ReefLink Database
Landscape Conservation & Restoration
Landscape conservation and restoration refers to efforts to protect and restore disturbed natural landscapes, such as through hydroseeding or beach renourishment.
CMap
CMap Description
A change in the provision of ecosystem services, or a desire to improve provision of ecosystem services, may elicit responses to reduce or manage changes to the landscape that can create pressures on the reef. Coastal development contributes to landscape changes, including impervious surfaces, devegetation, shoreline armoring, dredging, or filling for construction of roads and buildings, which can alter rates of pollutant runoff, directly impact coastal vegetation, and alter patterns of water flow. Landscape restoration, such as hydroseeding, may be used to reduce runoff along roads or other disturbed areas. Many of the same socio-economic sectors that drive coastal development and landscape changes, also benefit from reef ecosystem services, including aesthetic value, seafood, and shoreline protection.Citations
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Management Options
Management Option | Description | Sources | Database Topics |
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Agriculture & Aquaculture: Hydroseeding High Risk Soils | Hydroseeding is a process that creates a slurry of seeds, water, and mulch. This slurry can be applied with the use of trucks, trailers, and even aircrafts. This method is particularly useful because it promotes quick germination and reduces erosion. It is especially beneficial to use this method where there is a vastness of bare soil due to clearing vegetation for roads, homes, and farming. Higher elevations are typically steeper and often experience heavy rainfall, and ultimately an extreme amount of erosion occurs if soil is bare. Erosion from the highlands can fill the reservoirs in the drainage basin with sediment. Using hydroseeding would increase vegetation and ultimately the stabilization of the soil. Also, increased vegetation through hydroseeding would help with infiltration rates because the roots would aerate the soil. | Center for Watershed Protection. 2008. Guanica Bay watershed management plan. Natural Resources Conservation Service. 1999. Temporary Seeding. NRCS Planning and Design Manual. U.S. Depatrment of Agriculture. |
Agriculture; Agriculture, Aquaculture, & Forestry Policies; Biological Monitoring & Restoration; Civil Engineering & Construction; Construction Codes & Projects; Deforestation & Devegetation; Ditching & Soil Disturbance; Ecosystem Monitoring & Restoration; Environmental Monitoring & Restoration; Food & Energy Policies; Food & Raw Materials; Forestry; Infrastructure; Land-Based Civil Engineering; Landscape Changes; Landscape Conservation & Restoration; Landuse Management; Mining; Mining Policies; Reef Life; Sediment |
Agriculture & Aquaculture: Sodic Soil Management | In coastal agriculture it is important to manage and reduce accumulations of salts on the soil surface and down to the crop rooting depth. Saline seep often occurs in crop areas where the water table is very shallow. Irrigation management or drainage improvements may be necessary. Another option may be subsoiling, where internal soil drainage is restricted by layers of contrasting permeability and soil moisture levels are low enough to allow shattering and mixing of soil layers. Vegetative measures include planting deep rooted crops such as wheatgrass and alfalfa. Soil amendments can be used to treat sodium, displacing it with calcium depending on the specific chemistry of the soil. Though crop yield does not directly impact coral reefs, ground water restoration projects may change the raise the water table, making sodic soil management important. | Natural Resources Conservation Service. 2011. National Handbook of Conservation Practices. U.S. Department of Agriculture. |
Agriculture; Agriculture, Aquaculture, & Forestry Policies; Coastal Development; Ditching & Soil Disturbance; Food & Raw Materials; Landscape Conservation & Restoration; Salinity; Surface & Groundwater Flow; Water Depth & Sea Level |
Data Management & Decision Tools: Develop a Geographic Information System Incorporating Satellite and Aerial Images | This option involves the acquisition of high-resolution, low altitude photos of management areas and grounding hotspots. These photos can then be used for baseline documentation for natural resource litigation, research, and management decisions. If these images are to be incorporated into larger geodatabase, such as that proposed in # 166, a standardized protocol should be developed in advance, as suggested in management option #166. | 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; Cultural Services; Decision Support; Discharges; Ecosystem Monitoring & Restoration; Ecosystem Services; Educational & Research Opportunities; Landscape Changes; Landscape Conservation & Restoration; Physical Damage; Resource Use Management; Security & Public Administration Policies |
Develop & Distribute Educational Materials: Develop Roadside Signs | Roadside signs and billboards in local reef watershed areas should be created to inform travelers that they are entering/exiting the reef watershed. Partnerships should be explored to create multi-logo signs. | NOAA Marine Sanctuary Program. 2007. Florida Keys National Marine Sanctuary revised management plan. National Ocean Service, Key West, FL. |
Collaboration & Partnering; Environmental Education & Outreach; Infrastructural Policies; Landscape Conservation & Restoration; Permitting & Zoning; Resource Use Management; Security & Public Administration Policies; Tourism & Recreation Policies; Transportation Policies |
Develop & Distribute Educational Materials: Establish VHF Radio Stations | The local sanctuary staff should work to secure a VHF radio station dedicated to provide information about local boating and water activities in multiple languages. Broadcast messages can include, but are not limited to information about regulations, navigation, resources, weather, and reef conditions. This will help prevent boaters, divers, and fishermen from negatively affecting the ecosystem. Assessments regarding cost and target audience areas must be conducted and external funding pursued to supplement the expense. | 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; Ballast Discharge; Boating Activities; Boating Regulations; Decision Support; Designated Uses; Environmental Education & Outreach; Fisheries & Hunting Policies; Fishing & Harvesting Management; Security & Public Administration Policies; Trawling & Fishing Gear Damage |
Dissemination of Findings: Distribute Periodic Sanctuary Health Reports | The management option involves creating monitoring/condition reports on the health of the sanctuary and reef that is released for the public. The findings can be released through newsletters, presentations, reports, publications, and other written and oral methods. Criteria reported on typically include water quality, critical habitats, and species of particular interest. These reports will ultimately help reveal the effectiveness of marine protections and policies based on the conditions researched. | NOAA Marine Sanctuary Program. 2007. Florida Keys National Marine Sanctuary revised management plan. National Ocean Service, Key West, FL. |
Biological Monitoring, Mapping, & Scientific Research; Chemical Variables; Collaboration & Partnering; Cultural Protections; Decision Support; Designate Protected Species; Ecosystem Monitoring & Restoration; Education & Information; Educational & Research Opportunities; Environmental Education & Outreach; Environmental Monitoring, Mapping, & Scientific Research; Landscape Conservation & Restoration; Marine Protected Areas; Physical & Chemical Water Quality Criteria; Physical Variables; Provisioning Services; Resource Use Management; Socio-Economic Drivers; Tourism & Recreation |
Forestry Policy: Forestry Management Planning | There are many aspects to properly managing forestry sites to reduce point source and non-point source pollutants. Forestry activities can degrade water quality with several types of pollutants and impacts, including: sediment, nutrients, forest chemicals like pesticides, organic debris from tree litter, increased water temperature and increased streamflow. The Forestry management plan and practices include, but are not limited to: pre-harvest planning, road construction and use, prescribed burning and fire management, brush management, timber harvest, regeneration, and application of forest chemicals. Wetlands Forest Management has additional best practices. | Environmental Protection Agency Office of Water. 1993. Guidance Specifying Management Measures For Sources Of Nonpoint Pollution In Coastal Waters. EPA/840/B-92/002, US EPA, Washington, DC. Natural Resources Conservation Service. 2011. National Handbook of Conservation Practices. U.S. Department of Agriculture. |
Agriculture, Aquaculture, & Forestry Policies; Applied Chemicals; Biological Harvest; Chemical Use Regulations; Civil Engineering & Construction; Deforestation & Devegetation; Discharge Limitations; Ditching & Soil Disturbance; Fertilizer & Pesticide Use; Food & Raw Materials; Forestry; Landscape Changes; Landscape Conservation & Restoration; Landuse Management; Manufacturing & Trade; Non-point Source Controls; Non-point Source Runoff; Nutrients; Physical & Chemical Water Quality Criteria; Point & Mobile Source Controls; Point Source Discharges; Regulating Services; Resource Use Management; Sediment; Supporting Services; Surface & Groundwater Flow; Toxics; Waterborne Discharges; Wetlands; Wood, Plastics, & Chemical Products |
Forestry Policy: Forestry Streamside Management Areas | There are often surface waters, such as streams and lakes, within forestry areas that require special protection. This management option involves establishing and maintaining management areas (35 to 50 feet) around these surface waters to buffer against changes in temperature, increases in sediments and nutrients, and to provide bank stability. Canopy species in these areas also provide woody debris needed for instream channel structure and aquatic species habitat. | Environmental Protection Agency Office of Water. 1993. Guidance Specifying Management Measures For Sources Of Nonpoint Pollution In Coastal Waters. EPA/840/B-92/002, US EPA, Washington, DC. Natural Resources Conservation Service. 2011. National Handbook of Conservation Practices. U.S. Department of Agriculture. |
Agriculture, Aquaculture, & Forestry Policies; Carbon Storage & Cycling; Civil Engineering & Construction; Construction Codes & Projects; Deforestation & Devegetation; Discharges; Ditching & Soil Disturbance; Food & Raw Materials; Forestry; Impervious Surfaces; Infrastructural Policies; Landscape Changes; Landscape Conservation & Restoration; Landuse Management; Non-point Source Runoff; Point & Mobile Source Controls; Primary Production; Sediment; Surface & Groundwater Flow; Waterborne Discharges; Wood, Plastics, & Chemical Products |
Landuse Management: Household Landscaping Best Management Practices | Homeowners manipulate the visible features of the land surrounding their home through landscaping. This includes flora, fauna, and terrain. Best Management Practices (BMPs) for landscaping include selection of indigenous flora and fauna, landscape irrigation (sprinkler systems etc), stormwater runoff BMPs, reducing water use, integrated pest management, composting, and incorporation of permeable surfaces. | Natural Resources Conservation Service. 2011. National Handbook of Conservation Practices. U.S. Department of Agriculture. Irrigation Association. 2010. Turf and Landscape Irrigation Best Management Practices. |
Applied Chemicals; Biological Addition; Building & Home Construction; Chemical Variables; City Planning; Discharge Limitations; Environmental Education & Outreach; Escape & Release of Non-natives; Existence Value & Sense of Place; Fertilizer & Pesticide Use; Impervious Surfaces; Landscape Conservation & Restoration; Landscaping & Household Services; Landuse Management; Non-point Source Controls; Non-point Source Runoff; Nutrients; Sediment; Shelter; Supplemental Feeding; Toxics; Waterborne Discharges |
Landuse Management: Mine Reclamation | Lands disturbed by mining must be reclaimed to their Approximate Original Contour (AOC). Mine operators must backfill, compact, and grade in order to restore the AOC of the land with all highwalls, spoil piles, and depressions eliminated. Spoil material is prone to erosion, and may carry various disturbed toxics into groundwater if not properly managed. Temporary roads and impervious surfaces may have also been constructed for mining purposes. | Natural Resources Conservation Service. 2011. National Handbook of Conservation Practices. U.S. Department of Agriculture. Office of Surface Mining Reclamation and Enforcement. POSTMINING LAND USE: Exceptions to Approximate Original Contour Requirements for Mountaintop Removal Operations and steep Slope Mining Operations. Washington, DC. |
Chemical Use Regulations; Civil Engineering & Construction; Coal Mining; Construction Codes & Projects; Decision Support; Deforestation & Devegetation; Discharge Limitations; Discharges; Ditching & Soil Disturbance; Ecosystem Monitoring & Restoration; Environmental Monitoring & Restoration; Environmental Monitoring, Mapping, & Scientific Research; Food & Raw Materials; Hydrologic Management; Impervious Surfaces; Infrastructural Policies; Land-Based Civil Engineering; Landscape Changes; Landscape Conservation & Restoration; Landuse Management; Manufacturing & Trade; Manufacturing & Trade Policies; Mineral, Rock, & Metal Mining; Mining; Mining Policies; Mitigation; Non-point Source Controls; Non-point Source Runoff; Physical & Chemical Water Quality Criteria; Political Pressure; Remediation; Resource Use Management; Sediment; Surface & Groundwater Flow; Toxics; Valuation; Waterborne Discharges |
Landuse Management: Temporary Road Planning and Construction | This management option involves minimizing sediment discharges from forestry and other temporary roads through their planning and construction. Since these roads are seasonal or temporary, less time and effort is normally invested in construction. Road construction has four main phases, clearing, leveling, construction and surfacing. Construction timing should be targeted to avoid sensitive spawning periods and during low stream flow at water passes. Road surface drainage shaping requires proper moisture content, surfacing, and grading. Drainage should be installed to reduce the volume and velocity of runoff water passing over sensitive areas. Methods for road surface drainage include: broad-based dip construction, pole culverts, ditch relief culverts, road outsloping and grading, ditch and turnout construction. Roadway runoff should be prevented from flowing directly into watercourses by using turnouts, wing ditches and dips. Brush barriers, silt fences, riprap and filter strips can be used to trap sediment in runoff water. Where roads cross streams it is important to guard against erosion, as such erosion may necessitate road repairs. | Environmental Protection Agency Office of Water. 1993. Guidance Specifying Management Measures For Sources Of Nonpoint Pollution In Coastal Waters. EPA/840/B-92/002, US EPA, Washington, DC. |
Agriculture, Aquaculture, & Forestry Policies; Civil Engineering & Construction; Construction Codes & Projects; Decision Support; Deforestation & Devegetation; Discharge Limitations; Discharges; Ecosystem Monitoring & Restoration; Environmental Monitoring & Restoration; Food & Raw Materials; Forestry; Hydrologic Management; Impervious Surfaces; Infrastructural Policies; Infrastructure; Land & Air Transportation; Land-Based Civil Engineering; Landscape Changes; Landscape Conservation & Restoration; Landuse Management; Mining; Mining Policies; Non-point Source Controls; Non-point Source Runoff; Nutrients; Road Construction & Maintenance; Sediment; Transportation; Transportation Policies |
Marine Zoning: Wildlife Management Areas (WMAs) | Wildlife Management Areas include bird nesting, resting, or feeding areas, turtle nesting beaches, and other sensitive habitats including shallow flats that are important feeding areas for fish. These areas seek to provide protection for endangered/threatened species or their habitats while at the same time providing opportunity for public use. Wildlife Management Areas are achieved through placing and maintaining buoys along zone boundaries; implementing management responsibilities; adjusting existing zone boundaries if needed; evaluating allowable activities within the boundaries and make changes if needed; identifying potential areas that need additional zoning; monitoring the effectiveness of current zones; and revising GIS and NOAA charts. | NOAA Marine Sanctuary Program. 2007. Florida Keys National Marine Sanctuary revised management plan. National Ocean Service, Key West, FL. |
Accidental & Illegal Harvest; Beaches & Nature Parks; Biological Harvest; Biological Monitoring & Restoration; Boating Activities; Coastal Defense; Contact Uses; Cultural Services; Decision Support; Designate Protected Species; Designated Uses; Ecosystem Monitoring & Restoration; Entertainment & Accommodation Services; Environmental Monitoring & Restoration; Fisheries & Hunting Policies; Fishing & Harvesting Management; Fishing Sector; Landscape Conservation & Restoration; Marine Birds; Marine Protected Areas; Permitting & Zoning; Physical Damage; Recreational Fishing; Recreational Opportunities; Resource Use Management; Sea Turtles; Tourism & Recreation; Trampling; Water Transportation; Wetlands |
Marine Zoning: Special Use Areas | Special use areas are set aside for specific scientific or educational purposes. This is in order to encourage the recovery or restoration of injured or degraded resources. Also, the areas may be designated to facilitate access to, or use of, resources, and prevent other user conflicts. Special-use areas are 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; and determining/establishing appropriate zones for high-impact or user-conflict activities. | NOAA Marine Sanctuary Program. 2007. Florida Keys National Marine Sanctuary revised management plan. National Ocean Service, Key West, FL. |
Biological Addition; Biological Harvest; Biological Monitoring & Restoration; Biological Monitoring, Mapping, & Scientific Research; Biomedical Research Policies; Complex Habitat & Resources; Contact Uses; Cultural Services; Decision Support; Designated Uses; Ecosystem Monitoring & Restoration; Education & Information; Educational & Research Opportunities; Environmental Education & Outreach; Environmental Monitoring & Restoration; Environmental Monitoring, Mapping, & Scientific Research; Health Policies; Marine Protected Areas; Permitting & Zoning; Physical Damage; Provisioning Services; Resource Use Management; Scientific Research; Social Organizations; Special Use Permitting; Supporting Services; Wetland & Reef Restoration |
Monitor & Research: Adaptive Management | By definition, adaptive management is a structured management approach that links science to decision-making, thereby improving the probability of restoration success. It provides an efficient process to address risk and uncertainty inherent within ecosystem restoration by encouraging flexible plans and designs. Monitoring (#) is an important component of adaptive management. The affect of different restoration alternatives can be seen using monitoring data, and compared against other environmental variables to determine what the best future actions are based on results of previous projects. | CERP Committee. 2006. Comprehensive Everglades Restoration Plan Adaptive Management Strategy. |
Artificial Habitat; Biological Addition; Biological Monitoring & Restoration; Biological Monitoring, Mapping, & Scientific Research; Chemical Variables; Decision Support; Ecosystem Monitoring & Restoration; Educational & Research Opportunities; Environmental Monitoring & Restoration; Environmental Monitoring, Mapping, & Scientific Research; Landscape Changes; Landscape Conservation & Restoration; Landuse Management; Physical Variables; Public Administration; Regulating Services; Remediation; Scientific Research; Supporting Services |
Resource Use Management: Prevent Introduction of Invasive Species | Preventing the introduction of invasive species involves public awareness of the invasive species, minimizing modes and prone areas for invasion, and detecting small populations for early eradication. Some common modes of terrestrial transportation include livestock and domestic animals, mowing equipment, and firewood. Clean equipment before transport to a new location. Remove soil from plants, and plant bare-root. Use high grade seed and weed free livestock feeds. Reduce opportunities for invasive plants by keeping native plant populations strong and healthy and seeding in cover crops to reduce barren soil. | Agriculture, Aquaculture, & Forestry Policies; Aquarium & Pet Trade; Ballast Discharge; Biological Addition; Construction Codes & Projects; Discharge Limitations; Environmental Education & Outreach; Escape & Release of Non-natives; Invasive Species; Landscape Conservation & Restoration; Landscaping & Household Services; Manufacturing & Trade; Transportation; Water Transportation | |
Restoration: Land Reclamation Integrating Landslide Treatments | This management option is exercised to prevent down slope movement of earthen materials, including natural soils, and spoil/waste from mining or forestry activities. Extreme caution and planning must be exercised before permitting any personnel, equipment or other machinery into the slide area. An experienced engineer should analyze the stability of the site both before and after alterations are made to evaluate stability. Water Control: sources of water that enter the area can be controlled to keep the material dry, as it is typically more stable when dry. Loading Control: where appropriate, consider removing excess material from upper portions of the slide area to reduce slide mass. Slope Reduction: where practice, use grading to reduce the slope of the slide area. Increasing Internal Strength: consider the impact of removing and recompacting of material at designed levels of moisture and with biotechnical slope stabilization practices. External Restraints: external restraints can be used where slope movements must be limited due to surrounding valued improvements (e.g. structures), where manipulation of the material may not achieve desired improvements. External restraints must be designed to prevent overturning, sliding at or below the base, and bearing failure of the foundation. Vegetative Treatment: deep rooted grasses and shrubs with proven performance in soil bioengineering applications can be planted using selected soil bioengineering or biotechnical slope stabilization techniques appropriate to the site. Transpiration and infiltration should be considered when choosing vegetation. | Natural Resources Conservation Service. 2011. National Handbook of Conservation Practices. U.S. Department of Agriculture. |
Agriculture, Aquaculture, & Forestry Policies; Construction Codes & Projects; Discharges; Ditching & Soil Disturbance; Forestry; Infrastructure; Insurance; Landscape Conservation & Restoration; Mining; Mining Policies; Non-point Source Runoff; Sediment |
Restoration: Beach Renourishment and Nourishment | Beaches are subject to natural accretion and erosion. Tourism is often best supported by wide, accessible, public sandy beaches. Beaches can be restored to counteract natural erosion by transporting large quantities of sand onto the beach. This sand often comes from nearby dredging. Caution should be used when restoring long sections of beaches, as often the area above the mean high tide line is littoral, or privately owned, and restoration of these beaches can impact these property rights, see "Stop the Beach Renourishment, Inc. v. Florida Department of Environmental Protection (2010) U.S. Supreme Court decision." Beach protection or nourishment offers an alternative to this often expensive and abrupt type of renourishment, nourishment involves practices which encourage coastal accretion and discourage erosional forces. See "Florida's Beach and Shore Preservation Act" for some restrictions on this. | NOAA Coastal Services Center. Beach Nourishment: A Guide for Local Government Officials. Coastal Services Center Accessed 6/17/2011. |
Beach & Land Formation; Beaches & Nature Parks; Culture; Dredging, Draining, & Filling; Environmental Monitoring & Restoration; Landscape Conservation & Restoration; Recreational Opportunities; Shoreline Armoring; Shoreline Protection; Sunscreen Use; Tourism & Recreation |
Restoration: Beach Vegatation Restoration | Natural beaches are often host to important costal dune ecosystems. Due to tourism, much of the vegetation that comprises these dune ecosystems may be compromised. The natural vegetation provides an important ecosystem service, with roots providing deep stabilization against physical damage and removal of that sand. Without such vegetation sand and dunes can be completely washed away during hurricanes and other surge events. The dunes themselves offer some protection to nearby inland infrastructure during these same storm events. When the beach past the dunes is for public access it is beneficial to build raised walk-overs over the dune vegetation. This prevents trampling, which leads to dune blowouts. | Natural Resources Conservation Service, editor. 2007. Native Plants for Coastal Dune Restoration: What, When, and How for Florida. US Department of Agriculture. |
Beaches & Nature Parks; Biological Monitoring & Restoration; Culture; Deforestation & Devegetation; Ditching & Soil Disturbance; Ecosystem Monitoring & Restoration; Invasive Species; Landscape Changes; Landscape Conservation & Restoration; Landuse Management; Physical Damage; Regulating Services; Storms & Hurricanes; Tourism & Recreation; Trampling |
Stormwater BMPs: Biological Stormwater Filtration | This method attempts to reduce the negative impacts of stormwater runoff through implementing engineering techniques that allow natural processes and plants to act as filters. Such techniques would include using grass parking and turf covered swales. Many of these techniques, such as reversed elevations for planted areas in parking lots, can demonstrate benefits both as natural filters and for the vegetation that are used since it eliminates the need to water them with irrigation systems. | NOAA Marine Sanctuary Program. 2007. Florida Keys National Marine Sanctuary revised management plan. National Ocean Service, Key West, FL. Natural Resources Conservation Service. 2011. National Handbook of Conservation Practices. U.S. Department of Agriculture. Natural Resources Conservation Service. Basic Biofiltration Swale. Urban BMP's - Water Runoff Management Accessed 3/23/2011. Natural Resources Conservation Service. Bioretention System. Urban BMP's - Water Runoff Management Accessed 3/23/2011. Natural Resources Conservation Service. Constructed Wetland. Urban BMP's - Water Runoff Management Accessed 3/23/2011. Natural Resources Conservation Service. Filter Strips. Urban BMP's - Water Runoff Management Accessed 3/23/2011. Natural Resources Conservation Service. Reversed Elevations System for Parking Lots and Planting Areas. Urban BMP's - Water Runoff Management Accessed 3/23/2011. Natural Resources Conservation Service. Riparian Forest Buffer. Urban BMP's - Water Runoff Management Accessed 3/23/2011. Natural Resources Conservation Service. Roadway Landscape Treatment System. Urban BMP's - Water Runoff Management Accessed 3/23/2011. Natural Resources Conservation Service. Wet Biofiltration Swale. Urban BMP's - Water Runoff Management Accessed 3/23/2011. Natural Resources Conservation Service. Wet Pond Design. Urban BMP's - Water Runoff Management Accessed 3/23/2011. Natural Resources Conservation Service. Wet Swale. Urban BMP's - Water Runoff Management Accessed 3/23/2011. Water Environment Research Foundation, American Society of Civil Engineers, U.S. Environmental Protection Agency, Federal Highway Administration, American Public Works Association, editor. 2008. Overview of Performance by BMP Category and Common Pollutant Type. International Stormwater Best Management Practices (BMP) Database [1999-2008]. Leisenring, M., Clary, J., Stephenson, J., and Hobson, P. 2010. International Stormwater Best Management Practices (BMP) Database Pollutant Category Summary: Nutrients. Geosyntec Consultants, Inc. |
Applied Chemicals; Building & Home Construction; Chemical Variables; City Planning; Civil Engineering & Construction; Climate; Construction Codes & Projects; Deforestation & Devegetation; Discharge Limitations; Discharges; Ditching & Soil Disturbance; Fertilizer & Pesticide Use; Golf Course Operations; Impervious Surfaces; Infrastructure; Irrigation; Land-Based Civil Engineering; Landscape Changes; Landscape Conservation & Restoration; Landscaping & Household Services; Landuse Management; Non-point Source Controls; Non-point Source Runoff; Nutrient & Contaminant Processing; Physical Variables; Point & Mobile Source Controls; Point Source Discharges; Primary Production; Road Construction & Maintenance; Sediment; Storms & Hurricanes; Stormwater Management; Substrate; Supporting Services; Surface & Groundwater Flow; Toxics; Utilities; Waste Management; Waste Management Policies; Wastewater Discharge; Water; Waterborne Discharges |
Stormwater BMPs: Biological Stormwater Retention/Detention | This method attempts to reduce the negative impacts of stormwater runoff through implementation of natural structures that retain runoff water for further treatment or controlled release. These structures are typically characterized as retention ponds and incorporate natural vegetation such as grass. These ponds may be dry, or may drain into nearby wetlands. | Natural Resources Conservation Service. 2011. National Handbook of Conservation Practices. U.S. Department of Agriculture. Natural Resources Conservation Service. Dry Extended Detention Ponds. Urban BMP's - Water Runoff Management Accessed 3/23/2011. Poresky, A., Clary, J., Strecker, E., and Earles, A. 2011. International Stormwater Best Management Practices (BMP) Database. Technical Summary: Volume Reduction. Geosyntec Consultants. |
Applied Chemicals; Chemical Variables; City Planning; Civil Engineering & Construction; Discharge Limitations; Discharges; Hydrologic Management; Infrastructural Policies; Irrigation; Land-Based Civil Engineering; Landscape Changes; Landscape Conservation & Restoration; Landuse Management; Non-point Source Controls; Non-point Source Runoff; Nutrient & Contaminant Processing; Physical Variables; Point & Mobile Source Controls; Point Source Discharges; Primary Production; Sediment; Storms & Hurricanes; Stormwater Management; Substrate; Supporting Services; Surface & Groundwater Flow; Toxics; Utilities; Utility Policies; Waste Management; Waste Management Policies; Wastewater Discharge; Water; Waterborne Discharges |
Stormwater BMPs: Structural Stormwater Filtration | This method attempts to reduce the negative impacts of stormwater runoff through implementation of engineering structures that trap or filter impurities out of runoff water. These include but are not limited to, using swales, filter strips, oil/water separators, oil/grit separators, and sand filters. Often structural retrofitting is coupled with biological filters/controls to direct water as desired and to fully reap the benefits of both systems. Structural filters are often incorporated into retention/detention and infiltration systems as well. One disadvantage of structural filters is that they are often higher maintenance as sand and chambers fill and clog with pollutants over time. | NOAA Marine Sanctuary Program. 2007. Florida Keys National Marine Sanctuary revised management plan. National Ocean Service, Key West, FL. Natural Resources Conservation Service. Compost Filter System. Urban BMP's - Water Runoff Management Accessed 3/23/2011. Natural Resources Conservation Service. Dry Swale. Urban BMP's - Water Runoff Management Accessed 3/23/2011. Natural Resources Conservation Service. Median Strip Infiltration Trench. Urban BMP's - Water Runoff Management Accessed 3/23/2011. Natural Resources Conservation Service. Montgomery County Water Quality Inlet. Urban BMP's - Water Runoff Management Accessed 3/23/2011. Natural Resources Conservation Service. Off-Line Infiltration Basin. Urban BMP's - Water Runoff Management Accessed 3/23/2011. Natural Resources Conservation Service. Oil/Water Separators. Urban BMP's - Water Runoff Management Accessed 3/23/2011. Natural Resources Conservation Service. Organic Sand Filter. Urban BMP's - Water Runoff Management Accessed 3/23/2011. Natural Resources Conservation Service. Peat Sand Filter. Urban BMP's - Water Runoff Management Accessed 3/23/2011. Natural Resources Conservation Service. Perimeter Sand Filter. Urban BMP's - Water Runoff Management Accessed 3/23/2011. Natural Resources Conservation Service. Pocket Sand Filter. Urban BMP's - Water Runoff Management Accessed 3/23/2011. Natural Resources Conservation Service. Rockville Water Quality Inlet. Urban BMP's - Water Runoff Management Accessed 3/23/2011. Natural Resources Conservation Service. Sediment Basin (Water Quality Enhancement). Urban BMP's - Water Runoff Management Accessed 3/23/2011. Natural Resources Conservation Service. Side-by-Side Infiltration Basin. Urban BMP's - Water Runoff Management Accessed 3/23/2011. Natural Resources Conservation Service. Surface Sand Filter. Urban BMP's - Water Runoff Management Accessed 3/23/2011. Natural Resources Conservation Service. Underground Sand Filter. Urban BMP's - Water Runoff Management Accessed 3/23/2011. Natural Resources Conservation Service. Underground Trench with Oil/Grit Chamber. Urban BMP's - Water Runoff Management Accessed 3/23/2011. Natural Resources Conservation Service. Under-the-Swale Infiltration Trench. Urban BMP's - Water Runoff Management Accessed 3/23/2011. Natural Resources Conservation Service. Water Quality Volume (WQV) Storage Tank. Urban BMP's - Water Runoff Management Accessed 3/23/2011. Water Environment Research Foundation, American Society of Civil Engineers, U.S. Environmental Protection Agency, Federal Highway Administration, American Public Works Association, editor. 2008. Overview of Performance by BMP Category and Common Pollutant Type. International Stormwater Best Management Practices (BMP) Database [1999-2008]. Leisenring, M., Clary, J., Stephenson, J., and Hobson, P. 2010. International Stormwater Best Management Practices (BMP) Database Pollutant Category Summary: Nutrients. Geosyntec Consultants, Inc. US EPA. EPA Filtration BMPs. National Pollutant Discharge Elimination System Menu of BMPs Accessed 3/25/2011. US EPA. Manufactured Products for Stormwater Inlets. National Pollutant Discharge Elimination System Menu of BMPs Accessed 3/25/2011. US EPA. Alum Injection. National Pollutant Discharge Elimination System Menu of BMPs Accessed 3/25/2011. Natural Resources Conservation Service. 2010. Stormwater Runoff Controls. U.S. Depatrment of Agriculture. Natural Resources Conservation Service. 2005. Solid/liquid Waste Separation Facility. U.S. Depatrment of Agriculture. |
Applied Chemicals; Chemical Variables; City Planning; Civil Engineering & Construction; Coastal Engineering; Construction Codes & Projects; Dam Construction & Maintenance; Discharge Limitations; Discharges; Ditching & Soil Disturbance; Food & Energy Policies; Hydrologic Management; Impervious Surfaces; Improved Technology; Infrastructural Policies; Infrastructure; Land-Based Civil Engineering; Landscape Changes; Landscape Conservation & Restoration; Landuse Management; Non-point Source Controls; Non-point Source Runoff; Physical Variables; Point & Mobile Source Controls; Point Source Discharges; Road Construction & Maintenance; Sediment; Storms & Hurricanes; Stormwater Management; Surface & Groundwater Flow; Toxics; Utilities; Utility Policies; Waste Management; Waste Management Policies; Wastewater Discharge; Waterborne Discharges |
Stormwater BMPs: Stormwater Pollution Reduction Through Instituting Preventitive Best Management Practices | This method focuses on reducing the amount of harmful contaminants in stormwater runoff by establishing Best Management Practices that prevent the generation of the pollutant to begin with. These BMPs include educational programs, infrastructure improvements and agricultural BMPs. Examples of educational programs would be programs that educate the public on the importance of, and how to avoid depositing hazardous wastes, such as oil, into storm drains, or how to use landscape management controls to limit the chemical and debris that from enter stormwater runoff from their personal lawns. Infrastructure improvement could include the use of alternative turnarounds and street cleaning. Agricultural practices such as roofs and covers for pesticides and equipment, or use of bedding are both preventative stormwater practices. Some additional specific practices include: controlling fertilizer application, properly using and disposing of fertilizers, pesticides, motor oil, and other harmful chemicals, debris removal, exposure reduction, minimization of pollutants, parking lot cleaning, stormwater catch basin insert, eliminate curbs and gutters, green parking, green roofs, street design and patterns, bedding. | NOAA Marine Sanctuary Program. 2007. Florida Keys National Marine Sanctuary revised management plan. National Ocean Service, Key West, FL. Natural Resources Conservation Service. 2011. National Handbook of Conservation Practices. U.S. Department of Agriculture. US EPA. Alternative Turnarounds. National Pollutant Discharge Elimination System Menu of BMPs Accessed 3/25/2011. US EPA. Eliminate Curbs and Gutters. National Pollutant Discharge Elimination System Menu of BMPs Accessed 3/25/2011. US EPA. Green Parking. National Pollutant Discharge Elimination System Menu of BMPs Accessed 3/25/2011. US EPA. Green Roofs. National Pollutant Discharge Elimination System Menu of BMPs Accessed 3/25/2011. US EPA. Street Design and Patterns. National Pollutant Discharge Elimination System Menu of BMPs Accessed 3/25/2011. Natural Resources Conservation Service. Urban BMP's - Water Runoff Management. Urban BMP's - Water Runoff Management Accessed 3/25/2011. Irrigation Association. 2010. Turf and Landscape Irrigation Best Management Practices. |
Agriculture; Applied Chemicals; Chemical Use Regulations; Chemical Variables; City Planning; Construction Codes & Projects; Discharge Limitations; Discharges; Environmental Education & Outreach; Food & Energy Policies; Food & Raw Materials; Forestry; Housing; Hydrologic Management; Infrastructural Policies; Infrastructure; Land-Based Civil Engineering; Landscape Changes; Landscape Conservation & Restoration; Landscaping & Household Services; Landuse Management; Mining; Nutrient & Contaminant Processing; Nutrients; Oil & Gas Industry; Road Construction & Maintenance; Security & Public Administration Policies; Shelter; Solid Waste Disposal; Storms & Hurricanes; Stormwater Management; Supporting Services; Toxics; Utilities; Waste Management; Waste Management Policies; Waterborne Discharges |
Water Quality Management: Treating Effluent Water Through Wetlands | Additional treatment of sewage is often a necessary management option because secondary treatment alone leaves 20,000 times more nutrients in the water than the safe limit for corals. High concentrations of nutrients in the water leads to eutrophication, and coral reefs are more sensitive to nutrient enrichment than any other coastal system. Wetlands are extremely successful at reducing nitrogen levels in water. Using natural wetlands or "living machines" to perform this task can actually be more cost effective than further sewage treatment. Each successive wetland treatment cell of the series can provide incredible levels of denitrification, and thus protect corals from nutrient enrichment. | Center for Watershed Protection. 2008. Guanica Bay watershed management plan. Natural Resources Conservation Service. 2011. National Handbook of Conservation Practices. U.S. Department of Agriculture. Natural Resources Conservation Service. 2003. Waste Treatment Lagoon. CODE 359. U.S. Depatrment of Agriculture. |
Building & Home Construction; Chemical Variables; City Planning; Civil Engineering & Construction; Coastal Development; Coastal Engineering; Deforestation & Devegetation; Discharge Limitations; Discharges; Ditching & Soil Disturbance; Infrastructural Policies; Infrastructure; Land-Based Civil Engineering; Landscape Changes; Landscape Conservation & Restoration; Landuse Management; Mangroves; Nutrient & Contaminant Processing; Nutrients; Physical Variables; Point & Mobile Source Controls; Point Source Discharges; Primary Production; Security & Public Administration Policies; Sewage Treatment; Supporting Services; Surface & Groundwater Flow; Toxics; Utilities; Utility Policies; Waste Management; Waste Management Policies; Wastewater Discharge; Waterborne Discharges; Wetlands |
Waterway Management: Lagoon Restoration | Many times lagoons/wetlands are filled for urban development, agricultural development, etc. Lagoons/wetlands are a sink for nutrients, sediment, and contaminants. Wetlands close to reef watersheds can be huge contributors to reef health. This is because wetlands intercept surface-water runoff from higher, drier land and retain excess nutrients and pollutants. Also, lagoons are beneficial because they provide habitat for an array of wildlife. Overall, they can greatly reduce the amount nutrient-contaminated water that reaches corals. | Center for Watershed Protection. 2008. Guanica Bay watershed management plan. Natural Resources Conservation Service. 2011. National Handbook of Conservation Practices. U.S. Department of Agriculture. Natural Resources Conservation Service. 2008. Chapter 13, Part 650. Wetland Restoration, Enhancement or Creation. Engineering Field Handbook. U.S. Depatrment of Agriculture. |
Agriculture, Aquaculture, & Forestry Policies; Biological Monitoring & Restoration; Civil Engineering & Construction; Coastal Development; Coastal Engineering; Complex Habitat & Resources; Ecosystem Monitoring & Restoration; Infrastructural Policies; Landscape Changes; Landscape Conservation & Restoration; Landuse Management; Nutrient & Contaminant Processing; Reef Habitat; Reef Inhabitants; Reef Life; Supporting Services; Wetland & Reef Restoration; Wetlands |
Waterway Management: Remove Previous Canal and Irrigation Infrastructure | Canal and irrigation infrastructure typically includes concrete structures to control the flow of water. These low head dams, bulkheads, concrete footers, and other structures act as constricting forces in channels. This constriction leads to debris becoming lodged and thus changing the erosive forces. In turn, banks become destabilized. Channel erosion then increases along with bed scour and sediment transport. Removing these structures and making banks more gradual has the added benefit of allowing for riparian vegetation to be planted, which acts as a natural buffer. | Center for Watershed Protection. 2008. Guanica Bay watershed management plan. |
Agriculture; Agriculture, Aquaculture, & Forestry Policies; Boat Movement; Boating Activities; City Planning; Civil Engineering & Construction; Coastal Engineering; Construction Codes & Projects; Dam Construction & Maintenance; Deforestation & Devegetation; Discharge Limitations; Discharges; Ditching & Soil Disturbance; Ecosystem Monitoring & Restoration; Environmental Monitoring & Restoration; Food & Raw Materials; Hydrologic Management; Impervious Surfaces; Infrastructural Policies; Irrigation; Land-Based Civil Engineering; Landscape Changes; Landscape Conservation & Restoration; Landuse Management; Non-point Source Controls; Physical Damage; Sediment; Shoreline Protection; Small Boats; Substrate; Surface & Groundwater Flow; Transportation; Water; Water Resources; Water Transportation; Waterborne Discharges |
Waterway Management: Stream Bank Riparian Plantings | Planting native vegetation and trees in riparian zones helps to reduce erosion within channels. Such vegetation helps anchor the soil and sediment in place. Planting in riparian zones goes in hand with Remove Previous Canal and Irrigation Infrastructure (#274). This management option can be exercised in streams, canals used for boat passage, stormwater drainage ditches, or in agricultural irrigation channels. | Center for Watershed Protection. 2008. Guanica Bay watershed management plan. Natural Resources Conservation Service. 2011. National Handbook of Conservation Practices. U.S. Department of Agriculture. |
Agriculture; Agriculture, Aquaculture, & Forestry Policies; Boat Movement; Boating Activities; Carbon Storage & Cycling; City Planning; Civil Engineering & Construction; Coastal Development; Construction Codes & Projects; Deforestation & Devegetation; Discharge Limitations; Discharges; Ditching & Soil Disturbance; Ecosystem Monitoring & Restoration; Food & Energy Policies; Forestry; Hydrologic Management; Infrastructural Policies; Infrastructure; Irrigation; Landscape Changes; Landscape Conservation & Restoration; Landuse Management; Nutrient & Contaminant Processing; Primary Production; Provisioning Services; Sediment; Stormwater Management; Supporting Services; Surface & Groundwater Flow; Transportation; Utilities; Water; Water Resources; Water Transportation; Waterborne Discharges |
Laws
Legal Citation | Purpose of Law | Management Organization | Database Topics |
---|---|---|---|
American Antiquities Act of 1906, 16 United States Code §§ 431-433. | The Act provides penalties for unauthorized collection, excavation, or destruction of historic or prehistoric ruins, monuments, or objects of antiquity on lands owned or controlled by the United States. It authorized that areas of extrodinary geographical, historical , aesthetic value can be designated national monuments. Application to Coral Reefs:Has been used by Presidential Proclamation in 2001 to expand or create two national monuments; the Virgin Islands Coral Reef Monument and the Buck Island Reef National Monument. The monuments include coral reefs. Legislative Actions: Comments: |
National Park Service Jurisdiction: United States |
City Planning; Coastal Development; Coastal Engineering; Construction Codes & Projects; Coral; Docks & Marinas; Landscape Conservation & Restoration; Marine Protected Areas; Oil & Gas Research & Exploration; Ports & Harbors; Resource Use Management |
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 |
Chapter 3: Trees and vegetation next to waterways, 12 Virgin Islands Code. | Establishes buffer zone for protecting natural watercourses from vegetation clearing. The buffer zone either 30 feet from the center of the natural watercourse, or 25 feet from its edge, whichever is greater. Application to Coral Reefs:Assists in erosion control and can protect reefs from harmful sedimentation, if the stream or river sediment is capable of reaching the coral reef. Vegetation along river and stream banks will remove nutrients and assist in preventing eutrophocation of waters that can reach coral reefs. Legislative Actions:Enforcement is by conservation officers with assistance from local police when required. Penalties are fines of not more than $100, or 180 days in jail, or both Comments:Permits can be obtained if the purpose of clearing is for development. |
US Virgin Islands, Department of Planning and Natural Resources, Division of Environmental Protection Jurisdiction: US Virgin Islands |
Building & Home Construction; Coastal Development; Construction Codes & Projects; Ditching & Soil Disturbance; Dredging Regulations; Dredging, Draining, & Filling; Existence Value & Sense of Place; Landscape Conservation & Restoration; Landscaping & Household Services; Landuse Management; Resource Use Management; Shoreline Protection; Wetlands |
Coastal Zone Management Act of 1972, as amended through 2004,. | A voluntary national program to encourage coastal states to develop and implement coastal zone management plans and requires that "any federal activity within or outside of the coastal zone that affects any land or water use or natural resource of the coastal zone" shall be "consistent to the maximum extent practicable with the enforceable policies" of a state's coastal zone management plan. The law includes an Enhancement Grants program for protecting, restoring, or enhancing existing coastal wetlands or creating new coastal wetlands. It also establishes the National Estuarine Research Reserve System, guidelines for estuarine research, and financial assistance for land acquisition. Application to Coral Reefs:Protection of coastal areas can have an indirect influence on coral reef preservation and conservation by the use of environmentally sound construction and development by limiting runoff of contaminants and sediment that could have an adverse effect on inshore coral reefs if present. Legislative Actions:The 1985 amendments (PL 99-272) established the National Estuarine Reserve Research System a State-Federal process for designating national reserves and guidelines for estuarine research.The 1990 amendments (PL 101-508) established new Enhancement Grants for eight specific areas, including protecting, restoring or enhancing existing coastal wetlands or creating new coastal wetlands and assessing the cumulative effects of coastal development on coastal wetlands and fishery resource. Also, the 1990 statute established a new Coastal Nonpoint Source Pollution Control Program. The 1998 and 2004 (PL 105-383 and PL 108-456) established a program for the prevention and control of harmful algal blooms and hypoxia, and included authorization for a representative of the Department of Interior to assess the economic and ecological impacts of algal blooms and hypoxia. Comments:If implemented, the programs for economic, ecological and control of harmful algal blooms and hypoxia would be useful for coral reef issues. |
National Oceanic and Atmospheric Administration/US Fish and Wildlife Service Jurisdiction: United States |
Building & Home Construction; City Planning; Civil Engineering & Construction; Coastal Development; Construction Codes & Projects; Docks & Marinas; Economic Markets & Policies; Infrastructural Policies; Mangroves; Permitting & Zoning; Ports & Harbors; Seagrasses; Shoreline Armoring; Surface & Groundwater Flow |
Environmental Resource Permitting, 62-330 Florida Administrative Code Annotated (2005). | Under the Chapter, DEP exercises its independent authority under Part IV, Chapter 373, F.S., to regulate surface water management systems, including activities in, on or over wetlands or other surface waters. The term "surface water management system" or "system" include stormwater mangement systems, dams, impoundments, reservoirs, appurtenant works, or works, or any combination thereof, and includes dredging and filling. "Dredging" means excavation, by any means, in surface waters or wetlands Application to Coral Reefs:Regulating stormwater management systems, dams, reservoirs and dredging will contribute to controlling contaminates from entering estuarine and marine environments and protect ecosystems including coral reefs., Legislative Actions:Individual permits will contain the conditions for environmental protection. Comments: |
Florida Department of Environmental Protection Jurisdiction: State Coastal Waters; Designated Marine Areas |
City Planning; Construction Codes & Projects; Dam Construction & Maintenance; Docks & Marinas; Dredging Regulations; Dredging, Draining, & Filling; Mangroves; Nutrient & Contaminant Processing; Pipelines; Ports & Harbors; Resource Use Management; Road Construction & Maintenance; Sediment; Surface & Groundwater Flow; Utility Line Construction & Maintenance; Wastewater Discharge |
Florida Aquatic Preserves, 18-20 Florida Administrative Code. | 18-20.001 Intent.
(1) All sovereignty lands within a preserve shall be managed primarily for the maintenance of essentially natural conditions, the propagation of fish and wildlife, and public recreation, including hunting and fishing where deemed appropriate by the Board, and the managing agency.
(2) Aquatic preserves which are described in Part II of Chapter 258, Florida Statutes, were established for the purpose of being preserved in an essentially natural or existing condition so that their aesthetic, biological and scientific values may endure for the enjoyment of future generations.
(3) The preserves shall be administered and managed in accordance with the following goals: (a) To preserve, protect, and enhance these exceptional areas of sovereignty submerged lands by reasonable regulation of
human activity within the preserves through the development and implementation of a comprehensive management program; (b) To protect and enhance the waters of the preserves 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 preserves; (d) To use applicable federal, state, and local management programs, which are compatible with the intent and provisions of the act and these rules, and to assist in managing the preserves; (e) To encourage the protection, enhancement or restoration of the biological, aesthetic, or scientific values of the preserves, including but not limited to the modification of existing manmade conditions toward their natural condition, and discourage
activities which would degrade the aesthetic, biological, or scientific values, or the quality, or utility of a preserve, when reviewing applications, or when developing and implementing management plans for the preserves; (f) To preserve, promote, and utilize indigenous life forms and habitats, including but not limited to: sponges, soft coral, hard corals, submerged grasses, mangroves, salt water marshes, fresh water marshes, mud flats, estuarine, aquatic, and marine reptiles, game and non-game fish species, estuarine, aquatic and marine invertebrates, estuarine, aquatic and marine mammals, birds, shellfish and mollusks; (g) To acquire additional title interests in lands wherever such acquisitions would serve to protect or enhance the biological,
aesthetic, or scientific values of the preserves; (h) To maintain those beneficial hydrologic and biologic functions, the benefits of which accrue to the public at large. (4) Nothing in these rules shall serve to eliminate or alter the requirements or authority of other governmental agencies, including counties and municipalities, to protect or enhance the preserves provided that such requirements or authority are not inconsistent with the act and this chapter. Application to Coral Reefs:By maintaining coastal aquatic preserves in their natural condition, mangrove forests, wetlands and submerged aquatic vegetation will perform the functions of being sediment traps and removing some contaminants such as nutrients. Therefore, they will not reach marine ecosystems including coral reefs. Legislative Actions: Comments:Aquatic preserves which are described in Part II of Chapter 258, Florida Statutes, were established for the purpose of being preserved in an essentially natural or existing condition so that their aesthetic, biological and scientific values may endure for the enjoyment of future generations. All sovereignty lands within a preserve shall be managed primarily for the maintenance of essentially natural conditions, the propagation of fish and wildlife, and public recreation, including hunting and fishing where deemed appropriate by the Board, and the managing agency. |
Florida State Department of Environmental Protection Jurisdiction: State Coastal Waters |
Building & Home Construction; Coastal Development; Docks & Marinas; Dredging, Draining, & Filling; Educational & Research Opportunities; Environmental Education & Outreach; Existence Value & Sense of Place; Landuse Management; Mangroves; Marine Birds; Ports & Harbors; Recreational Opportunities; Resource Use Management; Seagrasses; Waste Management Policies |
General permit for activities seaward of the coastal construction control line, 62B-34 Florida Administrative Code Annotated (2010). | To implement the provisions of Section 161.053(19) F. S. providing General Permits for activities performed seaward of the Coastal Construction Control line. Persons wishing to use one or more of the General Permits as set forth in Part II of this rule chapter shall be subject to the notice provisions of subsection 62B-34.030(4) F. A. C. before any activity is conducted as authorized herein.The general conditions provided pursuant to Section 62-B34-0.50, F. A. C. , shall apply to all of the General Permits issued under this rule chapter. Strict compliance with all of the terms, conditions, requirements, limitations, and restrictions applicable to a desired General Permit under this rule chapter is required to qualify for such a permit. Application to Coral Reefs:The rule requires erosion control BMP. Therefore, sediment from construction will not enter the marine environment and damage coral reefs. Legislative Actions:Civil fines are applicable for work done that was not authorized in the permit. Comments: |
Florida Departrment of Environmental Protection Jurisdiction: State Coastal Waters |
Beaches & Nature Parks; Coastal Defense; Coastal Development; Coastal Engineering; Complex Habitat & Resources; Construction Codes & Projects; Docks & Marinas; Dredging, Draining, & Filling; Landscape Conservation & Restoration; Landuse Management; Mangroves; Ports & Harbors; Resource Use Management; Seagrasses; Sediment; Shoreline Armoring |
Land and Water Conservation Fund Act of 1965, 16 United States Code § 4601. | Provides funding through receipts from the sale of surplus federal land, appropriations from oil and gas receipts from the outer continental shelf, and other sources of land acquisition. Appropriations from the fund may be used for matching grants to states for outdoor recreation projects and for land acquisition by various federal agencies, including the Fish and Wildlife Service. Application to Coral Reefs:Protection of wetlands benefits coral reefs through nutrient removal and the control of sedimentation so that they do not enter near shore waters. Legislative Actions:The legislation was amended in 1986 by the Emergency Wetlands Resources Act and required the States to identify the agencies and organizations involved in wetland management, evaluate existing and proposed wetlands protection mechanisms, assess wetlands resources, identify wetlands loss and degradation factors, and establish priorities for protection. Comments: |
National Park Service Jurisdiction: United States |
Educational & Research Opportunities; Environmental Monitoring, Mapping, & Scientific Research; Existence Value & Sense of Place; Funding & Donations; Landuse Management; Public Administration; Recreational Opportunities; Resource Use Management |
Mitigation Banking, 62-342 Florida Administrative Code. | (1) The Department recognizes that, in certain instances, adverse impacts of activities regulated under Part IV of Chapter 373, F.S., can be offset through the utilization of mitigation credits from a permitted Mitigation Bank. This rule provides criteria for this mitigation alternative to complement existing mitigation criteria and requirements. This chapter is supplemental to and does not supersede any other criteria and requirements in rules promulgated under Part IV of Chapter 373, F.S.
(2) The Department intends that Mitigation Banks be used to minimize mitigation uncertainty associated with traditional mitigation practices and provide greater assurance of mitigation success. It is anticipated that the consolidation of multiple mitigation projects into larger contiguous areas will provide greater assurance that the mitigation will yield long-term, sustainable, regional ecological benefits. Mitigation Banks shall be consistent with Department endorsed watershed management objectives and emphasize restoration and enhancement of degraded ecosystems and the preservation of uplands and wetlands as intact ecosystems rather than alteration of landscapes to create wetlands. This is best accomplished through restoration of ecological communities that were historically present. The establishment and use of Mitigation Banks in or adjacent to areas of national, state, or regional ecological significance is encouraged, provided the area in which the Mitigation Bank is proposed to be located is determined appropriate for a Mitigation Bank and the Mitigation Bank meets all applicable permitting criteria.
(3) Nothing in this chapter shall affect the mitigation requirements set forth in any Mitigation Bank agreement or any permit issued under Chapter 84-79, Laws of Florida, or Part IV of Chapter 373, F.S., prior to February 2, 1994. If a permittee wishes to substantially modify a Mitigation Bank previously established by agreement or permit, the permittee must comply with this chapter. Additionally, some Mitigation Banks may be subject to the version of this section existing prior to July 1, 1996, under subsections 373.4136(9) and (10), F.S., and will not be affected by amendments adopted after that date. This chapter does not prohibit an applicant from proposing project-specific, pre-construction on-site or off-site mitigation, without establishing a Mitigation Bank. Application to Coral Reefs:Mitigation banking in coastal wetlands, as presented in the Chapter, can provide large areas of functioning wetlands. The wetlands can function as sediment and nutrient traps keeping sediment and nutrients from entering coastal waters and damaging marine ecosystems including coral reefs. Legislative Actions: Comments:Establishes the regulations and permitting requirements for mitigation banks. |
Florida State Department of Environmental Protection Jurisdiction: US State Waters |
Biological Monitoring & Restoration; Building & Home Construction; Coastal Development; Construction Codes & Projects; Docks & Marinas; Educational & Research Opportunities; Nutrient & Contaminant Processing; Ports & Harbors; Shoreline Armoring; Waste Management Policies |
National Environmental Policy Act of 1969, 42 United States Code §§ 4321-4377. | Requires analysis, public comment, and reporting for environmental impacts of federal actions. It stipulates the factors to be considered in environmental impact statements, and requires that federal agencies employ an interdisciplinary approach in related decision-making and develop means to ensure unqualified environmental values are given appropriate consideration, along with economic and technical considerations. Application to Coral Reefs:Requires an Environmental Assessment(EA), and potentially an Environmental Impact Statement (EIS) if the project review finds there will be a significant impact. The EIS must detail the environmental impacts of the proposed action, unavoidable adverse environmental impacts, and alternatives to the proposed action. The resulting studies could protect sensitive environmental ecosystems, including coral reefs. Legislative Actions:The Act potentially could protect coral reefs if the proposed federal project could have a significant impact on the reef. Comments:The Act is completely procedural; it does not include specific regulations. The Council on Environmental Quality (CEQ) was created by the Act. CEQ is part of the Executive Office of the President and one of the CEQ directives is to ensure that federal programs comply with NEPA. The puprose of the EIS is to disclose to the public and resource managers the probable long- and short-term impacts of the proposed project as well as consideration of less environmentally damaging alternatives to the recommended course of action. |
Federal agencies Jurisdiction: United States |
Agriculture, Aquaculture, & Forestry Policies; Biocriteria; Biological Monitoring, Mapping, & Scientific Research; Boating Regulations; Construction Codes & Projects; Decision Support; Designated Uses; Economic Markets & Policies; Energy Policy & Development; Environmental Monitoring, Mapping, & Scientific Research; Fishing & Harvesting Management; Landuse Management; Marine Debris; Microorganisms; Non-point Source Controls; Permitting & Zoning; Physical & Chemical Environment; Physical Variables; Point & Mobile Source Controls; Political Pressure; Public Administration; Reef Habitat; Reef Inhabitants; Reef Life; Remediation; Resource Use Management; Sectors Filling Human Needs; Security; Socio-Economic Drivers; Transportation Policies; Waste Management Policies; Wetlands |
Surface waters of the State, Florida Administrative Code Annotated §§ Chapter 62-301 (1996). | It is the intent of this Chapter to define the landward externt of surface waters of the state. Te findings, declarations, and intentfor this Chapter are the same as those for Chapter 62-302 F. A. C. Application to Coral Reefs:By defining the landward extent of surface waters of the State using dominant plant species, the guidance in the Chapter will include wetlands and transitional zones on many occasions. Through the protection of these areas, filtration of sediment and nutrients will be maintained and two of the harmful parameters for coral reefs will be reduced. Legislative Actions:The Chapter is a guidance document and does not contain penalties. The Chapter provides a list of plant species for use with the guidance as well as the methods of calculating the areas of state waters. Comments: |
Florida Department of Environmental Protection Jurisdiction: State Coastal Waters; US State Waters; Designated Marine Areas |
Arthropods; Ballast Discharge; Beaches & Nature Parks; Biotechnology Research & Development; Building & Home Construction; Coastal Development; Docks & Marinas; Dredging Regulations; Dredging, Draining, & Filling; Finfish & Shellfish Stock; Fish; Fishing & Harvesting Management; Forestry; Invertebrates; Landscape Conservation & Restoration; Landuse Management; Mangroves; Marine Birds; Marine Vertebrates; Molluscs; Non-point Source Runoff; Nutrient & Contaminant Processing; Petroleum Spills; Pipelines; Ports & Harbors; Recreational Fishing; Resource Use Management; Sea Turtles; Seagrasses; Sediment; Shoreline Armoring; Small Boats; Surface & Groundwater Flow; Utility Line Construction & Maintenance; Wastewater Discharge; Wetlands; Whales & Dolphins |
The DPNR states that wetlands in the Virgin Islands are covered by the Clean water Act and the Endangered and Indigenous Species Act of 1990 (Title 12, Chapter 2, US Virgin Island Code,. | To protect wetlands and wetland species from degradation, loss as a result of dredging and filling. Application to Coral Reefs:Protection of wetlands assists in controlling sedimentation and nutrient runoff from terrstrial locations, thus protecting coral reefs that are influenced by terrestrial sources. Legislative Actions: Comments:The wetlands portion of the USVI Division of Environmental Protection website was under construction at the time of this atlas preparation. However, it appears that DEP works with the USACE and USEPA on matters related to wetlands. |
US Virgin Islands, Department of Planning and Natural Resources, Division of Environmental Protection Jurisdiction: US Virgin Islands |
Building & Home Construction; Coastal Development; Coastal Engineering; Construction Codes & Projects; Dredging Regulations; Dredging, Draining, & Filling; Educational & Research Opportunities; Existence Value & Sense of Place; Mangroves; Nutrient & Contaminant Processing; Recreational Opportunities; Resource Use Management; Seagrasses; Shoreline Armoring; Wetlands |
Uniform Mitigation Assessment Method, Florida Administrative Code Annotated §§ Chapter 62-345 (2005). | Establishes a methodology that provides a standard procedure for assessing the functions provided by wetlands and other surface waters, the amount that those functions are reduced by a proposed impact, and the amount of mitigation necessary to offset that loss. Application to Coral Reefs:Protecting wetlands provides wetland areas that can act as buffers against nutrients, pollutants and contaminants from reaching habitats including coral reefs. Legislative Actions:The Chapter is administrative and provides methods to assess wetland value and appropriate mitigation to offset impact. Comments: |
Florida Department of Environmental Protection Jurisdiction: State Coastal Waters |
Agriculture, Aquaculture, & Forestry Policies; Building & Home Construction; Civil Engineering & Construction; Coastal Development; Coastal Engineering; Complex Habitat & Resources; Construction Codes & Projects; Dam Construction & Maintenance; Docks & Marinas; Dredging Regulations; Dredging, Draining, & Filling; Finfish & Shellfish Stock; Forestry; Land-Based Civil Engineering; Landuse Management; Mangroves; Nutrient & Contaminant Processing; Oil & Gas Research & Exploration; Pipelines; Ports & Harbors; Recreational Opportunities; Resource Use Management; Road Construction & Maintenance; Seagrasses; Sediment; Shoreline Armoring; Surface & Groundwater Flow; Utility Line Construction & Maintenance; Wetlands |