Register      Login
Marine and Freshwater Research Marine and Freshwater Research Society
Advances in the aquatic sciences
RESEARCH ARTICLE

Boating impacts to seagrass in Florida Bay, Everglades National Park, Florida, USA: links with physical and visitor-use factors and implications for management

David E. Hallac A C , Jimi Sadle B , Leonard Pearlstine B , Fred Herling B and Dilip Shinde B
+ Author Affiliations
- Author Affiliations

A Yellowstone Center for Resources, PO Box 168, Yellowstone National Park, WY 82190, USA.

B Everglades and Dry Tortugas National Parks, 40001 SR 9336, Homestead, FL 33034, USA.

C Corresponding author. Email: David_Hallac@nps.gov

Marine and Freshwater Research 63(11) 1117-1128 https://doi.org/10.1071/MF12025
Submitted: 30 January 2012  Accepted: 22 August 2012   Published: 26 November 2012

Abstract

Recreational motor boating in shallow water can damage submerged natural resources through propeller scarring and these impacts represent one of many factors that affect the health of seagrass ecosystems. Understanding the patterns of seagrass scarring and associations with physical and visitor-use factors can assist in development of management plans that seek to minimise resource damage within marine protected areas. A quantification of seagrass scarring of Florida Bay in Everglades National Park, using aerial imagery, resulted in the detection of a substantial number and length of seagrass scars. Geospatial analyses indicated that scarring was widespread, with the densest areas found in shallow depths, near navigational channels, and around areas most heavily used by boats. Modelling identified areas of high scarring probability, including areas that may experience increased scarring in the future as a result of a reallocation of impacts if management strategies are implemented. New boating-management strategies are warranted to protect seagrass in Florida Bay. An adaptive approach focusing on the most heavily scarred areas, should consider a variety of management options, including education, improved signage, new enforcement efforts and boating restrictions, such as non-motorised zones, or temporary closures. These methods and recommendations are broadly applicable to management of shallow water systems before and after resource impacts have occurred.

Additional keywords : groundings, marine protected areas, propeller, scarring, recreational impacts.


References

Andorfer, J., and Dawes, C. J. (2002). Production of rhizome meristems by the tropical seagrass Thalassia testudinum: the basis for slow recovery into propeller scars. Journal of Coastal Research 37, 130–142.

Ault, J. S., Smith, S. G., McClellan, D., Zurcher, N., McCrea, A., Vaughan, N. R., and Bohnsack, J. A. (2008). Final Report: aerial survey of boater use in Everglades National Park marine waters: Florida Bay and Ten Thousand Islands. University of Miami, Miami, FL.

Bell, S. S., Hall, M. O., Soffian, S., and Madley, K. (2002). Assessing the impacts of boat propeller scars on fish and shrimp utilizing seagrass beds. Ecological Applications 12, 206–217.
Assessing the impacts of boat propeller scars on fish and shrimp utilizing seagrass beds.Crossref | GoogleScholarGoogle Scholar |

Burfeind, D. D., and Stunz, G. W. (2006). The effects of boat propeller scarring intensity on nekton abundance in subtropical seagrass meadows. Marine Biology 148, 953–962.
The effects of boat propeller scarring intensity on nekton abundance in subtropical seagrass meadows.Crossref | GoogleScholarGoogle Scholar |

Burfeind, D. D., and Stunz, G. W. (2007). The effects of boat propeller scarring on nekton growth in subtropical seagrass meadows. Transactions of the American Fisheries Society 136, 1546–1551.
The effects of boat propeller scarring on nekton growth in subtropical seagrass meadows.Crossref | GoogleScholarGoogle Scholar |

Costanza, R., d’Àrge, R., Groot, R. D., Farber, S., Grasso, M., Hannon, B., Limburg, K., Naeem, S., O’Neill, R. V., Paruelo, J., Raskin, R. G., Sutton, P., and van der Belt, M. (1997). The value of the world’s ecosystem services and natural capital. Nature 387, 253–260.
The value of the world’s ecosystem services and natural capital.Crossref | GoogleScholarGoogle Scholar | 1:CAS:528:DyaK2sXjtlShtbs%3D&md5=a7bc7cbb1bab939add70f12a77960669CAS |

Dawes, C. J., Andorfer, J., Rose, C., Uranowski, C., and Ehringer, N. (1997). Regrowth of the seagrass, Thallasia testudinum, into propeller scars. Aquatic Botany 59, 139–155.
Regrowth of the seagrass, Thallasia testudinum, into propeller scars.Crossref | GoogleScholarGoogle Scholar |

Dinmore, T. A., Duplisea, D. E., Rackham, B. D., Maxwell, D. L., and Jennings, S. (2003). Impact of a large-scale area closure on patterns of fishing disturbance and the consequences for benthic communities. ICES Journal of Marine Science 60, 371–380.
Impact of a large-scale area closure on patterns of fishing disturbance and the consequences for benthic communities.Crossref | GoogleScholarGoogle Scholar |

Duarte, C. M., Terrados, J., Agawin, N. S. R., Fortes, M. D., Bach, S., and Kenworthy, W. J. (1997). Response of a mixed Philippine seagrass meadow to experimental burial. Marine Ecology Progress Series 147, 285–294.
Response of a mixed Philippine seagrass meadow to experimental burial.Crossref | GoogleScholarGoogle Scholar |

Duarte, C. M., Dennison, W. C., Orth, R. J. W., and Carruthers, T. J. B. (2008). The charisma of coastal ecosystems: addressing the imbalance. Estuaries and Coasts 31, 233–238.
The charisma of coastal ecosystems: addressing the imbalance.Crossref | GoogleScholarGoogle Scholar |

Durako, M. J., Hall, M. O., Sargent, F., and Peck, S. (1992). Propeller scars in seagrass beds: an assessment and experimental study of recolonization in Weedon Island State Preserve, Florida. In ‘Proceedings of the 19th Annual Conference on Wetlands Restoration and Creation, Tampa, Florida, 14–15 May 1992’. (Ed. F. J. Webb, Jr.) pp. 42–53. (Hillsborough Community College: Tampa, FL.)

Engeman, R. M., Duquesnel, J. A., Cowan, E. M., Smith, H. T., and Shwiff, S. A. (2008). Assessing boat damage to seagrass bed habitat in a Florida park from a bioeconomics perspective. Journal of Coastal Research 24, 527–532.
Assessing boat damage to seagrass bed habitat in a Florida park from a bioeconomics perspective.Crossref | GoogleScholarGoogle Scholar |

ESRI (2006). ‘ESRI ArcMAP (Version 9.2).’ Available at http://www.esri.com [accessed January 2006].

Falkenberg, L. J., Burnell, O. W., Connell, S. D., and Russell, B. D. (2010). Sustainability in near-shore marine systems: promoting natural resilience. Sustainability 2, 2593–2600.
Sustainability in near-shore marine systems: promoting natural resilience.Crossref | GoogleScholarGoogle Scholar | 1:CAS:528:DC%2BC3cXhtVGnsbvF&md5=6b01812dfd7cf3b0a5585c7c667e35d3CAS |

Florida Fish and Wildlife Conservation Commission (2007). ‘Florida’s Boating Safety Education Program – Executive Summary.’ Available at http://myfwc.com/media/100286/BoatingSafetyEdExSummOct07.pdf [accessed 27 January 2012].

Florida Fish and Wildlife Conservation Commission, Fish and Wildlife Research Institute (2004). Metadata for ISM_CSA_Florida_Bay_2004_imagery. Tallahassee, FL.

Florida Fish and Wildlife Conservation Commission, Fish and Wildlife Research Institute (2005). Dataset for Florida Bay Benthic Communities prepared by Avineon, Inc. Available at http://ocean.floridamarine.org [accessed June 2006].

Florida Fish and Wildlife Conservation Commission, Fish and Wildlife Research Institute (2006). Dataset for Florida marine facilities. metadata available at http://www.fgdl.org/metadata/fgdc_html/marfac.fgdc.htm [accessed 27 January 2012].

Fonseca, M. S., and Bell, S. S. (1998). Influence of physical setting on seagrass landscapes near Beaufort, North Carolina, USA. Marine Ecology Progress Series 171, 109–121.
Influence of physical setting on seagrass landscapes near Beaufort, North Carolina, USA.Crossref | GoogleScholarGoogle Scholar |

Fonseca, M. S., Whitfield, P. E., Kenworthy, W. J., Colby, D. R., and Julius, B. E. (2004). Use of two spatially explicit models to determine the effect of injury geometry on natural resource recovery. Aquatic Conservation: Marine and Freshwater Ecosystems 14, 281–298.
Use of two spatially explicit models to determine the effect of injury geometry on natural resource recovery.Crossref | GoogleScholarGoogle Scholar |

Hammerstrom, K. K., Kenworthy, W. J., Whitfield, P. E., and Merello, M. F. (2007). Response and recovery dynamics of seagrasses Thalassia testudinum and Syringodium filiforme and macroalgae in experimental motor vessel disturbances. Marine Ecology Progress Series 345, 83–92.
Response and recovery dynamics of seagrasses Thalassia testudinum and Syringodium filiforme and macroalgae in experimental motor vessel disturbances.Crossref | GoogleScholarGoogle Scholar |

Hansen, M., and DeWitt, N. T. (1999). 1890 and 1990 Bathymetry of Florida Bay. South Florida place based studies open-file report 00-347. US Geological Survey’s Center for Coastal and Regional Marine Geology, St Petersburg Field Office, United States Geological Survey, St Petersburg, FL. Available at http://sofia.usgs.gov/publications/ofr/00-347/ [accessed 27 January 2012].

Hastings, K., Hesp, P., and Kendrick, G. A. (1995). Seagrass loss associated with boat moorings at Rottnest Island, Western Australia. Ocean and Coastal Management 26, 225–246.
Seagrass loss associated with boat moorings at Rottnest Island, Western Australia.Crossref | GoogleScholarGoogle Scholar |

Kenworthy, W. J., Fonseca, M. S., Whitfield, P. E., and Hammerstrom, K. K. (2002). Analysis of seagrass recovery in experimental excavations and propeller-scar disturbances in the Florida Keys National Marine Sanctuary. Journal of Coastal Research SI 37, 75–85.

Koch, E. W. (2002). Impact of boat-generated waves on a seagrass habitat. Journal of Coastal Research 37, 66–74.

Kruer, C. R. (1994). Mapping assessment of vessel damage to shallow seagrasses in the Florida Keys. Report to the Florida Department of Natural Resources and the University of South Florida, Florida Institute of Oceanography, St Petersburg, FL.

Kuss, K. M. (1991). Lignumvitae Key Aquatic Preserve Survey of boating impacts/propeller scarring in shallow seagrass beds within LVKP. Report to State of Florida, Department of Natural Resources, Division of State Lands, Tallahassee, FL.

Marbà, N., Gallegos, M. E., Merino, M., and Duarte, C. M. (1994). Vertical growth of Thalassia testudinum: seasonal and interannual variability. Aquatic Botany 47, 1–11.
Vertical growth of Thalassia testudinum: seasonal and interannual variability.Crossref | GoogleScholarGoogle Scholar |

National Park Service and Florida Keys Fishing Guides Association (2006). ‘Florida Bay Map and Guide.’ (National Park Service.) Available at http://www.nps.gov/ever/planyourvisit/upload/FloridaBayMap&GuideSmall.pdf [accessed 27 January 2012].

National Park Service (2006). Year 2005 annual marine fisheries report. Everglades National Park. South Florida Natural Resources Center, Everglades National Park, Homestead, FL.

Orth, R. J., Carruthers, T. J. B., Dennison, W. C., Duarte, C. M., Fourqurean, J. W., Heck, K. L., Hughes, A. R., Hendrick, G. A., Kenworthy, W. J., Olyarnki, S., Short, F. T., Waycott, M., and Williams, S. L. (2006). A global crisis for seagrass ecosystems. Bioscience 56, 987–996.
A global crisis for seagrass ecosystems.Crossref | GoogleScholarGoogle Scholar |

R Development Core Team (2007). ‘R: a Language and Environment for Statistical Computing.’ R Foundation for Statistical Computing, Vienna. Available at http://www.R-project.org [accessed 27 January 2012].

Rigby, R. A., and Stasinopoulos, D. M. (2005). Generalized additive models for location, scale and shape, (with discussion). Applied Statistics 54, 507–554.
Generalized additive models for location, scale and shape, (with discussion).Crossref | GoogleScholarGoogle Scholar |

Rodriguez, R. W., Webb, R. M. T., and Bush, D. M. (1994). Another look at the impact of Hurricane Hugo on the shelf and coastal resources of Puerto Rico, USA. Journal of Coastal Research 10, 278–296.

Sargent, F. J., Leary, T. J., Crewz, D. W., and Kruer, C. R. (1995). Scarring of Florida’s seagrasses: assessment and management options. Florida Marine Research Institute Technical Report TR-1. Florida Department of Environmental Protection, St Petersburg, FL.

Susskind, L., Camacho, A. E., and Schenk, T. (2012). A critical assessment of collaborative adaptive management in practice. Journal of Applied Ecology 49, 47–51.
A critical assessment of collaborative adaptive management in practice.Crossref | GoogleScholarGoogle Scholar |

Tratalos, J. A., and Austin, T. J. (2001). Impacts of recreational SCUBA diving on coral communities of the Caribbean island of Grand Cayman. Biological Conservation 102, 67–75.
Impacts of recreational SCUBA diving on coral communities of the Caribbean island of Grand Cayman.Crossref | GoogleScholarGoogle Scholar |

Uhrin, A. V., and Holmquist, J. G. (2003). Effects of propeller scarring on macrofaunal use of the seagrass Thalassia testudinum. Marine Ecology Progress Series 250, 61–70.
Effects of propeller scarring on macrofaunal use of the seagrass Thalassia testudinum.Crossref | GoogleScholarGoogle Scholar |

United States Geological Survey (2007). ‘National Map Accuracy Standards.’ Available at http://nationalmap.gov/standards/nmas.html [accessed January 2007].

Whitfield, P. E., Kenworthy, W. J., Fonseca, M. S., and Hammerstrom, K. (2002). The role of a hurricane in expansion of disturbances initiated by motor vessels on subtropical seagrass banks. Journal of Coastal Research 37, 86–99.

Woolpert, Inc. (2007). Report of topographic survey minimum technical standards. Monroe County, Florida, 2006 Orthophoto Project. Report to Florida Department of Transportation, District VI, Tallahassee, FL.

Zieman, J. C. (1976). The ecological effects of physical damage from motor boats on turtle grass beds in southern Florida. Aquatic Botany 2, 127–139.
The ecological effects of physical damage from motor boats on turtle grass beds in southern Florida.Crossref | GoogleScholarGoogle Scholar |