Loading...
HomeMy Public PortalAbout150_021_buffer guidebook Prgfcct ' , L� B crj. • Ci&LthI , / • //4--,_ , , , 0", , j. Includes Model Coastal RiparianBuffer Ordinance Prepared by: UGA River Basin Center UGA School of Law, Land Use Clinic Contributing authors: •,111,%,, + Iii s3L��0 w ., : River Basin Center: .` Emily Franzen , • , • • Seth Wenger .�_ 1,.. 1;: ' • �! f. Laurie Fowler � Land Use Clinic: - ' ., _ { to- ,�. 'a Trent Myers Sandra Glaze . .r • December, 2006 4 �,. rI'I'V'erCENTER ;11 )( 1S1r) '' e � . university of georgic ,• -I . -A institute of ecology . - t•,., . , i Protecting Riparian Buffers in C Georgia : Management Options Includes Model Coastal RiparianBuffer Ordinance Prepared by: UGA River Basin Center UGA School of Law, Land Use Clinic Contributing authors: River Basin Center: Emily Franzen Seth Wenger Laurie Fowler Land Use Clinic: Trent Myers Sandra Glaze Cover photograph: Sandra Glaze December, 2006 iiiiir N'p'"°''' UEPi.UE NANAAL Vf GP Fq�c90 ^` NESUURCES F1veLNTE. (cRAA-) g a FIA ,� ° S snt/UN�SoF gH)hrENrofco`" Department of Natural Resources GEORGIA Coastal Management Program Protecting Riparian Buffers in Coastal Georgia: Management Options Table of Contents Executive Summary 1 I. Introduction 3 A. Why protect Georgia's coastal marshlands? 3 B. What are the threats to our marshlands? 3 C. What is a coastal riparian buffer? 4 D. Why coastal riparian buffers? 4 II. Functions of Coastal Riparian Buffers 6 A. Erosion and Sediment Control 6 B. Nitrogen and Phosphorus 6 C. Other Contaminants 8 D. Habitat Protection 8 E. Private Property Protection: Scenic Viewsheds 9 F. Private Property Protection: Flood and Drought Prevention 9 III. Tools to Protect Coastal Riparian Buffers in Georgia 10 A. Coastal Riparian Buffer Ordinance 10 B. Land Acquisition 11 C. Conservation Easements and Purchase of Development Rights 12 D. Transferable Development Rights 14 E. Clustering and Conservation Subdivisions 15 IV. Buffers and Private Property Rights 16 A. Federal Takings Law 16 B. Georgia Takings Law 17 V. Economic Considerations 20 A. The Costs 20 B. The Benefits 20 VI. Conclusion 23 VII. References 24 Appendix A: Model Coastal Riparian Buffer Ordinance for Georgia's Local Governments 28 Executive Summary There are many policy tools available to help local governments preserve coastal riparian buffers. A straightforward option is a coastal riparian buffer Scientists have long realized the important benefits ordinance, which is a local regulation to limit that tidally influenced areas, including estuaries, tidal development activities within buffers. Although creeks, and marshlands provide to communities. several model riparian buffer ordinances have been Tidal creeks and their adjacent marshes are extremely developed for Georgia's local governments, these important nursery areas for fisheries, "providing food current models were crafted for freshwater ecosystems and habitat to numerous species of fish and shellfish, and do not take into account the unique resources including commercially important species" (Mallin and issues of Georgia's coastal communities. and Lewitus 2004). However, in recent years, Therefore, a new model riparian buffer ordinance has Georgia's coast has come under increasing pressure been developed to meet the specific needs of local from development, resulting in an increase in non- governments along Georgia's coast (see Appendix point source pollution to the marshes. A). Preserving naturally vegetated buffers along Perhaps the biggest impediment to the adoption Georgia's marshlands and other surface water of riparian buffer ordinances is concern for private resources is an ecologically and cost effective tool ri hts. It is essential to draft the ordinance for protecting this valuable and fragile ecosystem. property g Coastal riparian buffers perform a wide range in a way that fully respects the rights of property of ecological functions and services having owners. Buffers protected by a riparian buffer high economic and social value. Studies have ordinance remain in the ownership of the property demonstrated that non-point source pollution to owner. This is in contrast to greenways, which are coastal marshes can be significantly reduced through generally publicly owned.A buffer ordinance should the preservation of coastal riparian buffers. The never mandate public access to private property, nor buffers act as filters, removing pollutants such as should it restrict activities on a property to such an sediment, nutrients, contaminants, and pesticides extent that the owner cannot make use of it. These before they enter waterways (South Carolina conditions would be grounds for a "takings" lawsuit. Department of Health and Environment 2002a). If a local government cannot provide adequate buffer Coastal vegetative buffer zones also provide: protection along a stream segment without infringing on property rights, then the government must either • Aquatic and terrestrial wildlife habitat, acquire the parcels in question (or conservation including nursery grounds for fish and habitat easements on those parcels) or try to offset the lack for shellfish of protection with controls (whether regulatory or • Floodwater storage voluntary) somewhere else in the stream basin. • Recreational opportunities There are also various non-regulatory options such as • Scenic and aesthetic benefits land acquisition,conservation easements,purchase of • Preservation of historical and cultural development rights, transferable development rights, resources and clustering that can be used to preserve riparian Reduced property damage from floods, high buffers. Governmental acquisition may be the best • tides and storm surges mechanism for protecting key pieces of riparian land, although acquisition is usually reserved for special • Increased property values cases because of the costs, particularly in coastal • Reduced maintenance costs compared to turf areas where land values are high. There are numerous grass sources of funds available to local governments that Protection of coastal fishing, recreation and can be applied toward riparian land acquisition. • tourism industries. Conservation easements are another option to protect environmentally sensitive areas such as riparian lands. Protecting Riparian Buffers in Coastal Georgia: Management Options 1 In a conservation easement, the landowner agrees unused development rights from owners of"sending to give up development, timber harvesting, or other areas." Once these rights are sold, the "sending area" similar rights in order to protect the riparian lands for may not be developed in the future and these parcels conservation use. The landowner retains such basic are protected by a conservation easement or similar property rights as the right to exclude,the right to sell legal tool. This transferability not only provides and the right to use the property in a manner that does compensation to landowners who forego development not impair the conservation value of the easement. opportunities,but it also provides the local government Local governments, charitable organizations and with the opportunity to focus growth where it is most private individuals may purchase or receive the appropriate. While TDR programs are used for a easement as a gift. It is then the responsibility of variety of purposes, several coastal communities in the easement holder to ensure that the easement has the United States use TDRs to protect their coastal not been violated and to pursue any necessary legal resources and wetlands. recourse for its enforcement. Landowners who donate a conservation easement or a parcel of land in fee Clustering is similar to a TDR program, except that simple may be eligible for preferential tax treatment clustering involves density transfers within a single at the federal and State levels. parcel of land. For example, a landowner with a 100- acre parcel,with a restriction of one unit per 20 acres, Another tool for preserving riparian areas and might want to concentrate all 5 units within a 5 acre protecting surface water resources is a transferable area to preserve the other 95 acres. By concentrating development rights (TDR) program. With a TDR denser development away from riparian lands,density program, a community can identify riparian lands transfers may help to protect stream buffers and coastal it would like to preserve as "sending areas." Other features. A common ways of implementing density areas where the community prefers to concentrate transfers is through a clustering or conservation growth and development are designated as"receiving subdivision ordinance. areas." Owners of "receiving areas" may purchase 2 Protecting Riparian Buffers in Coastal Georgia: Management Options Introduction wetlands protection when the Georgia legislature took action to protect the State's salt marshes by enacting the Coastal Marshlands Protection Act, O.C.G.A. § A recent study commissioned by the Coastal Georgia 12-5-280 et seq.Today,this statute remains one of the Regional Development Center and conducted by most protective tidal wetlands laws in the nation. The Georgia Tech projected that by 2030, over 840,000 preamble reads as follows: people will live in the 10-county area that makes up the Georgia Coast (Center for Quality Growth and The coastal marshlands of Georgia Regional Development 2006). This is a 50 percent comprise a vital natural resource system. increase in population from the roughly 558,000 people The estuarine area of Georgia is the living there in 2000. Already, this region has seen a habitat of many species of marine life and large population increase in recent years, with 17.5 wildlife that cannot survive without the food percent growth between 1990 and 2000 (Center for supplied by the marshlands. The estuarine Quality Growth and Regional Development 2006). marshlands of coastal Georgia are among Population growth at such a high rate adds pressure the richest providers of nutrients in the to fragile coastal ecosystems that are critical to the world. Such marshlands provide a nursery maintenance of the commercial and recreational for commercially and recreationally valued seafood industries, the coastal tourism industry and species of shellfish and other wildlife, overall quality of life on the Georgia Coast. provide an important buffer against flooding and erosion,and help control and disseminate A. Why protect Georgia's coastal pollutants. The coastal marshlands provide a natural recreation resource which has marshlands? become vitally linked to the economy of Georgia's coastal zone and to that of the Scientists have long realized the important entire state. benefits that tidally influenced areas, including estuaries, tidal creeks, and marshlands provide This coastal marshlands resource system to communities. Tidal creeks and their adjacent is costly, if not impossible, to reconstruct marshes are extremely important nursery areas or rehabilitate once adversely affected for fisheries and habitat for shellfish, including by man. It is important to conserve this commercially and recreationally important species system for the present and future use and (Mallin and Lewitus 2004). enjoyment of all citizens and visitors to our state.Activities and structures in the coastal In addition, these areas have value because of their marshlands must be regulated to ensure aesthetic beauty which attracts tourism and new that the values and functions of the coastal residents. The National Association of Regional marshlands are not impaired and to fulfill Councils estimates that tourism provides two billion the responsibilities of each generation as dollars annually to the coastal economy in Georgia. public trustees of the coastal marshlands for According to the Coastal Resources Division (CRD) succeeding generations. of the Georgia Department of Natural Resources (DNR),recreational game fishing in the State's coastal waters contributes about $363 million annually and B. What are the threats to our the commercial fishing industry adds over$22 million marshlands? annually to Georgia's coastal economy (Georgia Department of Natural Resources). In order to protect coastal ecosystems and the coastal Ahead of major federal environmental legislation economy that depends upon them, communities such as the Clean Water Act, in 1970 the State of along Georgia's coast must begin to deal with the Georgia established itself as a national leader in tidal environmental impacts associated with its increasing Protecting Riparian Buffers in Coastal Georgia: Management Options 3 population. Increased levels of development add the Marshland Protection Act and the Shoreline large amounts of impervious cover, such as parking Protection Act also give State regulatory agencies lots, rooftops, and roadways, and semi-pervious power to establish coastal riparian buffers through cover, such as lawns and compacted, unpaved the permitting and review process (Desbonnet driveways, to the landscape. These surfaces generate 1994). Because the effectiveness of NPS pollution increased levels of stormwater runoff which delivers minimization and removal measures are dependent numerous types of pollutants—such as oil,biological upon factors like slope, soil type,vegetation and type contaminants and excess nutrients—to marshes and of land use, regulating authorities believe that local creeks. A study conducted in tidal creeks in South government action will be the most successful way to Carolina found that creeks draining areas with higher address NPS pollution problems, and they encourage percentages of impervious cover were measurably local communities to adopt solutions, including impaired physically, chemically, and biologically riparian buffers, specifically tailored to the particular when compared with creeks draining undeveloped community's needs (NOAA 2001). areas (Holland et al. 2004). C. What is a coastal riparian buffer? Pollution like stormwater runoff that that does not emanate from a discrete source is called non-point A riparian buffer is a strip of land along a stream, source (NPS) pollution . Other sources of NPS river, lake or marsh consisting of either undisturbed pollution in coastal waters include agriculture and vegetation in its original natural state or undisturbed forestry practices, faulty septic systems, and leaking vegetation that has been restored to a state that sewer pipes. According to the U.S. Environmental closely mimics its original, natural state. The Protection Agency (U.S. EPA), a significant portion Georgia Erosion and Sedimentation Act defines a of the threats to coastal waters is now caused by buffer as the "area of land immediately adjacent NPS pollution (U.S. EPA 1996). Tidal creeks and to the banks of State waters in its natural state of estuarine systems are particularly sensitive to NPS vegetation, which facilitates the protection of water pollution, which can cause significant damage to the quality and aquatic habitat." In the coastal context, freshwater and marine organisms associated with riparian buffers have been defined as "corridors of these ecosystems, including commercially important ...vegetation along rivers, streams, and tidal wetlands species (Schiff et al. 2002; Lee 2005; Mallin 2006). that protect waterways by providing a transition zone Therefore, as resident populations in Georgia's between upland development and adjoining surface coastal communities grow and development along waters" (South Carolina Department of Health and our shorelines increases, control of NPS pollution Environment 2002a). For more information regarding becomes critical. An evaluation of the Georgia the types of vegetation that should be present in the Coastal Management Program in 2001 by the National buffer and how to best restore and maintain coastal Oceanic and Atmospheric Administration (NOAA) riparian buffers on your land and in your community, recommended that Georgia communities and officials please refer to the Georgia Coastal Riparian Buffer develop appropriate responses to water quality, land Guidebook, prepared by the River Basin Center for use and population growth in coastal areas and should the Georgia Environmental Protection Division. consider the use of buffers (NOAA 2001). Georgia legislators have already used buffers to D. Why coastal riparian buffers? address erosion and sedimentation problems to protect Georgia's waters and meet federal water quality Coastal riparian buffers perform a wide range of standards. The Georgia Erosion and Sedimentation ecological functions and provide services having Act of 1975 requires a minimum 25-foot riparian high economic and social value. Scientific research buffer along all State waters as a best management increasingly shows that riparian buffers play a crucial practice (BMP) to minimize and prevent erosion role in protecting our waters from the effects of NPS ollution by acting as filters and removing pollutants and the associated sedimentation problems. Both p 4 Protecting Riparian Buffers in Coastal Georgia: Management Options before they enter our waterways (South Carolina • Increased property values Department of Health and Environment 2002a). • Reduced maintenance costs compared to turf Coastal vegetative buffer zones also provide: grass • Aquatic and terrestrial wildlife habitat, • Protection of coastal fishing, recreation and including nursery grounds for fish and habitat tourism industries. for shellfish As a result,coastal riparian buffers are a"conservation • Floodwater storage bargain"because they provide so many functions and services to communities in a relatively small area. It • Recreational opportunities must be noted, however, that a riparian buffer is the • Scenic and aesthetic benefits last line of defense between our surface waters and • Preservation of historical and cultural nonpoint source pollutants. In order to protect water resources quality adequately, a buffer ordinance should be accompanied by an effective stormwater management • Reduced property damage from floods, high program. tides and storm surges Protecting Riparian Buffers in Coastal Georgia: Management Options 5 . Fu n ct i o n s of Coastal sta I Riparian and the erosion and sedimentation associated with those activities away from waterways and marshes. Buffers Buffers also slow the speed of stormwater runoff before it enters a waterway and stabilize stream banks, Provided here is a brief summary of riparian buffer thereby reducing scouring and channel erosion. functions, with emphasis on results of research regarding buffers in the coastal plain and tidally Studies have yielded a range of recommendations influenced ecosystems of the Southeast. A wide for buffer widths in order to perform the function variety of articles and reports were reviewed in order of erosion and sedimentation control. As a rule of to provide information about specific buffer functions thumb,the wider the buffer,the greater the amount of and,when available,the buffer widths and other buffer sediment removal (Wenger 1999; Young et al 1980; characteristics necessary to achieve those functions. Peterjohn and Correll 1984;Magette et al 1987, 1989; Dillaha et al 1988, 1989). To provide for long term A. Erosion and Sediment Control trapping of sediments, studies suggest that buffers likely must be in the range of 100 ft (Wenger and Sediment is the most significant pollutant in many Fowler 2000). A 1994 literature review developed streams and rivers. Sedimentation may originate from relationships between buffer width and percent a range of sources, including residential, commercial, removal of sediment and other pollutants (Desbonnet and industrial construction sites, construction of et al). Results showed that a 50%removal efficiency stream crossings for utilities and roads, for sediment should be achieved in the first 2 m but stream channel erosion (which increases with high that 90%removal requires a buffer width of 90 m.(See storm flows associated with Table 1). A 1997 study evaluating buffer effectiveness urbanization), agriculture and forestry, and historical in the inner coastal plain and tidal ecosystems of the land uses that left "legacy sediment" in streams and Chesapeake Bay Watershed found that, in the inner rivers (Wenger and Freeman 2006). coastal plain ecosystem, when the drainage area to buffer area ratio was 2:1, the buffer retained 96% of Excess amounts of sediment can have numerous sediment(Lowrance et al 1997). deleterious effects on water quality and stream biota: • Sediment in municipal water is harmful to B. Nitrogen and Phosphorus humans and to industrial processes. Excessive amounts of two nutrients - nitrogen and • Sediment deposited on stream beds reduces phosphorus - act as pollutants in aquatic systems, habitat for fish and for the invertebrates that with excessive amounts of nitrogen generally being many fish consume. a more gp dama g�in pollutant in marine and estuarine • Suspended sediment reduces light transmittance, systems and phosphorus being more damaging in decreasing algal production. freshwater systems(Guadagnoli 2005). Nitrogen and • High concentrations of fine suspended sediments phosphorus can lead to many changes in the ecology cause direct mortality for many fish. of aquatic systems. Both nutrients contribute to eutrophication, the process of"over-fertilization" of • Suspended sediments reduce the abundance of a water body due to an increase in nutrient loading. filter-feeding organisms, including mollusks Eutrophication often leads to algal blooms and low and some arthropods. oxygen levels in marine and estuarine systems,both of • Sedimentation reduces the capacity and the which have been documented in East Coast estuaries useful life of reservoirs. in recent years and have been linked to massive fish Riparian buffers that are naturally vegetated act as kills and releases of toxins that are poisonous to filters to remove sediment from surface runoff. They humans (Burkholder et al. 1997). Nonpoint sources also serve to keep development and grading activities of phosphorous and nitrogen include agricultural 6 Protecting Riparian Buffers in Coastal Georgia: Management Options and residential fertilizers, septic drain fields, leaking (Lowrance et al. 1997).Nitrate removal is also higher sewer pipes and animal wastes from concentrated in areas with poorly draining soils, such as clay/loam. animal feeding operations. Wetlands are particularly important for performing Nitrogen is readily removed from stormwater when the function of nitrate removal, as they contain a high filtered through a vegetated buffer because it is water table and poorly draining soils (Desbonnet et usually dissolved in the water column. Again, the al. 1994). wider the buffer, the more nitrogen removal function it will provide, but Desbonnet et al. (1994) report a Unlike nitrogen, phosphorus is almost always 50%removal efficiency for nitrogen at a buffer width undissolved and attached to sediments (Karr and of 3.5m and a 90% efficiency at 150m (See Table 1). Schlosser 1977,Peterjohn and Correll 1984, Osborne and Kovacic 1993) or organic matter (Wenger 1999) Nitrogen ispresentin stormwaterinnumerous inorganic when present in stormwater. As a result,buffer widths and organic forms. Two common forms include that are sufficient to remove sediments should also nitrate (NO3), which is toxic to humans and animals be sufficient to trap and remove phosphorus (Wenger at high concentrations (> 10mg/L), and ammonium 1999).Phosphorus is removed from the buffer mostly (NH4), which is toxic to many aquatic organisms. by uptake of the riparian vegetation. When the Ammonium is readily taken up by vegetation in vegetation dies, the nutrients are eventually returned the buffer, but buffers remove nitrate from runoff to the soil and then to the water through the process through a process performed by microorganisms of decomposition. known as denitrification. When nitrogen is present in stormwater in the form of nitrate, Desbonnet et The Desbonnet et al. (1994) study reports a 50% al. (1994) reports that riparian buffers are much less phosphorus removal efficiency at a buffer width of efficient at removing the nutrient, giving a removal 5 m and a 90% removal rate at 150 m. (See Table 1). efficiency of 50% at a buffer width of greater than Other studies have found that in the short term(before 100m. However,other studies have found that a much vegetation dies and the phosphorus is reintroduced narrower buffer efficiently removes most nitrate from into the system), buffers of 8 m and 16 m in width the water column (Fennesy and Cronk 1997; Gilliam trapped 66% and 95% of phosphorus, respectively 1994;Lowrance et al. 1997),and one study reports that (Vought et al 1994), and buffers of 20 m and 28 m a buffer width of 20m-30m removes nearly 100% of trapped 67% and 81% of phosphorus, respectively nitrate (Fennesy and Cronk 1997). The efficiency of (Mander et al 1997). Finally, studies have found that the buffer for removing nitrate depends largely upon grassy areas are more efficient than forested areas the way in which the water passes through the buffer. for nutrient removal. However, these studies also This, in turn, depends upon the water table depth and found that buffer effectiveness declined over time, soil type. If the water table is high so that the flow is presumably because vegetation was not harvested to shallow and comes into contact with the root zone of prevent reintroduction of the nutrients into the system the riparian vegetation,nitrate removal will be higher (Dillaha et al 1988 and 1989,Magette 1987 and 1989). Table 1. Buffer widths required to attain different removal efficiencies for pollutants(Adapted from Table 5,Desbonnet et al.(1990). Removal Sediment TSS Nitrogen Nitrate Phosphorus (%) Buffer width required to achieve removal (m) 50 0.5 2 3.5 >100 5 60 2 6 9 12 70 7 20 23 35 80 25 60 60 85 90 90 200 150 250 99 300 700 350 550 Protecting Riparian Buffers in Coastal Georgia: Management Options 7 For grassy buffer areas, studies found that the wider resources by displacing pesticide application away the buffer, the lower the concentration of phosphorus from the water body. In one study of Coastal Plain in runoff(Dillaha et al 1989,Magette 1987 and 1989; streams, unexpectedly low pesticide levels were Desbonnet 1994). found in streams located in agricultural watersheds in which pesticides were regularly applied, which C. Other Contaminants was hypothesized to be due to the presence of intact forested floodplains and wetlands (Frick et al. 1998). Along with sediment and excess nutrients, the other Buffers are effective at filtering and/or trapping main types of pollutants found in NPS pollution pesticides (Frick et al. 1998; Hatfield et al 1995; include pesticides, heavy metals, and biological Arora et al 1996; Lowrance et al 1997) and heavy contaminants and pathogens found in human and metals(Herson-Jones et al 1995;Groffman et al 1991) animal waste. Disease producing pathogens found in before than can enter a water body. Many pesticides human and animal wastes can cause illnesses when are broken down in the soil, and heavy metals bind to people come in contact with polluted water or eat soil particles, becoming trapped in the buffer rather contaminated fish and shellfish. Pathogens can also than in aquatic sediments. harm other aquatic organisms directly through disease or indirectly by using up all available oxygen in the As with other types of pollutants,the wider the buffer water column, which kills fish and other organisms. is, the greater its ability to protect water resources Just as they trap sediment and nutrients in their from these chemicals. Wider buffers provide more vegetation,riparian buffers can trap human and animal residence time for chemicals to break down and more wastes transported in surface runoff. Several studies sites for metals to bind to soil particles. A 1993 review have shown that concentrations of fecal coliform (an of studies on the use of buffers to reduce pesticide indicator of organic pollution) in surface runoff were contamination of water in the Southeast reported that reduced when the water was filtered through grass regular use of buffer strips kept pesticide residue buffer strips (Coyne et al 1995; Karr and Schlosser concentrations within water quality standards. The 1977). report found that the high concentrations of pesticide in the water occurred when no buffer was present or Pesticides are regularly applied to residential lawns when pesticides were applied within the buffer and and row crop agriculture and, in the Southeast, are concluded that buffers 15 m in width were effective to used increasingly in forestry practices (Neary et al minimize pesticide contamination in streams (Neary 1993). Heavy metals are a by-product of industrial et al. 1993). Other studies suggest much wider buffers activities in most cases and are usually found in may be required(Lowrance et al. 1997). the highest concentrations in urbanized watersheds (Crawford and Lenat 1989). Toxins in pesticides may D. Habitat Protection have immediate lethal effects on aquatic organisms if present in a water body in large amounts. At smaller Coastal buffer zones provide habitat for native plant, doses, these toxins may also have various harmful animal and aquatic species (Rhode Island Program effects on organisms (Cooper 1993). Toxic pollutants 1994). Vegetation provides shade and cover from such as pesticides and heavy metals can also become predators, as well as nesting and feeding habitat for trapped in aquatic sediments and persist for hundreds resident and migratory species. For example, buffers of years. When this occurs, they become virtually along the marsh-upland shoreline protect roosting impossible to remove from the system. Activities and foraging sites for colonial waterbirds. Wildlife such as boating, dredging or construction that disturb diversity is linked to a buffer's size; wider buffers contaminated sediments can then release these toxic support a greater variety and number of species. substances into the water column and cause harm to Furthermore,buffers that possess vegetation native to aquatic organisms and humans. the area provide more valuable habitat for sustaining resident species. A continuous buffer is of particular Buffers play an important role in protecting aquatic value in protecting amphibians,waterfowl,and coastal 8 Protecting Riparian Buffers in Coastal Georgia: Management Options fish spawning and nursery areas (South Carolina and visual resources along the coast and preserve the Department of Health and Environment 2002b). natural character of the shoreline,mitigating the visual impacts of coastal development. For aesthetic appeal, Since small tidal creeks are critically important a mix of native vegetation provides visual diversity. spawning andnursery areas for commerciallyimportant Utilization of native plants is also economical since aquatic species, wider buffers are recommended the costs of design and engineering are avoided. for small tidal creeks as well as bigger freshwater streams (South Carolina Department of Health and F. Private Property Protection: Flood Environment 2002b). For general-purpose buffers intended to provide some value as wildlife habitat, a and Drought Prevention minimum width of fifteen meters (about fifty feet) is suggested (Desbonnet et al.1994). Vegetated buffers Coastal buffer zones provide a natural transition of this width generally provide some water quality zone between the open coast, marshes, and upland protection for most waterways (approximately sixty development (Rhode Island Program 1994). In percent pollutant removal), offer minimal wildlife coastal areas, riparian buffers have been shown to habitat value,protect visual and aesthetic appeal, and reduce flooding by slowing surface water runoff can provide a natural physical barrier between public and spreading it over a wider area and by allowing and private properties (Desbonnet et al.1994). more water to percolate into the water table (Rhode Island Program 1994; South Carolina Department of Health and Environment 2002b). A 1998 Georgia E. Private Property Protection: coastal plain study reported that in 1994 and 1997, Scenic Views h ed s flooding was limited by largely intact natural riparian areas (Michener et al. 1998). Buffers also have been Of primary concern to many coastal area planners, found to mitigate property destruction by maintaining managers, and citizens is the preservation and undeveloped land along waterways and locating protection of the coastal region's visual diversity and development away from floodwaters, storm surges unique character. Coastal buffers protect the scenic and extreme high tides (Desbonnet et al. 1994). Protecting Riparian Buffers in Coastal Georgia: Management Options 9 Ill. Tools to Protect Coastal application of the 50-foot buffer rule recently adopted under the CMPA. In addition, the model ordinance Riparian Buffers is an excellent tool for managing activities in the in Georgia buffer after a marshlands permit has been granted. The model ordinance and the companion riparian buffer guidance manual specifically cover activities A. Coastal Riparian Buffer such as preservation and enhancement of vegetation, Ordinance use of native plants, limitations on use of pesticides and fertilizers, and creation of view corridors. These On February 28, 2007, the Georgia DNR Board activities are not addressed by the rules for the 50- adopted a new rule pursuant to the Coastal Marshlands foot buffer under the CMPA. Protection Act that provides for a 50-foot buffer adjacent to coastal marshlands. This new buffer In July 2007, the DNR Board will adopt additional requirement applies only to projects that require a rules for granting exceptions to the CMPA's 50-foot permit under the Coastal Marshlands Protection Act buffer. While the contents of the exceptions process (CMPA). Under the rules, permitted projects have are yet to be finalized,the draft document would grant two parts, a marshland component and an upland an exception if all of the following three conditions component. The marshland component includes any are met: parts of the project located in, on,or over an estuarine area. It also includes activities that "remove, fill, 1. Application of the marshlands buffer requirement dredge, drain, or otherwise alter any marshlands." will create a substantial hardship on the applicant; Examples include marinas, bulkheads, community and docks, boat ramps, public recreational docks, and 2. The purpose, function, and treatment capabilities piers. The upland component of a project includes of the marshlands buffer can be, or have been, the "service areas, amenities, and recreational achieved by alternative means such that the area" located inland of the coastal marshlands "that stormwater discharge to coastal marshlands from serve or augment the functioning of the marshlands the marshland buffer is managed according to component of the project."Examples listed in the rule the policy, criteria, and information, including include dry stack boat storage,dockmaster shops,fuel technical specifications and standards, found storage,and delivery facilities and restrooms intended in latest edition of the Georgia Stormwater to serve the marshlands component of the project. Management Manual as amended to address coastal specific issues, and is protective of water The 50-foot buffer requirement does not apply quality; and to projects or activities that are exempt under the 3. Consistent with the purpose and reasonable use CMPA. The buffer also does not apply to projects of the proposed project, the smallest practicable that do not require a permit under the CMPA, such encroachment into the marshlands buffer is as most single, private-use recreational docks or any utilized. development project that does not alter the marsh or include placement of a structure over the marsh. Although several model riparian buffer ordinances The rule does not generally extend to or apply to have been developed for Georgia's local residential development associated with a proposed governments, these current models were crafted with community dock or marina. As a result, local freshwater ecosystems in mind and do not take into governments that wish to protect riparian buffers account the unique resources and issues facing the adjacent to coastal marshlands during activities such tidally influenced ecosystems of Georgia's coastal as residential development,commercial development, communities. Therefore, there is a need for a model and construction of private,single-family recreational riparian buffer ordinance that meets the specific needs docks should consider adopting a coastal riparian of local governments along Georgia's coast. A Model buffer ordinance. Doing so will promote a consistent Coastal Riparian Buffer Ordinance for Georgia has 10 Protecting Riparian Buffers in Coastal Georgia: Management Options been developed and is available in Appendix A of this lands. These include water quality protection, flood document. protection, wetlands protection, reduction of erosion, and scenic protection.4 Therefore,projects that aim to use the funds in order to purchase riparian lands are B. Land Acquisition just the type of projects that the GLCP was created to serve and fund. For more information regarding the Acquisition is sometimes the best mechanism for application process and other details of the program, protecting key parcels of riparian lands. Generally, visit http://www.gadnrorg/g1cp/. acquisition is reserved for special cases. While cost is obviously the most significant barrier to use of Another funding source for the purchase of riparian acquisition as a protection tool, especially in coastal lands available to communities located in Georgia's areas where land values are generally extremely high, 11-county"coastal zone"area is NOAA's Coastal and there are numerous sources of funds available to local Estuarine Land Conservation Program(CELCP).5 This governments that can be applied toward riparian land program was established in 2002 topermanentlyprotect acquisition. coastal and estuarine lands "considered important for their ecological, conservation, recreational, historical The most significant source of funds available to or aesthetic values."It provides matching funds to state Georgia's local governments for land acquisition is and local governments for purchase of such lands or the new Georgia Land Conservation Program(GLCP). for purchase of permanent conservation easements on The GLCP was created in 2005 by the Georgia Land such lands.' From 2002-2006, CELCP has provided Conservation Act' and provides funding for land over $177 million nationally for purchase of coastal conservation projects in the form of loans and grants lands. The types of projects funded to date include to all cities and counties in Georgia, regardless of those with the goals of protecting wetlands and other their size or location. Since its beginning,the Georgia significant coastal habitats, reducing coastal water Land Conservation Council has approved projects pollution, and providing the public with recreational totaling over 18,000 acres.2 The funds from the access to the coast.' program can be used for all direct costs of activities required by State and local law in order to purchase Georgia's CELCP is administered by the Georgia a fee simple or lesser interest in real property. Such DNR, and program staff considers projects that are activities include the purchase price, the cost of due consistent with the State's Coastal and Estuarine Land diligence,title insurance costs,attorneys fees,fees for Conservation Plan. According to this Plan, funds will services related to acquisition (such as holding costs, be prioritized for purchases of key parcels of coastal overhead costs, finders fees, etc.) and costs related to the closing transaction.' 4 Id. In 5 National Oceanic and Atmospheric Administration,The n order to be considered for funding under the GLCP, Coastal and Estuarine Land Conservation Program,http:// projects must demonstrate that they will serve one or coastalmanagement.noaa.gov/land/welcome.html(last revised more of the conservation goals of the program. One of Sept. 15,2006). Georgia's coastal zone includes the 11 coun- the program's listed conservation goals is"protection ties that border tidally-influenced waters or have economies of riparian buffers and other areas that serve as natural that are closely tied to coastal resources. National Oceanic and Atmospheric Administration,State Coastal Zone Boundaries, habitat and corridors for native plant and animal available at http://coastalmanagement.noaa.gov/mystate/docs/ species," and several of the other listed conservation StateCZBoundaries.pdf(April 22,2004). goals are served through purchase of riparian 6 Georgia Coastal Resources Division,Georgia Coastal& 1 O.C.G.A. § 36-22-1 et seq. (2006). Estuarine Land Conservation Plan,http://crd.dnr.state.ga.us/ content/displaycontent.asp?txtDocument=1045(last revised 2 Georgia Department of Natural Resources,Recent Projects, Sept.27,2006). http://www.gadnrorg/glcp/Documents/Recent_Projects.pdf 7 National Oceanic and Atmospheric Administration,CELCP (last visited June 1,2006). Projects,http://coastalmanagement.noaa.gov/land/celcp_proj- 3 O.C.G.A. § 36-22-2(2006). ects.html(last revised July 13,2006). Protecting Riparian Buffers in Coastal Georgia:Management Options 11 or estuarine, tidally influenced lands that are under Conservation Easement Act, O.C.G.A. § 44-10-1 threat of development, in relatively good ecological et seq., which authorizes and encourages the use of condition and need no significant restoration work conservation easements in Georgia. A conservation in order to provide the community with ecological easement is a legally binding agreement between a services. To date, no projects in Georgia have been landowner and a governing authority or a federally funded by the program, although the Georgia DNR recognized charitable organization that restricts has submitted a proposal to CELCP for the fee simple certain development activities and uses of the land.10 purchase of lands adjacent to the Sansavilla Wildlife Fee simple ownership of land entitles one to a"bundle Management Area in the Altamaha River Basin. If of rights" including the right to sell, the right to the project is selected for the program, the funds exclude others,the right to farm or mine and the right will become available in March 2007.8 For more to develop, among others. In a conservation easement information, visit http://coastalmanagement.noaa. agreement,the fee simple landowner agrees to give up gov/land/welcome.html or contact Jill Andrews, or sell one or more of these rights in order to protect Georgia DNR Coastal Management Program, at 912- a natural resource. For example, a landowner may 262-3198. choose to give up or sell the right to harvest timber or conduct land-disturbing activity on forested riparian Other sources of funding for riparian land acquisition lands in order to protect water resources and wildlife include: habitat. The landowner retains such basic property • Clean Water Act Section 319. Funds for rights as the right to exclude others from their property, nonpoint source pollution control. Priority the right to sell and the right to use the property in goes to watersheds ranked highly in Georgia's a manner that does not compromise or interfere Unified Water Assessment Process. with the conservation goals of the easement. Local • Impact Fees. Local governments are governments, charitable organizations and private authorized to charge fees to developers to pay individuals may purchase or receive the easement as for the infrastructure necessary to support the a gift. It is then the responsibility of the easement development.9 These fees can be applied to holder to ensure that the terms of the easement are not protect and produce water supplies, acquire violated and to pursue any legal recourse necessary and protect parks and open space, protect and for its enforcement." improve shores (stream banks), and provide for flood control, among other purposes. Conservation easements have been used effectively • Creation of a stormwater utility. In recent to protect environmentally sensitive areas and can years, several Georgia local governments be useful in preserving tracts of riparian lands.12 In have instituted a stormwater utility to help pay addition to these environmental benefits,conservation for the maintenance and construction costs easements offer other advantages to local governments, associated with stormwater infrastructure. such as reduced maintenance and service costs.13 These funds could potentially be used by a local Though it is difficult to predict what the level of government to purchase key riparian lands for participation in such a voluntary program might be, the purposes of stormwater control and water a number of recent developments in Georgia should quality protection. serve to encourage landowner participation. C. Conservation Easements and 10 Fowler,Laurie, Conservation Easements for Natural Re- Purchase of Development Rights source Protection, (1st ed. 1994),available at http://outreach. ecology.uga.edu/tools/easements/cons_easements_1 st_ed.html. In 1992, the Georgia legislature passed the Uniform 11 1d. 12 Wenger,Seth and Laurie Fowler,Protecting Stream and 8 Personal communication with Jill Andrews,Georgia DNR River Corridors: Creating Effective Local Riparian Buffer Coastal Management Program. Ordinances 27(2000). 9 O.C.G.A. § 36-71-1 et seq(2006). 13 Id. 12 Protecting Riparian Buffers in Coastal Georgia: Management Options The Uniform Conservation Easement Act empowers protection, tax incentives may also encourage both governmental bodies and certain charitable landowners to donate or sell conservation easements. corporations or trusts to become holders of easements.14 These tax deductions and credits give landowners Though local governments do hold some easements, an extra incentive to donate or sell conservation charitable organizations provide an attractive easements because they are able to recoup some of the alternative holder,and charitable organizations known value of the property lost by foregoing development.19 as land trusts have become increasingly active in the At the same time, the local government saves by not State in the past decade. Land trusts are capable of paying full fair market value for the interests in land accepting and enforcing conservation easements, (if the easement is sold rather than donated).20 thereby relieving local government of the burden of monitoring and oversight.15 There are now 46 land Both federal and State tax laws allow landowners to trusts active in Georgia.16 deduct the value of a donated conservation easement or land in fee simple (considered a charitable gift) The following land trusts currently maintain property from their income tax so long as the easement furthers or will consider maintaining property along Georgia's one of four conservation purposes. These purposes coast: include"the protection of relatively natural habitat of • St. Simon's Land Trust. Since 2000, the St. fish, wildlife, or plants, or similar ecosystems" and Simon's Land Trust has preserved 72 acres, "the preservation of open space yielding significant including 5 easements containing coastal riparian public benefit for the scenic enjoyment of the general lands. In evaluating acquisition, St. Simon Land public or pursuant to a clearly delineated federal,state Trust looks at the overall conservation value of or local government conservation policy,"21 both of the land and inquires whether its preservation which would likely be satisfied in the case of coastal fits into the overarching Greenprint Plan for riparian buffers. The value of the easement or the the island." For more information, visit http:// fee simple interest in land,which must be determined wwwsslt.org/ by a qualified appraiser if it exceeds $5,000, is the difference between the fair market value (FMV) of • The Georgia Land Trust. With a staff of nine the land without the restriction and the FMV after the individuals, the Georgia Land Trust currently restriction. In most cases the landowner can deduct preserves over 1400 acres of coastal land, most up to 30% of his adjusted gross income (AGI) over a of which contain riparian lands. The Trust period of six years until the value of the easement is has easements in Effingham, Bryan, Liberty, exhausted. If a landowner acts quickly, however, he Camden and Chatham counties, including two may be eligible for more advantageous treatment. In small easements on Tybee Island.'$ For more August 2006, Congress enacted a provision in the tax information, visit http://wwwgalandtrust.org/ code allowing a landowner to deduct up to 50% of • The Nature Conservancy. For more information, his AGI over sixteen years or until the amount of the visit www nature.orgl value of the gift is used up. This provision will sunset on December 31, 2007, after which the deductions In addition to a commitment to environmental revert to the previous limits of 30% of AGI and a six- year carryover. 22 14 O.C.G.A. §44-10-2(2)(2006). 19 Fowler,Laurie,Hans Neuhauser,and Curt Soper,A State 15 Wenger and Fowler,supra note 12,at 27. Income Tax Credit Program:An Incentive for Private Land 16 Georgia Land Trust Service Center,Georgia Environmental Conservation 3 (2004)(on file with author). Policy Institute,http://wwwgepinstitute.com/landtrust.asp(last 20 Id,at 5. visited June 1,2006). 21 I.R.C. § 170(2006). 17 Personal communication with Michelle Pugliese,St. 22 Memorandum from Lee Carter and Beau Howell,Upper Al- Simon's Land Trust. tamaha Practicum,River Basin Center,University of Georgia, 18 Personal communication with Frank McIntosh,Georgia to Peyton Ferry Farm Members 6-7(Dec. 1,2006)(on file with Land Trust. author). Protecting Riparian Buffers in Coastal Georgia:Management Options 13 In 2006, the Georgia legislature passed and the community). For information on funding sources Governor Purdue signed HB 1107, the Georgia Land for PDR programs, please see the preceding section Conservation Tax Credit. The Georgia Conservation entitled "Land Acquisition," as the sources of funds Income Tax Credit Program (GCTCP) allows for outright acquisition and easement purchase by Georgia landowners that donate either a conservation local governments in Georgia are similar, if not easement or land in fee simple to the State or qualified identical. organization to receive a State income tax credit of 25% of the value of the donated land or easement, as Because conservation easements have the potential determined by the local tax assessor. In addition, the to preserve additional riparian lands beyond those value of the donation cannot exceed the taxpayer's protected by a riparian buffer ordinance, easements income tax liability, and, in any event, is capped at have great potential to provide for supplemental $ 250,000 for individual donors or $ 500,000 for protection of riparian lands. Local governments can corporate donors. The tax credit may be applied to encourage the donation of conservation easements the landowner's tax liability over a period of up to with public information campaigns, cooperation six years. 23 Lands eligible for the GCTCP include with local land trusts, and the inclusion of positive wetlands, riparian buffers, and"other areas that serve statements in their comprehensive plans regarding the as natural habitat and corridors for native plant and preservation of riparian lands.26 animal species. Donations must be made to the State or to a "qualified organization," which include any D. Transferable Development charitable non-profit organization that has adopted Rights the Land Trust Standards and Practices and has been in existence for five or more years at the time of Another preservation tool for communities donation. 24 confronted with growth management is a transferable development rights (TDR) program. With this tool, Finally, the landowner who places a conservation the community can focus future development away easement on his property may be eligible for a property from environmentally sensitive areas,such as riparian tax deduction. Georgia's Uniform Conservation buffers, to more appropriate locations.27 With a TDR Easement Act provides that the landowner may program, a community can identify riparian lands it demand a revaluation of his property so as to reflect would like to preserve as "sending areas." In many the existence of the encumbrance on the next tax cases,the local government zones these areas at a low digest.25 density. Other areas where the community prefers to concentrate growth and development are designated In addition to soliciting donations of conservation as"receiving areas."Owners of"receiving areas"may easements to protect buffers, local governments purchase unused development rights from owners of can establish purchase of development rights "sending areas" in order to gain the right to develop (PDR) programs. Under such a program, the local more densely than the underlying zoning would government purchases the development rights from allow.28 Once these rights are sold, the sending area willing landowners and a conservation easement is may not be developed in the future and these parcels subsequentlyplaceduponthe landowner's pare el.Local are protected by a conservation easement or similar governments select lands for purchase based upon the legal tool. This transferability not only provides willingness of landowners and the conservation value compensation to landowners for low-density zoning, of the land (as determined by criteria established by but provides the local government with the opportunity 23 O.C.G.A. §48-7-29.10(2006);see also Ga.Dep't of Natu- ral Resources,Procedures for the Georgia Conservation Tax 26 Wenger and Fowler,supra note 12,at 27. Credit Program 8(2006),available at http://www.galandtrust. org/PDF%20files/ConservationTaxCreditDraftRegs.pdf 27 Rick Pruetz,Saved by Development:Preserving Environ mental Areas, Farmland and Historic Landmarks with Transfer 24 Ga.Comp.R. &Regs. § 391-1-6.-03 (2006). of Development Rights 3(1997). 25 O.C.G.A. §44-10-8(2006). 28 Id. 14 Protecting Riparian Buffers in Coastal Georgia: Management Options to focus growth where it is most appropriate.Although E. Clustering and Conservation it is possible to designate all coastal stream and river corridors as "sending areas,"this may have the effect Subdivisions of flooding the market with a large number of small TDR credits. The establishment of a TDR banking Though similar to the concept of TDRs, clustering is system may address this problem. 29 different in that the transfer of density occurs within a single parcel of land.34 For example, a landowner While TDR programs are used for a variety of with a 100-acre parcel that is zone at one unit per purposes, the following coastal communities use 20 acres, might want to concentrate all five units TDRs specifically to protect their coastal resources within a five acre area to preserve the other 95 acres. and wetlands. By concentrating denser development away from riparian lands, clustering may help to protect stream • Clearwater, Florida adopted a TDR ordinance buffers and coastal features.35 A common way of in order to preserve open space, specifically implementing clustering in a community is through a limiting development in those properties clustering or conservation subdivision ordinance. For "seaward of the coastal construction control line along the beaches of the Gulf of Mexico!'" more information on these tools and how to implement them in Georgia, visit http://www.rivercenteruga. • Lee County, Florida protects wetlands and the edu/service/tools/cons_subdivisions.htm. adjacent transitional zones by heavily restricting development in these areas. The county's TDR program allows development rights in these areas to be purchased and used in more intensely developed urban, commercial and industrial zones.31 • Hollywood, Florida rezoned one of its last undeveloped beachfront areas from twenty-five units per acre to seven units per acre. The city's TDR program allows developers to transfer density credits from this area to a multiple- family residential zone further away from the beach.32 • Brevard County, Florida adopted a TDR ordinance to encourage preservation of coastal areas and to compensate landowners whose property was rezoned from 30 units per acre to one unit per acre.33 29 Wenger and Fowler,supra note 12,at 26. 30 Pruetz,supra note 27,at 359. 31 Id. at 272. 32 Id. at 370. 34 Id.at 7. 33 Id. at 29,340. 35 Wenger and Fowler,supra note 12,at 26. Protecting Riparian Buffers in Coastal Georgia:Management Options 15 V. B u f f e rs and n d Private Property government acquires property from private parties through the condemnation process, adhering Rights scrupulously to the requirements of the takings clause.39 However, a more difficult case is presented Perhaps the biggest impediment to establishing when government, or a government agency, issues a riparian buffer ordinances is concern for private regulation, like a riparian buffer ordinance, that may property rights. Yet, a well written ordinance that inadvertently reduce or eliminate the value of the is administered fairly will balance natural resource privately owned land.4° protection with the rights of property owners. It is entirely possible to provide strong protection for Initially, only when the government physically riparian buffers while respecting the rights of property exerted dominion or control over private property did owners. the courts require compensation under the Takings Clause.41 Therefore historically, governments Buffers protected by a riparian buffer ordinance could regulate the use of private property without remain in the ownership of the property owner and compensating the owner.42 This formalistic approach preclude general public access. This is in contrast to changed in 1922 when Justice Oliver Wendell Holmes, greenways, which are generally publicly owned. A Jr., speaking for the U.S. Supreme Court, specified buffer ordinance should never mandate public access "while property may be regulated to a certain extent, to private property, nor should it restrict activities on if regulation goes too far it will be recognized as a a property to such an extent that the owner cannot `taking."'43 Justice Holmes elaborated, "whether the make use of it. These conditions would be grounds state's regulation has "[gone] too far" is a question for a takings lawsuit. If a local government cannot of degree — and therefore cannot be disposed of by provide adequate buffer protection along a stream general propositions." Since that decision, courts segment or marsh without infringing on property have attempted to clarify when a statute"goes to far."45 rights, then the government must either acquire the The Court later endorsed "ad hoc, factual inquiries" based on the specific facts of each case.46 This inquiry parcels in question(or conservation easements on the uses a three-part balancing test to determine whether a parcels) or try to offset the lack of protection with taking requiring compensation has occurred. The Penn controls(whether regulatory or voluntary)somewhere Central balancing test analyzes the economic impact else in the stream basin. on the claimant, the extent to which the regulation A. Federal Takings Law 39 Marzulla,Nancie,State Private Property Rights Initiatives As a Response to "Environmental Takings", 46 S.C.L.Rev. Today, any discussion of land-use management 613,623 (1995). and regulation must include the takings issue. The 40 Burcat,Joel R.and Julia M.Glencer, The Law of Regula- provision of the Fifth Amendment that prohibits tory Takings: Part I—Development of the Law 1 (2002), government from taking property for a public use available at http://www.king.com/files/tbl_s48News/PDFUp- load307/7641/bu rcatwhtpape r..pdf. without just compensation is the key to constitutional land use law.36 The Takings Clause of the Fifth 41 Hutchinson,David,A Setback For The Rivers of Massachu- setts? An Application of Regulatory Takings Doctrine To The Amendment provides: "nor shall private property be Watershed Protection Act And the Massachusetts River Protec- taken for public use, without just compensation."37 tion Act,73 B.U.L.REV.237,246-47(1993). This provision is applied to the states through 42 Id. the Fourteenth Amendment.38 Traditionally, the 43 Pennsylvania Coal Co. v.Mahon,260 U.S. 393,415 (1922) 36 Jurgensmeyer,Julian C. &Thomas Roberts E.,Land Use (emphasis added). Planning and Development Planning Regulation Law, Consti- 44 Id. at 416. tutional Limitations: The Takings Issue, §10.2(Pt ed. 1998). 45 Burcat and Glencer,supra note 40. 37 U.S.Const. amend.V. 46 Penn Central Transportation Co. v. City of New York,438 38 Jurgensmeyer&Roberts,supra note 36. U.S. 104, 124(1978). 16 Protecting Riparian Buffers in Coastal Georgia:Management Options interferes with investment-backed expectations and be protected from takings claims on those grounds as the character and extent of the government action.47 well.53 Conversely,the Court's emphasis on economic In 1992 the Court decided an important regulatory and developmental uses in the case may suggest a bias takings case, Lucas v. South Carolina Coastal against purely environmental purposes.54 The Court Council.48 In Lucas, the landowner purchased two states that it does consider non-economic interests undeveloped beachfront lots on a South Carolina in land in its takings analysis and environmental barrier island,intending to build a single family home regulations like riparian buffer ordinances have both on each. In 1988, before Lucas began construction, market and non-market economic value.55 the State legislature enacted a land use statute that effectively barred any development on Lucas's B. Georgia Takings Law property. The trial court found the statute had rendered the property valueless and granted Lucas The Georgia constitution has it own takings clause compensation for the taking. The State appealed and that parallels the U.S.Constitution's Takings Clause.56 the South Carolina supreme court reversed, holding Governmental regulations, such as riparian buffer the State's purpose in preventing harm to the coastline ordinances, may be challenged under the federal outweighed Lucas's economic interest.49 The U.S. Constitution, the Georgia constitution, or both. Supreme Court took the opportunity to elaborate on Consequently, any riparian buffer regulation should its takings jurisprudence and held that a taking occurs comply with all applicable federal and State laws.57 when a land use regulation "does not substantially The Georgia supreme court has twice visited the advance legitimate State interests or denies an owner constitutionality of mandatory riparian buffers and economically viable use of his land." The Court both times has upheld the laws.58 Many of the local characterized denial of all economically viable use jurisdictions in the metropolitan Atlanta area have as a "categorical" rule automatically triggering a enacted buffer ordinances requiring a buffer width of taking. 5° The Court did establish one exception to from 75 to 150 feet; these ordinances have not been this rule - if it is clear that the landowner purchased challenged in court. A brief analysis of the evolution the property after the regulation that denies him or her of regulatory takings jurisprudence in Georgia follows all economically viable use of the land was already below. in place, then no compensation will be given.51 The case was returned to the lower court to allow the State In 1975, the Georgia supreme court clarified to identify background principles of nuisance and that governmental regulations are "subject to the property law that would prohibit the landowner from constitutional prohibition against taking private making his desired use of the property.52 property without just compensation."59 In the same case,the court employed a balancing test that weighed Also in Lucas, the Court noted specifically that the economic loss to the property owner against the uses of property may be denied, regardless of the public benefits that the regulation provided in order economic impact, if they constitute a public nuisance in accordance with long-established principles of 53 Wenger and Fowler,supra note 12,at 36(2000). common law. Since non-point source pollution may 54 Lucas v South Carolina Coastal Council,505 U.S. 1003, constitute a public nuisance and riparian buffers are an 1020(1992). effective way to prevent such pollution, buffers may 55 Lucas,505 U.S.at 1019n.8.Stream buffer regulations have economic value elements that are both market and non-market; 47 Id. see infra, section entitled"Economic Considerations"for a full 48 Lucas v South Carolina Coastal Council,505 U.S. 1003 explanation of the economic value of coastal riparian buffers. (1992). 56 Ga. Const. art.I, §1,para.I. 49 Id. at 1008-10. 57 Id. 50 Id.at 1015. 58 Pope v. City of Atlanta,240 S.E.2d 241,242(1977); Threatt 51 Id. at 1027. v Fulton County,266 Ga.466(1996). 52 Id. at 1031-32. 59 Barrett v.Hamby, 235 Ga.262,264(1975). Protecting Riparian Buffers in Coastal Georgia: Management Options 17 to determine if the regulation constituted a taking (with one exception).67 Third, similarities exist under the Georgia constitution.60 In 1986, the court between the federal concept of"distinct investment- rearticulated the balancing test to be applied in backed expectations"in Penn Central and the Georgia challenges to governmental regulations in Gradous concept of"vested rights," although there are some v. Richmond County.61 First, the court established significant differences between the two concepts.68 the presumption that regulations are valid.62 Then, in order to overcome that presumption,the claimant must The Georgia supreme court has defined vested prove two things:(i)"significant detriment"caused by rights as "interests which it is proper for the state to the challenged regulation; and (ii) an "insubstantial recognize and protect and of which [the] individual relationship" between the challenged regulation cannot be deprived arbitrarily without injustice."69 and the public interest. If both prongs are met, the Georgia's vested rights doctrine is among the most court will then balance the economic detriment to the liberal in the nation, requiring consideration and property owner against the public interest advanced caution by government regulators. Georgia has by the regulation. 63 adopted the minority rule regarding vested rights, holding that a landowner's right to develop his land In Parking Association of Georgia, Inc. v. City of "vests" and he is entitled to a building permit when Atlanta,64 the City ofAtlanta enacted a comprehensive he makes "substantial investments in his land in regulation requiring landscaping in surface parking reliance upon an existing ordinance and the assurance lots that had been cited by the city for environmental of zoning officials."70 This is the case regardless of and aesthetic problems. The parking lot owners whether a regulation that would prohibit the activity claimed the regulation violated the State takings for which the building permit is sought is passed after clause. The court applied the Gradous test to the any substantial investments and/or assurance from a regulation and found that while the claimants would zoning official occurs. In order to ensure that they do experience profit losses and costs if they complied, not violate the vested rights doctrine when enacting this value diminution did not constitute the required riparian buffer ordinances, local governments in "significant detriment." The court also found, "the Georgia should take several precautions. First, means adopted have a real and substantial relation to localities should provide ample public notice during the goals to be obtained" and upheld the regulation.65 the ordinance adoption process. Local governments should also consider placing a moratorium on There are several differences between the State and encroachments into the proposed buffer area during federal analyses for regulatory takings. In Georgia, a the ordinance development process so as to cut down finding of a "significant detriment" does not require on the number of vested rights claims. Finally, the the total or nearly total loss of the property's value in ordinance should clearly state that it does not apply order to meet the state takings test. Instead,a severely to landowners that receive a building permit and/or detrimental loss in value is sufficient.66 Second, in other assurances from zoning officials before the Georgia, monetary compensation for regulatory ordinance's effective date. takings is not authorized if a court holds a taking has occurred; invalidation of the regulation is sufficient Only two state takings cases specifically address whether a riparian buffer regulation constitutes a 60 Id. 67 Id.at 11. The exception is if the government acts in con- 61 256 Ga.469(1986). tempt of court after being ordered to rescind the unlawful regu- 62 Id. at 470. lation. A line of three cases clearly establishes this principle: Fulton County v. Wallace,260 Ga. 358 (1990), Cobb County v. 63 Id. at 471. McCollister,261 Ga. 876(1992)and Alexander v. Dekalb Co., 64 264 Ga.764(1994),cert. den. 115 S.Ct. 2268. 264 Ga. 362(1994). 65 Id. 68 Zoeckler,supra note 66 at 11. 66 Zoeckler,Robert L.,A Summary of Takings Law 10(1997) 69 Fortson v. Weeks,208 S.E.2d 68(Ga. 1974). (on file with author). 70 Barker v. Forsyth Co.,281 S.E.2d 549(Ga. 1981). 18 Protecting Riparian Buffers in Coastal Georgia:Management Options taking under the state or federal constitution. In both be left undisturbed for a distance of fifty feet from cases, the riparian buffer regulations were upheld the banks of the Chattahoochee River and prohibited as constitutional. In Pope v. City of Atlanta, Pope construction of impervious surfaces within 150 feet wished to build a tennis court on the rear portion of of the river's banks.75 The Georgia supreme court her property bordering on the Chattahoochee River.71 rejected the claim that the buffer regulation constituted The City of Atlanta issued a stop work order claiming a taking under the state and federal constitutions, that at least part of the tennis court was within 150 holding that,"there has been no showing that the buffer feet of the river and that construction of the tennis area or any other applicable regulation has deprived court violated the Metropolitan Rivers Protection the [landowners] of any or all economically viable Act.72 The case went to the Georgia supreme court or beneficial use of their property."76 Referencing where the court concluded: "the River Act does not ParkingAssociation, the court went on to state,"nor is constitute zoning within the definition set out in the this a situation in which it can be argued that fairness Georgia Constitution...but instead falls within the and justice dictate that the burden imposed by the reserved powers [police powers] of the State to act, regulation be borne by the public as a whole."77 along with local governing authorities, with regard to the water system, as is set out in the purpose of Private property is a core constitutional concept the River Act."73 This case clearly establishes that in this country. Therefore it is not surprising that environmental regulations, such as riparian buffer governmental interaction with private property rights ordinances, are a valid exercise of the police power. can create controversy. But private property rights have always been tempered by the needs of the Threatt v. Fulton County, the second case involving general public.78 As Justice Scalia stated in Lucas, riparian buffers that has been litigated in Georgia, "[T]he property owner necessarily expects the uses involves another challenge to the buffer requirements of his property to be restricted from time to time, of the Metropolitan River Protection Act (MRPA).74 by various measures newly enacted by the State in TheAtlanta Regional Commission adopted a regulation legitimate exercise of its police powers."79 pursuant to the MRPA that required a vegetated buffer 75 Id. at 468. 76 Id. at 470. 71 240 S.E.2d 241,242(1977). 77 Id. 72 O.C.G.A. § 12-4-440 et. seq. (2006). 78 Zoeckler,supra note 66,at 16. 73 240 S.E. 2d at 244(clarification added). 79 Lucas v. South Carolina Coastal Council,505 U.S. 1003, 74 266 Ga.466(1996). 1027 (1992). Protecting Riparian Buffers in Coastal Georgia:Management Options 19 V. Economic Considerations For landowners, the most significant cost of the ordinance is likely to be the loss of full use of the land in the riparian buffer. For a developer, a buffer As discussed above,many studies have demonstrated ordinance may slightly decrease the lot yield of a that coastal riparian buffers have value in protecting property, especially in areas zoned at high density; coastal marshes and tidal creeks from non-point for low-density areas, the buffers can usually be source pollution. They also provide numerous other incorporated into the backside of individual lots,with valuable benefits to coastal communities, such as little impact on yield. For owners of individual lots, recreation, flood protection, and protection wildlife the limitation on use can also conceivably reduce habitat and diversity. However, what are the actual property values,but this is likely offset by the positive economic values of these benefits? And what are effects of improved aesthetics and recreational the costs associated with implementing buffers opportunities discussed in the next section. Other in a coastal community? While the current status costs include time spent delineating the riparian of economic research on coastal buffers cannot buffer and completing necessary documentation to provide full answers to these questions, there is some submit to the local government authority. Protecting information available on the economic costs and the riparian buffer during construction might also add benefits of coastal riparian buffers that can help local to construction costs. governments make better decisions about protecting buffers in their communities. B. The Benefits This section was first published in its original form in Wenger and Fowler (2000). Information regarding The value of riparian buffer zones can be broken the economic valuation of riparian buffers in coastal down into a number of components, some of which areas was added to this material, and it is intended to are obvious and some of which are not. An obvious provide a short summary of economic research on the value is that of the timber in a riparian zone that can costs and benefits associated with preserving riparian be cut and sold.A less obvious value is the protection buffers in coastal communities. No attempt is made of the scenic vista of the tidal marshes that the to quantify the actual economic benefits or costs of vegetation of the riparian zone provides by shielding buffers, because such an assessment is beyond the development from view. The obvious values are what scope of this project. The purpose here is to show that economists call "market values" because we can riparian buffers do have economic benefits, and these measure them in actual prices, while the less obvious can be equal to or greater than the economic costs of ones are "nonmarket." They are real, but are harder a buffer ordinance. to measure because they don't correspond to things that are commonly bought and sold. It is important A. The Costs to note that most of the actual costs of having buffer ordinances relate to market values,while many of the benefits are nonmarket. If these nonmarket values The economic costs of a buffer ordinance are are ignored, people will tend to undervalue riparian related to the costs of administration and the loss buffers,which can lead to poor protection and negative of unrestricted use of properties. A buffer ordinance impacts on both the environment and the economy imposes costs on a local government in the form of (Bollman 1984). staff time, staff training,public education efforts, and technical assistance to landowners and developers. For most local governments, the greatest expense 1. The Value of Recreation and Tourism is staff time (Herson-Jones 1995). Once a buffer Rivers, streams, lakes, coastal marshlands, and other ordinance is established and integrated into the plan water bodies are natural magnets for recreational review process, however, this cost should be low in activities and tourism. A protected riparian buffer most cases. acquired by the local government can serve as a public park or greenway, a function with significant 20 Protecting Riparian Buffers in Coastal Georgia: Management Options economic value. Of course, most buffers protected near seven restored streams in California were found by an ordinance will remain in the ownership of to be 3 -13% higher than the values of similar homes individuals, and it is usually not legal or desirable for located near unrestored streams. In Colorado, a study a government to mandate access to these lands. Still, found that housing prices were 32% higher when the these buffers can contribute positively to recreation houses were located adjacent to a buffer managed as and tourism by improving water quality and by a greenbelt(Schueler 1997). In addition to increasing protecting the aesthetics of stream corridors and community aesthetics so that property values increase, scenic marsh vistas, both of which are important for buffers have also been found to increase property water-based recreational activities. values due to the water quality services they provide. A study of shoreline buffers on several lakes in Maine Determining the economic value of stream and found that a difference of 3 feet in water clarity (i.e. marshland recreation gives us an indication of the the ability to see an additional 3 feet deeper into the value of riparian buffers. There are several ways to lake with the naked eye) resulted in an increase in calculate this. the value of the adjacent shoreline property of$11 to Using a method know as contingent valuation, $200 per foot of water clarity (Schueler 1997). researchers asked visitors to a river preserve in Arizona how much they would be willing to pay to ensure For a developer, a riparian buffer ordinance may that there were adequate flows to maintain a healthy have the effect of requiring residential development river system, which resulted in an estimated value projects to take the form of conservation subdivisions. of $520,000 for the preserve (Crandall et al. 1992). That is, the property is subdivided in such a way that Using another valuation method known as the travel individual lots are clustered together and a significant cost method, the river preserve was valued based on area of riparian land is preserved in a natural state. the amount of money and time visitors spent to visit Studies have shown that home buyers will pay more it, which was estimated at $613,360. Finally, local to live in a well designed conservation subdivision economic impact analysis determined that visitors than a traditional development (National Park who came to the area specifically to visit the preserve Service 1995). In addition, clustering homes allows contributed $88,240 to the local economy (Crandall the developer to save money on infrastructure costs, et al. 1992). These methods have been used to value which itself can offset the costs of development. parks in Georgia as well.Visitors to State parks spend Georgia developer Steve MacCaulay,who specializes as much as $13.26 per visit(Bergstrom et al.1990). in conservation subdivisions, says that he can make the same profits off of conservation subdivisions as The value of buffers on the Georgia coast in protecting he can from conventional designs (1999). the tourism, recreation and fishing industries is significant considering the enormous contributions that 3. The Value of Clean Water water-based tourism and recreation make to Georgia's In Georgia's coastal areas, water quality is extremely coastal economy. Indeed, the National Association important for maintenance of the commercial and of Regional Councils estimates that tourism provides recreational fish,shrimp,and shellfish industries. The two billion dollars annually to the coastal economy in tourism industry,which depends on the availability of Georgia(Guadagnoli et al. 2005). Recreational game water that is fishable and swimmable, is also affected fishing alone contributes about$363 million annually significantly when water quality is degraded. One and commercial fishing provides an additional $22 can estimate the value of clean water to Georgia's million(Georgia Department of Natural Resources). coastal communities by examining the contribution that the recreational and commercial fish, shellfish, 2. Property Value Increases and shrimp industries make to Georgia's economy. A protected stream or river corridor is an aesthetic Based upon data compiled by the Coastal Resources amenity that can increase property values in the nearby Division of the Georgia Department of Natural community. In one study using a method known as Resources, over 6.8 million pounds of commercially hedonic pricing, property values of homes located valuable fish, shellfish, and other organisms, valued Protecting Riparian Buffers in Coastal Georgia: Management Options 21 at over$12.2 million,were harvested from Georgia's land along waterways and steering development coastal waters in 2005 (Georgia Department of away from floodwaters, storm surges and extreme Natural Resources 2006a). Over the last ten years high tides (Desbonnet et al. 1994). Specifically, (1994-2004), an average of 10.8 million pounds of one study of ten programs from across the country commercially valuable organisms was harvested per that protected floodplains from development found year, for an average worth of$22.4 million (Georgia that land adjacent to such protected floodplain areas Department of Natural Resources). increased in value by an average of$10,427 per acre (Schueler 1997). Another way to measure a buffer's water quality services is to determine how much it would cost 5. The Value of Endangered Species&Other to provide similar services using technological Wildlife approaches. A study in Maryland determined that Riparian buffers in coastal settings have been shown using riparian buffers and nonstructural controls to protect wildlife habitat for many species. The was more cost-effective than engineered solutions wildlife-watching opportunities afforded by buffers in reducing nutrient pollution by 40 percent. (Palone can increase property values. In one study,researchers and Todd 1998). The city of Boulder, Colorado, found that about 60%of suburban residents engage in decided that the services provided by Boulder Creek wildlife viewing near their homes,and a majority were and its riparian zone were more valuable than those willing to pay a premium for homes located near areas provided by a new nitrification tower, and chose to that attract wildlife (Schueler 1997). Threatened and restore the stream system rather than to construct the endangered species have value to people even when technological solution (National Park Service 1995). they provide no direct economic benefits. Economists Riparian buffers can also eliminate the need for have used the contingent valuation method to engineered stormwater management systems, which determine how much people are willing to pay to can cost from $500 to $10,000 per acre (Palone and ensure that these organisms survive. Studies have Todd 1998). shown that people will pay$3—$9 per year to preserve habitat for relatively obscure nongame species such 4. The Value of Flood Protection as the Colorado Squawfish (Ptychocheilus lucius) As discussed above, in coastal areas, riparian buffers and the Striped Shiner (Notropis chrysocephalus). have been shown to reduce flooding by slowing They will pay considerably more ($30—$60 per year) surface water runoff and spreading it over a wider for higher profile species such as the Chinook Salmon area and by allowing more water to percolate into (Oncorhynchus tshwytscha) (Loomis and White the water table (Rhode Island Program 1994; South 1996). One study found that Washington households Carolina Department of Health and Environment would pay $73 per year to remove dams and restore 2002a). Buffers also have been found to mitigate the Elwha River to improve salmon populations property destruction by maintaining undeveloped (Loomis 1998). 22 Protecting Riparian Buffers in Coastal Georgia: Management Options VI. Conclusion sedimentation problems to protect Georgia's waters and meet federal water quality standards, there is overwhelming evidence that more work that needs As the population of Georgia's coastal region continues to be done to protect the state's invaluable coastal to thrive and grow, the development pressures that resources from non-point source pollution. As a result, accompany this population increase are beginning to in January 2007,the Board of the Georgia Department threaten the very resources that attract people to the of Natural Resources adopted a resolution regarding region– Georgia's abundance of undisturbed coastal non-point source pollution control in coastal Georgia. marshlands and its tidal ecosystem. As Georgia's The resolution finds that the increasing impairment coastal communities look toward the future, tools of water resources from non-point source pollution such as riparian buffer ordinances are becoming is evidence that "current state statutes and rules, and increasingly important for protecting the scenic local ordinances and practices intended to prevent value of Georgia's marshes, the state's coastal fish non-point source pollution are not effective in many and shellfish industries, and private property, from areas of the state." The Board goes on to note that the unwanted effects of development. Increased riparian buffers are known to be effective tools in levels of development on the coast have begun to add preventing non-point source pollution, and it requests large amounts of impervious cover, such as parking the state Environmental Advisory Council (EAC) lots, rooftops, and roadways, and semi-pervious conduct a review of current statutes, regulations cover, such as compacted lawns and unpaved and programs aimed at controlling non-point source driveways, to the landscape. These surfaces generate pollution. Furthermore, in conducting its review, the increased levels of stormwater runoff which delivers Board requests that the EAC pay specific attention to numerous types of pollutants—such as oil,biological the use of"riparian buffers, impervious surfaces, and contaminants and excess nutrients—to marshes and storm water management practices." creeks. As this report has shown, recent scientific research indicates that riparian buffers play a crucial role in protecting our waters from the effects of NPS As the state begins to focus on riparian buffers as a pollution by acting as filters and removing pollutants primary tool to curb non-point source pollution in before they enter our waterways. Furthermore, as our Georgia's coastal region, local governments along scientific understanding of the benefits and functions the coast can enhance and further state efforts by of riparian buffers in coastal Georgia continues to implementing their own coastal riparian buffer grow, scientists and other experts will be able to make ordinances. By working together, Georgia's state recommendations for protecting buffers that are more and local governments can ensure a bright future for effective and successful at protecting these important Georgia's coastal region, one in which the economic resources. and social benefits of development go hand-in-hand with conservation of the unique natural resources that While Georgia legislators have already recognized this region has to offer. the value of buffers in addressing erosion and Protecting Riparian Buffers in Coastal Georgia: Management Options 23 V . References Center for Watershed Protection.2001. The Economic Benefits of Better Site Design in Virginia. http://www dcrvirginia.gov/sw/docs/swmecon.pdf Arora,K., S.K. Mickelson,J. L.Baker,D. P.Tierney, C. J. Peters. 1996. Herbicide retention by vegetative Center for Quality Growth and Regional Development, buffer strips from runoff under natural rainfall. Georgia Institute of Technology.2006. Georgia Coast Transactions of the ASAE 2155-2162. 2030: Population Projections for the 10-County Coastal Region. http://www.cggrd.gatech.edu/PDFs/ Bergstrom, J. C., H. K. Cordell, A. E. Watson, and coastal a o G.A.Ashley. 1990. Economic impacts of state parks p� J p f ections. d. ro on the economies of the South. Southern Journal of Coastal Georgia Regional Development Center. Agricultural Economics (December): 6977. http://www.coastalgeorgiac.org. Bollman, F. H. 1984. Economic analysis and the Cooper, C.M. 1993. Biological Effects of management of riparian resources. Pages 221-25 in Agriculturally Derived Surface Water Pollutants on R. E. Warner and K. M. Hendrix, eds., California Aquatic Systems-AReview.Journal ofEnvironmental riparian systems: Ecology, conservation and Quality 22:402-408. management. Berkeley: University of California. Coyne, M.S., R.A. Gilfillen, R.W. Rhodes and R. L. Bradford, B. D. 1991. An economic analysis of river Blevins. 1995. Soil and Fecal Coliform Trapping by corridor protection. Master's thesis, University of Grass Filter Strips During Simulated Rain. Journal Georgia. of Soil and Water Conservation 50(4): 405-408. Burcat, Joel R. and Julia M. Glencer. 2002. The Law Crandall, K. B., B. G. Colby, and K. A. Rait. 1992. of Regulatory Takings: Part I—Development of the Valuing riparian areas: A southwestern case study. Law. Boston: Kirkpatrick and Lockhart. http://www. Rivers 3 (2): 88-98. king.com/files/tbl_s48News/PDFUpload3 07/7641/ burcatwhtpaperpdf Crawford, J.K. and D.R. Lenat. 1989. Effects of Land Use on the Water Quality and Biota of Three Burkholder, J.M., M.A. Mallin, H.B. Glasgow, Jr., L Streams in the Piedmont Province of North Carolina. M. Larsen, M.R. McIver, G.C. Shank, N. Deamer- In: Water Resources Investigation Report 89-4007. Melia, D.S.Briley, J. Springer, B.W. Touchette, and Raleigh,NC: US Geological Survey. E.K. Hannon. 1997. Impacts to a Coastal River and Estuary From Rupture of a Large Swine Waste Croke, K., R. Fabian, and G. Brenniman. 1986. Holding Lagoon. Journal of Environmental Quality Estimating the value of improved water quality in an 26: 1451-1466 urban river system.Journal of Environmental Systems 16 (1): 13-24. Carson, R. T., and R. C. Mitchell. 1993. The value of clean water: The public's willingness to pay for Desbonnet,A., P. Pogue, V. Lee, and N. Wolf. 1994. boatable, fishable, and swimmable quality water. Vegetated buffers in the coastal zone: A summary Water Resources Research 29 (7): 2445-54. review and bibliography. Providence: University of Rhode Carter, L. and B. Howell. 2006. Conservation Island. Easement at Peyton Ferry Farm. Athens:River Basin Center, University of Georgia. 2'4 Protecting Riparian Buffers in Coastal Georgia: Management Options Dillaha, T.A., J. H. Sherrard, D. Lee, S. Mostaghimi, Georgia Department of Natural Resources. 2006b. V.O. Shanholtz. 1988. Evaluation of vegetative filter Procedures for the Georgia Conservation Tax Credit strips as a best management practice for feed lots. Program.Atlanta,Ga.:Georgia Department ofNatural Journal of the Water Pollution Control Federation Resources.http://wwwgalandtrust.org/PDF%20files/ 60(7):1231-1238. Conservation TaxCreditDraftRegs.pdf Dillaha, T. A., R. B. Reneau, S. Mostaghimi, D. Gilliam, J. W. 1994. Riparian wetlands and water Lee. 1989. Vegetative Filter Strips for Agricultural quality. Journal of Environmental Quality 23: Nonpoint Source Pollution Control. Transactions of 896900. the ASAE 32(2):513-519. Groffman, P.M., A.J. Gold, T.P. Husband, R.C. English,D.B. K., and J. M. Bowker. 1996. Economic Simmons, W. R. Eddleman. 1991. An Investigation impacts of guided whitewater rafting: A study of five Into Multiple Uses of Vegetated Buffer Strips. rivers. Water Resources Bulletin 32 (6): 1319-28. Kingston: University of Rhode Island. Fennessy, M. S. and J. K. Cronk. 1997. The Guadagnoli, D., B. Good, J. Mackinnon, P. Flourney, effectiveness and restoration potential of riparian J. Harvey, and L. Harwell. 2005. The Condition ecotones for the management of nonpoint source of Georgia's Estuarine and Coastal Habitats 2000- pollution, particularly nitrate. Critical Reviews in 2001 Interim Report. Georgia Department of Natural Environmental Science and Technology 27(4):285- Resources, Coastal Resources Division. 317. Hatfield,J. L., S.K. Mickelson,J.L. Baker,K.Arora, Fowler, Laurie. 1994. Conservation Easements for D. P. Tierney, and C. J. Peter. 1995. Buffer strips: Natural Resource Protection. Resource Paper #1. Landscape modification to reduce off-site herbicide Georgia Environmental Policy Institute and Sautee- movement. In: Clean Water, Clean Environment, 21st Nacoochee Community Association. http://www. Century: Team Agriculture, Working to Protect Water rivercenter.uga.edu/service/tools/easements/cons_ Resources, Vol. 1. St. Joseph, MI: American Society easements 1st ed.html of Agricultural Engineers. Fowler, Laurie, Hans Neuhauser, and Curt Soper. Herson-Jones, L. M. 1995.Riparian buffer strategies 2004. A State Income Tax Credit Program: An forurban watersheds.Washington,D.C.:Metropolitan Incentive for Private Land Conservation. Washington Council of Governments. Frick, E. A., D. J. Hippe, G. R. Buell, C. A. Couch, Holland, A.F. et al. 2004. Linkages between tidal E. H. Hopkins, D. J. Wangsness, J. W. Garrett. 1998. creek ecosystems and the landscape and demographic Water Quality in the Apalachicola- Chattahoochee- attributes of their watersheds.Journal ofExperimental Flint Basin, Georgia, Alabama, and Florida, 1992- Marine Biology and Ecology 298: 151-178. 1995. U.S. Geological Survey Circular 1164. Hutchinson, David. 1993. A Setback For The Rivers Georgia Department of Natural Resources. Georgia of Massachusetts? An Application of Regulatory Commercial Fisheries Statistics for 1995-2004. Takings Doctrine To The Watershed Protection Act http://www.crd.dnrstate.ga.us And the Massachusetts River Protection Act. Boston Univ. Law Review 73: 237. Georgia Department of Natural Resources. 2006a. Summary of Georgia Historical Landings By Broad Jurgensmeyer, Julian C. & Thomas Roberts E. 1998. Category. Atlanta, Ga.: Georgia Department of Constitutional Limitations: The Takings Issue. In: Natural Resources. http://wwwcrd.dnrstate.ga.us Land Use Planning and Development Planning Regulation Law. St. Paul, Minn.: West Group. Protecting Riparian Buffers in Coastal Georgia: Management Options 25 Karr, J. R. and I. J. Schlosser. 1977. Impact of Mallin, M.A. (2006) Wading in Waste. Scientific Nearstream Vegetation and Stream Morphology on American June 2006 issue: 50-59. Water Quality and Stream Biota. Ecological Research Series. (EPA-600/3-77/097). Athens, Ga.: U.S. Mander,U.Kuusemets,K.Lohmus,T.Mauring. 1997. Environmental Protection Agency. Efficiency and dimensioning of riparian buffer zones in agricultural catchments.Ecological Engineering 8: Kulshreshtha,S.N.,and J.A.Gillies. 1993.Economic 299-324. evaluation of aesthetic amenities. Water Resources Bulletin 29 (2): 257-66. Marzulla,Nancie. 1995. State Private Property Rights Lant, C. L., and G. A. Tobin. 1989. The economic Initiatives As a Response to`Environmental Takings. value of riparian corridors in cornbelt floodplains: South Carolina Law Review 46: 613. A research framework. Professional Geographer 41 (3): 337-49. Michener, W.K., E.R. Blood, J.B. Box, C.A. Couch, S.W. Golladay, D. J. Hippe, R.J. Mitchell and B.J. Lee, R.F. 2005. Genotoxicants in Retention Ponds Palik. 1998. Tropical Storm Flooding of a Coastal and Adjacent Estuaries in Urban/Suburban Sites in Plain Landscape. Bioscience 48(9): 696-705. Coastal Georgia. Skidaway Institute of Oceanography, University of Georgia. National Association of Regional Councils (NARC). National Economic Development Forum,2001.http:// Loomis, J. B. 1998. Estimating the public's values www.narc.org/ed/articles/edaregionsjulaug01.pdf. for instream flow: Economic techniques and dollar values. Journal of the American Water Resources National Oceanic and Atmospheric Administration, Association Office of Ocean and Coastal Resource Management. 34 (5): 1007-14. 2001. Evaluation Findings for the Georgia Coastal Management Program from January 1998 through Loomis,J.B.,and D.S.White. 1996.Economic values April 2001. Washington, D.C.: National Oceanic and of increasingly rare and endangered fish.Fisheries 21 Atmospheric Administration. (11): 6-10. National Park Service. 1995. The economic impacts Lowrance,R.,G.Vellidis,R.D.Wauchope,P.Gay and of protecting rivers, trails and greenway corridors:A D.D.Bosch. 1997. Herbicide Transport in a Managed resource book. San Francisco: National Park Service Riparian Forest Buffer System. Transactions of the Western Regional Office. ASAE 40(4): 1047-1057. Neary,D.G.,P.B.Bush and J.L.Michael. 1993. Fate, MacCaulay, S. 1999. Personal communication with Dissipation and Environmental Effects of Pesticides in author, 31 March. Southern Forests: A Review of a Decade of Research Progress. Environmental Toxicology and Chemistry. Magette, W. L., R. B. Brinsfield, R. E. Palmer and 12:411-428. J. D. Wood. 1989. Nutrient and sediment removal by vegetated filter strips. Transactions of the ASAE Osborne, L. L. and D. A. Kovacic. 1993. Riparian 32(2): 663-667. vegetated buffer strips in water-quality restoration and stream management. Freshwater Biology 29: Mallin,M.A. and A.J.Lewitus. 2004.The importance 243-258. of tidal creek systems. J.Exp.Mar.Biol.Ecol. Special Issue 298:145-149. 26 Protecting Riparian Buffers in Coastal Georgia: Management Options Palone, R. S., and A. H. Todd (eds.). 1998. U.S. Department of Agriculture Forest Service. 1997. Chesapeake Bay riparian handbook: A guide for Essential buffers provide economic benefits. Inside establishing and maintaining riparian forest buffers. Forestry(Fall),USDA Forest Service,Rocky Mountain Radnor, Pa.: USDA Forest Service. NA-TP-0297. Research Station. Peterjohn, W.T. and D. L. Correll. 1984. Nutrient U.S. Environmental Protection Agency (U.S. EPA). Dynamics in an Agricultural Watershed: 1996.Liquid assets. Washington, D.C.: U.S. EPA. Observations on the role of a riparian forest. Vought, L.B., M.J. Dahl, C.L. Pedersen and J.O. Ecology 65(5): 1466-1475. Lacoursiere. 1994. Nutrient Retention in Riparian Ecotones. Ambio 23(6): 343-348. Rick Pruetz. 1997. Saved by Development: Preserving Environmental Areas, Farmland and Wenger,Seth. 1999.AReview of the ScientfcLiterature Historic Landmarks with Transfer of Development On Riparian Buffer Width,Extent and Vegetation.Office Rights. Burbank, Calif.:Arje Press. of Public Service and Outreach, Institute of Ecology, University of Georgia. Rhode Island Coastal Zone Buffer Program. 1994. Section 150 Coastal Buffer Zones. Wenger, Seth and Laurie Fowler. 2000. Protecting Stream and River Corridors, Creating Effective Local Schueler, Thomas R. 1997. The Economics of Riparian Buffer Ordinances. Carl Vinson Institute of Watershed Protection. Watershed Protection Government, University of Georgia. Techniques 2(4): 469-481. Wenger, Seth and Mary Freeman. 2006. Stressors to Schiff, K., S. Bay, and C. Stransky. 2002. Imperiled Fishes in the Etowah Basin: Mechanisms, Characterization of stormwater toxicants from Sources and Management under the Etowah HCP. an urban watershed to freshwater and marine Athens,Ga.:River Basin Center,University of Georgia. organisms. Urban Water 4: 215-227. http://www.rivercenteruga.edu/publications/pdf/ stressors_2006.pdf South Carolina Department of Health and Environmental Control, Office of Coastal Resource Young, R. A., T. Huntrods and W. Anderson. 1980. Mgmt. 2002a. Backyard Buffers for the South Effectiveness of vegetated buffer strips in controlling Carolina Lowcountry. Columbia, South Carolina: pollution from feedlot runoff.Journal of Environmental SC DHEC-OCRM. Quality 9(3):483-487. South Carolina Department of Health and Robert L. Zoeckler. 1997. A Summary of Takings Law. Environmental Control, Office of Coastal Resource Resource Paper#5,Atlanta,Ga.:Georgia Environmental Mgmt. 2002b. Vegetated Riparian Buffers and Policy Institute. Buffer Ordinances. Columbia, South Carolina: SC DHEC-OCRM. http://scdhec.gov/environment/ ocrm/pubs/docs/Buffer_Ord.pdf Protecting Riparian Buffers in Coastal Georgia: Management Options 27 Appendix A: Model Coastal Riparian Buffer Ordinance for Georgia's Local Governments Guidance & Recommendations Although several model riparian buffer ordinances have been developed for Georgia's local governments, these models were crafted with freshwater ecosystems in mind and do not take into account the unique resources and issues facing the tidally influenced ecosystems of Georgia's coastal communities. Therefore, there is a need for a model riparian buffer ordinance that meets the specific needs of local governments along Georgia's coast. In working with local governments in Georgia's coastal region and in other areas of the State, several issues and points of confusion regarding riparian buffers have arisen. Below are clarifications regarding three common points of confusion about the role of local governments in maintaining and protecting riparian buffers in light of the 25-foot buffer required by the state Erosion and Sedimentation Control Act. The fourth section is a description of buffer averaging, an optional tool available to local governments for setting buffer width that has been incorporated into this Model Ordinance. The fifth section is an explanation of the buffer encroachment permit, which is a new permit introduced in the Model Ordinance. 1. Local regulation of activities in the statewide 25-foot riparian buffer. Within the 25 ft. riparian buffer established along state waters under the Georgia Erosion and Sedimentation Control Act of 1975 (E&S Act), the Georgia Environmental Protection Division(EPD)has the primary authority to approve or deny a variance request for intrusion into the buffer. In addition, local governments in Georgia that have been certified as local issuing authorities under the E&S Act retain some decision- making authority regarding variance requests in the 25-foot buffer. Op.Att'y Gen. No. 90-40 (1990). The shared state-local responsibility for issuing variances in the state 25-foot buffer works in the following way. The EPD receives all variance requests and first decides whether to deny or issue the variance. If EPD denies a variance request, a local issuing authority with jurisdiction over the property may not issue its own variance and no intrusion into the 25-foot buffer is permitted. However, if EPD issues a variance allowing intrusion into the 25-foot buffer, the local issuing authority has two options: it may allow encroachment into the 25-foot buffer pursuant to the EPD variance, or it may disallow intrusion by issuing a land disturbance permit without allowing for intrusion into the 25-foot buffer. The Georgia Dept. of Natural Resources regulations state it this way: If a variance issued by the [EPD] Director is acceptable to the [local] issuing authority,the variance shall be included as a condition of permitting and therefore becomes a part of the permit for the proposed land disturbing activity project. If a stream buffer variance is not acceptable to the issuing authority,the issuing authority may issue a land disturbing permit without allowing encroachment into the buffer. Ga. Comp. R. & Regs. § 391-3-7-.05(8) (2006). 2. Minor Landscaping Activities. The Erosion and Sedimentation Control Act of 1975 allows for minor land disturbing activities such as home landscaping and gardening within the state 25 ft. buffer through an exemption. No variance request is 28 Protecting Riparian Buffers in Coastal Georgia: Management Options necessary to engage in these activities. However,because the model coastal buffer ordinance intends to protect riparian lands from environmental degradation beyond the purpose of erosion and sedimentation control, its stricter requirements likely fall within the purview of the savings clause in the E&S Act's best management practices provision. This clause states that"nothing shall prevent a local government from adopting...ordinances...which contain stream buffer requirements that exceed the minimum requirements of[the E&S Act]." O.C.G.A. §12-7-6(c) (2006). Furthermore, it is likely within the "home rule" powers of local governments to regulate landscaping activities. The Home Rule clause of the Georgia Constitution gives local governments wide "legislative power to adopt clearly reasonable ordinances, resolutions, or regulations relating to its property, affairs, and local government for which no provision has been made by general law." Ga. Constit.Art. IX, Sec. 2, para. 1. Regulating landscaping activities most likely falls within the boundaries of this wide grant of authority of a local government to regulate its property and affairs. 3. Buffers in areas where bulkheads exist. Local governments may require maintenance of buffers in areas where bulkheads exist. As explained above, because the model coastal buffer ordinance intends to protect riparian lands from environmental degradation beyond the purpose of erosion and sedimentation control, any stricter requirements likely fall within the purview of the savings clause in the E&S Act's best management practices provision. O.C.G.A. §12-7-6(c) (2006). Therefore, regardless of whether the state 25-foot buffer applies to areas in which bulkheads exist, local governments have the ability to require buffers in these areas through adoption of multi-purpose riparian buffer ordinance. 4. Buffer averaging. Providing local governments with a flexible method for delineating riparian buffer width is important for creating a successful ordinance. Often, cases will arise in which it is necessary or ecologically defensible to reduce the buffer width at certain points. This was addressed in the model ordinance by including an optional buffer averaging provision. Buffer averaging is a system that allows for a reduction of the buffer's width at a certain point or points within a single parcel so long as the average buffer width across the entire parcel is the minimum width required by the ordinance. In any case, buffer averaging may not be used to reduce the buffer at any one point to less than the 25-foot State-mandated buffer. Buffer averaging is incorporated into the attached ordinance in Section 5, "Buffer Encroachment Permits." It is recommended that buffer averaging not be used when the width of the buffer is less than 75 feet, because it may result in an unacceptably narrow buffer at a certain point or points within a single parcel. It is essential to clearly establish the conditions under which a buffer encroachment permit for buffer averaging may be issued.A buffer encroachment permit for buffer averaging should be considered in two cases: a)When the width of the buffer as related to the size and shape of the parcel results in a situation in which it is impossible for the property owner to make reasonable economic use of the portion of the parcel not in the buffer. The buffer should be reduced only as much as necessary to allow for reasonable activity, and never less than 25 feet. b)When the width of the buffer as related to the size and shape of the parcel results in a situation in which it is impossible for the property owner to construct a single family dwelling on the portion of the parcel not in the buffer. The buffer should be reduced only as much as necessary to allow for reasonable activity, and never less than 25 feet. Protecting Riparian Buffers in Coastal Georgia: Management Options 29 5. Buffer encroachment permit. Under the Model Ordinance, a landowner should apply for a buffer encroachment permit when he or she desires to encroach into the buffer for the purpose of placing an accessory structure to a residential dwelling, such as a deck, in the buffer. Use of the buffer encroachment permit is also appropriate when the landowner wishes to use buffer averaging. The buffer encroachment permit and the ordinance's variance procedure are intended to be used for two separate situations. If the landowner wishes to encroach for a purpose other than use of buffer averaging or placement of an accessory structure to a residential dwelling in the buffer, use of the variance procedure is the appropriate method. 30 Protecting Riparian Buffers in Coastal Georgia: Management Options Model Coastal Riparian Buffer Ordinance for Georgia's Local Governments Description This model ordinance provides a framework for local governments to establish buffer zones for streams, lakes, coastal marshlands, and freshwater wetlands as well as the requirements that minimize land development within those buffers. It is the purpose of these buffer zone requirements to protect and stabilize stream banks, prevent sedimentation of coastal water resources, protect water quality for important nursery areas for fisheries, and preserve aquatic and riparian habitat. Note All bulleted text with this symbol > and in italics should be interpreted as comments, instructions, or information to assist the local government in tailoring the ordinance. This text would not appear in a final adopted ordinance. Section 1. Intent and Purpose 1) The rivers, streams, wetlands, and coastal marshlands constituting the riparian lands of[local government] are a significant natural resource and are essentially linked to [local government]'s economy. The [Board of Commissioners/City Council] recognizes that these lands provide numerous benefits and are vital to the health, safety and economic welfare of its citizens. The [Board of Commissioners/City Council] finds that buffers adjacent to these lands provide substantial benefits including: a) Minimizing activities that degrade, destroy or otherwise negatively impact the value and function of coastal marshlands; b) Maintaining stream and river water quality; c) Trapping sediment and other pollutants found in surface runoff; d) Promoting bank stabilization and reducing erosion; e) Protecting terrestrial coastal habitat for nesting and feeding wildlife; f) Reducing the impact of flooding by increasing floodwater storage areas; g) Enhancing the marshlands' scenic value and recreational opportunities; h) Protecting property values of individual landowners; and, i) Protecting and restoring greenspace and the natural character of the coastal region; and j) Protecting important nursery areas for fisheries, which provide food and habitat to numerous species of fish and shellfish, including commercially important species. 2) It is therefore the purpose and intent of this ordinance to establish a coastal riparian buffer zone of restricted development and limited land use adjacent to coastal streams, rivers, marshes and wetlands. The purposes of this coastal riparian buffer zone are to: a) Protect the public health, safety, environment and general welfare of the citizens of[local government]; b) Minimize public and private land loss due to erosion, sedimentation, and water pollution; c) Maintain water quality for human use and for protecting the important nursery areas for fisheries, which provide food and habitat to numerous species of fish and shellfish, including commercially important species; d) Protect terrestrial coastal habitat for nesting and feeding wildlife; Protecting Riparian Buffers in Coastal Georgia: Management Options 31 e) Reduce the impact of flooding by increasing floodwater storage areas; f) Protect the natural and native vegetation in the zone; g) Protect the coastal region's visual character and unique natural resources; and, h) Avoid land development within such buffers by establishing buffer zone requirements and by requiring authorization for any land disturbing activities. 3) The standards and regulations set forth in this ordinance are created under the authority of the [local government]'s Home Rule and zoning powers defined in Article IX, Section 2 of the Georgia Constitution. Section 2. Definitions "Access path"means a pervious path designed, constructed, and maintained pursuant to the "Coastal Riparian Buffer Guidance Manual"that provides for access to water dependent uses through the buffer and takes the route that impacts the natural vegetation of the buffer to the least extent possible. "Buffer encroachment permit"means the permit issued by [local government] and required to undertake certain buffer encroaching activities as described in Section 4 herein. "Coastal marshland" or"marshland"means any marshland intertidal area, mud flat, tidal water bottom, or salt marsh within the estuarine area of the [local government] whether or not the tidewaters reach the littoral areas through natural or artificial watercourses. "Vegetated marshlands" shall include those areas upon which grow one,but not necessarily all, of the following: salt marsh grass (Spartina alterniflora), black needlerush (Juncus roemerianus), saltmeadow cordgrass (Spartina patens), big cordgrass (Spartina cynosuroides), saltgrass (Distichlis spicata), coast dropseed(Sporobolus virginicus), bigelow glasswort (Salicornia bigelovii), woody glasswort(Salicornia virginica), saltwort (Batis maritima), sea lavender (Limonium nashii), sea oxeye (Borrichia frutescens), silverling (Baccharis halimifolia), false willow (Baccharis angustifolia), and high-tide bush (Iva frutescens). The occurrence and extent of salt marsh peat at the undisturbed surface shall be deemed to be conclusive evidence of the extent of a salt marsh or a part thereof. Coastal Marshlands Protection Act, O.C.G.A. § 12-5-282. "Coastal riparian buffer" or"buffer"means, on any given parcel of land, a natural or enhanced vegetated area of riparian land lying adjacent to a stream, pond, impoundment, wetland, or coastal marshland. "Estuarine area"means all tidally influenced waters, marshes, and marshlands lying within a tide- elevation range from 5.6 feet above mean tide level and below. Coastal Marshlands Protection Act, O.C.G.A. § 12-5-282. "Impervious cover"means a surface composed of any material that greatly impedes or prevents the natural infiltration of water into soil. Impervious surfaces include, but are not limited to, rooftops, buildings, streets and roads, except those designed specifically to allow infiltration. "Impoundment"means any lake,pond, or other body of freshwater. "Land disturbing activity"means: (1) any installation of impervious cover; (2) any grading, scraping, excavating or filling of land; (3) any construction, rebuilding or significant alteration of a structure that damages or destroys vegetation; (4) any other activity that destroys vegetation in the buffer. 32 Protecting Riparian Buffers in Coastal Georgia: Management Options "Land disturbance permit"means the permit issued by[EPD or local government] pursuant to the Georgia Erosion and Sedimentation Control Act and required for undertaking any land disturbing activity. "Littoral area" means the tidal area between the high water and low water marks. "Native vegetation"means vegetation that is naturally found in the area and is listed in the native vegetation list found in the "Coastal Riparian Buffer Guidance Manual." "Person"means any individual, partnership, firm, association,joint venture,public or private corporation, trust, estate, commission, board,public or private institution, utility, cooperative, state agency, municipality or other political subdivision of this State, any interstate body or any other legal entity. "Riparian land"means any land along the edge of a stream, wetland, coastal marshland, pond or impoundment. "Stream" means any freshwater stream,beginning at: (1) the location of a spring, seep or groundwater outflow that sustains streamflow; or(2) a point in the stream channel with a drainage area of 25 acres or more; or(3) a point in a stream channel with a drainage area of less than 25 acres, if evidence from field studies required by the [local government] verify the existence of a stream. "Wetland"means those areas, which are not coastal marshlands, that are inundated or saturated by surface or groundwater at a frequency and duration sufficient to support, and that under normal circumstances do support, a prevalence of vegetation typically adapted for life in saturated soil. Ga. Comp. R. &Regs. r.391-3-16-.03 (2006). Section 3. Applicability This ordinance shall apply to all land disturbing activity on property containing a coastal riparian buffer. These requirements are in addition to, and do not replace or supersede, any other applicable buffer requirements established under state law. Approval or exemption from these requirements does not constitute approval or exemption from buffer requirements established under state law or from other applicable local, state or federal regulations. 3.1. Grandfather Provisions This ordinance shall not apply to the following activities: 1) Existing development and land disturbance activities as of[the effective date of this ordinance] except that new development or new land disturbing activities on such properties will be subject to all applicable buffer requirements. 2) Any land disturbing activity that is scheduled for permit approval or has been submitted for approval as of[the effective date of this ordinance.] 3) Land disturbing activity that has not been submitted for approval, but that is part of a larger master development plan, such as for an office park or other phased development and that has been previously approved within one year of[the effective date of this ordinance.] After [the effective date of this ordinance], this Ordinance shall apply to all new subdividing and platting activities. Protecting Riparian Buffers in Coastal Georgia: Management Options 33 3.2. Exemptions > It is recommended that the seven exemptions listed below be adopted as part of the local government's ordinance because similar exemptions exist in the Georgia Erosion & Sedimentation Control Act. In Georgia, a local law regulating a particular subject or issue is preempted by a state law that regulates that same subject or issue (unless the state law explicitly allows for local laws on the subject) . Ga. Constit. art. III, sec. VI,para. IV(a). Therefore, if the local law conflicts with the state law, then state law prevails. In this instance, the state law establishing the 25 foot buffer exempts certain activities. Therefore, any local law regulating activities in the 25 foot buffer should contain those same exemptions in order to avoid preemption by the way of conflict. A local government could, most likely, disallow these exemptions in areas of the buffer beyond the first 25 feet without facing the risk of preemption by state law since the state does not regulate activities in buffers beyond 25 feet. The following specific activities are exempt from this Ordinance: 1) Public sewer line easements paralleling the stream, lake, impoundment, wetland, and/or coastal marshlands, except that all easements (permanent and construction) and land disturbance should be at least 25 feet from the mean high water line in coastal marshlands and wetlands or the top of the bank for streams, lakes, and impoundments. This includes such impervious cover as is necessary for the operation and maintenance of the utility, including but not limited to manholes, vents and valve structures. This exemption shall not be construed to allow the construction of roads, bike paths, or other transportation routes in such easements, regardless of the type of paving material used. 2) Land disturbing activities by governments within a road right of way existing at the time this ordinance takes effect, or approved under the terms of this ordinance. Development activities are only allowed if they cannot reasonably be located outside the buffer. 3) Land disturbing activities within utility easements existing as of the effective date of this ordinance or approved under the terms of this ordinance when necessary for the operation and maintenance of the utility, including but not limited to manholes, vents and valve structures. 4) Emergency maintenance and repairs necessary to preserve life and/or property. However, when emergency work is performed under this section, the person performing it shall report such work to the [local government] as soon as possible and within 24 hours of the commencement of the work. Within ten(10) days thereafter, the person shall apply for a variance and perform such work within such time period as may be determined by the [local government] to be reasonably necessary to correct any impairment such emergency work may have caused to the water conveyance capacity, stability or water quality of the protection area. 6) Forestry and silviculture activities on land that is zoned for forestry, silvicultural or agricultural uses, provided these activities are not incidental to other land disturbing activity and are conducted using applicable best management practices. If such activity results in land disturbance in the buffer that 34 Protecting Riparian Buffers in Coastal Georgia: Management Options would otherwise be prohibited, no land disturbing activity other than normal forest management practices will be allowed on the entire property for three years after the end of the activities that intruded on the buffer. 7) Stream crossings for water lines or stream crossings for sewer lines, provided that they occur at an angle, as measured from the point of crossing, within 25 degrees of perpendicular to the stream; cause a width of disturbance of not more than 50 feet within the buffer; and adequate erosion control measures are incorporated into the project plans and specifications and are implemented. > Menu of Options: The following list is a menu containing possible exemptions that local governments may wish to include in its ordinance depending on the community's needs and desires. 1) Activities for the purpose of constructing public water supply intake or public wastewater outfall structures, when designed, constructed and maintained pursuant to the "Coastal Riparian Buffer Guidance Manual." 2) Activities to restore and enhance stream bank stability, vegetation, water quality, and/or aquatic habitat, when designed, constructed and maintained pursuant to the "Coastal Riparian Buffer Guidance Manual." > See the "Coastal Riparian Buffer Guidance Manual" for a list of native vegetation and bioengineering techniques. 3) Any trimming or pruning of vegetation for the purpose of creating a keyhole view corridor and/or access path and conducted in accordance with the "Coastal Riparian Buffer Guidance Manual." This exemption shall not allow for the removal of trees. 4) Creation of an access path to water-dependent uses through the buffer when designed, constructed and maintained pursuant to the "Coastal Riparian Buffer Guidance Manual." 5) Structural maintenance and repair(not replacement or enlargement) of any damaged structure that existed in the buffer as of the effective date of this ordinance,provided the repair is less than fifty (50)percent of the value of the structure, as determined by a local building inspector and is constructed and designed pursuant to the "Coastal Riparian Buffer Guidance Manual." Section 4. Standards and Regulations All land disturbing activity that is not exempt from this Ordinance pursuant to subsection 3.2 above, shall meet the following requirements: Protecting Riparian Buffers in Coastal Georgia: Management Options 35 1) A buffer shall be maintained for a minimum of 75 feet along both banks of streams and along all impoundments, as measured from the top of the bank of the stream or impoundment.All land disturbing activity is prohibited within the 75 foot buffer unless a variance or buffer encroachment permit is granted pursuant to Section 4.3 or Section 4.4 below. 2) A buffer shall be maintained for a minimum of 75 feet along all coastal marshlands, measured horizontally from the estuarine area.All land disturbing activity is prohibited within the 75 foot buffer unless a variance or buffer encroachment permit is granted pursuant to Section 4.3 or Section 4.4 below. 3) A buffer shall be maintained for a minimum of 75 feet along all wetlands as measured from the inland edge of the wetland. All land disturbing activity is prohibited within the 75 foot buffer unless a variance or buffer encroachment permit is granted pursuant to Section 4.3 or Section 4.4 below. > Buffer widths used in this ordinance model are intended as minimums. Local governments are encouraged to adopt wider buffers as necessary to receive the benefits of other buffer services such as increased sediment and pollutant removal, general wildlife and avian habitat,floodwater control, recreational and aesthetic benefits and protection of commercially important fish and shellfish.A description of recommended buffer widths for each of these services is available in the attached document entitled "Protecting Riparian Buffers in Coastal Georgia:Management Options. " 4) No septic tanks or septic tank drain fields shall be permitted within the buffer. 5) The establishment of a manicured lawn shall not be permitted in the buffer. 6) The application of herbicides shall not be permitted in the buffer. > Menu of Options: The following is an optional provision that a local government may choose to adopt in addition to the above standards and regulations. This provision establishes a variable-width buffer. 7) A buffer shall be maintained for feet along all high value areas. High value areas include [those designated by the local government]. > Under a variable width buffer ordinance, the local government requires a wider buffer adjacent to aquatic areas that the local government designates as having high value. In all other areas, the buffer width is set by Section 4 (1), (2), and(3) above. Examples of areas that a local government may wish to designate as high value include: small, headwater tidal creeks that have high value as nursery grounds for fish and shellfish in certain seasons; oyster habitat; endangered species habitat and; streams or creeks listed on the Clean Water Act§303(d) list for non-compliance with water quality standards (other than sediment). The width of the buffer in high value areas is determined by the local government. Please refer to the document entitled "Protecting Riparian Buffers in Coastal Georgia:Management Options, "for suggested buffer widths. 36 Protecting Riparian Buffers in Coastal Georgia: Management Options Section 5. Buffer Encroachment Permit 5.1 General 1) No person shall conduct any land disturbing activity within the coastal riparian buffer without first obtaining a buffer encroachment permit from the [local government] to perform such activity. 2) Buffer encroachment permits may be issued by the [local government] only if the land disturbing activity constitutes one of the following activities: > Menu of Options: The following is a list of options from which a local government may choose when determining the activities for which it wishes to require citizens to obtain a buffer encroachment permit. a) construction of a porch, deck,boardwalk, or similar structure that is an accessory use to a residential dwelling, constructed and designed in accordance with the "Coastal Riparian Buffer Guidance Manual"; > For boardwalks that will extend into the coastal marshlands, landowners must first receive a permit or license, whichever is applicable,from the Coastal Marshlands Protection Committee before applying for a buffer encroachment permit. b) any other land disturbing activity that results in a reduction in buffer width over a portion of a parcel, in exchange for an increase in buffer width elsewhere on the same parcel,provided that the average buffer width on the entire parcel is 75 feet and the buffer width at any given point on the parcel is not less than 25 feet. 3) The following factors will be considered in determining whether to issue a permit: a) whether the buffer encroachment will result in a reduction of the quality of the water exiting the parcel, or a diminishment of a uniform coastal marshland scenic vista; b) whether the proposed development in the buffer will be conducted in accordance with all design guidelines, low impact development techniques, and other guidance found in the "Coastal Riparian Buffer Guidance Manual;" c) whether the proposed intrusion into the buffer is the minimum intrusion necessary to accomplish the purpose of the intrusion; d) whether a feasible alternative design exists that would result in no intrusion into the buffer; e) when the permit is sought pursuant to subsection 5.1 (d), whether the width of the buffer as related to the size and shape of the parcel results in a situation in which it is impossible for the property owner to make reasonable economic use of the portion of the parcel not in the buffer; and f) when the permit is sought pursuant to subsection 5.1 (d), whether the width of the buffer as related Protecting Riparian Buffers in Coastal Georgia: Management Options 37 to the size and shape of the parcel results in a situation in which it is impossible for the property owner to construct a single family dwelling on the portion of the parcel not in the buffer. 5.2 Application Requirements and Procedures 1) The application for a buffer encroachment permit shall be submitted to the [local government] and must include the following: a) A site plan showing: • The location of all riparian lands on or immediately adjacent to the property; • Identification of any streams found on the Clean Water Act § 303(d) list that are adjacent to the property; • Boundaries of the riparian buffer, as described by Section 4 of this Ordinance, on the property; • Buffer zone topography with contour lines at no greater than five (5)-foot contour intervals; • Delineation of forested and open areas in the buffer zone; and, • Detailed plans of all proposed land development and land disturbing activity on the site; b) A description of any potential development impact on the buffer and how it will be avoided; c) Any other documentation that the [local government] may reasonably deem necessary for review of the application and to insure that the coastal riparian buffer ordinance is addressed in the approval process; and d) Payment of the application fee of 2) The coastal riparian buffer shall be clearly delineated on all development plans and plats submitted for buffer encroachment permit approval and buffer limits must be staked in the field in a manner approved by the [local government] before and during construction with posted signs that describe allowable activities. Buffer boundaries shall be printed on all development and construction plans,plats, and official maps. 3) All buffer areas must be recorded on the final plat of the property following plan approval. 4) Within [ten] working days of receiving an application for a permit, the [planning department or public works department] shall review it for completeness and notify the public of the application by placing a notice [on its website or in a local newspaper]. If the [planning department or public works department] finds that the application is incomplete, it shall within such [ten] day period, send to the applicant a notice of the specific ways in which the application is deficient, with appropriate references to the applicable sections of this ordinance. 5) The [planning department or public works department] shall process all buffer encroachment permit applications within [thirty] business days of the [planning department or public works department]'s actual receipt of a completed application and a permit fee. The [planning department or public works department] shall give notice to the applicant of its decision by hand delivery or by mailing a notice, by Certified Mail, Return Receipt Requested, to the address on the permit application on or before the [thirtieth] business day after the [planning department or public works department]'s receipt of the 38 Protecting Riparian Buffers in Coastal Georgia: Management Options completed application. If the jurisdiction fails to act within the [thirty day] period, the permit shall have been deemed to have been granted. 6) In the event the [planning department or public works department] determines that all requirements for approval have not been met, it shall promptly notify the applicant of such fact and shall automatically deny the permit. 7) An individual whose permit application has been denied or a permittee whose permit has been revoked may appeal the decision of the [planning department or public works department] to the [County Commission/City Council] provided that they file written notice of an appeal with the [County/City Clerk] within [fifteen] business days of the [local government]'s decision. Such appeal shall be considered by the [County Commission/City Council] at the next [County Commission/City Council] meeting held after the [county/city's] receipt of the written notice of appeal,provided that notice of appeal is received by the [County Commission/City Council] a minimum of[five] full business days before the meeting. In the event an individual whose permit has been denied or revoked is dissatisfied with the decision of the [County Commission/City Council], they may petition for writ of certiorari to the [superior court] as provided by law. 8) The [planning department or public works department] shall inspect each lot for which a permit for a new land disturbing activity or for modification of an existing land disturbing activity is issued. This inspection shall occur on or before [six months] from the date of issuance of such permit. a) If the land disturbing activity is not complete within [six months] from the date of issuance, the permit shall lapse and become void. No refunds will be made for permit fees paid for permits that expired due to failure to engage in the land disturbing activity. If later, an individual desires to continue land disturbing activities at the same location, a new application must be processed and another fee paid in accordance with the fee schedule applicable at such time. b) If the land disturbing activity is substantially complete, but not in full compliance with this ordinance the [planning department or public works department] shall give the applicant notice of the deficiencies and shall allow an additional [thirty days] from the date of inspection for the deficiencies to be corrected. If the deficiencies are not corrected by such date, the permit shall lapse and become void. Section 6. Inspection The [planning department or public works department] or its authorized representative may inspect on-going work in the buffer to be made periodically during the course thereof and shall make a final inspection following completion of the work. The landowner shall assist the [planning department or public works department] or authorized representative in making such inspections. The [planning department or public works department] shall have the authority to conduct such investigations as it may reasonably deem necessary to carry out its duties as prescribed in this Ordinance, and to enter at a Protecting Riparian Buffers in Coastal Georgia: Management Options 39 reasonable time upon any property,public or private, for the purpose of investigating and inspecting the sites of any land disturbing activities within the buffer protection area. No person shall refuse entry or access to any authorized representative or agent who requests entry for purposes of inspection, and who presents appropriate credentials, nor shall any person obstruct, hamper or interfere with any such representative while in the process of carrying out official duties. Section 7. Variance Procedure Variances from the above buffer requirements may be granted in accordance with the following provisions: 1) Where a parcel was platted prior to the effective date of this ordinance, and its shape, topography, or other existing physical condition prevents land disturbing activity consistent with this ordinance, and such land disturbing activity cannot be authorized through issuance of a buffer encroachment permit, the [local government] may grant a variance that shall allow a reduction in buffer width only to the extent necessary to provide relief from the conditions which prevented land disturbing activity on the parcel, provided adequate mitigation measures are implemented by the landowner to offset the effects of such variance. 2) Variances shall not be considered when: a) following adoption of this ordinance, actions of any property owner of a given property have created conditions of a hardship on that property; or b) the owner previously applied for a buffer encroachment permit that was denied by [the local government]. The buffer encroachment permit and the variance procedure are intended to be used for two separate situations. A landowner should apply for a buffer encroachment permit when he or she desires to encroach into the buffer for the purpose of placing an accessory structure to a residential dwelling, such as a deck, in the buffer Use of the buffer encroachment permit is also appropriate when the landowner wishes to use buffer averaging. However, if the landowner wishes to encroach for a purpose other than use of buffer averaging or placement of an accessory structure to a residential dwelling in the buffer use of the variance procedure is the appropriate method. 3) Except as provided above, the [local government] shall grant no variance from any provision of this ordinance. 4) When a public hearing on the application for a variance is conducted, the [local government] shall give public notice of each such public hearing in a newspaper of general circulation within the [local government]. The [local government] shall require that the applicant post a sign giving notice of the proposed variance and the public hearing. The sign shall be of a size and posted in such a location on 40 Protecting Riparian Buffers in Coastal Georgia: Management Options the property as to be clearly visible from the primary adjacent road right-of-way. 5) At a minimum, a variance request shall include the following information: a) A site map that includes locations of all streams, wetlands, coastal marshlands, floodplain boundaries and other natural features, as determined by field survey; b) A description of the shape, size, topography, slope, soils, vegetation and other physical characteristics of the property; c) A detailed site plan that shows the locations of all existing and proposed structures and other impervious cover, the limits of all existing and proposed land disturbance both inside and outside the buffer; d) The exact area of the buffer to be affected shall be accurately and clearly indicated; e) Documentation of the inability to develop the property without a variance; f) Documentation that shows how buffer encroachment will be minimized to the greatest extent possible; g) Documentation that shows how the buffer encroachment will not result in reduction of water quality or diminishment of a uniform coastal marshland scenic vista; h) At least one alternative plan, which does not include a buffer encroachment, and an explanation of why such a plan is not possible; i) A calculation of the total area and length of the proposed encroachment; j) A stormwater management site plan, if applicable; and, > A stormwater management site plan may be required if the property is located in a Phase I or II NPDES permitted area pursuant to the federal Clean Water Act or if the local government otherwise requires such a plan. k) A proposed mitigation plan designed pursuant to the "Coastal Riparian Buffer Guidance Manual"that offsets the effects of the proposed encroachment. If no mitigation is proposed, the application must include an explanation of why none is being proposed. > Acceptable mitigation might include restoration and/or enhancement and protection of a degraded area of coastal riparian buffer on an adjacent or nearby property. 1) Payment of the application fee of 6) The following factors will be considered in determining whether to issue a variance: Protecting Riparian Buffers in Coastal Georgia: Management Options 41 a) Whether the requirements of the riparian buffer represent an extreme hardship for the landowner, such that little or no reasonable economic use of the land is available without the reduction of the width of the riparian buffer; b) Whether actions of the landowner of a given property have created conditions of a hardship on that property; c) The size, shape, topography, soils, vegetation and other physical characteristics of the property that may prevent land development; d) The location and extent of the proposed buffer encroachment; e) Whether alternative designs are possible which require less or no intrusion; f) The long-term water-quality impacts of the proposed variance; g) The water quality impacts of any construction that the granting of the variance would allow in the buffer; h) Whether the issuance of a variance and the completion of the applicant's proposal will unreasonably interfere with the conservation of fish, shrimp, oysters, crabs, clams, or other marine life, wildlife, or other resources, including but not limited to water and oxygen supply; and i) whether the proposed development in the buffer will be conducted in accordance with all design guidelines, low impact development techniques, and other guidance found in the "Coastal Riparian Buffer Guidance Manual." > Only the Georgia Environmental Protection Division may approve buffer variances within the 25- foot buffer established along state waters under Georgia's Erosion and Sedimentation Act of 1975. Op.Att'y Gen. No. 90-40 (1990). For purposes of the Erosion and Sedimentation Act of 1975, state waters include, inter alia,ponds, lakes, reservoirs, and coastal marshlands. Op. Att'y Gen. No. 93-7 (1993). > A local issuing authority does not have to allow encroachment into the 25 foot buffer, despite the issuance of a variance by EPD. If a variance issued by the Director is acceptable to the issuing authority, the variance shall be included as a condition ofpermitting and therefore becomes a part of the permit for the proposed land disturbing activity project. If a stream buffer variance is not acceptable to the issuing authority, the issuing authority may issue a land disturbing permit without allowing encroachment into the buffer Ga. Comp. R. &Regs. § 391-3-7-.05(8) (2006). 42 Protecting Riparian Buffers in Coastal Georgia: Management Options Section 8. Compatibility with Other Regulations and Requirements This ordinance is not intended to interfere with, abrogate or annul any other ordinance, rule or regulation, statute or other provision of law. The requirements of this ordinance should be considered minimum requirements. Where any provision of this ordinance imposes restrictions or protective standards different from those imposed by any other ordinance, rule, regulation, or other provision of law, the more restrictive provision applies. The requirements of this ordinance shall in no case be interpreted to preempt the need for other relevant local, state and federal permits and approvals. > All land disturbing activities must comply with the requirements of the Erosion and Sedimentation Act of 1975 and all applicable best management practices therein. > A 100 foot buffer must be maintained along perennial rivers with an average annual flow of at least 400 cubic feet per second pursuant to the Mountain and River Corridor Protection Act, O.C.G.A. 12- 2-8. For purposes of the Act, the 100 foot buffer begins from the river bank at mean high water. This subsection only applies to counties or cities whose jurisdiction extends beyond tidally influenced waters governed by the Coastal Marshland Protection Act. > Construction of docks,piers and marinas are not governed by this ordinance and require permits from the Department of Natural Resources (Coastal Resources Division) and/or Army Corps of Engineers. Permit information can be found at http://crd.dnrstate.ga.us and http://www.usace. army.mil. However, any land disturbing activity encroaching the buffer area associated with construction of a dock,pier, or marina must satisfy the requirements of the ordinance. >Construction of bulkheads, groins, revetments, and any other shoreline engineering activities are not governed by this ordinance and require permits from the Department of Natural Resources (Coastal Resources Division) and/or Army Corps of Engineers. Permit information can be found at http://crd.dnrstate.ga.us and http://www.usace.armymil. However, any land disturbing activity encroaching the buffer area associated with the construction must satisfy ordinance requirements. Section 9. Violations, Enforcement and Penalties Any action, or inaction, which violates the provisions of this ordinance or the requirements of an approved site plan may be subject to the enforcement actions outlined in this Section. Any such action, or inaction, which is continuous with respect to time, is deemed to be a public nuisance and may be abated by injunctive or other equitable relief. The imposition of any of the penalties described below shall not prevent such equitable relief. 9.1. Notice of Violation Protecting Riparian Buffers in Coastal Georgia: Management Options 43 If the [local government] determines that a permitee or other responsible person has failed to comply with the terms and conditions of a permit, an approved stormwater management plan or the provisions of this ordinance, it shall issue a written notice of violation to such permitee or other responsible person. Where a person is engaged in activity covered by this ordinance without having first secured a permit therefore, the notice of violation shall be served on the owner or the responsible person in charge of the activity being conducted on the site. The notice of violation shall contain: 1) The name and address of the owner or the applicant or the responsible person; 2) The address or other description of the site upon which the violation is occurring; 3) A statement specifying the nature of the violation; 4) A description of the remedial measures necessary to bring the action or inaction into compliance with the permit, the stormwater management plan or this ordinance and the date for the completion of such remedial action; 5) A statement of the penalty or penalties that may be assessed against the person to whom the notice of violation is directed; and, 6) A statement that the determination of violation may be appealed to the [local government] by filing a written notice of appeal within thirty(30) days after the notice of violation (except, that in the event the violation constitutes an immediate danger to public health or public safety, 24 hours notice shall be sufficient). 9.2. Penalties In the event the remedial measures described in the notice of violation have not been completed by the date set forth for such completion in the notice of violation, any one or more of the following actions or penalties may be taken or assessed against the person to whom the notice of violation was directed. Before taking any of the following actions or imposing any of the following penalties, the [local government] shall first notify the permitee or other responsible person in writing of its intended action, and shall provide a reasonable opportunity, of not less than 72 hours (except,that in the event the violation constitutes an immediate danger to public health or public safety, 24 hours notice shall be sufficient) to cure such violation. In the event the permitee or other responsible person fails to cure such violation after such notice and cure period, the [local government] may take any one or more of the following actions or impose any one or more of the following penalties. 1) Stop Work Order-The [local government] may issue a stop work order which shall be served on the permitee or other responsible person. The stop work order shall remain in effect until the permitee or other responsible person has taken the remedial measures set forth in the notice of violation or has otherwise cured the violation or violations described therein, provided the stop work order may be withdrawn or modified to enable the permitee or other responsible person to take the necessary remedial measures to cure such violation or violations. 2) Withhold Certificate of Occupancy - The [local government] may refuse to issue a certificate of occupancy 44 Protecting Riparian Buffers in Coastal Georgia: Management Options for the building or other improvements constructed or being constructed on the site until the permitee or other responsible person has taken the remedial measures set forth in the notice of violation or has otherwise cured the violations described therein. 3) Suspension, Revocation or Modification of Permit- The [local government] may suspend, revoke or modify the permit authorizing the land development project. A suspended, revoked or modified permit may be reinstated after the permitee or other responsible person has taken the remedial measures set forth in the notice of violation or has otherwise cured the violations described therein,provided such permit may be reinstated (upon such conditions as the [local government] may deem necessary) to enable the permitee or other responsible person to take the necessary remedial measures to cure such violations. 4) Civil Penalties - In the event the permitee or other responsible person fails to take the remedial measures set forth in the notice of violation or otherwise fails to cure the violations described therein within 72 hours, or such lesser period as the [local government] shall deem appropriate (except, that in the event the violation constitutes an immediate danger to public health or public safety, 24 hours notice shall be sufficient) after the[local government] has taken one or more of the actions described above, the [local government] may impose a penalty on the permitee or other responsible person not to exceed $1,000 (depending on the severity of the violation) for each day the violation remains un-remedied after receipt of the notice of violation. 5) Criminal Penalties -For intentional and flagrant violations of this ordinance, the [local government] may issue a citation to the permitee or other responsible person, requiring such person to appear in [appropriate municipal, magistrate or recorders] court to answer charges for such violation. Upon conviction, such person shall be punished by a fine not to exceed $1,000 or imprisonment for 60 days or both. Each act of violation and each day upon which any violation shall occur shall constitute a separate offense. Protecting Riparian Buffers in Coastal Georgia: Management Options 1+5 The River Basin Center is the public service and outreach office of the University of Georgia Institute of Ecology. The Center's mission is to integrate science and policymaking, particularly relating to the intersection of land use with water quality/quantity and biodiversity issues. Faculty,staff and graduate students include research scientists, policy analysts,outreach specialists,and attorneys.Major projects of the Center include the development of an aquatic habi- tat conservation plan for the local governments of the Etowah River basin,funded by the U.S. Fish &Wildlife Service; and the Initiative for Watershed Excellence: Upper Altamaha Pilot Project,funded by the U.S. EPA and Georgia EPD. For more information about the River Basin Center: UGA River Basin Center 110 Riverbend Road, Room 101 Athens,GA 30602-1510 (706) 583-0%3 • Fax (706) 583-0612 www.rivercenter.uga.edu The UGA Land Use Clinic provides innovative legal tools and strategies to help preserve land,water and scenic beau- ty while promoting creation of communities responsive to human and environmental needs. The clinic helps local governments,state agencies, landowners,and non-profit organizations to develop quality land use and growth man- agement policies and practices. The clinic also gives UGA law students an opportunity to develop practical skills and provides them with knowledge of land use law and policy. For more information about the UGA Land Use Clinic: Jamie Baker Roskie, Managing Attorney UGA Land Use Clinic 110 Riverbend Road, Room 101 Athens,GA 30602-1510 (706) 583-0373 • Fax(706) 583-0612 jroskie @uga.edu This report was funded by the Georgia Department of Natural Resources Environmental Protection Division Coastal Nonpoint Source Program. This report was prepared by the UGA River Basin Center and UGA Land Use Clinic under award# NA05NOS4191212 from the Office of Ocean and Coastal Resource Management, National Oceanic and Atmospheric Administration.The statements,findings,conclusions,and recommendations are those of the author(s) and do not necessarily reflect the views of OCRM or NOAA.