween 20 per 100 ml of PBS), blocked with PBS Blotto (5 g nonfat dry milk per 100 ml PBS), and incubated at room temperature on a gentle shaker (600 rpm) for 2 hrs. A primary Vtg antibody developed from T. scripta was then presorbed at room temperature for 1 hr in 1:1000 PBS Blotto with 12 μl male terrapin plasma determined to have undetectable concentration of Vtg. This antibody solution was then diluted at 250 μl:10,000 μl prior to plating. The plate was washed before being filled with the primary antibody and incubated for 2 hrs at room temperature on a gentle shaker. A secondary antibody, goat anti-rabbit IgG coupled to horseradish peroxidase (Bio-Rad Laboratories Inc, Hercules, CA), was diluted 5 μl:10,000 μl and added to the plate after washing, and again allowed to incubate for 2 hrs at room temperature. Following the wash of the secondary antibody, 100 μl of 3,3′,5,5′-170 tetramethylbenzidine peroxidase ELISA substrate kit substrate (Bio-Rad) was added to each well and allowed to incubate for 10 min. The subsequent reaction was stopped using 100 μl of 1 N H2SO4 per well. Following the addition of the stop solution, the plate was read using a Bio-Rad 550 microplate reader at 450 nm. Concentrations were predicted via the standard curve analysis (SigmaPlot 13.0) and corrected by the corresponding dilution factor before analysis.

Statistical Analysis

A 1-way analysis of variance was used to investigate the relationship between sampling period, follicle size, hormones, and Vtg. We performed a Levene's test to check for homogeneity of variance (p > 0.05). Normality of data was tested using a 1-sample Kolmogorov-Smirnov test with Lilliefors p-value (p > 0.05). In order to meet the assumption of a normal distribution and equal variances, data for T, E2, and Vtg, were rank, log, or square-root transformed if p < 0.05. A Tukey's post hoc test or contrasts study was used to discern significant differences between sampling periods (p < 0.05). Analyses were performed in SigmaPlot 13.0 and SYSTAT 13.0. All figures display raw untransformed data. Statistics are reported as  ± SE.

RESULTS

Capture Effort

A total of 29 capture events took place of 18 individual terrapins: May (n = 11), June (n = 7), July (n = 8), and (n = 3) in late December–January. Nine of these individuals were recaptured in different sampling periods (Table 1), likely because of a small population size with a greater than 60% recapture probability (C. Lechowicz, unpubl. data, 2013). Recaptures that occurred in separate months were treated as independent samples, while 3 individuals that were recaptured within the same sampling month were removed from analysis to avoid pseudoreplication.

Table 1. List of recaptured terrapins by ID and capture month; x represents no sample.

              Table 1.

Ultrasound/Radiographic Imaging

Ultrasound data revealed multiple size classes of follicles (C1–C4) across months (Fig. 1). The average follicle diameter did not vary significantly throughout sampling periods, with animals exhibiting C3- and C4-sized preovulatory follicles in each period (F3,16 = 3.238; p = 0.815). Seventy-eight percent of the terrapins (n = 18) examined via ultrasound had C3 or C4 follicles. No follicular atresia or ovarian quiescence was detected in any sampling period. Radiography revealed 13 (n = 18) gravid females (shelled eggs) from May to July with an average clutch size of 6.15 ± 0.30 eggs. Second clutches of eggs were detected in 4 individuals (Fig. 2), with some of these gravid females showing large C3 and C4 follicles that could yield potential third (or more) clutches. No shelled eggs were detected during winter sampling.

Figure 1. (A) C3 class 1.52-cm follicle as indicated by calipers from the female terrapin (ID 22) in December 2015. (B) C2 and C3 class follicles from same terrapin in June 2014. Follicle size as indicated by calipers from left to right: 1.41 cm (squares), 0.9 cm (plus signs), and 1.59 cm (× symbols).Figure 1. (A) C3 class 1.52-cm follicle as indicated by calipers from the female terrapin (ID 22) in December 2015. (B) C2 and C3 class follicles from same terrapin in June 2014. Follicle size as indicated by calipers from left to right: 1.41 cm (squares), 0.9 cm (plus signs), and 1.59 cm (× symbols).Figure 1. (A) C3 class 1.52-cm follicle as indicated by calipers from the female terrapin (ID 22) in December 2015. (B) C2 and C3 class follicles from same terrapin in June 2014. Follicle size as indicated by calipers from left to right: 1.41 cm (squares), 0.9 cm (plus signs), and 1.59 cm (× symbols).
Figure 1. (A) C3 class 1.52-cm follicle as indicated by calipers from the female terrapin (ID 22) in December 2015. (B) C2 and C3 class follicles from same terrapin in June 2014. Follicle size as indicated by calipers from left to right: 1.41 cm (squares), 0.9 cm (plus signs), and 1.59 cm (× symbols).

Citation: Chelonian Conservation and Biology 17, 2; 10.2744/CCB-1310.1

Figure 2. (A) Female terrapin (ID 71) showing a clutch of 6 eggs on 28 May 2014. (B) The same female on 27 June 2014 with a clutch of 5 eggs, signifying a second clutch.Figure 2. (A) Female terrapin (ID 71) showing a clutch of 6 eggs on 28 May 2014. (B) The same female on 27 June 2014 with a clutch of 5 eggs, signifying a second clutch.Figure 2. (A) Female terrapin (ID 71) showing a clutch of 6 eggs on 28 May 2014. (B) The same female on 27 June 2014 with a clutch of 5 eggs, signifying a second clutch.
Figure 2. (A) Female terrapin (ID 71) showing a clutch of 6 eggs on 28 May 2014. (B) The same female on 27 June 2014 with a clutch of 5 eggs, signifying a second clutch.

Citation: Chelonian Conservation and Biology 17, 2; 10.2744/CCB-1310.1

Hormone and Vtg Assays

T was detectable in all analyzed samples (n = 25) with a range of 8.3–412.2 pg/ml. E2 was detectable in all but 2 samples (n = 26) ranging from 0 to 318.7 pg/ml. Terrapins showed no significant differences in T across the summer sampling period but did show a significant drop during the winter sampling period (F1,21 = 4.611; p = 0.044) (Fig. 3). E2 showed no significant differences across summer sampling months until a significant decline in concentration was observed in December–January (F1,22 = 5.042; p = 0.035) (Fig. 3). The average T intra-assay coefficient of variation (CV) was 8.66% and the interassay CV was 10.58%. The average intra-assay CV for E2 was 9.74% and the interassay CV was 12.3%.

Figure 3. Mean testosterone, estradiol, and vitellogenin concentrations in terrapins across sampling months. Letters indicate significant differences. Sample size indicated by numbers within bars.Figure 3. Mean testosterone, estradiol, and vitellogenin concentrations in terrapins across sampling months. Letters indicate significant differences. Sample size indicated by numbers within bars.Figure 3. Mean testosterone, estradiol, and vitellogenin concentrations in terrapins across sampling months. Letters indicate significant differences. Sample size indicated by numbers within bars.
Figure 3. Mean testosterone, estradiol, and vitellogenin concentrations in terrapins across sampling months. Letters indicate significant differences. Sample size indicated by numbers within bars.

Citation: Chelonian Conservation and Biology 17, 2; 10.2744/CCB-1310.1

All females analyzed (n = 26) had detectable concentrations of Vtg ranging from 14.28 to 51.74 mg/ml. Vtg showed significant variation between months sampled (F3,22 = 7.626; p = 0.001). Vtg concentrations showed a significant increase from May to June followed by a significant decrease in July with no significant differences from May or July detected in December–January samples (Fig. 3). The average Vtg intra-assay CV was 4.9% and the interassay CV was 14.4%.

DISCUSSION

Patterns in Ovarian Development and Egg Production

The presence of large (C3 and C4) preovulatory follicles and the lack of atretic follicles in any sampling period suggest that ovulation, fertilization, and oviposition could be possible even in the winter months, as has been documented in other closely related species in the Emydidae family (Iverson 1977; Vogt 1990). However, the small sample sizes, particularly during winter months, limit the depth of the conclusions that can be made.

The only other study to our knowledge to examine ovarian development in this species was an unpublished thesis by Lee (2003), in which follicular quiescence was observed in late summer, with recrudescence beginning during the fall in a South Carolina population. In this same study, follicles of preovulatory size (< 1.0 cm) were first documented in the winter, showing little change until ovulation in the spring. This suggests a postnuptial cycle that arrests during winter months. Our Florida data, although limited in scope by comparison, showed no instances of quiescence or atresia in our later samples, and large follicles (> 1.0 cm, designated as C3 and C4 classes) were observed through all sampling periods, consistent with Lee's (2003) observations.

Hormonal Patterns

T showed no significant difference across summer sampling periods but did show a significant decrease in the December–January sampling period. T has been observed to decrease as the nesting period progresses in northern populations of M. terrapin (Winters et al. 2016) and in other turtle species (Licht et al. 1985; Currylow et al. 2013; Myre et al. 2016); however, we did not see the same trend in this population during the confirmed nesting months. This may suggest an extended summer period of reproduction, with a decrease potentially not beginning until later in August or the following fall.

Similarly, E2 showed sustained concentrations throughout the nesting season in Florida before declining in December–January. These sustained concentrations during the nesting season correspond to trends seen in other multiclutching species of turtles (McPherson et al. 1982, with elevations in E2 during the nesting season corresponding to the maintenance of ovarian follicles for the production of additional clutches of eggs. This is further supported by the existence of multiple clutches of eggs in the same females in the May–June sampling period.

The winter decline in both T and E2 was somewhat unexpected as the animals captured were actively foraging and swimming and presented large presumably steroidogenic preovulatory follicles, suggesting the environmental conditions were acceptable for reproductive activity. However, it is possible that even in a warmer winter scenario, these terrapins may have a hormonal cycle conserved from their more northern relatives, where an arrest in steroidogenesis might occur until the beginning of the nesting period. It is also possible that elevated concentrations of E2 are not required to sustain follicular proliferation outside of the nesting season, given its potency in chelonians. In a study involving exogenous injections of E2 in Lepidochelys kempii, a small dose has been shown to increase Vtg concentrations for months after the termination of injection (Heck et al. 1997).

Vtg Patterns

Terrapins were expected to show elevated concentration of Vtg throughout the year as part of a continuous reproductive cycle. However, a significant increase in Vtg was observed in June with a significant decline shown in July and December–January. This is similar to the trend seen by Wolfe (2014) in M. terrapin in the northern distribution of their range. In that study, Vtg showed significant decreases from June to July, followed by a further significant drop in early August to below detectable limits (0 mg/ml). Limited ultrasound data were gathered in the Wolfe (2014) study; however, it is highly likely that gonadal quiescence had begun in later summer samples given the large decrease in circulating Vtg. Similar patterns have been documented at the end of nesting cycles in Chrysemys picta (Duggan et al. 2001) and Chinemys reevesii (Saka et al. 2011). However, in our study no significant differences were observed between May, July, and December–January, with all 3 of these periods showing concentrations well within detectable limits. The small winter sample size may play a role in the lack of significance between some of these other months; however, it should be noted that the range of concentrations in winter samples was 14.3–22.4 mg/ml, values well above basal concentrations and within the range of Vtg concentrations detected during the summer months.

There were no signs of ovarian quiescence or follicular atresia observed in any July-sampled turtles with several individuals exhibiting C4 size class follicles. One female (ID 22) was sampled in both July and December and displayed C3-sized follicles in both instances with Vtg concentrations of 19.3 and 15.1 mg/ml, respectively. This, and the lack of follicular atresia observed in any female turtle, is consistent with the idea that the vitellogenic cycle in the Florida population may be continuous and is extending past typically known periods. This has been documented in some species such as the spotted turtle (Clemmys guttata). Clemmys guttata females begin developing follicles a year in advance and undergo a continuous vitellogenic cycle with perhaps only a brief dormancy period during winter, while not ovulating until the spring nesting season (Ernst and Zug 1994).

Conclusions

Here we report a portion of the seasonal reproductive patterns M. terrapin exhibit in southwest Florida. Our data suggest that the reproductive cycle of terrapins in southern Florida may be modified in the form of extended reproduction with animals having the potential to produce additional clutches of eggs into and past August given the lack of atretic follicles observed, as well as the high concentrations of Vtg relative to other studies that were observed. This is consistent with the idea of a continuous vitellogenic cycle in these animals; however, without access to data from these turtles in the late summer or fall we cannot be certain.

Although incomplete and with sample-size limitations in some sampling periods, the data collected for this study, provide baseline trends and values for Vtg, gonadal steroids, and ovarian observations for future comparative studies in other populations. The limits of this study highlight the need for continued research in this region and across the range of M. terrapin, in order to further our knowledge on the reproductive endocrinology of this species. Endocrinology has been used in variety of ways to both inform and apply conservation tactics to chelonian taxa. Currylow et al. (2017) used both reproductive and stress hormone production as an indicator of potential reproductive success in the critically endangered species, Astrochelys yniphora, to help facilitate more efficient captive management of assurance colonies. Fluctuations of hormone concentrations may also serve as indicators of environmental stressors such as contaminants, climate change, and habitat degradation (Crews et al. 1995; Shelby and Mendonca 2001; Cash and Holberton 2005), with baseline data serving as critical information for comparisons in the future. Thus, further understanding the reproductive output and variations in the reproductive cycle of Malaclemys could aid in defining conservation objectives and policies, facilitating a wider breadth of protections for the species.

Acknowledgments

We would like to thank Heather Barron and the staff at the Clinic for the Rehabilitation of Wildlife for the use of their radiograph and ultrasound equipment. We thank Eric Milbrandt and Rick Bartleson of the Sanibel Captiva Conservation Foundation Marine laboratory, and Jennifer Mauser of the Florida Gulf Coast University science department for sample storage space. We thank Gary Childers and the Southeastern Louisiana University Microbiology laboratory for access to their plate reader. We thank Michael Garafolo of Enzo Life Sciences for providing a discounted rate on ELISA kits. We also thank Josh Cahal, Pam Clarkson, Andy Coleman, Andrea Currylow, Joshua Allen Donini, Jennifer Lamb, Chris Long, and Gary Shafer for input on statistical analysis, image and figure enhancement, and reviewing early drafts of the manuscript. We would also like to thank both anonymous reviewers for their comments and suggestions during the review process. Funding for this project was provided by the Diamondback Terrapin Working Group research grant, the Minnesota Herpetological Society research grant, the Ding Darling Friends of Wildlife scholarship fund, and the Southeastern Louisiana University Biology Department developmental fund. Research activities for this project were approved by the Southeastern Louisiana University Institutional Animal Care and Use Committee (Protocol 30). All capture and sampling were conducted under FWC permit LSSC-13-00036A.

LITERATURE CITED

  • Allman, P.E.,
    Place, A.R.,
    and
    Roosenburg, W.M.
    2012. Geographic variation in egg size and lipid provisioning in the diamondback terrapin Malaclemys terrapin. Physiological and Biochemical Zoology85:442449.
  • Amey, A.P.
    and
    Whittier, J.M.
    2000. Seasonal patterns of plasma steroid hormones in males and females of the bearded dragon lizard, Pogona barbata. General and Comparative Endocrinology117:335342.
  • Bishop, J.M.
    1983. Incidental capture of diamondback terrapin by crab pots. Estuaries6:426430.
  • Boykin, C.
    2011. The status and demography of the ornate diamondback terrapin (Malaclemys terrapin macrospilota) within the Saint Martins Marsh Aquatic Preserve.
    Department of Environmental Protection
    ,
    Florida
    .
  • Butler, J.A.,
    Heinrich, G.L.,
    and
    Siegal, R.A.
    2006. Third workshop on the ecology, status and conservation of diamondback terrapins (Malaclemys terrapin): results and recommendations. Chelonian Conservation and Biology5:331334.
  • Cagle, F.R.
    1939. A system of marking turtles for future identification. Copeia1939:170173.
  • Carr, A.F.
    1952. Handbook of Turtles.
    Ithaca, NY
    :
    Comstock Publishing Association
    ,
    60
    pp.
  • Cash, B.W.
    and
    Holberton, R.L.
    2005. Endocrine and behavioral response to a decline in habitat quality: effects of pond drying on the slider turtle, Trachemys scripta. Journal of Experimental Zoology Part A: Ecological and Integrative Physiology303:872879.
  • Cheung, S.M.
    and
    Dudgeon, D.
    2006. Quantifying the Asian turtle crisis: market surveys in southern China, 2000–2003. Aquatic Conservation: Marine and Freshwater Ecosystems16:751770.
  • Cole, R.V.
    and
    Helser, T.E.
    2001. Effect of three bycatch reduction devices on diamondback terrapin Malaclemys terrapin capture and blue crab Callinectes sapidus harvest in Delaware Bay. North American Journal of Fisheries Management21:825833
  • Coleman, A.T.,
    Roberge, T.,
    Wibbles, T.,
    Marion, K.,
    Nelson, D.,
    and
    Dindo, J.
    2014. Size-based mortality of adult female diamond–backed terrapins (Malaclemys terrapin) in blue crab traps in a Gulf of Mexico population. Chelonian Conservation and Biology13:140145.
  • Crawford, B.A.,
    Maerz, J.C.,
    Nibblelink, N.P.,
    Buhlmann, K.A.,
    Norton, T.M.,
    and
    Albeke, S.E.
    2014. Hot spots and hot moments of diamondback terrapin road-crossing activity. Journal of Applied Ecology51:367375.
  • Cree, A.,
    Guillette, L.J., Jr.,
    Brown, M.A.,
    and
    Chambers, G.K.
    1991. Slow estradiol–induced vitellogenesis in the tuatara, Sphenodon punctatus. Physiological and Biochemical Zoology64:12341251.
  • Crews, D.,
    Bergeron, J.M.
    and
    McLachlan, J.A.
    1995. The role of estrogen in turtle sex determination and the effects of PCBs. Environmental Health Perspectives103:7377.
  • Currylow, A.F.,
    Mandimbihasina, A.,
    Gibbons, P.,
    Bekarany, E.,
    Stanford, C.B.,
    Louis, E., Jr.,
    and
    Crocker, D.E.
    2017. Comparative ecophysiology of a critically endangered (CR) ectotherm: implications for conservation management. PLoS One 12:p.e0182004.
  • Currylow, A.F.,
    Tift, M.S.,
    Meyer, J.L.,
    Crocker, D.E.,
    and
    Williams, R.N.
    2013. Seasonal variations in plasma vitellogenin and sex steroids in male and female eastern box turtles, Terrapene carolina carolina. General and Comparative Endocrinology180:4855.
  • Duggan, A.,
    Paolucci, M.A.,
    Tercyak, A.,
    Gigliotti, M.,
    Small, D.,
    and
    Callard, I.
    2001. Seasonal variation in plasma lipids, lipoproteins, apolipoprotein A-I and vitellogenin in the freshwater turtle, Chrysemys picta. Comparative Biochemistry and Physiology Part A: Molecular & Integrative Physiology130:253269.
  • Edwards, A.
    and
    Jones, S.M.
    2001. Changes in plasma testosterone, estrogen, and progesterone concentrations throughout the annual reproductive cycle in male viviparous blue–tongued skinks, Tiliqua nigrolutea, in Tasmania. Journal of Herpetology35:293299.
  • Ernst, C.H.
    and
    Zug, G.R.
    1994. Observations on the reproductive biology of the spotted turtle, Clemmys guttata in southeastern Pennsylvania. Journal of Herpetology28:99102.
  • Ganzhorn, D.
    and
    Licht, P.
    1983. Regulation of seasonal gonadal cycles by temperature in the painted turtle, Chrysemys picta. Copeia1983:347358.
  • Georges, A.
    1983. Reproduction of the Australian freshwater turtle Emydura krefftii (Chelonia: Chelidae). Journal of Zoology201:331350.
  • Gibbons, J.W.
    1968. Reproductive potential, activity, and cycles in the painted turtle, Chrysemys picta. Ecology49:399409.
  • Gibbons, J.W.
    and
    Lovich, J.E.
    1990. Age at maturity influences adult sex ratio in the turtle Malaclemys terrapin. Oikos1990:126134.
  • Gibbons, J.W.,
    Lovich, J.E.,
    Tucker, A.D.,
    Fitzsimmons, N.N.,
    and
    Greene, J.L.
    2001. Demographic and ecological factors affecting conservation and management of the diamondback terrapin (Malaclemys terrapin) in South Carolina. Chelonian Conservation and Biology4:6674.
  • Gorman, G.C.,
    Licht, P.,
    and
    McCollum, F.
    1981. Annual reproductive patterns in three species of marine snakes from the central Philippines. Journal of Herpetology15:335354.
  • Greaves, W.F.
    and
    Litzgus, J.D.
    2009. Variation in life-history characteristics among populations of North American wood turtles: a view from the north. Journal of Zoology279:298309.
  • Hackney, A.D.
    2010. Conservation biology of the diamondback terrapin in North America: policy status, nest predation, and managing island populations. MS Thesis,
    Clemson University
    ,
    Columbia, SC
    .
  • Hamann, M.,
    Limpus, C.,
    and
    Owens, D.
    2003. Reproductive cycles of males and females. In:
    Lutz, P.,
    Musick, J.,
    and
    Wyneken, J.
    (Eds.). The Biology of Sea Turtles. Volume II.
    Boca Raton, FL
    :
    CRC Press
    , pp. 135161.
  • Hart, K.M.
    and
    McIvor, C.C.
    2008. Demography and ecology of mangrove diamondback terrapins in a wilderness area of Everglades National Park, Florida, USA. Copeia2008:200208.
  • Heck, J.,
    Mackenzie, D.S.,
    and
    Owens, D.
    1990. Vitellogenin from the Kemp's ridley sea turtle. American Zoologist30:A23.
  • Heck, J.,
    Mackenzie, D.S.,
    Rostal, D.,
    Medler, K.,
    and
    Owens, D.
    1997. Estrogen induction of plasma vitellogenin in the Kemp's ridley sea turtle. General and Comparative Endocrinology107:280288.
  • Ho, S.M.,
    Kleis, S.,
    McPherson, R.,
    Heisermann, G.J.,
    and
    Callard, I.P.
    1982. Regulation of vitellogenesis in reptiles. Herpetologica38:4050.
  • Huot-Daubremont, C.,
    Bradshaw, S.D.,
    Bradshaw, F.J.,
    Kuchling, G.,
    and
    Grenot, C.J.
    2003. Variation of plasma sex steroid concentrations in wild and captive populations of Hermann's tortoise (Testudo hermanni hermanni) in Southern France. General and Comparative Endocrinology130:299307.
  • Iverson, J.B.
    1977. Reproduction in freshwater and terrestrial turtles of North Florida. Herpetologica1977:205212.
  • Iverson, J.B.
    and
    Moler, P.E.
    1997. The female reproductive cycle of the Florida softshell turtle (Apalone ferox). Journal of Herpetology31:399409.
  • Kuchling, G.
    1999 a. Gonadal cycles and gamete production. In:
    Kuchling, G.
    (Ed.). The Reproductive Biology of the Chelonia.
    Berlin
    :
    Springer
    , pp. 3167.
  • Kuchling, G.
    1999 b. Reproductive cycles and environment. In:
    Kuchling, G.
    (Ed.). The Reproductive Biology of the Chelonia.
    Berlin
    :
    Springer
    , pp. 91106.
  • Lahanas, P.N.
    1982. Aspects of the life history of the southern black-knobbed sawback, Graptemys nigrinoda delticola. MS Thesis,
    Auburn University
    ,
    Auburn, AL
    .
  • Lazell, J.D.
    and
    Auger, P.J.
    1981. Predation on diamondback terrapin (Malaclemys terrapin) eggs by dunegrass (Ammophila breviligulata). Copeia1981:723724.
  • Lee, M.A.
    2003. Reproductive biology and seasonal tesosterone patterns of the diamondback terrapin, Malaclemys terrapin, in the estuaries of Charleston, South Carolina. MS Thesis,
    College of Charleston
    ,
    Charleston, SC
    .
  • Levesque, E.M.
    2000. The distribution and ecology of the diamondback terrapin, (Malaclemys terrapin) in South Carolina Salt Marshes. MS Thesis,
    College of Charleston
    ,
    Charleston, SC
    .
  • Licht, P.
    1984. Season cycles in reptilian reproductive physiology. In:
    Lamming, E.
    (Ed.). Marshall's Physiology of Reproduction.
    Edenborough
    :
    Churchill Livingstone
    , pp. 206282.
  • Licht, P.,
    Breitenbach, G.L.,
    and
    Congdon, J.D.
    1985. Seasonal cycles in testicular activity, gonadotropin, and thyroxine in the painted turtle Chrysemys picta under natural conditions. General and Comparative Endocrinology59:130139.
  • Licht, P.,
    Owens, D.,
    Cliftton, K.,
    and
    Penaflores, C.
    1982. Changes in LH and progesterone associated with the nesting cycle and ovulation in the olive ridley turtle, Lepidochelys olivacea. General and Comparative Endocrinology48:247253.
  • Mahmoud, I.Y.,
    Guillette, L.J.,
    Mcasey, M.E.,
    and
    Cady, C.
    1989. Stress-induced changes in serum testosterone, estradiol-17β and progesterone in the turtle, Chelydra serpentina. Comparative Biochemistry and Physiology Part A: Physiology93:423427.
  • McPherson, R.J.,
    Boots, L.R.,
    MacGregor, R.,
    and
    Marion, K.R.
    1982. Plasma steroids associated with seasonal reproductive changes in a multiclutched freshwater turtle, Sternotherus odoratus. General and Comparative Endocrinology48:440451.
  • McPherson, R.J.
    and
    Marion, K.R.
    1981. The reproductive biology of female Sternotherus odoratus in an Alabama population. Journal of Herpetology15:389396.
  • Mendonca, M.T.
    1987. Photothermal effects on the ovarian cycle of the musk turtle, Sternotherus odoratus. Herpetologica43:8290.
  • Meylan, P.A.,
    Schuler, R.,
    and
    Moler, P.
    2002. Spermatogenic cycle of the Florida softshell turtle, Apalone ferox. Copeia2002:779786.
  • Mitchell, J.C.
    1985. Female reproductive cycle and life history attributes in a Virginia population of painted turtles, Chrysemys picta. Journal of Herpetology19:218226.
  • Mitro, M.G.
    2003. Demography and viability analyses of a diamondback terrapin population. Canadian Journal of Zoology81:716726.
  • Moll, D.L.
    and
    Moll, E.O.
    1990. The slider turtle in the neotropics: adaptation of a temperate species to a tropical environment. In:
    Gibbons, J.W.
    (Ed.). Life History and Ecology of the Slider Turtle.
    Washington, DC
    :
    Smithsonian Institution Press
    , pp. 152161.
  • Myre, B.L.,
    Guertin, J.,
    Selcer, K.,
    and
    Valverde, R.A.
    2016. Ovarian dynamics in free-ranging loggerhead sea turtles (Caretta caretta). Copeia2016:921929.
  • Owens, D.W.
    1997. Hormones in the life history of sea turtles. In:
    Lutz, P.L.
    and
    Musick, J.A.
    (Eds.). The Biology of Sea Turtles.
    New York
    :
    CRC Press
    , pp. 315341.
  • Roosenburg, W.M.
    1994. Nesting habitat requirements of the diamondback terrapin: a geographic comparison. Wetlands Journal6:912.
  • Saka, M.,
    Tada, N.,
    and
    Kamata, Y.
    2011. The annual ovarian cycle of the Reeves' pond turtle Chinemys reevesii (Reptilia: Geoemydidae) based on seasonal variations in the serum vitellogenin level and follicular growth. Current Herpetology30:103110.
  • Schaffer, C.,
    Wood, R.C.,
    Norton, T.M.,
    and
    Schaffer, R.
    2008. Terrapins in the stew. Iguana15:7885.
  • Schneider, C.A.,
    Rasband, W.S.,
    and
    Eliceiri, K.W.
    2012. NIH Image to ImageJ: 25 years of image analysis. Nature Methods9:671675.
  • Seigel, R.A.
    1980. Nesting habits of diamondback terrapins (Malaclemys terrapin) on the Atlantic coast of Florida. Transactions of the Kansas Academy of Science83:239246.
  • Selman, W.,
    Baccigalopi, B.,
    and
    Baccigalopi, C.
    2014. Distribution and abundance of diamondback terrapins (Malaclemys terrapin) in southwestern Louisiana. Chelonian Conservation and Biology. 13:131139.
  • Shelby, J.A.
    and
    Mendonca, M.T.
    2001. Comparison of reproductive parameters in male yellow-blotched map turtles (Graptemys flavimaculata) from a historically contaminated site and a reference site. Comparative Biochemistry and Physiology Part C: Toxicology & Pharmacology129:233242.
  • Smelker, K.,
    Smith, L.,
    Arendt, M.,
    Schwenter, J.,
    Rostal, D.,
    Selcer, K.,
    and
    Valverde, R.A.
    2014. Plasma vitellogenin in free-ranging loggerhead sea turtles (Caretta caretta) of the northwest Atlantic Ocean. Journal of Marine Biology2014:110.
  • Tinkle, D.W.
    1961. Geographic variation in reproduction, size, sex ratio and maturity of Sternotherus odoratus (Testudinata: Chelydridae). Ecology42:6876.
  • Tucker, A.D.,
    Fitzsimmons, N.N.,
    and
    Gibbons, J.W.
    1995. Resource partitioning by the estuarine turtle Malaclemys terrapin: trophic, special, and temporal foraging constraints. Herpetologica51:167181.
  • Van Wyk, J.H.
    1995. The male reproductive cycle of the lizard, Cordylus giganteus (Sauria: Cordylidae). Journal of Herpetology29:522535.
  • Vogt, R.C.
    1990. Reproductive parameters of Trachemys scripta venusta in southern Mexico. In:
    Gibbons, J.W.
    (Ed.). Life History and Ecology of the Slider Turtle.
    Washington, DC
    :
    Smithsonian Institution Press
    , pp. 162168.
  • Winters, J.M.,
    Carruth, W.C.,
    Spotila, J.R.,
    Rostal, D.C.,
    and
    Avery, H.W.
    2016. Endocrine indicators of a stress response in nesting diamondback terrapins to shoreline barriers in Barnegat Bay, NJ. General and Comparative Endocrinology235:136141.
  • Wolfe, S.A.
    2014. Plasma vitellogenin in two diamondback terrapin populations (Malaclemys terrapin). MS Thesis,
    Southeastern Louisiana University
    ,
    Hammond
    .
  • Wood, R.C.
    and
    Herlands, R.
    1997. Turtles and tires: the impact of road kills on northern diamondback terrapin, Malaclemys terrapin terrapin, populations on the Cape May peninsula, southern New Jersey. In:
    Abbema J.V.
    (Ed.). Conservation, Restoration, and Management of Tortoises and Turtles—An International Conference New York: New York Turtle and Tortoise Society, pp. 4653.
Copyright: © 2018 Chelonian Research Foundation 2018
<bold>Figure 1.</bold>
Figure 1.

(A) C3 class 1.52-cm follicle as indicated by calipers from the female terrapin (ID 22) in December 2015. (B) C2 and C3 class follicles from same terrapin in June 2014. Follicle size as indicated by calipers from left to right: 1.41 cm (squares), 0.9 cm (plus signs), and 1.59 cm (× symbols).


<bold>Figure 2.</bold>
Figure 2.

(A) Female terrapin (ID 71) showing a clutch of 6 eggs on 28 May 2014. (B) The same female on 27 June 2014 with a clutch of 5 eggs, signifying a second clutch.


<bold>Figure 3.</bold>
Figure 3.

Mean testosterone, estradiol, and vitellogenin concentrations in terrapins across sampling months. Letters indicate significant differences. Sample size indicated by numbers within bars.


Contributor Notes

Corresponding author

Handling Editor: Jeffrey A. Seminoff

Received: 28 Mar 2018
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