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Ecology and Vulnerability Piping Plover
Ecology and Vulnerability
Piping Plover
Background
The piping plover is an iconic shorebird along Atlantic Coast beaches. Although frequently associated with these coastal beaches, among the three recognized... Read More
Background
The piping plover is an iconic shorebird along Atlantic Coast beaches. Although frequently associated with these coastal beaches, among the three recognized breeding populations, two are actually found inland. In addition to the Atlantic Coast population, which extends from Canada to North Carolina, populations are found on the Great Plains extending from Nebraska through Alberta, Canada and along the shorelines of Lakes Michigan, Superior, and Huron 1. All of these populations are short distance migrants that winter along the Gulf or southern Atlantic Coast and in the Bahamas 1.
In Massachusetts, piping plovers arrive on breeding grounds in late March and April 2. The birds are found on wide, barren, sandy beaches, and will nest on sparsely vegetated beaches above the high tide line. Most will leave Massachusetts for wintering grounds by late August.
Increased human populations and intense development pressure associated with coastal areas have led to a decline in piping plover populations 3. The species was federally listed as threatened in 1986 when only 790 pairs remained 4. Management efforts in the years since have resulted in population increases so that there were approximately 8,000 individuals globally in 2006 5.
Climate Impacts
Climate change is expected to result in rising sea levels due to the melting of glacial ice and thermal expansion of water 6. Sea levels have been rising at an accelerated rate for at least the past 50 years in New England, exceeding average global rates 7,8. In addition, there is an expected increase in the frequency of severe storms along with higher storm surges, which is likely to result in increased inundation of tidal areas during storms 9,10. The northeast in particular has experienced approximately one foot of sea-level rise since 1900, and is projected to experience anywhere between 1.5 to 6 feet of additional sea-level rise over the next century 8,11.
Habitat for piping plovers has the potential to migrate as sea level rises and beaches are pushed inland 3,13. However, the extent to which this can happen depends on whether the area inland of beaches is developed, as beachfront development does not leave room for beaches to migrate inland and can instead result in 'coastal squeezing' and loss of habitat 3,12. Piping plover habitat on barrier islands of Suffolk County, NY was projected to decline by as much as 41% with 1.6 feet of sea level rise when habitats were unable to migrate (static response). However, their habitat was projected to increase by as much as 15% with increasing sea levels if these barrier islands respond dynamically by migrating. However, when development is considered, this expansion in habitat can be reduced by 12% 3. Some actions designed to mitigate climate change impacts, such as building sea walls, can also prevent habitat migration 12. Along with sea level rise, human populations of coastal communities are anticipated to increase3, putting further pressure on available habitat. Strategies to reduce conflict between development and conservation of piping plover habitat in the face of climate change have been recommended, including controversial measures such as zoning regulations and closing of public access 3,5.
In addition to loss of habitat, increasing occurrence of severe storms has the potential to directly impact piping plovers through flooding of nests 3. Such storms may result in increased nest abandonment and bird mortality. The combined effects of sea level rise and coastal storms could be severe. Storm surge from a major hurricane under a 4.9 ft sea level rise was projected to flood over 95% of plover habitat in Suffolk County, NY 3. In some cases, storms can create or enhance habitat while resulting in localized losses elsewhere. After storm events, piping plover populations can increase where overwash areas are created. Where barrier islands are allowed to migrate in response to SLR and storms, the occupation of new inlets and beaches created by overwash events is also possible 14.
1. Roche, E.A., J.B. Cohen, D.H. Catlin, D.L. Amirault-Langlais, F.J. Cuthbert, C.L. Gratto-Trevor, J. Felio, and J.D. Fraser. 2010. Range-wide piping plover survival: correlated patterns and temporal declines. Journal of Wildlife Management 74:1784-1791.
2. Massachusetts Audubon. 2015. Piping plover Charadrius melodus. Breeding Bird Atlas 1 Species Accounts. < http://www.massaudubon.org/our-conservation-work/wildlife-research-conse...(id)/54> (Accessed 23 June 2015).
3. Seavey, J.R., B. Gilmer, and K.M. McGarigal. 2011. Effects of sea-level rise on piping plover (Charadrius melodus) breeding habitat. Biological Conservation 144:393-401.
4. Cohen, J.B., L.M. Houghton, and J.D. Fraser. 2009. Nesting density and reproductive success of piping plovers in response to storm- and human-created habitat changes. Wildlife Monographs 173:1-24.
5. Gratto-Trevor, C.L., and S. Abbott. 2011. Conservation of piping plover (Charadrius melodus) in North America: science, successes, and challenges. Canadian Journal of Zoology 89:401-418.
6. Rahmstorf, S. 2007. A semi-empirical approach to projecting future sea-level rise. Science 315:368-370.
7. Warren, R.S., and W.A. Niering. 1993. Vegetation change on a northeast tidal marsh: interaction of sea-level rise and marsh accretion. Ecology 74:96-103.
8. Horton, R., G. Yohe, W. Easterling, R. Kates, M. Ruth, E. Sussman, A. Whelchel, D. Wolfe, and F. Lipschultz. 2014. Ch. 16: Northeast. Climate Change Impacts in the United States: The Third National Climate Assessment. Pages 371-395 in J. M. Melillo, T.(.C.). Richmond, and G. W. Yohe, editors. U.S. Global Change Research Program.
9. Thorne, K.M., J.Y. Takekawa, and D.L. Elliott-Fisk. 2012. Ecological effects of climate change on salt marsh wildlife: a case study from a highly urbanized estuary. Journal of Coastal Research 28:1477-1487.
10. Anthes, R.A., R.W. Corell, G. Holland, J.W. Hurrell, M.C. MacCracken, and K.E. Trenberth. 2006. Hurricanes and global warming-potential linkages and consequences. Bulletin of the American Meteorological Society 87:623-628.
11. Horton, R., C. Little, V. Gornitz, D. Bader, and M. Oppenheimer. 2015. Chapter 2: Sea Level Rise and Coastal Storms. New York City Panel on Climate Change 2015 Report. Annals of the New York Academy of Sciences, New York, NY:36-44.
12. Sims, S.A., J.R. Seavey, and C.G. Curtin. 2013. Room to move? Threatened shorebird habitat in the path of sea level rise—dynamic beaches, multiple users, and mixed ownership: a case study from Rhode Island, USA. Journal of Coastal Conservation 17:339-350.
13. Woods Hole Coastal and Marine Science Center. 2015. Beach-dependent Shorebirds. U.S. Geological Survey <http://woodshole.er.usgs.gov/project-pages/sea-level-rise_hazards/biolog... (Accessed 25 March 2016).
14. Titus, J.G., K.E. Anderson, K.R. Cahoon, D.B. Gesch, S.K. Gill, B.T. Gutierrez, E.R. Thieler, and S.J. Williams, 2009: Coastal Sensitivity to Sea-Level Rise: A focus on the Mid-Atlantic region. U.S. Climate Change Science Program, Synthesis and Assessment Product 4.1. 320 p.
This species was identified as moderately vulnerable to climate change because of the following factors:
- Sea level rise
- Depends on natural disturbance likely to be... Read More
This species was identified as moderately vulnerable to climate change because of the following factors:
- Sea level rise
- Depends on natural disturbance likely to be affected by climate change
- Has already experienced variations in annual precipitation (over the last 50 years)
- Slightly impacted by changes due to human response to climate change
The factors below decrease this species' vulnerability to climate change:
- Ability to move across the landscape and/or disperse relatively long distances
Sneddon, L. A., and G. Hammerson. 2014. Climate Change Vulnerability Assessments of Selected Species in the North Atlantic LCC Region. NatureServe, Arlington, VA. Available from: http://northatlanticlcc.org/projects/completing-northeast-regional-vulne...
This species was identified as highly vulnerable to climate change because of the following factors:
- Suitable beach habitat expected... Read More
This species was identified as highly vulnerable to climate change because of the following factors:
- Suitable beach habitat expected to decrease due to sea level rise and storm events
Adaptation Subcommittee to the Governor’s Steering Committee on Climate Change. 2010. The impacts of climate change on Connecticut agriculture, infrastructure, natural resources, and public health. Available from: http://www.ct.gov/deep/lib/deep/climatechange/impactsofclimatechange.pdf
This species was identified as moderately vulnerable to climate change because of the following factors:
- Sea level rise
- Depends on natural disturbance likely to be... Read More
This species was identified as moderately vulnerable to climate change because of the following factors:
- Sea level rise
- Depends on natural disturbance likely to be affected by climate change
- Requires specialized habitat
The factors below decrease this species' vulnerability to climate change:
- Ability to move across the landscape and/or disperse relatively long distances
- Has already experienced slight increases in annual precipitation (over the last 50 years)
Schlesinger, M.D., J.D. Corser, K.A. Perkins, and E.L. White. 2011. Vulnerability of at-risk species to climate change in New York. New York Natural Heritage Program, Albany, NY. Available from: https://connect.natureserve.org/sites/default/files/documents/ccvi_repor...
This species was identified as highly vulnerable to climate change because of the following factors:
- Requires specialized habitat
- Part of life-cycle depends on a very... Read More
This species was identified as highly vulnerable to climate change because of the following factors:
- Requires specialized habitat
- Part of life-cycle depends on a very specific feature of the habitat
- Already at southern edge of range in less than half of northern part of state
- Habitat is likely to experience significant declines (by at least two-thirds)
- Species distribution is highly fragmented because of habitat loss or populations that are very spread out across the landscape
- Growth or reproduction may be harmed by additional stress from high temperatures
- Dependent on stable hydrology for survival and reproduction (flooding may destroy nests)
- Natural and anthropogenic barriers prevent dispersal or shifts in species' range
- Sensitive to change in the timing of seasons and/or other environmental cues
Whitman, A., A. Cutko, P. DeMaynadier, S. Walker, B. Vickery, S. Stockwell, and R. Houston. 2013. Climate change and biodiversity in Maine: vulnerability of habitats and priority species. Report SEI-2013-03. Manomet Center for Conservation Sciences (in collaboration with Maine Beginning with Habitat Climate Change Working Group), Brunswick, ME. Available from: https://www.manomet.org/sites/default/files/publications_and_tools/BwHSu...
This species was identified as moderately vulnerable to climate change because of the following factors:
- Sea level rise
- Depends on natural disturbance likely to be... Read More
This species was identified as moderately vulnerable to climate change because of the following factors:
- Sea level rise
- Depends on natural disturbance likely to be affected by climate change
- Has already experienced slight variations in annual precipitation (over the last 50 years)
- Slightly impacted by changes due to human response to climate change
- Already at southern edge of range
The factors below decrease this species' vulnerability to climate change:
- Ability to move across the landscape and/or disperse relatively long distances
Sneddon, L. A., and G. Hammerson. 2014. Climate Change Vulnerability Assessments of Selected Species in the North Atlantic LCC Region. NatureServe, Arlington, VA. Available from: http://northatlanticlcc.org/projects/completing-northeast-regional-vulne...
This species was identified as moderately vulnerable to climate change because of the following factors:
- Sea level rise
- Depends on natural disturbance likely to be... Read More
This species was identified as moderately vulnerable to climate change because of the following factors:
- Sea level rise
- Depends on natural disturbance likely to be affected by climate change
- Has already experienced slight variations in annual precipitation (over the last 50 years)
- Slightly impacted by changes due to human response to climate change
The factors below decrease this species' vulnerability to climate change:
- Ability to move across the landscape and/or disperse relatively long distances
Sneddon, L. A., and G. Hammerson. 2014. Climate Change Vulnerability Assessments of Selected Species in the North Atlantic LCC Region. NatureServe, Arlington, VA. Available from: http://northatlanticlcc.org/projects/completing-northeast-regional-vulne...
This species was identified as extremely vulnerable to climate change because of the following factors:
- Major loss of suitable breeding, wintering, and migration habitat expected... Read More
This species was identified as extremely vulnerable to climate change because of the following factors:
- Major loss of suitable breeding, wintering, and migration habitat expected
- Highly specific habitat used year-round
Note: This report evaluated coastal and inland populations separately. This entry refers to the coastal population; inland Piping Plovers are not found in Massachusetts.
Galbraith, H., D. W. DesRochers, S. Brown, J. M. Reed. 2014. Predicting Vulnerabilities of North American Shorebirds to Climate Change. PLoS ONE 9(9): e108899. Available from: http://journals.plos.org/plosone/article?id=10.1371/journal.pone.0108899
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