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Action Plan Bog Natural Diversity Section June 2011

Species Action Plan: ( muhlenbergii)

Purpose: This plan provides an initial five year blueprint for the actions needed to attain near-term and, ultimately, long-term goals for the conservation and recovery of the bog turtle. The action plan is a living document and will be updated, as needed, to reflect progress toward those goals and to Figure 1. Bog Turtle (Glyptemys muhlenbergii . incorporate new information as it becomes Photo -PFBC file. available. Description: The bog turtle is a small, semi- Goals: The immediate conservation goal for aquatic turtle with a maximum carapace the bog turtle is to significantly increase length of 114 mm (Figure 1). The bog efforts towards recovery of the bog turtle turtle’s brown or black carapace is slightly through habitat restoration, management, sculpted, somewhat domed, and has a slight and protection; and to continue to collect mid-dorsal keel. Growth rings are typically baseline data for long-term monitoring and visible on the scutes of young to middle- assessment of the bog turtle aged bog but often become smoothed population. The long-term recovery goal is by sediments in older specimens. The to increase viable, reproducing, and plastron is hingeless, posteriorly notched protected populations of bog turtle and and connected to the carapace by a wide ultimately, in cooperation with the US Fish bridge. The coloration of the plastron is and Wildlife Service (USFWS), to remove predominantly dark brown to black, with the bog turtle from the lists of Pennsylvania some individuals exhibiting tan or brownish endangered, threatened and candidate markings that typically originate along the species (58 Pa. Code §75). centerline. The background color of the skin is dark brown to black, with a mottled Natural History appearance on the head. An orange colored blotch located behind the eyes on the dark : Class Reptilia, skin of the neck and head is diagnostic Testudines (turtles), (Hulse et al. 2001). (water turtles), Bog Turtle (Glyptemys muhlenbergii) Habitat: The bog turtle is a habitat specialist that relies on early successional,

Page | 1 Species Action Plan Bog Turtle Natural Diversity Section June 2011 groundwater-driven, emergent wetlands. are typically deposited between the Primary bog turtle habitat typically consists blades of tussock sedge or within a of wetlands with wet, mucky soils, and mat above the water line (Hulse open, sunny, emergent vegetation. The et al., 2001). classic example of bog turtle habitat is a spring-fed meadow with dominant Hatchlings in the wild typically emerge from vegetation consisting of low pedestal- mid-August through September and forming grasses and sedges, often containing overwinter at or near the nest site. The bog a scrub-shrub wetland component, and with turtle is considered to be mature at a plastron soft mud or “mucky” soils. The turtles are length of 70 mm (Ernst 1977) (carapace often associated with tussock sedge (Carex length of approximately 75 mm) and an age stricta). This sedge and other pedestal- of 6 to 10 years, depending on conditions. forming vegetation (Scirpus, Cyperinus, and Carex spp.) create a wide range of micro- Bog turtles are omnivorous and will eat climates. Reed canary-grass (Phalaris insects, , worms, , salamanders, arundinacea), purple loosestrife (Lythrum Carex seeds, Japanese beetles, berries, salicaria) and common reed ( cattails, skunk cabbage, snails, and carrion australis) are invasive plant species that (Nemuras 1967, Zappalorti 1976, Holub and commonly occur in altered, disturbed or Bloomer 1977 as cited in Ernst et al. 1994, degraded sites. The bog turtle hibernates in Ernst 1985). spring seeps, most often under root masses and with maximum solar exposure (Ernst et al. 1989, Eichelberger 2005, Gress pers. comm.).

Life History: Bog turtles in Pennsylvania typically emerge from in late March through April, dependent upon local weather conditions, and return to the hibernacula in October. Breeding occurs from late April through early June (Barton and Price 1955). Generally, nesting occurs 21 to 31 days after copulation and, in Pennsylvania, bog turtles generally nest from June through early July (Hulse et al., 2001, C. Urban, personal observation). An average of three (range 1-6) elliptical white

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Distribution and Status

National Distribution: Two separate geographical populations of Glyptemys muhlenbergii are recognized (USFWS 2001) (Figure 2). The northern population exists within New York, Massachusetts, Connecticut, Pennsylvania, , Delaware, and Maryland. A disjunct southern population, separated by 250 miles from the northern population, exists in , North Carolina, Tennessee, South Carolina, and , primarily in the Blue Ridge Province (Lee and Herman 1999).

Pennsylvania Distribution: Within Pennsylvania, bog turtles are limited in Figure 2. Distribution of Glyptemys distribution to portions of 15 southeastern muhlenbergii in and eastern counties and possibly other (NatureServe 2010). isolated areas in northwestern Pennsylvania (Figure 3). Fragmented populations occur from Adams and Cumberland Counties eastward to the Delaware River and northward to Monroe County. Historically, a western population existed in Crawford and Mercer Counties and is currently considered historic or extirpated. Although significant suitable habitat acreage exists, researchers have searched for and failed to confirm the northwestern Figure 3. Distribution of Glyptemys muhlenbergii in population in the last 25 years Pennsylvania. (PFBC 2010). (Ruhe 2009).

Pennsylvania Legal Status: The bog turtle was listed as Endangered in Pennsylvania in 1974.

Federal Status: The US Fish and Wildlife Service (USFWS) listed the bog turtle as Threatened in 1997 (USFWS 1997).

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Management Status (PAS) (i.e., groups of wetland complexes Previously undocumented bog turtle sites that are thought to support bog turtle continue to be discovered every year subpopulations with likely dispersal among through ad hoc surveys, surveys related to the wetlands; from USFWS 2001), which environmental review, incidental encounters represented an increase of 57 PAS from and some targeted surveys (USFWS 2008). 2000 to 2007 (USFWS 2008). A total of 42 Limited targeted surveys have failed to find occurrences had some level of land bog turtles within the historic range in protection, and management had occurred at northwestern Pennsylvania (Ruhe 2009). To 17 of those wetlands as of 2007 (USFWS assess the effects of development on bog 2008). Management of individual wetlands turtles, the PFBC is currently sponsoring a supporting bog turtles is ongoing at several monitoring study of bog turtle populations sites in Pennsylvania, initiated by a variety and their habitat (Rocco and Brooks 2009). of entities, including the USFWS Partners Sites in the study will be re-visited in 10 for Wildlife Program, land trusts, and years to monitor changes in their respective individual landowners. The USFWS has bog turtle colonies and associated habitat. funded a review of bog turtle occurrence As the planning phase to develop a data including mapping and assessment of mitigation mechanism for protecting the wetland habitats, which should be completed highest priority sites within the framework in 2011. Additional federal funding has of environmental review of proposed recently been allocated to locating potential development projects, a Habitat bog turtle sites in southern York County. Conservation Plan (HCP) to Establish Conservation Banks for the Bog Turtle in In 2010, a Landowner Incentive Program Chester County, Pennsylvania and part of (LIP) grant provided for development of 20 Delaware was developed in 2009 (The HCP management plans for landowners in the Team 2009). This plan has been reviewed Cherry Valley area. These plans provide by the USFWS. To meet USFWS guidance for landowners to protect habitat stipulations resulting from the review, and minimize indirect loss of individual bog further funding needs to be secured. Upon turtles. approval of the HCP by the USFWS, funding will be sought for implementation The Pennsylvania Fish & Boat Commission of the plan. (PFBC) has recently obtained a grant through the National Fish and Wildlife As of 2007, 214 extant bog turtle Foundation (NFWF) to coordinate habitat occurrences have been documented in restoration efforts in Pennsylvania. This Pennsylvania. The 214 occurrences made project will take effect in 2011. up a total of 132 population analysis sites

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Threats 4) Illegal collection: Given their high black 1) Habitat loss by anthropogenic alteration market value, bog turtles are in constant or destruction danger of illegal collection by poachers a. Historical and ongoing residential, (Hulse et al. 2001, USFWS 2001). commercial and industrial development, road construction, and 5) Predation (especially of nests): agricultural practices Predominant predators of nests and b. Genetic isolation and risk of local juveniles are meso-mammals (i.e., extirpation are exacerbated by loss of , opossum, mink, ), but small habitat and its connectivity. mammals such as shrews have been documented as predators (Zappalorti 2) Habitat loss by natural succession and et al. 1995). lack of habitat management a. Disturbance processes (e.g., beaver Conservation and Recovery ponds, low density cattle grazing) are needed at many sites to create and maintain suitable wet meadow Conservation Actions: habitat b. Encroachment by trees and shrubs The USFWS Recovery Plan for the Bog creates shading, thereby eliminating Turtle, Northern Population calls for actions bog turtle nesting and basking for the protection and restoration of bog habitat turtle wetland habitat and the hydrologic processes that create and maintain it, 3) Invasive plant species: Invasive plants protection of upland habitat buffers and such as reed canarygrass (Phalaris dispersal corridors, and external threat arundinacea), common reed abatement to minimize common mortality (Phragmites australis), purple loosestrife factors like , predation, and roadkill (), and narrow-leaved (National Fish and Wildlife Foundation. cattail ( augustifolia) can form 2009, USFWS 2009). Of the specific dense homogenous stands thus proposed actions in that recovery plan, the eliminating or reducing basking and PFBC advocates implementation of the nesting areas, creating barriers to turtle following: movements, and can be responsible for excessive uptake of water from the 1) Identify known bog turtle sites and wetlands. develop management plans based upon priority of current needs.

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a. Determine the acreage and habitat disturbances to known bog turtle improvement needs for each site. habitat. b. Develop habitat restoration training b. Spot check projects to confirm program for PFBC habitat managers adherence to recommended actions. c. Encourage private landowners to c. Investigate the possibility of enroll in conservation incentive developing a bog turtle conservation programs such as the Wetlands fund with the USFWS. Reserve Program (WRP). d. Complete management plans for 5) Continue to survey for undocumented WRP-protected sites. Manage populations of bog turtle within their habitat, through grazing and other historically-occupied range. forms of vegetation management, to a. Use existing models to identify become suitable for bog turtle potential habitat (See Bog Turtle nesting HCP) e. Initiate restoration in early b. Obtain landowner permissions for successional wetland habitat as survey. deemed necessary. c. Inventory sites. f. Develop and implement methodologies to protect bog turtle 6) Develop plans to establish bog turtle nests from predators. wetland connectivity corridors. a. Map contiguous habitat and potential 2) Obtain funding to complete and dispersal barriers. implement HCP for Chester County, b. Seek opportunities for reducing which could be used as a model in other dispersal barriers. bog turtle counties. c. Work with partners to protect corridor habitats through easements. 3) Monitor occupied bog turtle sites. a. Continue long-term research on the response of bog turtle populations to

development pressures

b. Develop monitoring program at sites undergoing habitat management to measure population response.

4) Continue and expand ongoing protection measures for the bog turtle populations.

a. Review and comment on permit

applications that involve proposed temporary and/or permanent

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References The HCP Team. 2009. Habitat Barton, A.J., and J.W. Price, Sr. 1955. Our conservation plan to establish knowledge of the bog turtle, Clemmys conservation banks for the threatened muhlenbergi, surveyed and augmented. bog turtle (Glyptemys muhlenbergii) in Copeia 1955(3):159-165. portions of Chester County, Pennsylvania and New Castle County, Eichelberger, C. H. 2005. Habitat use by the Delaware, corresponding to the bog turtle (Glyptemys muhlenbergii) in a Delaware West Recovery Unit. Report south central Pennsylvania wetland. submitted to Pennsylvania Fish and Boat Masters thesis. Shippensburg Commission. University. Holub, R.J. and T.J. Bloomer. 1977. The Ernst, C.H. 1977. Biological notes on the bog turtle, Clemmys muhlenbergi…a bog turtle, Clemmys muhlenbergii. natural history. Bulletin of the New Herpetologica 33(2):241-246. York Herpetological Society 13(2):9-23.

Ernst, C.H. 1985. Bog turtle. In H.H. Hulse, A.C., C.J. McCoy, and E.J. Censky. Genoways and F.J. Brenner (eds.), 2001. Amphibians and of Species of Special Concern in Pennsylvania and the Northeast. Cornell Pennsylvania. Special Publication No. University Press. Ithaca, NY. 11 of the Carnegie Museum of Natural History, pp. 270-273. Pittsburgh, Hulse, A.C. and D.W. Herman. 1999. Pennsylvania. Proposed zoogeographic history of the bog turtle, Clemmys muhlenbergii. In Ernst, C.H., Lovich, J.E., and R.W. Barbour. C.W. Swarth, W.R. Roosenberg, and E. 1994. Turtles of the United States and Kiviat (eds.), Conservation and Canada. Smithsonian Institution Press. of Turtles of the Mid-Atlantic Region: A Washington, D.C. Symposium. pp. 31-42. Bibliomania!, Salt Lake City, Utah. Ernst, C.H., Zappalorti, R.T., and J.E. Lovich. 1989. Overwintering sites and National Fish and Wildlife Foundation. thermal relations of hibernating bog 2009. Business plan for early turtles, Clemmys muhlenbergii. Copeia successional habitat and conservation of 1989(3):761-764. the bog turtle. Draft.

Nemuras, K.T. 1967. Notes on the natural history of Clemmys muhlenbergi. Bulletin Maryland Herpetological Society 3(4):80-96.

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Rocco, G. L. and R. P. Brooks. 2009. U.S. Fish and Wildlife Service (USFWS). Monitoring of bog turtle colonies at sites 2008. Bog turtle (Clemmys {= in immediate proximity to development Glyptemys} muhlenbergii), northern in southeastern Pennsylvania: Year 2 population, 5-year review summary and (2008) report of activities. Report evaluation. Draft. State College, submitted to Pennsylvania Fish and Boat Pennsylvania. Commission. U.S. Fish and Wildlife Service (USFWS). Ruhe, B. M. 2009. Survey for the bog turtle 2009. Bog turtle (Clemmys {= (Glyptemys muhlenbergii) in the Glyptemys} muhlenbergii), spotlight Pymatuning area (Prairie Peninsula/Lake species action plan. State College, Plain Recovery Unit) of Pennsylvania. Pennsylvania. Report to the USFWS, Pennsylvania Field Office. Zappalorti, R.T., 1976.The amateur zoologist’s guide to turtles and U.S. Fish and Wildlife Service (USFWS). 4 crocodilians. Stackpole Books. November 1997. Final rule to list the Harrisburg, PA. northern population of the bog turtle as threatened and the southern population Zappalorti, R.T., G. Rocco, and P.J. Drake. as threatened due to similarity of 1995. Results of a two phase bog turtle appearance. Federal Register (Clemmys muhlenbergii) study within 62(213):59605-59623. Pennsylvania, with special notes on nesting, February 25. Herpetological U.S. Fish and Wildlife Service (USFWS). Assoc. File Nos. 94.18 & 94.19. 2001. Bog turtle (Clemmys muhlenbergii), northern population, recovery plan. Hadley, Massachusetts.

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