ReefLink Database
Large Ships
Large Ships includes commercial shipping and the military, which operate large watercraft for transportation of goods or people.
CMap
CMap Description
Operation of boats, ships and the ports, harbors, and docks they depend on, can create numerous pressures on the reef ecosystem. Boat and ship activities can lead to groundings, anchor drops, or use of fishing gear that can damage reef habitat, and movement can cause resuspension of sediment in the reef environment. Boats and ships may discharge wastewater into open water, and operators may use cleaners & solvents in harbor to maintain boats. Operation of ships and boats often leads to emissions of greenhouse gasses into the environment, and runs the risk, particularly for oil & gas tankers, of petroleum spills. Ballast discharge from large ships increases the risk of an invasive species entering the reef ecosystem, and competing with native species. Dredging of coastal vegetation or reef habitat may be needed for construction of ports, harbors, marinas, and docks, or to create channels for ship traffic. Maritime transportation sectors benefit from shoreline protection provided by the reef, including calm waters for boat activity and reducing the likelihood of damage to coastal engineering structures during storm events. Commercial fishing boat operators benefit from availability of finfish & shellfish stock. The aesthetic value of the reef provides recreational opportunities and contributes to the cultural identity of the local community, which can improve business for small boat and cruise ship operators. Decision-makers can influence numbers, distribution, technology, and discharges from boats and ships through policies and regulations. Resource use management can be used to control boating activities through mooring buoys or protected areas.Citations
Citation | Year | Study Location | Study Type | Database Topics |
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Morgan, O. A., D. M. Massey, and W. L. Huth. 2009. Diving demand for large ship artificial reefs. Marine Resource Economics 24:43-59. | 2009 | Model | Artificial Habitat; Dive, Snorkeling, & Swimming Tourism; Large Ships; Monetary Valuation; Non-Monetary Valuation; Recreational Opportunities; Tourism & Recreation; Valuation | |
Newell, C. 2008. USS Kitty Hawk docks after final voyage. Jane's Defence Weekly. | 2008 | US Pacific & Hawaii; Japan | Artificial Habitat; Coastal Defense; Docks & Marinas; Large Ships; Military; Museums, Amusement Parks, Historical Sites | |
Walker, S. J., T. A. Schlacher, and M. A. Schlacher-Hoenlinger. 2007. Spatial heterogeneity of epibenthos on artificial reefs: Fouling communities in the early stages of colonization on an East Australian shipwreck. Marine Ecology 28:435-445. | 2007 | Australia | Model | Artificial Habitat; Coastal Defense; Complex Habitat & Resources; Invertebrates; Large Ships; Military; Sediment; Sponges; Surface & Groundwater Flow; Water Depth & Sea Level |
Armstrong, M. J. and M. B. Powell. 2005. A stochastic Salvo model analysis of the Battle of the Coral Sea. Military Operations Research 10:27-37. | 2005 | Model | Large Ships | |
Haynes, D. and D. Loong. 2002. Antifoulant (butyltin and copper) concentrations in sediments from the Great Barrier Reef World Heritage Area, Australia. Environmental Pollution 120:391-396. | 2002 | Australia | Anchoring & Vessel Grounding; Docks & Marinas; Large Ships; Sediment; Tourism & Recreation | |
Hutchings, P. A., R. W. Hilliard, and S. L. Coles. 2002. Species introductions and potential for marine pest invasions into tropical marine communities, with special reference to the Indo-Pacific. Pacific Science 56:223-233. | 2002 | South & Central America; US Pacific & Hawaii; Australia; Panama; Papua New Guinea; Indonesia; Philippines; Caribbean | Ballast Discharge; Discharges; Docks & Marinas; Escape & Release of Non-natives; Finfish Harvest; Invasive Species; Large Ships; Military; Pathogens; Ports & Harbors; Shipping, Storage, & Warehousing; Small Boats | |
Watkinson, C. J. 2000. Oil spill prevention and response initiatives in the Great Barrier Reef. Spill Science and Technology Bulletin 6:31-44. | 2000 | Australia | Large Ships; Monetary Valuation; Petroleum Spills; Shipping, Storage, & Warehousing | |
McKenna Jr., J. E. 1997. Influence of physical disturbance on the structure of coral reef fish assemblages in the Dry Tortugas. Caribbean Journal of Science 33:82-97. | 1997 | Anchoring & Vessel Grounding; Complex Habitat & Resources; Corallivorous Fish; Fish; Large Herbivorous Fish; Large Ships; Planktivorous Fish | ||
Barthel, V. 1982. Wave motion in estuary. in [No source information available]. | 1982 | Coastal Engineering; Large Ships; Shoreline Protection; Water Depth & Sea Level |
Management Options
Management Option | Description | Sources | Database Topics |
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Damage Assessment, Documentation & Response: Respond to Natural Resource Injuries from Large Vessel Achoring | Damage from freighter anchor is extreme due to the mere weight and size of the anchor and chain. The chain can even be more damaging as it drags along the benthic environment leaving behind catastrophic ruin. This management response would encourage the creation of restoration and monitoring methodologies in shallow reef areas as well as at greater depths. If unacceptable damages are occurring restrictions and regulations prohibiting the use of anchors in high risk areas should be instituted. | NOAA Marine Sanctuary Program. 2007. Florida Keys National Marine Sanctuary revised management plan. National Ocean Service, Key West, FL. Collier, C., Dodge, R., Gilliiam, Gracie, K., Gregg, L., Jaap, W., Mastry, M., and Poulos, N. 2007. Rapid Response and Restoration for coral reef injuries in the southeest Florida. Southeast Florida Coral Reef Initiative. |
Anchoring & Vessel Grounding; Biological Monitoring & Restoration; Biological Monitoring, Mapping, & Scientific Research; Boating Activities; Boating Regulations; Cruise Ships; Ecosystem Monitoring & Restoration; Large Ships; Physical Damage; Resource Use Management; Transportation; Water Depth & Sea Level; Water Resources; Water Transportation; Wetland & Reef Restoration |
Damage Assessment, Documentation & Response: Respond to Natural Resource Injuries form Derelict Vessels | Semi- permanent/permanent vessels can have a negative impact on the surrounding local environment both due to the effects of shade and from the direct contact with the substrate. Sunken vessels that cannot be seen from the surface may present a danger to navigation. Derelict vessels that do not remain stationary may cause harm in multiple locations before becoming stationary. If fishing gear is still intact, it may cause further biological damage through "ghost fishing� (#283). Early response, creating mooring fields, pump-out stations, and providing support for removing derelict vessels, reduces the impact of these vessels. Also, the removal of intrusive vessels will help contribute to the restoration of reef areas to previous conditions. | NOAA Marine Sanctuary Program. 2007. Florida Keys National Marine Sanctuary revised management plan. National Ocean Service, Key West, FL. |
Anchoring & Vessel Grounding; Artificial Habitat; Artisanal Fishing; Biological Monitoring & Restoration; Boat Movement; Boating Activities; Boating Regulations; Coastal Defense; Commercial Fishing Boats; Coral; Ecosystem Monitoring & Restoration; Environmental Monitoring & Restoration; Large Ships; Marine Debris; Military; Physical Damage; Reef Habitat; Reef Life; Resource Use Management; Seagrasses; Small Boats; Stony Coral; Substrate; Transportation Policies; Water Depth & Sea Level; Water Transportation; Wetlands |
Damage Assessment, Documentation & Response: Coordinated Oil & Hazardous Spill Response | This management option calls for developing unified response protocols to deal with containment and clean-up of oil spills. This is important to protect corals, mangroves, and seagrasses from adverse impacts of hazardous materials. Given the limited number of spills and the importance of responding quickly, interagency coordination of reporting and response is essential for success. | NOAA Marine Sanctuary Program. 2007. Florida Keys National Marine Sanctuary revised management plan. National Ocean Service, Key West, FL. Puerto Rico and USVI Area Planning Committees. 2008. Hazardous Substances Pollution Area Contingency Plan. Puerto Rico and the U.S. Virgin islands. |
Collaboration & Partnering; Decision Support; Discharges; Ecosystem Monitoring & Restoration; Energy Policy & Development; Environmental Monitoring & Restoration; Large Ships; Oil & Gas Industry; Oil & Gas Rigs; Oil & Gas Tankers; Petroleum Spills; Pipelines; Point Source Discharges; Remediation; Resource Use Management; Security & Public Administration Policies; Small Boats; Toxics; Transportation; Water Transportation; Waterborne Discharges |
Damage Assessment, Documentation & Response: Collaborate with Towing & Salvage Operators in Grounding Notification | This option advocates the establishment of rapport between local operators and regulatory agencies. This is achieved through regular meetings and training sessions to emphasize the importance of operator cooperation in regards to vessel groundings. | NOAA Marine Sanctuary Program. 2007. Florida Keys National Marine Sanctuary revised management plan. National Ocean Service, Key West, FL. |
Anchoring & Vessel Grounding; Boating Activities; Coastal Defense; Collaboration & Partnering; Commercial Fishing Boats; Cruise Ships; Cultural Policies; Environmental Education & Outreach; Large Ships; Military; Oil & Gas Tankers; Physical Damage; Security & Public Administration Policies; Small Boats; Transportation; Transportation Policies; Water Transportation |
Marine Zoning: Sanctuary Preservation Areas (SPAs) | This is a type of Marine Zoning used by the Florida Keys National Marine Sanctuary (FKNMS). SPAs focus on the protection of shallow, heavily used reefs where conflicts occur between user groups, and where concentrated visitor activity leads to resource degradation. They are designed to enhance the reproductive capabilities of renewable resources, protect areas critical for sustaining and protecting important marine species, and reduce user conflicts in high-use areas. This is accomplished through a prohibition of consumptive activities within these areas. They have been chosen based on the status of important habitat, the ability of a particular area to sustain and protect the habitat, the level of visitor use, and the degree of conflict between consumptive and non-consumptive users. The actual size and location of these zones have been determined by examination of user patterns, aerial photography, and ground-truthing of specific habitats. | NOAA Marine Sanctuary Program. 2007. Florida Keys National Marine Sanctuary revised management plan. National Ocean Service, Key West, FL. |
Accidental & Illegal Harvest; Anchoring & Vessel Grounding; Aquaculture; Aquarium & Pet Trade; Aquarium Stock; Artisanal Fishing; Beaches & Nature Parks; Biological Addition; Biological Harvest; Biological Monitoring & Restoration; Boat Movement; Boating Activities; Boating Regulations; Coastal Defense; Coastal Development; Coastal Engineering; Commercial Fisheries; Commercial Fishing Boats; Complex Habitat & Resources; Cruise Ships; Cultural Services; Decision Support; Designated Uses; Dive, Snorkeling, & Swimming Tourism; Dredging Regulations; Dredging, Draining, & Filling; Ecosystem Monitoring & Restoration; Educational & Research Opportunities; Entertainment & Accommodation Services; Environmental Monitoring & Restoration; Finfish & Shellfish Stock; Finfish Harvest; Fisheries & Hunting Policies; Fishing & Harvesting Management; Fishing Sector; Invertebrate Harvest; Landscape Changes; Large Ships; Live Collection; Marine Protected Areas; Oil & Gas Tankers; Ornamental Jewelry & Art; Permitting & Zoning; Physical Damage; Public Administration; Recreational Fishing; Recreational Opportunities; Resource Use Management; Security; Small Boats; Souvenir & Decorative Trade; Supporting Services; Tourism & Recreation; Tourism & Recreation Policies; Trampling; Travel Services & Tour Operators; Trawling & Fishing Gear Damage; Water Resources; Water Transportation |
Marine Zoning: Ecological Reserves (ERs) | Ecological Reserves set aside areas with minimal human interference. These reserves aim to enhance and protect biodiversity through encompassing large, contiguous habitats. The goal of ecological reserves is to encourage spawning, nurseries, and residence areas that contribute to genetic protection of fish and marine life. Ecological Reserves can be achieved through a variety of methods such as: placing/maintaining buoys along zone boundaries; adjusting boundaries if necessary; evaluating allowable activities within zone boundaries; identifying potential areas that need additional zoning; reviewing the effectiveness of the zoning; and revising NOAA and GIS charts. | NOAA Marine Sanctuary Program. 2007. Florida Keys National Marine Sanctuary revised management plan. National Ocean Service, Key West, FL. |
Biochemical & Genetic Resources; Biological Addition; Biological Harvest; Biological Monitoring & Restoration; Boating Activities; Boating Regulations; Coastal Defense; Commercial Fishing Boats; Complex Habitat & Resources; Cruise Ships; Decision Support; Designated Uses; Dredging Regulations; Dredging, Draining, & Filling; Ecosystem Monitoring & Restoration; Environmental Monitoring & Restoration; Finfish Harvest; Fisheries & Hunting Policies; Fishing & Harvesting Management; Fishing Sector; Invertebrate Harvest; Large Ships; Live Collection; Marine Protected Areas; Oil & Gas Tankers; Permitting & Zoning; Physical Damage; Provisioning Services; Resource Use Management; Security Policies; Small Boats; Tourism & Recreation; Trampling; Water Transportation |
Regulatory Review and Development: Evaluate Artificial Reef Regulations | Discharge/depositing of materials and constructions on the seabed are both prohibited without permits, regulating the construction of new artificial reefs. Likewise, existing artificial reefs are protected through permit requirements for any alternation of the seabed. There are still further considerations for protecting artificial reefs. Artificial reef materials and construction choices are very important and may change based on the specific location and desired impacts. An artificial reef to attract recreational fishing differs from one for recreational divers or shoreline storm protection. Many artificial reefs were formally large ships, oil rigs or other types of waste that have been decommissioned and would be too large and expensive to dismantle on land. In these cases it is important to put restrictions on the sinking process to ensure there won�t be any type of chemical leakage and that the structure is stable on the seabed. (#189) (#190) | National Oceanic and Atmospheric Administration. 2007. National Artificial Reef Plan: Guidelines for Siting, Construction, Development, and Assessment of Artificial Reefs. US Department of Commerce. NOAA Marine Sanctuary Program. 2007. Florida Keys National Marine Sanctuary revised management plan. National Ocean Service, Key West, FL. |
Artificial Habitat; Coastal Defense; Contact Uses; Discharge Limitations; Discharges; Dive, Snorkeling, & Swimming Tourism; Dredging Regulations; Environmental Monitoring & Restoration; Large Ships; Oil & Gas Industry; Permitting & Zoning; Physical Damage; Recreational Fishing; Solid Waste Disposal; Special Use Permitting; Tourism & Recreation; Waste Management; Waterborne Discharges |
Regulatory Review and Development: Develop Mobile Source Discharge Controls | Pollution discharge controls regulate where different types of discharges are allowed and what acceptable quantities released are. Typically discharge controls target point sources in the form of effluent pipes (#280), but discharges also occur from mobile sources such as boats and ships. There may need to be revisions on where depositing fish, fish parts, bait, cooling water, engine exhaust, deck wash, and effluent can be released. In many areas, these items are often excluded as prohibited, and they should possibly be included. Pollution discharge controls are different from Water Quality Standards (#22) which set acceptable environmental limits and leave it up to the manager to meet those criteria. | NOAA Marine Sanctuary Program. 2007. Florida Keys National Marine Sanctuary revised management plan. National Ocean Service, Key West, FL. |
Artisanal Fishing; Ballast Discharge; Boating Activities; Boating Regulations; Chemical Variables; Coastal Engineering; Commercial Fisheries; Commercial Fishing Boats; Cruise Ships; Discharge Limitations; Discharges; Docks & Marinas; Finfish Harvest; Fishing & Harvesting Management; Fishing Sector; Food & Energy Policies; Large Ships; Littering; Oil & Gas Tankers; Physical Damage; Point & Mobile Source Controls; Point Source Discharges; Ports & Harbors; Recreational Fishing; Small Boats; Tourism & Recreation; Wastewater Discharge; Water Transportation; Waterborne Discharges |
Water Quality Management: Protection of Resources from Hazardous Materials & Spills | Wherever possible, take actions to decrease the likelihood of hazardous materials spills near corals. Even when risks are reduced significantly, spills may still occur, necessitating contingency plans (#56). In order for reef managers to stay informed of the latest spills/updates, a spill-reporting system should be established along with a geo-referenced database that keeps track of all spills within a certain distance of reefs. | NOAA Marine Sanctuary Program. 2007. Florida Keys National Marine Sanctuary revised management plan. National Ocean Service, Key West, FL. Puerto Rico and USVI Area Planning Committees. 2008. Hazardous Substances Pollution Area Contingency Plan. Puerto Rico and the U.S. Virgin islands. USCG. 2007. Hazardous Substances Pollution Area Contingency Plan. Florida Keys. |
Discharge Limitations; Discharges; Energy Policy & Development; Food & Energy Policies; Food & Raw Materials; Large Ships; Oil & Gas Industry; Oil & Gas Rigs; Oil & Gas Tankers; Petroleum Spills; Pipelines; Point & Mobile Source Controls; Point Source Discharges; Small Boats; Toxics; Transportation; Waste Management; Waste Management Policies; Water Transportation; Waterborne Discharges |
Laws
Legal Citation | Purpose of Law | Management Organization | Database Topics |
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25 Virgin Islands Code. | Under Title 25, in addition to requirements for boat registration and administration of harbors, among other things, sections pertaining to the mooring and anchoring of vessels and houseboats provide for the protection of important marine resources in USVI waters. The Law requires mandatory boating education and safety courses for all boat operators. Application to Coral Reefs:Mooring and anchoring are restricted and not allowed near fragile systems. Not anchoring on coral reefs is abig plus of this legislation. Legislative Actions:Penalties for violation of the Chapter include fines not to exceed $1,000, a lien on the vessel and potential libel suit Comments:A houseboat or vessel is allowed to moor or anchor only in those areas designated by the Department. Section 404(g) of the legislation lists areas designated as areas of special concern. |
US Virgin Islands, Department of Planning and Natural Resources, Division of Environmental Protection Jurisdiction: US Virgin Islands |
Boating Regulations; Commercial Fishing Boats; Cruise Ships; Environmental Education & Outreach; Large Ships; Mangroves; Marine Protected Areas; Oil & Gas Tankers; Resource Use Management; Seagrasses; Small Boats; Transportation Policies |
25-Year Permits for Maintenance Dredging in Deepwater Ports; Deepwater Ports Maintenance Dredging and Disposal Manual, 62-045 Florida Administrative Code. | 62-45.001 Authority, Intent and Policy.
(1) This chapter is promulgated under the authority of Sections 403.061(26) and 403.816(1), F.S.
(2) It is the intent of this chapter to establish a permitting system for maintenance dredging in deep water commercial navigation
areas of the ports listed in Rule 62-45.020, F.A.C. This chapter incorporates standards and criteria which recognize the present most
beneficial use of these waters for deep water commercial navigation. Since the implementation of a comprehensive maintenance
dredging management plan is a major factor in determining the adequacy of a long-term maintenance dredging program, it is the
further intent of this chapter to give a position of prominence to such a plan within this permit system.
(3) It is the policy of the Department to provide a regulatory process which will enable the ports to conduct maintenance
dredging in an environmentally sound, expeditious and efficient manner.62-45.020 Scope.
(1) The permit system established by this chapter applies only to the ports of Ft. Pierce, Jacksonville, Miami, Palm Beach,
Panama City, Pensacola, Port Canaveral, Port Everglades, Port Manatee, Port St. Joe, St. Petersburg, and Tampa.
(2) The activities which may be included within a permit issued under this chapter are limited to maintenance dredging and
disposal of the maintenance dredged material.
(3) Applicants for permits under this chapter are limited to the port authorities or private interests using the port for deep water
commercial shipping and the U.S. Army Corps of Engineers. The Department shall not issue separate permits to the port authority or
private interests and the U. S. Army Corps of Engineers when the responsibility of maintenance dredging or the disposal of the
maintenance dredged material from the port is shared by any of the parties. The permit, if issued, shall clearly specify the duties and
responsibilities of each party.
(4) A permit may be issued for any length of time up to 25 years. There shall be no more than one such permit for each of the
ports listed in subsection (1).
(5) The area within which work under this permit system may take place is limited to the federally maintained, port authority
maintained, or private interest maintained navigation channels, turning basins, or harbor berths associated with deep water
commercial navigation and associated dredged material disposal sites. Eligible port maintenance dredging areas are depicted on
NOS Charts Nos. 11491 (Port of Jacksonville), 11478 (Port Canaveral), 11475 (Fort Pierce Harbor), 11466 (Port of Palm Beach),
11468 (Port of Miami), 11470 (Port Everglades), 11413 (Tampa Bay, Northern Part), 11414 (Tampa Bay, Southern Part), 11393
(Port St. Joe), 11391 (Panama City), and 11383 (Port of Pensacola) on file with the Department and adopted here by reference.
Copies are available at cost upon request from the Office of Beaches and Coastal Systems, 3900 Commonwealth Boulevard, MS
300, Tallahassee, Florida 32399-3000. Application to Coral Reefs:Proper, environmentally sound, dredging and disposal of dredged material, as reviewed by permit processers, will limit the amount of sediment and nutrients released to open water. The process will be particularly applicable to coral reefs for the dredging and disposal of Miiami harbor. Legislative Actions: Comments: |
Florida State Department of Environmental Protection Jurisdiction: US State Waters |
Dredging Regulations; Dredging, Draining, & Filling; Large Ships; Nutrients; Oil & Gas Tankers; Ports & Harbors; Resource Use Management; Sediment |
Amendment to the Florida Keys National Marine Sanctuary Regulations revising the boundary of the northernmost area to be avoided off the coast of Florida, Federal Register § Volume 65, Number226 (2000). | NOAA, in conjunction with the US Coast Guard, proposed to revise the northernmost area to be avoided (ATBA) off the coast of the Florida Keys. The change was expected to increaase maritime safety and to avoid harm to the marine environment and its resources. Application to Coral Reefs:The amendments directly protect coral reefs because the change of the nothernmost area presented in the regulation as Area To Be Avoided resulted in large vessels not entering the area that had been the site of large vessel groundings. Legislative Actions: Comments: |
National Oceanic and Atmospheric Administration in conjunction with the US Coast Guard Jurisdiction: US Coral Reefs; State Coastal Waters; US State Waters; Designated Marine Areas |
Anchoring & Vessel Grounding; Boat Movement; Civil Engineering & Construction; Commercial Fishing Boats; Coral; Cruise Ships; Fish; Large Ships; Oil & Gas Tankers; Physical Damage; Reef Inhabitants; Transportation Policies; Water Transportation |
Dredge and Fill Activities, 62-312 Florida Administrative Code. | This part provides the requirements and procedures for obtaining permits and jurisdictional declaratory statements from the Department pursuant to Sections 403.91 through 403.929, F.S. Dredging or filling which is grandfathered by subsections 403.913(6), (8) and (9), F.S., is governed by Rules 62-312.150 and 62-312.160, F.A.C. The requirements of this part are in addition to and not in lieu of the water quality standards which are required by other portions of these sections. Except for the definitions contained in Rule 62-312.020, F.A.C., which shall also apply to activities regulated under Part IV of Chapter 373, F.S., the provisions of this Part shall only apply to activities in the geographical territory of the Northwest Florida Water Management District and to activities grandfathered under Sections 373.414(9), (11), (12)(a), (13), (14), (15) and (16), F.S.
Specific Authority 373.414(11)-(16), 373.4145, 403.805(1) FS. Law Implemented 373.409, 373.413, 373.414(9), (11), (12)(a), (13), (14), (15), (16), 373.4145, 373.416, 373.418, 403.061, 403.813, 403.814 FS. History�New 12-10-84, Amended 8-7-85, Formerly 17-12.010, 17-312.010, Amended 10-3-95. Application to Coral Reefs:The permit reviewers will require BMP for dredge and fill activities. This will include siltation reduction methods that will keep sediment, nutrient and other contaminants from leaving the work site and getting into the water column and potentially reaching sensitive ecosysten, including coral reefs. Legislative Actions: Comments:This part provides the requirements and procedures for obtaining permits and jurisdictional declaratory statements from the Department for dredge and fill activities. |
Florida State Department of Environmental Protection Jurisdiction: State Coastal Waters; US State Waters |
Complex Habitat & Resources; Cruise Ships; Dredging Regulations; Dredging, Draining, & Filling; Large Ships; Nutrients; Oil & Gas Tankers; Physical & Chemical Water Quality Criteria; Ports & Harbors; Sediment; Toxics |
Florida Keys National Marine Sanctuary Regulations; Final Rule, Code of Federal Regulations § Parts 922, 929, 937 (1997). | NOAA developed the comprehensive Final Management Plan for the FKNMS and issued the Plan on January 30, 1997. Congress and the Governer of Florida were provided a 45-day period to provide certification of unacceptable regulations that needed amendments. NOAA incorporated the certified changes provided and issued the final regulations and management plan for the Sanctuary that went into effect with the publication of the final rule, including waters within the State of Florida in the Sanctuary. Application to Coral Reefs:The Sanctuary sets aside the coral reef system that is the third largest barrier coral reef in the world. Included in the FKNMS are the Key Largo Marine Sanctuary containing 103 square nautical miles of coral reefs and Looe Key National Marine Sanctuary containing 5.32 square nautical miles of coral reefs. The Act protects the reefs from anchoring directly into the coral formation and taking coral dead or alive. The Act protects mangrove islands and submerged aquatic vegetation, both potential buffers for the reef system against eutrophication and sediment deposition. The Act prohibits oil and hydrocarbon exploration, mining or altering the seabed, restricts large shipping traffic, and restricts the discharge of pollutants, further protecting coral, mangroves, and submerged aquatic vegetation. Legislative Actions:The Act requires the preparation of a comprehensive management plan and implementing regulations to protect Sanctuary resources. Comments:The final rule codifies the Act and further defines boundaries of the Sanctuary as well as providing a list of species protected in the Sanctuary. |
National Oceanic and Atmospheric and Administration Jurisdiction: US Coral Reefs; US Territorial Waters; State Coastal Waters; US State Waters; Designated Marine Areas |
Ballast Discharge; Biological Monitoring, Mapping, & Scientific Research; Boating Regulations; Collaboration & Partnering; Commercial Fishing Boats; Cruise Ships; Cultural Protections; Designate Protected Species; Dive, Snorkeling, & Swimming Tourism; Educational & Research Opportunities; Environmental Education & Outreach; Finfish & Shellfish Stock; Finfish Harvest; Fishing & Harvesting Management; Invertebrate Harvest; Invertebrates; Large Ships; Live Collection; Mangroves; Marine Debris; Nutrient & Contaminant Processing; Oil & Gas Tankers; Point & Mobile Source Controls; Recreational Fishing; Recreational Opportunities; Reef Inhabitants; Resource Use Management; Seagrasses; Sediment; Shoreline Protection; Small Boats; Tourism & Recreation; Tourism & Recreation Policies; Transportation Policies; Waste Management Policies; Wetlands |
Marine Sanitation Devices (MSDs); Regulations to establish a No Discharge Zone (NDZ) for State waters within the boundary of the Florida Keys National Marine Sanctuary,Code of Federal Regulations § 40 CFR Part 140, 67 FR 35735. | US EPA established a no discharge zone within the boundaies of the FKNMS pursuant to section 312 (f) (4) (a) of the Clean Water Act. Application to Coral Reefs:Prohibition of waste discharges protects reefs system from eutrophication by the nutrients in waste (particularly nitrogen and phosphorus) as well as the debris and sediment in the waste. Legislative Actions: Comments: |
US Environmental Protection Agency Jurisdiction: US Coral Reefs; US Federal Waters; State Coastal Waters; Designated Marine Areas |
Algae; Ballast Discharge; Commercial Fishing Boats; Cruise Ships; Large Ships; Marine Debris; Nutrient & Contaminant Processing; Nutrients; Oil & Gas Tankers; Pathogens; Petroleum Spills; Physical & Chemical Water Quality Criteria; Small Boats; Waste Management Policies; Wastewater Discharge |
National Marine Sanctuaries Act of 1972, 16 United States Code §§ 1431-1445. | Authorizes the Secretary of Commerce to designate and manage areas of the marine environment with special national significance due to their conservation, recreational, ecological, historical, scientific, cultural, archeological, educational, or esthetic qualities as National Marine Sanctuaries. Application to Coral Reefs:Protects marine resources, such as coral reefs, sunken historical vessels, or unique habitats. Legislative Actions:NOAA may impose civil penalties up tp $130,000 per day per violation. Criminal penalties were added in the 2000 amendments for interfering or resisting with any enforcement of the NMSA, or providing false information to the Secretary or any officer authorized to enforce NMSA. The 2000 amendments made it illegal to offer for sale, purchase, import, or export, any sanctuary resource and increased enforcement authority. Comments:There are 13 marine sanctuaries in the National Marine Sactuary System, six of which were created after 1990. Each sanctuary has a separarte staff and program in its local region. |
National Oceanic Aatmospheric Administration Jurisdiction: Designated Marine Areas |
Apex Fish Predators; Biological Monitoring, Mapping, & Scientific Research; Boating Regulations; CO2; Coastal Development; Commercial Fishing Boats; Coral; Corporate Responses; Designate Protected Species; Designated Uses; Dive, Snorkeling, & Swimming Tourism; Dredging, Draining, & Filling; Educational & Research Opportunities; Environmental Education & Outreach; Environmental Monitoring, Mapping, & Scientific Research; Existence Value & Sense of Place; Fishing & Harvesting Management; Large Ships; Marine Birds; Marine Protected Areas; Nutrients; Ocean Acidity; Oil & Gas Research & Exploration; Political Pressure; Recreational Opportunities; Remediation; Resource Use Management; Seagrasses; Sediment; Tourism & Recreation Policies; Wetlands |
Rivers and Harbors Act of 1899, 33 United States Code § 1252. | This law prohibits the discharge of any type of refuse matter in U.S. waters without permission (section 13). In addition, the excavation, fill, or alteration of the course, condition, or capacity of any port, channel, river, or other areas within the limits of this law is prohibited. This law prohibits the construction or alteration of a structure in wetlands of the U.S. (sections 9 and 10). Construction in wetlands and waters of the U.S. requires a permit from the U.S. Army Corps of Engineers. Application to Coral Reefs:Under section 10, excavation or fill within navigable waters requires approval of the Chief of Engineers and concerns about contaminated sediments with dredge and fill projects in navigable waters is addressed within the permitting process. Indirect protection of coral reefs is offered by the Act and its prohibition of dumping refuse into navigable waters and the process of anaylzing sediment in proposed dredge and fill operations. Legislative Actions:Violations of the law are punished under section 309 of the Clean Water Act and section 205 of National Fishing Enhancement Act. Fines imposed for violation will not be less than $10,000 per violation or more than $25,000 per violation. Comments:Many states, including Florida, require additional permits for constuction of docks, piers, wharfs, jetties and other structures in navigable waters and wetlands in addition to the Corps of Engineers permit. Authority to issue permits for discharge of refuse matter under section 13 was modified by the amendments to Federal Water Pollution Control Act of 1972 and established the National Pollutant Discharge Elimination System Permit process. The Act was initially established to protect interstate commerce in navigable waters. The permit review process involves factors including economics, aethetics, general envitonmental concerns, historical values, water quality, and fish and wildlife impact before project approval is granted. |
US Army Corps of Engineers (COE), and US Coast Guard Jurisdiction: United States |
Coastal Development; Coastal Engineering; Construction Codes & Projects; Ditching & Soil Disturbance; Docks & Marinas; Dredging Regulations; Dredging, Draining, & Filling; Landuse Management; Large Ships; Marine Debris; Marine Protected Areas; Oil & Gas Tankers; Permitting & Zoning; Point & Mobile Source Controls; Political Pressure; Ports & Harbors; Resource Use Management; Sediment; Transportation Policies; Waste Management Policies |
Significant amendments to the National Marine Sanctuaries Act of 1972. Amendments of 1980 were PL 96-332, 1984 were PL98-498, 1988 were Title II of PL 100-627, 1992 were PL 102-587, 1996 were PL 104-283 and for 2000 were PL106-513,. | Title III of the Marine Protection, Reseach and Sanctuaries Act was amended to create the National Marine Sanctuaries Program. The amendments of 1980 mandated the terms of designation to include the geographic area included within the sanctuary and the characteristics of the area that give it conservation, recreational, ecological, or esthetic value, and the types of activities that would be subject to regulation to protect those characteristics. The 1984 amendments required a Resource Assessment Report documenting present and potential use of the area. 1998 amendments established a special use permit for commercial operations, added a section that a vessel or person causing damage to the resources of a sanctuary would be liable for both response and cleanup costs as well as damages for any sanctuary resource destroyed. Amendments of 1992 provided that Title III may be cited as 'The National Marine Sanctuaries Act." Also, federal agencies had to be consistent with the National Environmental Policy Act in commenting on proposed designations. Application to Coral Reefs:Strenghtened the protectinon of marine sanctuaries and their resources. Some specific purposes of the Act that add to coral reef protection include; to identify and designate national marine sanctuaries of the marine environment, to maintain the natural b Legislative Actions: Comments: |
National Oceanic Aatmospheric Administration Jurisdiction: Designated Marine Areas |
Anchoring & Vessel Grounding; Ballast Discharge; Boating Activities; Collaboration & Partnering; Commercial Fisheries; Commercial Fishing Boats; Construction Codes & Projects; Coral; Cruise Ships; Deforestation & Devegetation; Economic Markets & Policies; Educational & Research Opportunities; Environmental Education & Outreach; Environmental Monitoring, Mapping, & Scientific Research; Existence Value & Sense of Place; Finfish & Shellfish Stock; Fishing & Harvesting Management; Large Ships; Mangroves; Nutrient & Contaminant Processing; Oil & Gas Tankers; Physical & Chemical Water Quality Criteria; Recreational Fishing; Recreational Opportunities; Reef Habitat; Reef Inhabitants; Reef Life; Resource Use Management; Seagrasses; Tourism & Recreation Policies; Wetland & Reef Restoration |
The Florida Keys National Marine Sanctuary and Protection Act, Public Law 101-605 (H.R. 5909 United States Code (1990). | To protect the resources of the area delineated in section 5(b) of the Act, to educate and interpret for the public regarding the Florida Keys marine environment, and to manage such human uses of the Sanctuary consistent with the Act. Nothing in the Act is intended to restrict activities that do not cause adverse effects to the resources or property of the Sanctuary or that do not pose harm to the users of the Sanctuary. Application to Coral Reefs:The Sanctuary sets aside the coral reef system that is the thrid largest coral reef barrier in the world. Included in the FKNMS are Key Largo Marine Sanctuary containing 103 square nautical miles of coral reefs and Looe Key National Marine Sanctuary containing 5.32 squared nautical miles of coral reefs.The Act protects the reefs from anchoring directly into the coral formation and taking coral dead or alive in the Sanctuary. From Miami to the Marquesas Keys there are over 6000 patch reefs. The Act also protects mangrove islands and submerged aquatic vegetation, both potential buffers for the reef system against eutrophication and sediment deposition. The Act prohibits oil and hydrocarbon exploration, mining or altering the seabed, restricts large shipping traffic, and restricts the discharge of pollutants, futher protecting mangroves, and submerged aquatic vegetation. Legislative Actions:The Act required the preparation of a comprehensive mangement plan and implementing regulations to protect Sanctuary resources. Comments:Large vessel groundings on coral reefs in the Florida Keys was a major driver for the designation of the Sanctuary. In 1989, there were three groundings of large commercial vessels on the coral reef tract within an eighteen day period. |
National Oceanic and Atmospheric Administration as lead agency and Florida Department of Environmental Protection, Florida Fish and Wildlife Commission, and Monroe County as Co-Trustees Jurisdiction: US Coral Reefs; US Federal Waters; US State Waters; Designated Marine Areas |
Anchoring & Vessel Grounding; Ballast Discharge; Boating Regulations; Complex Habitat & Resources; Coral; Economic Markets & Policies; Educational & Research Opportunities; Environmental Education & Outreach; Existence Value & Sense of Place; Finfish Harvest; Fish; Fishing & Harvesting Management; Invertebrate Harvest; Large Ships; Marine Debris; Marine Protected Areas; Recreational Opportunities; Reef Habitat; Reef Inhabitants; Reef Life; Shoreline Protection; Substrate; Tourism & Recreation Policies; Water Transportation |