ReefLink Database

Seawater Flow
Seawater flow reflects circulation patterns, currents, and wave action that move water throughout the ocean and towards the coastline.
CMap
CMap Description
Human activities that alter the landscape, including shoreline armoring and impervious surfaces, can alter surface and groundwater flow, causing freshwater discharge into coastal waters, and altering patterns of seawater flow. Seawater flow and circulation patterns influence sea surface temperature levels and alter the concentration and distribution of contaminants. Seawater circulation also influences the transport and recruitment of passive larvae and mobile adults, and ultimately the connectivity among marine aquatic populations. Coral reefs and wetlands can also alter seawater flow through wave energy attenuation, providing calm waters that may enhance recruitment of larval fish and invertebrates, in additional to protecting coastal communities from flooding or erosion. Water flow patterns can be monitored and mapped to better understand connectivity among populations, or potential patterns of contaminant distribution. Landuse or hydrological management can be implemented to minimize alterations to water flow patterns. Many of the same socio-economic sectors, such as transportation, civil engineering, and construction that create pressures on the reef also benefit from reef goods and services, such as shoreline protection or recreational opportunities that contribute to the cultural identity of the local community.Citations
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Citation | Year | Study Location | Study Type | Database Topics |
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Management Options
Management Option | Description | Sources | Database Topics |
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Energy Policy & Development: Develop Offshore Wind and Hydrokinetic Alternative Energies | Policies encouraging or authorizing construction of offshore facilities are evolving, and there are many sides to the issue of how to best manage them. Alternative energies are desirable and would reduce the dependence on fossil fuel resources. However, hydrokinetic technologies are just becoming viable, meaning long term impacts are still unknown. Facilitative policies reduce barriers for alternative energy development or increase barriers or costs for incumbent technologies. These include research and innovation policies, technology improvement subsidies, market based policies that internalize externalities, and regulatory changes that simplify the permitting process. | Energy Efficiency & Renewable Energy. 2009. Report to Congress on the Potential Environmental Effects of Marine and Hydrokinetic Energy Technologies. Department of Energy. Portman, M.E. 2010. Marine Renewable Energy Policy: Some US and International Perspectices Compared. Oceanography 23:98-105. |
Artificial Habitat; Biological Addition; Construction Codes & Projects; Economic Markets & Policies; Energy Policy & Development; Funding & Incentives; Infrastructural Policies; Natural Gas & Electric Power; Oil & Gas Industry; Permitting & Zoning; Petroleum Spills; Physical Variables; Point Source Discharges; Provisioning Services; Seawater Flow; Utilities; Utility Line Construction & Maintenance; Utility Policies |
Monitor & Research: Research Historical Hydrology | This activity involves a historical assessment of the hydrology of the surrounding water area around the sanctuary as it has affected water quality and biological communities within the sanctuary. It will clarify the role of freshwater inflows and water quality from local freshwater bodies. Also, this activity will examine the effects of structural modification and changes in quality, quantity, timing and distribution of freshwater releases from existing structures and will examine land-based practices affecting the water quality of runoff. | NOAA Marine Sanctuary Program. 2007. Florida Keys National Marine Sanctuary revised management plan. National Ocean Service, Key West, FL. |
Applied Chemicals; Chemical Variables; Coastal Development; Coastal Engineering; Dam Construction & Maintenance; Deforestation & Devegetation; Discharge Limitations; Discharges; Ditching & Soil Disturbance; Dredging, Draining, & Filling; Ecosystem Monitoring & Restoration; Environmental Monitoring & Restoration; Environmental Monitoring, Mapping, & Scientific Research; Hydrologic Management; Impervious Surfaces; Infrastructural Policies; Landscape Changes; Landuse Management; Physical Variables; Salinity; Seawater Flow; Shoreline Armoring; Stormwater Management; Surface & Groundwater Flow; Water; Water Depth & Sea Level; Water Transportation; Waterborne Discharges |
Monitor & Research: Research Global Change | This management option involves research to examine the effects of stresses associated with global change on the ecosystem. Stresses can include changes in temperature, hydrology, salinity, frequency and intensity of storms, turbidity, sea level change, and ultra violet and visible radiation. | NOAA Marine Sanctuary Program. 2007. Florida Keys National Marine Sanctuary revised management plan. National Ocean Service, Key West, FL. |
Atmospheric Emissions; Calcium Carbonate Deposition; Carbon Storage & Cycling; Chemical Variables; Climate; Climate Regulation; CO2; Discharges; Ecosystem Monitoring & Restoration; Environmental Monitoring & Restoration; Environmental Monitoring, Mapping, & Scientific Research; Greenhouse Gas Emissions; Nutrient & Contaminant Processing; Ocean Acidity; Physical & Chemical Water Quality Criteria; Physical Variables; Regulating Services; Salinity; Sea Temperatures; Seawater Flow; Shoreline Protection; Storms & Hurricanes; Supporting Services; Surface & Groundwater Flow; Water Depth & Sea Level |
Monitor & Research: Research Artificial Reef Siting, Size, and Materials Impact for Future Management Decisions | The effects of artificial reefs on fish and invertebrate abundance and community composition and on other sanctuary resources need to be assessed. Siting and size considerations should include spatial components such as nearest natural reef, species connectivity, currents, distance to shore, expected use, hurricane occurances, etc. The longevity of artificial reefs composed of different materials needs to be evaluated and considered heavily. | 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; Biological Addition; Biological Monitoring & Restoration; Biological Monitoring, Mapping, & Scientific Research; Chemical Variables; Complex Habitat & Resources; Coral; Cultural Services; Decision Support; Ecosystem Monitoring & Restoration; Educational & Research Opportunities; Environmental Monitoring & Restoration; Finfish & Shellfish Stock; Fish; Invertebrates; Marine Debris; Physical Variables; Provisioning Services; Public Administration; Recreational Opportunities; Reef Habitat; Reef Inhabitants; Reef Life; Regulating Services; Seawater Flow; Security & Public Administration Policies; Shoreline Protection; Sponges; Storms & Hurricanes; Substrate; Tourism & Recreation Policies; Toxics; Water Resources; Wetland & Reef Restoration |
Monitor & Research: Research and Monitor Wetlands | This management option involves monitoring and research of mangroves, both for biotic and abiotic factors. Some biotic factors include disease, species, invasive species, abundance, age and leaf litter. Important abiotic factors include sedimentation rates, types and causes of turbidity, and soil chemistry. The activity would document changes to the extent of mangrove vegetation by using historical aerial photography and other records. Wetland nutrient and contaminant processing productivity depends on maintaining a balance and not exceeding thresholds. There remain many unknowns in wetland restoration as to optimal capacity and how to achieve this. | NOAA Marine Sanctuary Program. 2007. Florida Keys National Marine Sanctuary revised management plan. National Ocean Service, Key West, FL. |
Biological Monitoring & Restoration; Biological Monitoring, Mapping, & Scientific Research; Carbon Storage & Cycling; Chemical Variables; Climate Regulation; Complex Habitat & Resources; Deforestation & Devegetation; Discharges; Ecosystem Monitoring & Restoration; Educational & Research Opportunities; Environmental Monitoring & Restoration; Environmental Monitoring, Mapping, & Scientific Research; Invasive Species; Mangroves; Nutrient & Contaminant Processing; Nutrients; Physical & Chemical Water Quality Criteria; Physical Variables; Primary Production; Regulating Services; Scientific Research; Seawater Flow; Sediment; Shoreline Protection; Substrate; Supporting Services; Surface & Groundwater Flow; Wetland & Reef Restoration; Wetlands |
Waterway Management: Manage Canal Water Quality | This management option addresses water quality issues that may arise from nearshore, confined areas, specifically dead-end canals. This management response does not focus on wastewater discharges into canals, but instead on the hydrologic structure and orientation of the canal itself. Physical problems with canal orientation can lead to such problems as low flushing and build-up of weed wrack. This is a problem because the build-up of weed wrack consumes oxygen and releases nutrients as it decays. When combined with low flushing and circulation, dead end canals have decreased oxygen concentrations, accelerated eutrophication, and accumulate organic materials, pollutants and sediment. To improve the current canal system, management can inventory and map canals to identify high risk hotspots and candidates for future canal restoration projects. Canals are typically constructed to best suit the water access needs of local homes and businesses. Preventing high risk canals from being constructed, or placing certain requirements on their construction through permitting is one way to reduce future problem spots. Some design strategies include: Construct non-linear canals without right-angles and flared inlets oriented to prevailing winds. Instead of dead-ends, canals should include a flow through water exchange system or install mechanical pumps. Canals should be as wide as possible in relation to depth and length. Canal depth should be uniform or progressively shallower away from the parent waterbody, with sloping banks (eliminate requirements for navigable depths to shoreline). Some canal improvement strategies include: Implement weed gates, air curtains, and aeration systems. Direct all stormwater and effluent away from canal systems. Reduce bulkheading and restore native vegetative buffers (#1). Promote diversity of substrates and habitats. | NOAA Marine Sanctuary Program. 2007. Florida Keys National Marine Sanctuary revised management plan. National Ocean Service, Key West, FL. |
Applied Chemicals; Biological Monitoring & Restoration; Boat Movement; Boating Activities; Building & Home Construction; Chemical Variables; City Planning; Civil Engineering & Construction; Coastal Development; Coastal Engineering; Construction Codes & Projects; Decision Support; Deforestation & Devegetation; Discharge Limitations; Discharges; Ditching & Soil Disturbance; Docks & Marinas; Ecosystem Monitoring & Restoration; Environmental Monitoring & Restoration; Fishing Sector; Food & Energy Policies; Hydrologic Management; Improved Technology; Infrastructural Policies; Infrastructure; Land-Based Civil Engineering; Landscape Changes; Landscaping & Household Services; Landuse Management; Non-point Source Controls; Non-point Source Runoff; Nutrient & Contaminant Processing; Physical & Chemical Water Quality Criteria; Physical Damage; Physical Variables; Point & Mobile Source Controls; Point Source Discharges; Ports & Harbors; Provisioning Services; Regulating Services; Seawater Flow; Shoreline Armoring; Shoreline Protection; Small Boats; Surface & Groundwater Flow; Tourism & Recreation; Transportation; Transportation Policies; Utilities; Utility Policies; Waste Management; Waste Management Policies; Wastewater Discharge; Water; Water Depth & Sea Level; Water Resources; Water Transportation; Waterborne Discharges; Wetland & Reef Restoration; Wetlands |
Laws
Legal Citation | Purpose of Law | Management Organization | Database Topics |
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Biscayne Bay Aquatic Preserve, 18-18 Florida Administrative Code. | 18-18.001 Intent.
(1) The Biscayne Bay Aquatic Preserve, the boundaries of which are fully described in Rule 18-18.002, F.A.C., was established for the purpose of preserving and enhancing Biscayne Bay and all natural waterways tidally connected to the bay in an essentially natural condition so that its biological and aesthetic values may endure for the enjoyment of future generations.
(2) These rules shall apply to all lands public and private within the boundaries of the preserve. However, privately owned uplands shall be excluded from these rules except as otherwise provided for herein.
(3) In promulgating and implementing these rules, it is the intent of the Department to construe the provisions of Sections 258.397 and 258.35 through 258.46, F.S., together and to apply the more stringent statutory provisions for the maintenance of the preserve.
(4) The preserve shall be administered and managed in accordance with the following goals:
(a) To preserve, protect, and enhance Biscayne Bay and all natural waterways tidally connected to the bay by reasonable regulation of human activity within the preserve through the development and implementation of a comprehensive management program;
(b) To protect and enhance the waters of the preserve so that the public may continue to enjoy the traditional recreational uses of those waters such as swimming, boating and fishing;
(c) To coordinate with federal, state, and local agencies to aid in carrying out the intent of the legislature in creating the preserve;
(d) To use applicable federal, state, and local management programs, which are compatible with the intent and provisions of the Act and these rules, to assist in managing the preserve;
(e) To encourage activities that protect or enhance the biological and aesthetic values of the preserve, including but not limited to the modification of existing manmade conditions towards their natural condition, when reviewing applications or developing and implementing management plans for the preserve;
(f) To preserve and promote indigenous life forms and habitats including but not limited to sponges, soft corals, hard corals, seagrasses, mangroves, mud flats, marine reptiles, game and non-game fish species, marine mammals, tropical marine invertebrates, birds and shellfish;
(g) To acquire additional title interests in land wherever such acquisitions would serve to protect or enhance the biological or aesthetic values of the preserve. Application to Coral Reefs:Biscayne Bay Aquatic Preserve protection of water quality will contribute to a lowering of contaminants leaving the preserve on tides and thus limiting the contaminants that reach off-shore ecosystems including the FKNMS and the reef system within the sanctuary. Legislative Actions: Comments:This chapter establishes the rules to protect the Biscayne Bay Aquatic Preserve, which was established for the purpose of preserving and enhancing Biscayne Bay and all natural waterways tidally connected to the bay in an essentially natural condition so that its biological and aesthetic values may endure for the enjoyment of future generations. |
Florida State Department of Environmental Protection Jurisdiction: Designated Marine Areas |
Accidental & Illegal Harvest; Anchoring & Vessel Grounding; Ballast Discharge; Boat Movement; Coastal Development; Docks & Marinas; Dredging Regulations; Dredging, Draining, & Filling; Environmental Education & Outreach; Existence Value & Sense of Place; Finfish & Shellfish Stock; Finfish Harvest; Hydrologic Management; Landuse Management; Mangroves; Marine Birds; Marine Debris; Nutrients; Point Source Discharges; Recreational Opportunities; Resource Use Management; Seagrasses; Seawater Flow; Sediment; Sewage Treatment; Small Boats; Waste Management Policies; Wastewater Discharge |
Rules and Procedures for Application for Coastal Construction Permits, 62B-041 Florida Administrative Code. | No coastal construction shall be conducted without a permit issued by the Department under this chapter, unless it is determined that the coastal construction does not fall within the requirements of section 161.041, F.S., or unless the interior tidal water body is exempted by the Department pursuant to subsection 161.041(1), F.S. Application to Coral Reefs:Requiring a permit with regulatory review of the construction project will assist in minimizing potential adverse environmental impacts from the work and such potential detrimental portions of the project (e.g. sedimentation) will not enter the marine environment resulting in ecosystem damage. Legislative Actions: Comments:No coastal construction shall be conducted without a permit issued by the Department under this chapter, unless it is determined that the coastal construction does not fall within the requirements of section 161.041, F.S., or unless the interior tidal water body is exempted by the Department pursuant to subsection 161.041(1), F.S. |
Florida State Department of Environmental Protection Jurisdiction: State Coastal Waters |
Building & Home Construction; Coastal Development; Docks & Marinas; Dredging Regulations; Dredging, Draining, & Filling; Ports & Harbors; Resource Use Management; Seawater Flow; Sediment |
Rules and Procedures for Coastal Construction and Excavation, 62B-033 Florida Administrative Code (2008). | (1) The beach and dune system is an integral part of the coastal system and represents one of the most valuable natural resources in Florida, providing protection to adjacent upland properties, recreational areas, and habitat for wildlife. A coastal construction control line (CCCL) is intended to define that portion of the beach and dune system which is subject to severe fluctuations caused by a 100-year storm surge, storm waves, or other forces such as wind, wave, or water level changes. These fluctuations are a necessary part of the natural functioning of the coastal system and are essential to post-storm recovery, long term stability, and the preservation of the beach and dune system. However, imprudent human activities can adversely interfere with these natural processes and alter the integrity and functioning of the beach and dune system. The control line and 50-foot setback call attention to the special hazards and impacts associated with the use of such property, but do not preclude all development or alteration of coastal property seaward of such lines.
(2) In order to demonstrate that construction is eligible for a permit, the applicant shall provide the Department with sufficient information pertaining to the proposed project to show that adverse and other impacts associated with the construction have been minimized and that the construction will not result in a significant adverse impact.
(3) After reviewing all information required pursuant to this rule chapter, the Department shall:
(a) Deny any application for an activity which either individually or cumulatively would result in a significant adverse impact including potential cumulative effects. In assessing the cumulative effects of a proposed activity, the Department shall consider the short-term and long-term impacts and the direct and indirect impacts the activity would cause in combination with existing structures in the area and any other similar activities already permitted or for which a permit application is pending within the same fixed coastal cell. The impact assessment shall include the anticipated effects of the construction on the coastal system and marine turtles. Each application shall be evaluated on its own merits in making a permit decision; therefore, a decision by the Department to grant a permit shall not constitute a commitment to permit additional similar construction within the same fixed coastal cell.
(b) Deny any application for an activity where the project has not met the Department�s siting and design criteria; has not minimized adverse and other impacts, including stormwater runoff; or has not provided mitigation of adverse impacts.
(4) The Department shall issue a permit for construction which an applicant has shown to be clearly justified by demonstrating that all standards, guidelines, and other requirements set forth in the applicable provisions of Part I, Chapter 161, F.S., and this rule chapter are met, including the following:
(a) The construction will not result in removal or destruction of native vegetation which will either destabilize a frontal, primary, or significant dune or cause a significant adverse impact to the beach and dune system due to increased erosion by wind or water;
(b) The construction will not result in removal or disturbance of in situ sandy soils of the beach and dune system to such a degree that a significant adverse impact to the beach and dune system would result from either reducing the existing ability of the system to resist erosion during a storm or lowering existing levels of storm protection to upland properties and structures;
(c) The construction will not direct discharges of water or other fluids in a seaward direction and in a manner that would result in significant adverse impacts. Forthe purposes of this rule section, construction shall be designed so as to minimize erosion induced surface water runoff within the beach and dune system and to prevent additional seaward or off-site discharges associated with a coastal storm event.
(d) The construction will not result in the net excavation of the in situ sandy soils seaward of the control line or 50-foot setback;
(e) The construction will not cause an increase in structure-induced scour of such magnitude during a storm that the structure-induced scour would result in a significant adverse impact;
(f) The construction will minimize the potential for wind and waterborne missiles during a storm;
(g) The activity will not interfere with public access, as defined in Section 161.021, F.S.; and
(h) The construction will not cause a significant adverse impact to marine turtles, or the coastal system.
(5) In order for a manmade frontal dune to be considered as a frontal dune defined under Section 161.053(6)(a)1., F.S., the manmade frontal dune shall be constructed to meet or exceed the protective value afforded by the natural frontal dune system in the immediate area of the subject shoreline. Prior to the issuance of a permit for a single-family dwelling meeting the criteria of Section 161.053(6)(c), F.S., the manmade frontal dune must be maintained for a minimum of 12 months and be demonstrated to be as stable and sustainable as the natural frontal dune system.
(6) Sandy material excavated seaward of the control line or 50-foot setback shall be maintained on site seaward of the control line or 50-foot setback and be placed in the immediate area of construction unless otherwise specifically authorized by the Department.
(7) Swimming pools, wading pools, waterfalls, spas, or similar type water structures are expendable structures and shall be sited so that their failure does not have adverse impact on the beach and dune system, any adjoining major structures, or any coastal protection structure. Pools sited within close proximity to a significant dune shall be elevated either partially or totally above the original grade to minimize excavation and shall not cause a net loss of material from the immediate area of the pool. All pools shall be designed to minimize any permanent excavation seaward of the CCCL.
(8) Major structures shall be located a sufficient distance landward of the beach and frontal dune to permit natural shoreline fluctuations, to preserve and protect beach and dune system stability, and to allow natural recovery to occur following storm-induced erosion. Where a rigid coastal structure exists, proposed major structures shall be located a sufficient distance landward of the rigid coastal structure to allow for future maintenance or repair of the rigid coastal structure. Although fishing piers shall be exempt from this provision, their foundation piles shall be located so as to allow for the maintenance and repair of any rigid coastal structure that is located in close proximity to the pier.(9) If in the immediate area a number of existing major structures have established a reasonably continuous and uniform construction line and if the existing structures have not been unduly affected by erosion, except where not allowed by the requirements of Section 161.053(6), F.S., and this rule chapter, the Department shall issue a permit for the construction of a similar structure up to that line.
(10) In considering applications for single-family dwellings proposed to be located seaward of the 30-year erosion projection pursuant to Section 161.053(6), F.S., the Department shall require structures to meet criteria in Section 161.053(6)(c), F.S., and all other siting and design criteria established in this rule chapter.
(11) In considering project impacts to native salt-tolerant vegetation, the Department shall evaluate the type and extent of native salt-tolerant vegetation, the degree and extent of disturbance by invasive nuisance species and mechanical and other activities, the protective value to adjacent structures and natural plant communities, the protective value to the beach and dune system, and the impacts to marine turtle nesting and hatchlings. The Department shall restrict activities that lower the protective value of natural and intact beach and dune, coastal strand, and maritime hammock plant communities. Activities that result in the removal of protective root systems or reduce the vegetation�s sand trapping and stabilizing properties of salt tolerant vegetation are considered to lower its protective value. Construction shall be located, where practicable, in previously disturbed areas or areas with non-native vegetation in lieu of areas of native plant communities when the placement does not increase adverse impact to the beach and dune system. Planting of invasive nuisance plants, such as those listed in the Florida Exotic Pest Plant Council�s 2005 List of Invasive Species � Categories I and II, will not be authorized if the planting will result in removal or destruction of existing dune-stabilizing native vegetation or if the planting is to occur on or seaward of the dune system. A copy of this list is available on the Internet at www.fleppc.org; or can be obtained by writing to the Department of Environmental Protection, Bureau of Beaches and Coastal Systems, 3900 Commonwealth Boulevard, Mail Station 300, Tallahassee, Florida 32399-3000; or by telephoning (850) 488-7708. Special conditions relative to the nature, timing, and sequence of construction and the remediation of construction impacts shall be placed on permitted activities when necessary to protect native salt-tolerant vegetation and native plant communities. A construction fence, a designated location for construction access or storage of equipment and materials, and a restoration plan shall be required if necessary for protection of existing native salt-tolerant vegetation during construction.
(12) Special conditions relative to the nature, timing, and sequence of construction shall be placed on permitted activities when necessary to protect marine turtles and their nests and nesting habitat. In marine turtle nesting areas, all forms of lighting shall be shielded or otherwise designed so as not to disturb marine turtles. Tinted glass or similar light control measures shall be used for windows and doors which are visible from the nesting areas of the beach. The Department shall suspend any permitted construction when the permittee has not provided the required protection for marine turtles and their nests and nesting habitat. Application to Coral Reefs:Regulation of coastal construction through permit review and modification will protect coastal ecosystems from degradation and loss and in doing so protects other marine ecosystems including coral reefs. Legislative Actions:Chapter 62B-33 Florida Administrative Code, provides the design and siting requirements that must be met to obtain a coastal construction control line permit.Approval or denial of a permit application is based upon a review of the potential impacts to the beach dune system, adjacentproperties, native salt resistant vegetation, and marine turtles. Comments:The Coastal Construction Control Line (CCCL) is an essential element of Florida's coastal management program. It provides protection for Florida's beaches and dunes while assuring reasonable use of private property. Recognizing the value of the state's beaches, the Florida legislature initiated the Coastal Construction Contorl Line Program to protect the coastal system from improperly sited and designed structures which can destabilize or destroy the beach and dune system. Once destabilized, the valuable natural resources are lost, as are its important values for recreation, upland property protection and environmental habitat. Adoption of a coastal construction line establishes an area of jurisdiction in which special siting and design criteria are applied for construction and related activities.These standards may be more stringent than those already applied in the rest of the coastal building zone because of the greater forces expected to occur in the more seaward zone of the beach during a storm event. |
Florida State Department of Environmental Protection Jurisdiction: State Coastal Waters; Designated Marine Areas |
Beach & Land Formation; Building & Home Construction; City Planning; Civil Engineering & Construction; Coastal Development; Construction Codes & Projects; Cruise Ships; Docks & Marinas; Dredging Regulations; Dredging, Draining, & Filling; Hydrologic Management; Landuse Management; Mangroves; Marine Protected Areas; Oil & Gas Tankers; Pipelines; Ports & Harbors; Resource Use Management; Seagrasses; Seawater Flow; Sediment; Shoreline Armoring; Shoreline Protection; Storms & Hurricanes; Tourism & Recreation Policies; Water Depth & Sea Level |
Significant amendments to the Coastal Barrier Resources Act of 1982 include (1) Coastal Barrier Improvement Act of 1990, (2) Coastal Barrier Resources Reauthorization Act of 2000, (3) Coastal Barriers Resources Reauthorization Act of 2005,. | (1) Added additional areas along the Great Lakes, Puerto Rico, the Florida Keys and the Virgin Islands and established "Otherwise Protected Areas OPAs); (2) amended the guidelines for making recommendations regarding additions to the CBRS and reqired a pilot digital mapping project; (3) reauthorized CBRA and required the submission of the final digital mapping pilot project. Application to Coral Reefs:Development of coastal barrier islands can cause sedimentation, through runoff and construction activities, that could reach inshore coral reefs. Legislative Actions:Restricted most federal expenditures and financial assistance that encourage development including federal flood insurance. Comments:Recognized coastal barriers as essential habitat for many fish, water fowl and other aquatic animals |
U.S. Fish & Wildlife Service Jurisdiction: United States |
Beach & Land Formation; Coastal Development; Dam Construction & Maintenance; Existence Value & Sense of Place; Forestry; Mangroves; Seagrasses; Seawater Flow; Shoreline Protection |
Sovereign submerged lands management, 18-21 Florida Administrative Code Annotated (2006). | To manage, protect, and enhance sovereignty lands so that the public may continue to enjoy traditional uses, including, but not limited to, navigation, fishing and swimming, public drinking water supply, shellfish harvesting, public recreation, and fish and wildlife propagation and management. Application to Coral Reefs:Permitting activities on submerged lands owned by Florida will improve water quality which will indirectly protect reef systems. Legislative Actions:These rules are to implement the administration and management responsibilities of the board and department regarding sovereign submerged lands. Responsibility for environmental permitting of activities and water quality protection on sovereign lands is vested with the Department of Environmental Protection. These rules are considered cumulative. Comments: |
Florida Department of Environmental Protection Jurisdiction: State Coastal Waters |
Anchoring & Vessel Grounding; Aquaculture; Beach & Land Formation; Coastal Defense; Commercial Fisheries; Construction Codes & Projects; Docks & Marinas; Dredging Regulations; Dredging, Draining, & Filling; Energy Policy & Development; Existence Value & Sense of Place; Oil & Gas Research & Exploration; Pipelines; Point Source Discharges; Ports & Harbors; Recreational Fishing; Recreational Opportunities; Resource Use Management; Seawater Flow; Sediment; Shoreline Protection; Trawling & Fishing Gear Damage |