Findings Of Fact Stipulated Facts Jim and Paulette Holzinger own Lot 17, Section B, Long Beach Estates, located on Big Pine Key in unincorporated Monroe County, Florida. The property is south of Long Beach Drive. The property is located within the Florida Keys Area of Critical State Concern. See Sections 380.05 and 380.0552, Florida Statutes. Under these statutes, Monroe County adopted a comprehensive plan and implemented it with land development regulations which are consistent with the Principles for Guiding Development found in Section 380.0552(7), Florida Statutes. The Department of Community Affairs approved the County's comprehensive plan in Rule Chapter 9J-14, Florida Administrative Code, and the Administration Commission approved the comprehensive plan in Chapter 28-29, Florida Administrative Code. The County's comprehensive plan is implemented through its land development regulations, codified as Chapter 9.5 of the Monroe County Code. Monroe County is responsible for issuing development orders for land development in unincorporated Monroe County, including these development orders (building permits). The Local Government Comprehensive Planning and Land Development Act, Chapter 380, Florida Statutes, restricts the County from permitting development which is inconsistent with the Monroe County Comprehensive Land Use Plan, Sections 163.3161(2) and 163.3194(1), Florida Statutes. No person may undertake any development within an area of Critical State Concern except in conformity with Chapter 380; Section 380.05(16), Florida Statutes. After the County issued the three related permits, the Holzingers engaged Pinewood Enterprises, Inc., as general contractor, for the construction of their single-family residence. Those permits were rendered to the Department of Community Affairs on July 21, 1992, and the Department issued its notice of appeal of those permits on September 4, 1992. No party disputes the timeliness of the appeal. The Holzingers' lot is vegetated by mangroves, transitional plant species, and beach berm plant species. The site plan, and which was part of the Holzingers' application for the permits, which Monroe County approved, includes the approval of dredging of a portion of Lot 17 and the placement of fill on site to provide driveway access to the single-family residence. The site plan locates the single-family residence in an area of Bay Cedar thicket. The mangroves are located along the north of the lot along Long Beach Drive. Facts Found Based on Evidence Adduced at the Final Hearing The Holzingers' lot is located at the southernmost area of Big Pine Key, and is separated from the rest of the key by a wetland to the north of the property. To its south is the Atlantic Ocean. The lot is approximately 100' x 230' and contains approximately 22,750 square feet from property line to property line. On the lower keys land elevations only extend from sea level to a maximum of approximately five or six feet above sea level. The soil or substrate conditions on the lot are white calcareous deposits which appear to the untrained eye to be sand. It is not quartzite, but deposits from the breakdown of marine grasses or marine algae which have the appearance of sand. There is no caprock on the property. B (1). Habitats Recognized in the Monroe County Plan The Monroe County Comprehensive Development Plan is based upon the Data and Analysis found in volume 1 of the Plan. According to that Data and Analysis, there are different types of habitat found in the Keys. These include salt marsh, salt marsh and buttonwood association, mangrove community, tropical hardwood hammock, and beach berm complex. The most significant one here is beach berm complex; it includes: "bare, sandy shoreline with a mound or ridge of unconsolidated sand that is immediately landward of and usually parallel to the shoreline and beach. The sand is calcareous material that is the remains of marine organism such as corals, algae and mollusks. The berm may include forested costal ridges and may be colonized by hammock vegetation." Section 9.5-4(B-3), Monroe County Code [the land development regulations]. In the Data and Analysis, the County records that on Long Beach Key the most landward area of the berm is tropical hardwood hammock. The low hammocks are upland hardwood forest communities containing species such as blolly, buttonwoods, darling plums, spanish stopper and wild dilly, all of which are found on the vegitation survey of the lot done by a biologist for Mother Nature's Enterprises, Linda Pierce, as part of the Holzinger building permit application. See Section 9.5-4(L-10), Monroe County Code, which defines low hammocks. Low hammocks include berm hammock, and the beach berm association described in the County comprehensive plan includes berm hammocks (Tr. 184). B (2). The Land Use Maps and their Designations The existing conditions map which is part of the Monroe County comprehensive plan designates the area of the Holzingers' property as beach berm association. That map is drawn at the sale of one inch equals 2,000 feet. Similar aerial maps at a scale an order of magnitude smaller (one inch equals 200 feet) also show the land as beach berm with fringing mangroves. These aerial photographs have been overlaid with the Comprehensive Plan's habitat designations for use in the practical application of the land development regulations by County employees. Under the land use regulations found in the Monroe County Code, the County Commission is required to follow the existing conditions map it adopted, Section 9.5-227, Monroe County Code. Under the first paragraph of Section 9.5- 345 the environmental design criteria applicable to development of a parcel of land depend upon the habitat designated for the parcel on the existing conditions map (the map drawn at the larger scale of one inch equals 2,000 feet). Ground proofing of the habitat on the lot done by the Lower Keys' biologist, Diana Stephenson, and by the Department of Community Affairs planner/biologist, Kathleen Edgerton, show that the land is actually beach berm from the ocean to the mangroves, and there is a small area of disturbed saltmarsh landward from the mangroves to the county road which runs down the center of the key. I am not persuaded by the testimony of the biologist for the Holzingers, Mr. Smith, who believes that there is a separate tropical hardwood hammock habitat on the Holzingers' lot. A full habitat analysis would have been required if there were mixed habitats on the lot (Tr. 88, 96) and the Holzingers did not submit one to the County as part of their application. Because the County biologist found no separate low hardwood hammock habitat on the lot, she believed that no habitat evaluation index was required in processing the Holzinger application, and none was done independently by the County. Mr. Smith contended at final hearing that there are several distinct habitats on the single lot. Moving south from Long Beach Drive toward the ocean he first finds a disturbed saltmarsh of approximately 4,000 square feet; then a mangrove community of about 2,500 square feet; then a saltmarsh and buttonwood association of about 2,500 square feet; next a tropical hardwood hammock of moderate quality and finally, closest to the ocean, beach berm complex. This analysis, which designates a separate saltmarsh and buttonwood association waterward of the mangrove community, and then a separate tropical hardwood hammock waterward of the saltmarsh and buttonwood association, fails to give significant weight to the fact that low hammocks are typically found within beach berm complex. While Mr. Smith testified to the square footages for each of the five habitats, he only performed rough calculations for their size, he was not working with, nor did he perform an actual survey which would define the boundaries of the various habitats he believes are present. He readily acknowledged his preliminary habitat analysis was incomplete. Moreover, accepting for the sake of argument that there is a mixed habitat on the lot under the evidence adduced by the Holzingers, a complete habitat evaluation index should have been performed by the Holzingers as a necessary part of their application, since the County biologist did not do one in the belief there was no need for one. The essential problem with the view expressed by Mr. Smith that there are five habitats on this 100-foot lot is his contention that due to the very small changes in elevation through the Keys, one must identify different habitats recognized in the Monroe County comprehensive plan and land development regulations by assessing the predominance of different types of vegitation typical of a habitat. To Mr. Smith, if the vegitation is of a type normally found in a tropical hardwood hammock, and it predominates over the other vegitation, that area must be classified as a tropical hardwood hammock. At that level of generalization, the statement is no doubt true. Neither the land development regulations or the County's Comprehensive Plan require, or even permit, a microanalysis of the vegitation for the purpose of defining multiple habitats on a lot. Taking a broad view, such as that embodied in the existing conditions map, the predominate vegetative and soil conditions on the southern part of the island where Lot 17 is located are consistent with the categorization as beach berm association. The same is true using the aerial maps on which the different habitat designations from the land development regulations have been overlaid. What Mr. Smith has done is to look for small areas within the 100' x 230' parcel to identify areas where tropical hardwood species may be said to "predominate." The obvious purpose of Mr. Smith's division of the lot into small areas is to be able to characterize these uplands species as "predominating." This is essential to justify intensive use of the property. The comprehensive plan and the land development regulations do not permit any use of areas colonized by mangroves, which are wholly protected by a 100 percent open space requirement. This means that 100 percent of the area colonized by mangroves must be maintained in its natural condition and free and open to the sky, Section 9.5-343, Monroe County Code. Open space ratio for saltmarsh and buttonwood associations is .85 but for moderate quality low hammocks is only .60. Beach berm association is highly protected, with an open space requirement of 90 percent. Only 10 percent of the land area waterward of the mangrove habitat, therefore, can be covered with the footprint of the single-family residence and any associated driveway or other access way because it is beach berm complex. Accepting the mangrove line contained in the vegitation assessment submitted by the Holzingers in their application done by Mother Nature's Enterprises, and then using a "planimeter" to measure the area from the mangrove line to the mean high water line on the lot, there is 16,594 square feet of property. Given the 90 percent open space requirement, a very small area of 1,659 square feet may be covered with the footprint of the single-family home, including its porch, eaves, and driveway. The footprint of the house, its porch, and driveway shown on the site plan approved by the County, with the addition of a five-foot clearing zone around the footprint of the house [because it is essentially impossible to clear land only to the footprint of the completed building] reveals that the County's permits would allow the clearing of 2,880 square feet. Even without the five-foot construction zone around the house, porch and driveway, the County permits allow the clearing of 2,172 square feet. It is very difficult to understand how the Monroe County official in charge of the office which issues building permits could have determined that the development proposed by the Holzingers was permittable. That official did not testify. The County biologist for the Lower Keys who did testify, Ms. Stephenson, was adamant that the project was never permittable under the Monroe County land development regulations. The only explanation by which the permit conceivably could have been granted would be to do something the land development regulations do not permit: aggregate the square footage which the code makes available for development on the landward side of the mangroves, in the area of disturbed saltmarsh between the road and the mangroves, and add the usable square footage for that habitat area to the usable square footage on the waterward side of the mangroves, in the beach berm association. But the amount of each habitat which must remain as open space is determined for each habitat type. They cannot be aggregated across habitats, to give some total usable number of square feet, to be cleared anywhere on the property. That would ignore the significance of the separate habitat designations. The 1,659 square feet available for development in the beach berm association must be used only within that habitat, and square footage available for development within the disturbed salt marsh cannot be added to it. Fill Issues The site plan approved by the County permits fill to be used to construct a driveway on the property through the mangrove area and the beach berm area. This is simply an error on the part of the County, for no party disputes that fill is forbidden in these areas. The performance standards in the land development regulations do permit certain piers, docks, utility pilings and walkways over mangrove areas, but no fill is permitted. Section 9.5- 345(m)(1), Monroe County Code (Tr. 139). The Holzingers could receive a permit to build a raised bridge over the mangroves for access to the beach berm association portion of the lot, as has been done on a nearby lot to the west of the Holzingers' lot. They cannot, however, fill the mangroves to create the driveway shown on the site plan the County approved. The building permit the County granted which purports to allow fill in mangrove areas is inconsistent with the County's own land development regulations and cannot stand. The next question is whether there is some alternate means of access to the lot which can be used instead of that permitted. At the final hearing Mr. Smith stated that on a recent visit to the Holzingers' property, he found an old road on the east side of the property which is high land which could serve as a location for a driveway or accessway to the interior of the Holzingers' property. There is, however, actually no old road anywhere on Lot 17. There was an old road on Lot 16, and a bit of the spoil from that road may be found on Lot 17, but there simply never has been a road on the Holzingers' lot which they can use for a driveway. Fill will be required to locate any driveway, and that is inconsistent with the County land development regulations. The only thing the Holzingers can do to overcome this problem would be to build a bridge over the mangrove area and completely avoid the use of any fill. Summary of Findings The scarified or a disturbed saltmarsh area from the county road to the mangrove area is too small to be useful. The Holzingers do not plan to build in that area. Whatever portion of that area which is not required to be open space cannot be "banked" to allow additional clearing in the beach berm association on the waterward side of the mangroves. For all practical purposes, that disturbed saltmarsh area adds nothing to the buildable or clearable area on Lot 17. The mangrove area has a 100 percent open space requirement. Mangroves are a highly protective habitat, which contribute nothing to the buildable area on Lot 17. The remaining portion of the Lot 17 waterward from the mangrove area to the mean high water line is too small to permit the construction and erection of the house and driveway permitted by the development orders (building permits) issued by Monroe County. The buildable area in the beach berm association is no more than a total of 1,660 square feet for the house, its porch, the driveway. The County has issued a permit to use 2,880 square feet of that habitat (including an allowance for a construction zone), or at least 2,172 square feet, assuming the location of the house, porch, and an eight-foot wide driveway and no construction clearing around the footprint around the house/porch. This fails to meet the 90 percent open space requirement found in the Monroe County Code. The building permits issued by Monroe County to the Holzingers are therefore invalid. To obtain valid permits, the Holzingers must substantially reduce the footprint of the house, including an allowance for a construction clearing zone. A house that small may be undesirable, but it could be permitted. What the County has attempted to permit, however, is invalid under its own regulations.
Recommendation It is RECOMMENDED that development approval for the subject lot be denied, unless the applicant presents, and the County and the Department approve, a revised permit and site plan which demonstrates compliance with the mandatory open space requirements for the beach berm and mangrove habitats, and which eliminates the placement of fill in the beach berm complex and the mangrove wetlands on site. DONE AND ENTERED in Tallahassee, Leon County, Florida, this 9th day of July 1993. WILLIAM R. DORSEY, JR. Hearing Officer Division of Administrative Hearings The DeSoto Building 1230 Apalachee Parkway Tallahassee, Florida 32399-1550 (904) 488-9675 Filed with the Clerk of the Division of Administrative Hearings this 9th day of July 1993. APPENDIX The Findings of Fact proposed by the Department have been generally adopted, although the long quotation from Volume I and II of the County Comprehensive Plan are not essential or necessary. See proposed finding 10. The Respondents submitted no proposed Findings of Fact. COPIES FURNISHED: Stephanie M. Callahan Assistant General Counsel Department of Community Affairs 2740 Centerview Drive Tallahassee, Florida 32399-2100 Theodore W. Herzog, Esquire 209 Duval Street Key West, Florida 33040 Linda Loomis Shelley, Secretary Department of Community Affairs 2740 Centerview Drive Tallahassee, Florida 32399-2100 G. Steven Pfeiffer, General Counsel Department of Community Affairs 2740 Centerview Drive Tallahassee, Florida 32399-2100 David K. Coburn, Secretary Florida Land & Water Adjudicatory Commission Executive Office of the Governor 311 Carlton Building Tallahassee, Florida 32301
Findings Of Fact Based on my observation of the witnesses and their demeanor while testifying, the documentary evidence received, including the parties' proposed findings of fact and conclusions of law, the following relevant facts are found. Petitioner owns and operates the Hilton Inn located generally on the southern portion of Clearwater Beach, Florida. Its ownership extends from the seawall in the area under consideration seaward for a distance of fifty (50) feet. The Hilton Inn is situated within an area currently zoned by the City of Clearwater as CTF-28 (high density commercial/tourist). This district provides for a complete range of motel/hotel development with a major emphasis on tourist facilities. The primary permitted uses and structures within the CTF-28 zone district are combination hotel, motel, apartment, and business buildings, apartment houses, townhouse development and restaurants. A number of special exceptions to the permitted uses are authorized within a CTF-28 district. Such exceptions include three types of marina facilities. The special exception granted Petitioner by the Board of Adjustment and Appeal on Zoning is considered to be an exception to construct a marina facility. The immediate area may be generally described as a combination of high- density residential and hotel buildings and structures catering to tourists, part-time, and permanent residents. The most seaward portion of the dock will be approximately 225 feet from the closest point of the channel of Clearwater Pass and the dock itself will be between 250 and 200 feet west of the bridge under which the narrow portion of Clearwater Pass and the swiftest portion of the current flows. The primary concern of the adjacent property owners who testified in the subject hearing is a fear that the proposed dock will block pedestrian traffic along the beach and that persons who use the dock will be in jeopardy due to the swift currents in the adjoining waters. (Testimony of Arthur Marini, James Scalderbank, Frank Marrow, Don Guntherson, and Intervenors Gibson and Miller.) Bill Burchfield, director of the Marine Department, City of Clearwater, is in charge of monitoring docks, bridges, and similar structures for Respondent. Director Burchfield examined the subject application for its navigational impact and determined that the dock, as proposed by Petitioner, would have no discernible adverse impact on navigation.
Findings Of Fact Background Petitioner is incorporated in the State of Florida as a not-for-profit corporation. The corporate purpose of Petitioner includes the improvement of environmental health. Petitioner's activities in this regard are especially focused upon Manatee and Sarasota Counties, including the City of Bradenton (Bradenton). Petitioner has about 2500 members. Members of Petitioner reside in Bradenton. These persons use the water and roads adjacent to Perico Island. Insubstantial evidence suggests that Petitioner, through its members, submitted oral objections to Bradenton at anytime during the planning process. Petitioner mailed a letter dated March 7, 1989, to the Department of Community Affairs (DCA) with a copy sent to Bradenton. The letter clearly constitutes written objections to the proposed plan. Bradenton initially received the March 7 letter on March 9. It is difficult to determine whether Bradenton received a copy of the March 7 letter after the issuance of the Objections, Recommendations, and Comments (ORC) by DCA. Even if Bradenton received a copy of the March 7 letter prior to the issuance of the ORC, it is impossible to determine if Bradenton received another copy of the letter with the ORC, which may contain numerous attachments consisting of the comments of other parties. The ORC was not introduced into evidence. The only indication in the record, including pleadings, of the date of the ORC is in Exhibit 2 attached to the Deposition of Robert Pennock, which itself is City Exhibit 6. Exhibit 2, which is a letter from DCA to Bradenton, mentions the ORC dated March 17, 1989. This date would be at the outside of the range for DCA to submit an ORC in response to a proposed plan transmitted, as in the present case, on November 23, 1988. 9/ By Request for Admission served November 21, 1990, Petitioner requested Bradenton to admit: "that [Petitioner] submitted written objections to [Bradenton's plan] which [Bradenton] received after it received DCA's ORC report." Bradenton's response to the request, in its entirety, states: The City has received a copy of the correspondence relating to possible "objections" to the City's Plan that were mailed directly to [DCA]. The date of that correspondence was March 7, 1989 and addressed to Robert G. Nave, Chief, Bureau of Local Planning, and was written by Attorney Thomas W. Reese. By date stamp on the copy of the correspondence in the possession of the City, it is believed that the document was received on March 9, 1989. The City does not admit that the correspondence of March 7, 1989 from Mr. Reese to Mr. Nave meets the intent of the statute for establishing standing and to the contrary, does not comply and does not establish such standing. The response ignores the portion of the request directed toward the factual question of the order in which Bradenton received the March 7 letter and the ORC. The significance of the chronology, as opposed merely to the acknowledgement of receipt of the March 7 letter, may have been lost upon Petitioner's counsel, who inexplicably asserted in opening statement that the ORC was issued on December 19, 1988. Transcript, page 57. Given the probable chronology of events recited in the preceding footnote, one of the few certainties concerning this matter is that the ORC was not issued on December 19, 1988. Intervenor is a Delaware corporation that owns property in Bradenton. Intervenor owns the western peninsula of Perico Island, which is described in detail below. Intervenor submitted oral or written objections to Bradenton not later than the transmittal hearing on November 23, 1988. Prior to transmitting the proposed plan to DCA, Bradenton removed the coastal high hazard designation from much of the western peninsula of Perico Island and changed the designation of the affected land to ten units per acre. Bradenton is a municipality located in western Manatee County. The city, which straddles the mouth of the Braden River to the east, generally lies along the southern bank of the Manatee River less than three miles upstream from where it empties into lower Tampa Bay. Wares Creek runs from south to north through the center of Bradenton and empties into the Manatee River. Palma Sola Bay divides the majority of the city from Perico Island. The southern half of Perico Island, which consists of eastern and western peninsulas, is within the city limits. Perico Island, which is generally bounded on the west by Anna Maria Sound and Sarasota Pass, is located between Tampa Bay to the north and Sarasota Bay to the south. Barrier islands to the west, most notably Anna Maria Island, tend to protect Bradenton from direct Gulf waves. On August 1, 1989, Bradenton adopted its comprehensive plan (Plan). As Bradenton noted accurately in its cover letter to DCA, no DCA representative attended the final adoption hearing on July 26, 1989, although Bradenton had requested that DCA send a representative to the hearing. 10/ On September 16, 1991, DCA issued a notice of intent to find the Plan in compliance. Designation of Coastal High Hazard Area Data and Analysis The Data and Analysis 11/ contains a Coastal Area Map, which is on page 150 of the Plan. The map depicts those areas below two feet elevation as the Coastal High Hazard Area. The map shows that the Coastal High Hazard Area includes about one-half of the western peninsula of Perico Island and relatively thin strips along the south and east borders of the eastern peninsula of Perico Island. The only other portions of Bradenton designated as Coastal High Hazard Area are parts of islands in the Braden River and two small parcels on the west bank of the Braden River. The Data and Analysis does not further address the Coastal High Hazard Area. In particular, the Data and Analysis fails to explain why the two-foot elevation was selected to define the Coastal High Hazard Area. The Data and Analysis does not mention the location of the Federal Emergency Management Agency velocity zone (V-zone) or the Department of Natural Resources Coastal Construction Control Line. The portion of Perico Island within the city is bounded on the north by State Road 64. Immediately north of State Road 64, the remainder of Perico Island is in unincorporated Manatee County. The Manatee County comprehensive plan designates the entire island north of the road as coastal high hazard area. However, the county plan notes extends the coastal high hazard area to the five- foot contour. The county plan also divides the coastal high hazard area into two areas: the more critical area, which corresponds to the V-zone, that is subject to wave action and the less critical area that is subject to storm- induced damage. Some testimony suggests that the Manatee County plan has more stringent land use constraints for land uses within the V-zone than for land uses elsewhere within the county's coastal high hazard area. Nothing in the record indicates the extent of the V-zone over any part of Perico Island. Early in the consideration by the City Council of the proposed plan, the coastal high hazard area included all land seaward of four feet elevation. The four-foot contour had been selected because of data suggesting that the "spring high tide" runs to an elevation of 3.62 feet, which was rounded up because Bradenton had only one-foot contour maps. By letter dated November 16, 1988, a representative of Intervenor complained that the four-foot contour was "scientifically unjustified and legally unsupportable." The letter states: Only a portion of the westerly peninsula is in the [V-zone] and even that portion of the property could be partially used with proper construction safeguards. The staff position of four feet seems to be based upon the fact that spring high tide occurs at elevation 3.56 feet but no one knows where that elevation occurs on this property nor does anyone know where the elevation 4.0 feet occurs on this property. The relationship between spring high tide and coastal high hazard is likewise unestablished. Bradenton's Chief of Planning and Zoning, Margaret Swanson, testified that the two-foot contour line "definitely" includes the entire V-zone. Deposition of Margaret Swanson, page 48. Jerry West, Bradenton Planning and Development Director and Ms. Swanson's supervisor, testified likewise at the hearing. Transcript, page 90. Petitioner produced no contrary evidence as to the location of the V- zone or the Coastal Construction Control Line. Likewise, there is no evidence that either peninsula has historically experienced destruction or severe damage from storm surge, waves, erosion, or other manifestations of rapidly moving or storm driven water. The spring high tide appears to be an unusual event, perhaps even occurring less often than annually. The evidence fails to link the spring high tide with destruction or severe damage from rapidly moving or storm driven water anywhere in Bradenton. Plan Provisions Coastal Management/Conservation Element (Coastal) Goal 5 states: Use of coastal areas in a way which preserves natural systems, provides for public access, and minimizes storm and flood hazards to population and property, including public facilities. Objective 1: Severely limit development in low lying coastal areas. Policy 1: A coastal high-hazard area shall be established through the Land Use and Development Regulations to include all coastal lands along the Braden and Manatee Rivers and Palma Sola Bay which are below 2 feet in elevation. Policy 2: Establish a conservation zone including all conservation lands as shown on the Future Land Use Map and all undeveloped areas below the Coastal High Hazard Line (2-foot contour line) and prohibit construction of building, roadways and parking areas in that zone except to provide shoreline access points as determined necessary or of overriding public interest by City Council. . . . Policy 3: Prohibit the filling of coastal areas below the 2-foot contour line except in cases where such lands are completely separated from the shoreline by land of higher elevation or where determined necessary or of overriding public interest by City Council. Policy 4: The City shall not locate infrastructure in the Coastal High Hazard Area (below the 2-foot contour line) except as determined necessary or of overriding public interest by City Council. * * * Objective 5: Keep population and investment low in areas vulnerable to coastal flooding. Policy 1: Designate undeveloped coastal acreage with areas below the 8-foot elevation contour line as PDP (planned development project) and limit residential development to low density below the 8-foot contour. Limit non-residential development below the 8-foot contour line to water dependent uses. Policy 2: Locate all public facilities outside of the coastal high hazard area. * * * Policy 4: Discourage the location of high density residential projects, public housing, housing for the elderly, mobile homes and group homes in high priority hurricane evacuation zones through the Land Use and Development Regulations. The Future Land Use Map (FLUM) designates as Conservation all of the land on Perico Island below the two-foot contour. According to Policy 1 under Objective 1 of the Future Land Use Element (FLUE), the "Recreational/Conservation" designation is for "[p]arks, designated open areas and conservation." No residential uses are permitted in the Recreation/Conservation category. The only FLUE goal is: A land use pattern which promotes the well being of the community in regard to compatibility of adjacent uses, building types and residential densities, efficiency of utilities and roadways, harmony with the natural environment and protection from natural hazards. Objective 1: Location of new development and redevelopment in a manner conducive to compatibility of land uses, sensitive to natural resources and natural hazards and consistent with the availability of public facilities. * * * Housing Element (Housing) Policy 1 under Objective 1 is: Designate vacant tracts of land for residential use on the future land use map except where unsuitable for that use because of incompatible adjacent existing uses, inappropriate elevation or drainage conditions or other safety hazard. State Plan Provisions There are no relevant provisions of the State Plan with which the Coastal High Hazard Area is arguably inconsistent. Designation of Ten Units Per Acre on Western Peninsula of Perico Island Data and Analysis The Data and Analysis identifies Perico Island and the islands of the Braden River as the two areas of major environmental concern in Bradenton. The Data and Analysis states: The value of these lands is that they are coastal lands with abundant sea life and habitat. In an urbanized area where much of the natural shoreline has been destroyed, these remaining lands should be protected because of their intrinsic value as well as because of their dwindling supply. Plan, page 157. The Data and Analysis notes that Perico Island is entirely within the 100-year flood zone and is less than five feet above sea level with "large areas" below the mean high water line. The western peninsula of Perico Island is lower than the eastern peninsula. The highest elevation on the western peninsula is five feet, which is within 100 feet of State Road 64. The elevation of most of the upland beyond 100 feet of the road is less than three feet. The elevation of much of the interior of the eastern peninsula is 3-4 feet. Although Perico Island contains Australian Pine and Brazilian Pepper, which are nuisance exotics, the Data and Analysis explains that valuable natural habitat remains: A great diversity of animal and plant life is found on the island[, including roseate spoonbills, brown pelicans, osprey, and an occasional bald eagle]. The mangrove swamps, mud flats, and marine grass flats fringing Perico Island support a variety of marine life including commercial and game fishing species such as mullet, trout, redfish, and snook, as well as shellfish. Plan, page 158. The habitat of the endangered West Indian Manatee includes the coastal areas in question. In addition to the above-noted animal species that are listed as endangered, threatened, or of special concern, the threatened butterfly orchid is also found on Perico Island. The Data and Analysis reports that Palma Sola Bay is a Class II waterbody, which means that it is suitable for shellfishing. Although it has not been approved for such purpose, its waters regularly satisfy Class II standards with only an occasional violation of the Class II bacteriological standards. According to the Data and Analysis, Palma Sola Bay has been designated as part of the Sarasota Bay Estuary of National Significance. Plan, page 98. Both Anna Maria Sound and Palma Sola Bay are part of the Sarasota Bay estuarine system and, as such, are Outstanding Florida Waters. 12/ Concluding its discussion of the two areas of major environmental concern to Bradenton, the Data and Analysis states: As with Perico Island, the Braden River and its wetlands are an invaluable natural resource. Such tidal wetlands not only reduce water pollution by filtering pollutant-laden runoff, but also influence water quantity by retaining water during dry periods and absorbing it during flooding. Wetlands also stabilize the shoreline and act as a hurricane buffer. They provide essential breeding, nesting, resting areas for myriad fish and bird species and support a diverse food web extending to terrestrial animals as well. ... Plan, page 159. The Coastal Vegetation map shows that the portion of the western peninsula corresponding roughly with the Coastal High Hazard Area is vegetated by coastal wetlands with considerable mangrove growth. Plan, page 151. Perico Island is one of "three areas where future development will impact the coastal area." Plan, page 160a. The Data and Analysis notes that an historic shell mound on the western peninsula must be "protect[ed from r]esidential development." However, the designation of the western peninsula at ten units per acre, as necessarily conceded by Mr. West, is not a low density. The Data and Analysis surmises that the impact of future development on at least the eastern peninsula of Perico Island is largely unavoidable: Because of a Development Order issued on a 1975 Development of Regional Impact application, the conditions of development are established and little can be done to modify them to meet the policies of this plan. Id. The Data and Analysis describes the 1975 development order as: authoriz[ing] 1512 dwelling units and a neighborhood commercial center and call[ing] for the preservation of lands below the 1.5 foot elevation and in an historic shell mound on the western peninsula of the site. Development of the western peninsula was prohibited by the approval stipulations. Plan, page 158. At the time of the application for what is known as the Spoonhill Bay DRI, Intervenor or an affiliate of Intervenor owned both peninsulas. After obtaining the development order, Intervenor sold all or part of the eastern peninsula to developers, but retained the western peninsula. The application for development approval was for a total of 1776 units on 102.6 acres. The entire land area was about 546 acres with 171 acres of mangroves conservation, 200 acres of marine conservation, 10 acres of historic preservation, almost 2 acres of neighborhood commercial, 26 acres of lakes, and 35 acres of other open space and recreation. The map accompanying the application shows two sites for historic conservation, both evidently above the two-foot contour line. According to the DRI application, both peninsulas of Perico Island contain about 184 acres above the 1.5-foot contour. The western peninsula encompasses 114 acres with about 10-16 acres higher than 1.5 to 2 feet in elevation. According to the application, the dwelling units per gross acre would be 3.2 and the dwelling units per net acre would be 9.7. The gross acreage density is based on total acres, including mangroves, lakes, and marine conservation. The net acreage density is impossible to calculate from the information provided. 13/ The development order, which was approved May 28, 1975, by the Bradenton City Council, approves the development subject to the following conditions: The developer shall initiate a positive program for the long run protection of the ecologically important undeveloped areas of the site. . . . * * * 3. The applicant shall work in consultation with the State Division of Archives, History and Records Management to insure the protection and preservation of the two sites of historical and archaeological significance found on the project site. Protection of the Indian Mound area shall be by deed, dedication, or other appropriate legal instrument to insure that such sites are preserved in perpetuity. * * * 5. With respect to responsibility for roadway improvements outlined in the transportation section of the DRI report: * * * (d) To further reduce traffic impact of the project, no residential development as originally proposed by the developer will be carried out on the westerly peninsula of the developer's property. ... Total number of residential units as proposed shall be reduced by 15% from 1,778 units to 1,512 units, all to be located on the easterly peninsula. * * * 7. Developer shall furnish at no cost to City not less than one acre site to accommodate governmental services that will be generated by the development, e.g., fire, police, etc. Site location shall be subject to approval of both parties. The Data and Analysis includes among "acreage not presently slated for development . . . 10 acres, western peninsula, Perico Island[,] includes Mangrove areas, low-lying areas and an Indian shell mound." Plan, page 12. However, the Data and Analysis determines that this area is "suitable for development," which means that the land is "above mean high water line and is served by public facilities." Plan, page 14. The soils map shows that the entire western peninsula, as well as the western half of the eastern peninsula, is characterized by nearly level, very poorly drained sandy and organic soils in tidal mangrove swamps. Plan, page 13. The soils of the western peninsula and western half of the eastern peninsula of Perico Island, as well as the soils of the Braden River islands, are the only soils in Bradenton that are generally "very poorly drained" and account for very little of the land area of the city. Both peninsulas of Perico Island are identified as Neighborhood 12.04 in the Plan. In the discussion of Neighborhood 12.04, the Data and Analysis states that a condition of the development order "was that the smaller of the two peninsulas is not to be developed because of environmentally sensitive and historically significant areas as well as traffic impacts." Plan, page 97. The Data and Analysis notes that the two shell middens, which date from "prehistoric times," have been damaged by erosion and amateur excavation. But the Data and Analysis recommends that the Indian mounds be professionally excavated or protected "because of their potential value in adding to the small amount of information available about prehistoric settlements in this area." Plan, page 97. The Data and Analysis notes that approved development has provided 600 units through 1986 at a density of 6.3 units per acre. As of that time, 116 acres were in residential use, one acre in commercial use, and 70 acres were vacant. The Data and Analysis projects that 800 units will have been constructed by 1990. In discussing Neighborhood 12.04, the Data and Analysis reports that no public recreation areas are proposed for the development, which will be served exclusively by private recreation areas. In addition, State Road 64 is the hurricane evacuation route for Perico Island as well as Anna Maria Island, which is also served by another escape route. The discussion of Neighborhood 12.04 concludes with several recommendations. Among them are the following: Require the preservation of and protection of the historic shell middens on the western peninsula if the peninsula is ever developed. Strictly enforce the flood protection ordinance for development of the island. Require mangrove and water quality protection as part of development approvals. Hurricane evacuation and traffic impacts on State Road 64 shall be considered as an important issue in review of applications for development approval. Any applications by property owners to increase the density of development in the neighborhood shall be denied. Participate in the studies of Sarasota and Palma Sola Bays under the National Estuary Program and utilize the recommendations coming forth from that program to the extent possible. Nothing in this Plan shall limit or modify the rights of any person to complete any development that has been authorized as a development of regional impact pursuant to Chapter 380 or who has been issued a final local development order, and development has commenced and is continuing in good faith. Any amendments to the development order for the Development of Regional Impact shall comply with or require compliance with all of the policies of this plan particularly those concerning protection of environmentally and historically sensitive lands, the coastal high hazard area and hurricane vulnerability zone. Plan, pages 98-99. The Evacuation Map shows that all of Perico Island is in Evacuation Zone A. Plan, page 153. This is the highest priority evacuation zone in Bradenton. This zone also encompasses bands of land along the Manatee River and both shorelines of the Braden River. Additional data and analysis are included in the Surface Water Improvement and Management Program for Tampa Bay published on August 30, 1988 (SWIM Plan). The SWIM Plan notes that the Tampa Bay estuary, of which Anna Maria Sound, Palma Sola Bay, and the Manatee and Braden Rivers are a part, suffers from interconnected problems, including habitat destruction (e.g., dredging, filling, hardened shorelines); water quality inclusive of eutrophication (e.g., point and non-point stormwater runoff, municipal and industrial effluents, septage); [and] altered freshwater inputs (e.g., dams, withdrawals). SWIM Plan, page 1. Addressing the functions of area wetlands, the SWIM Plan states: In addition to their contributions to the biology of the marine ecosystems, coastal and estuarine wetlands play an important role in modifying the geologic and hydrographic characteristics of the area. Acting as baffles, roots and leaves reduce the velocity of water over the bottom causing suspended particles to settle out and become trapped at the base of the plants. In this way mangroves, marshes, and seagrasses reduce turbidity, increase sedimentation rates, stabilize sediments, and attenuate wave action on adjacent shorelines. The binding and stabilization characteristics of these habitats are documented by reports of some coastal marshes and seagrass meadows surviving the destructive scouring forces of coastal storms and hurricanes in the Gulf states. SWIM Plan, page 23. However, these wetland systems "face increasing pressure from development of all types," notwithstanding the Warren S. Henderson Wetlands Protection Act of 1984. SWIM Plan, page 27. The water quality is directly threatened by the nutrients introduced into the water by, among other things, untreated stormwater runoff and the "extensive transformation of rural uplands to urban uses." SWIM Plan, pages 26-27. Plan Provisions The FLUM contains only two residential categories. All of Perico Island above the Coastal High Hazard Area is designated "Residential--maximum 10 units per acre." The other category permits up to 15 units per acre. FLUE Policy 1 under Objective 1 describes the Residential categories as follows: Residential with densities limited to 15 units per acre in the high density area and 10 units per acre in the moderate density area and limited by recommendations by neighborhood in this plan. . . . Neighborhood commercial uses permitted as part of the residential development plan. .. . FLUE Policy 2 under Objective 1 is: The recommendations for each neighborhood contained in this plan are hereby adopted as part of this plan and are to be adhered to in all land use decisions to be made by the City. FLUE Policy 3 under Objective 1 states: The future land use map, neighborhood recommendations and all other relevant policies under this plan are to be used as a basis for the revision of the land use and development regulations, including the zoning atlas. FLUE Objective 3 provides: Management of future development through adoption and enforcement of regulations which promote the use of land in a manner sensitive to public health and safety and to soils and topography. FLUE Objective 4 and relevant policies are: Objective 4: Limitation of population in first priority hurricane evacuation zones identified in the local and regional hurricane evacuation plan. Policy 1: Deny requests for increases in density on property approved for development if the property is located in the first priority regional hurricane evacuation zone. Policy 2: On the Braden River islands, designate as conservation area all lands below the 2 ft. contour line, and allow only recreational/open space or residential use at a gross density maximum of 3 units per acre on the uplands. Coastal Goal 2 is "[i]mprovement of surface water quality." Objective 1 is: "Preservation of water quality cleansing and erosion control capabilities of natural, vegetated shorelines." Policy 4 is to "[r]equire by ordinance by December 1, 1989 best management practices for erosion control during and after land alteration projects." Coastal Objective 2 under Goal 2 is: "Reduction of pollutant loads reaching waterways from urban stormwater." Policy 2 defers to land development regulations the job of establishing standards for new developments to "provide on-site detention and filtration of stormwater runoff to remove oils, silt, sediment, nutrients, and heavy metals, and [to] require erosion control during construction." Coastal Goal 4 provides: "Protection and enhancement of wildlife habitat and vegetation." Objective 1 deals with the Braden River estuary and islands and includes policies restricting development to uplands, generally prohibiting the removal of wetlands vegetation, and requiring that development proceed as a planned development project "to ensure site-sensitive planning and review." No similar provisions apply to Perico Island. Coastal Objective 2 under Goal 4 is: "Preservation of wetlands, including coastal wetlands vegetation, living marine resources and wildlife habitat." Policy 1 states: "[b]y December 1, 1989 adopt regulations to prohibit the removal of wetland vegetation except for limited access points." Policy 2 is, "[b]y December 1, 1989 require that development approvals for land with wetland area stipulate wetland protection measures to ensure that upland construction and land use do no affect the wetlands." Policy 3 states: "[b]y December 1, 1989 adopt regulations to require the identification of wildlife habitats as part of planned development project applications and . . . provide mechanisms to require protection of valuable habitat." Policy 5 provides: "[b]y December 1, 1989 adopt regulations to limit disturbance of seagrass beds by prohibiting development and land uses in seagrass areas and where they will result in an increase in boating in seagrass areas except where necessary to maintain existing facilities." Policy 7 is to develop with Manatee County a management plan for the Braden River estuary, Manatee River, and Palma Sola Bay. Policy 8 is to adopt by ordinance, within six months of their issuance, the recommendations of the Sarasota Bay National Estuary Program. Coastal Goal 6 is: "Fast evacuation prior to natural disasters such as hurricanes." Objective 1 is a "workable evacuation plan, geared toward maintaining present evacuation times." Goal 4 of the Public Facilities Element (PFE) provides: "Prevention of flood damage and improvement of surface water quality." PFE Objective 1 under Goal 4 sets forth the following provisions concerning drainage level of service standards. Policy 1a. The peak discharge rate from new development shall be equal to or less than the peak discharge rate that existed prior to development based on a 25-year frequency, 24-hour duration storm event. * * * Policy 1c. Internal or on-site drainage facilities of developments shall be designed to accommodate the stormwater resulting from a design storm of 10-year frequency, critical duration, based on the project site's time of concentration. Policy 2: The applicability of the level of service standards to various types and sizes of private development shall be set forth in the land use and development regulations adopted by December 1, 1989. PFE Objective 4 under Goal 4 is: "Nondegradation of capacity of natural drainage features." Policy 1 states: All new developments shall be required by land use regulations adopted by December 1, 1989 to provide stormwater retention and drainage facilities to curb increased runoff to natural drainage features. PFE Objective 5 under Goal 4 is: "Upgrading of existing drainage facilities to meet future needs." Policy 1 states: Stormwater facility improvements as proposed in the Comprehensive Stormwater Management Study, 1981 and subsequent updates shall be scheduled into the Capital Improvements program. 14/ State Plan Provisions The relevant provisions of the State Plan are set forth in Findings of Fact Paragraphs 74 et seq. Stormwater Provisions Plan Provisions Already cited above, PFE Goal 4; PFE Objectives 1, 4, and 5, as well as various policies under these objectives; Coastal Goal 2, Objective 2 under Goal 2, Policy 2 under Objective 2; and Housing Policy 1 under Objective 1 address stormwater and drainage. PFE Goal 1 is: Provision of public facilities in a manner which protects investments in existing facilities, promotes orderly, compact urban growth, and promotes the quality of natural resources, particularly surface waters. PFE Objective 1 and Policy 1 under Goal 1 are to maintain the applicable level of service standards for public facilities and not to issue development orders if the issuance would result in a violation of a level of service standard. PFE Objective 2 under Goal 4 is: "Correction of existing stormwater facility deficiencies by the year 2010." Policy 1 is: Stormwater facility improvements as proposed in the Comprehensive Stormwater Management Study 1981 hereby adopted as an appendix to this plan and subsequent updates shall be scheduled into the Capital Improvements program. PFE Objective 3 under Goal 4 is: "Water conservation through use of stormwater runoff for irrigation." SWIM Plan Provisions The SWIM Plan provides as follows with respect to water quality: Initiative 1. Reduce point and non-point source pollutant loadings to attain water quality necessary to restore and maintain healthy and productive natural systems, protect human health, and . . . attain the highest possible water use classification. * * * 1.c. Urban Stormwater Management Strategies: --Reduce the levels of nutrients and other contaminants in urban stormwater runoff by requiring, if feasible, that the quality of stormwater discharges be no worse than the State water quality criteria or the existing quality of the receiving water body, whichever is better. The feasibility of implementing this objective will be examined through a review of federal, state, District, and local rules pertaining to stormwater management. * * * --For all new upland development or redevelopment within the Tampa Bay watershed, runoff rates should not exceed those of natural, undisturbed conditions. The feasibility of implementing this objective will be examined through a review of federal, state, District, and local rules pertaining to stormwater management. Perico Island, Anna Maria Sound, and Palma Sola Bay, as well as the Manatee and Braden Rivers, are within the jurisdiction of the Southwest Florida Water Management District's SWIM program for Tampa Bay. State Plan Provisions Section 187.201(8) addresses water resources. The goal is to "maintain the functions of natural systems and the overall present level of surface and ground water quality." Policy 8 is to "[e]ncourage the development of a strict floodplain management program by state and local governments designed to preserve hydrologically significant wetlands and other natural floodplain features." Policy 12 is to "[e]liminate the discharge of inadequately treated wastewater and stormwater runoff into the waters of the state." Section 187.201(9) addresses coastal and marine resources. The goal includes ensuring that development does not "endanger . . . important natural resources." Policy 4 is to "[p]rotect coastal resources [and] marine resources from the adverse effects of development." Policy 6 is to "[e]ncourage land and water uses which are compatible with the protection of sensitive coastal resources." Policy 7 is to "[p]rotect and restore long-term productivity of marine fisheries habitat and other aquatic resources." Section 187.201(16) addresses land use. The goal is to direct development to those areas that have, among other things, the "land and water resources . . . to accommodate growth in an environmentally sensitive manner." Policy 6 is to "[c]onsider, in land use planning and regulation, the impact of land use on water quality and quantity; the availability of land, water, and other natural resources to meet demands; and the potential for flooding." Section 187.201(22) addresses the economy. The goal is to "promote an economic climate which provides economic stability, maximizes job opportunities, and increase per capita income for its residents." Policy 3 is to "[m]aintain, as one of the state's primary economic assets, the environment, including clean air and water, beaches, forests, historic landmarks, and agricultural and natural resources." Historic Provisions Data and Analysis The Data and Analysis discloses that 85 structures in Bradenton were added to the Florida Master Site File following an historic survey in 1980. As a result of the survey, two historic districts were established: Downtown Bradenton and Old Manatee. The Data and Analysis reports that the Braden Castle ruins and Braden Castle Tourist Camp are included on the National Register of Historic Places. Plan Provisions The sole goal of the Historic Preservation Element (Historic) is: "To preserve Bradenton's architectural heritage as part of the effort to redevelop the old portions of the City." Historic Objective 1 is: "Disseminate information on the historic-architectural resources of the community and of the incentives for preservation and restoration of these resources." Historic Objective 2 is: "Restoration of historic structures and sites." Historic Objective 3 is: "Encourage other governmental agencies to consider historic and architectural value when taking actions affecting such properties in Bradenton and to modify their actions as to enhance rather than detract from these resources." Historic Policies include the dissemination of information pertinent to historic preservation, allowance of exemptions from the building code for certain historic rehabilitation, and cooperation with other governmental agencies in historic preservation efforts. Miscellaneous Provisions Plan Provisions Regarding Level of Service Standard for Recreational Facilities Recreation Element (Recreation) Objective 3 is: Provision of neighborhood parks located within walking distance of population served and having adequate acreage and facilities to serve the size and type of population served. Recreation Policies under Objective 3 include: Policy 1: One acre of neighborhood park per 500 people shall be the level of service standard for recreation. Policy 2: A neighborhood park shall be defined as a parcel of land of a half-acre or more located within a half-mile of the population served and having the following minimum improvements: benches, trees, open or grassy areas and play or exercise equipment facilities geared to the type of population served. Policy 3: Land use and development regulations adopted pursuant to this plan will require new residential development to provide recreation areas which meet the needs of that development based upon the adopted level of service standard for neighborhood parks. Such recreations shall serve in lieu of public neighborhood parks for new development. Plan Provisions Regarding Scheduling of Capital Improvements Necessary to Attain Level of Service D for Roads There are no roads identified in the Traffic Circulation Element (Traffic) for which Bradenton has jurisdiction that are projected not to achieve a level of service of D or better. The Data and Analysis states that seven road segments in Bradenton will attain a level of service standard worse than D during the planning timeframe. Plan, pages 125-27. However, the Data and Analysis indicates that the federal, state, or county has jurisdiction over each of these segments. Plan, page 114. Ultimate Findings of Fact Designation of Coastal High Hazard Area Petitioner has failed to prove to the exclusion of fair debate that the designation of the Coastal High Hazard Area is inconsistent with the criterion of supporting data and analysis. The Data and Analysis fails to indicate whether the Coastal High Hazard Area encompasses at least the V-zone or the land seaward of the Coastal Construction Control Line. However, Petitioner has failed to prove that the Coastal High Hazard Area excludes any part of the V-zone or the land seaward of the Coastal Construction Control Line. Testimony suggests that the Coastal High Hazard Area includes at least the V-zone. Petitioner has failed to prove to the exclusion of fair debate that the designation of the Coastal High Hazard Area is inconsistent with the criterion of the use of available appropriate data concerning historic damage and scientifically predicted damage of moving or storm driven water. The record contains no substantial evidence as to qualifying damage or destruction to areas outside the V-zone or landward of the Coastal Construction Control Line. Petitioner has failed to prove that the designation of the Coastal High Hazard Area is inconsistent with Plan provisions to protect coastal resources, protect the public from natural disasters, and maintain and hurricane evacuation times. Likewise, Petitioner has failed to prove that the designation of the Coastal High Hazard Area is inconsistent with provisions of the State Plan concerning housing, public safety, water resources, natural systems and recreational lands, land use, and governmental efficiency. As noted above, Petitioner failed to prove that the designation of the Coastal High Hazard Area is unsupported by data and analysis. Without proof that the designation of the Coastal High Hazard Area is incorrect, Petitioner is unable to prove the inconsistencies identified in the preceding Paragraph. Designation of Ten Units Per Acre on Western Peninsula of Perico Island Petitioner has proved to the exclusion of fair debate that the designation of up 10 units per acre is inconsistent with the criterion of supporting data and analysis, including a land use suitability analysis. The density of ten units per acre is, to the exclusion of fair debate, excessive under the circumstances. The soils are very poorly drained. The land above the Coastal High Hazard Area is very low. Except for 100 feet of frontage along the road, the entire upland will be flooded with the spring tide, which occurs with some regularity if not annually, as well as by flooding associated with hurricanes and tropical storms, even if the water is not storm driven. In the absence of an entirely elevated community, the spring tide and other coastal flooding will render inaccessible any interior residences, as well as inundate interior public facilities, unless natural drainage features and the mangrove fringes of the western island are significantly altered. The low elevation and very poorly drained soils increase the difficulty of effective stormwater management. At the same time, stormwater management is more critical on the island, which is surrounded by Outstanding Florida Waters and, in the case of Palma Sola Bay, Class II waters. The Spoonbill Bay DRI Development Order, which also serves as data and analysis, does not support the designation of ten units per acre for the western peninsula of Perico Island. The Development Order does not expressly transfer development rights from the western to the eastern peninsula. However, the Development Order rejects a request to develop the western peninsula at a density approximately equal to that accorded the western peninsula by the Plan. The Development Order expressly bases the denial upon transportation considerations. In light of other evidence, including quoted portions of the Data and Analysis, the cited transportation considerations probably included concerns as to the impact of transportation, including attendant stormwater runoff, upon the island's natural resources. In any event, Bradenton chose merely to designate up to ten units per acre on the western peninsula without addressing the bases for its denial, 15 years earlier, of approval to develop any portion of the western peninsula. Petitioner has proved to the exclusion of fair debate that the designation of ten units per acre is inconsistent with Coastal Goal 5, Objective 1 under Goal 5, Objective 5 under Goal 5, and Policies 1 and 4 under Objective 5. Goal 5 is to use coastal areas so as to preserve natural systems and minimize storm and flood hazards, among other things. Objective 1 is to limit development severely in low lying coastal areas. Objective 5 under Goal 5 is to keep population and investment low in areas vulnerable to coastal flooding. Policy 1 under Objective 5 is to limit residential development to low density below the eight-foot contour. Policy 4 is to discourage the location of high density residential projects in high priority hurricane evacuation zones, of which Perico Island is one. The Plan provisions set forth in the preceding paragraph preclude the designation of ten units per acre on the western peninsula. It is irrelevant whether the Plan's density designation is gross, so as to include some combination of Coastal High Hazard Area, mangrove fringe, wetlands, lakes, and Indian mounds, or net, so as to exclude all of such nonbuildable features of the land and waterscape characterizing the western peninsula. Even ten units per net acre is inconsistent with and repugnant to each of the provisions described above. 15/ Petitioner has proved to the exclusion of fair debate that the designation of ten units per acre is inconsistent with FLUE Objective 1; FLUE Objective 4; and Housing Policy 1 under Objective 1. Petitioner has not proved to the exclusion of fair debate that the designation of ten units per acre is inconsistent with FLUE Objective 3 or FLUE Policy 6 under Objective 1, which incorporates into the operative provisions of the plan Recommendation 6 for Neighborhood 12.04. FLUE Objective 1 is to locate new development in a manner sensitive to natural resources and natural hazards. FLUE Objective 4 is to limit population in the first priority hurricane evacuation zones. Housing Policy 1 under Objective 1 is to designate residential tracts except where unsuitable due to inappropriate elevation or drainage or other safety hazard. The designation of ten units per acre, even on a net acreage basis, is inconsistent with FLUE Objective 1 because the new development is not located in a manner sensitive to natural hazards and natural resources. The density designation is also inconsistent with FLUE Objective 4 to limit population in the first priority hurricane evacuation zones. There is no difference whatsoever between the density accorded the western peninsula, which is in Hurricane Evacuation Zone A, and the density accorded large areas of Bradenton, especially just east of Palma Sola Bay, although the latter areas are excluded on the Evacuation Map from any priority evacuation zone. The density designation is also inconsistent with Housing Policy 1 under Objective 1 due to the low elevation and poor drainage associated with the western peninsula. Policy 6 under FLUE Objective 1 incorporates the Recommendations for Neighborhood 12.04, which covers Perico Island. Recommendation 6 is to deny applications to increase the density of development in the neighborhood. FLUE Objective 3 is to manage future development through the adoption and enforcement of regulations to promote the use of land in a manner sensitive to the public health and safety and to soils and topography. Based on the Spoonbill Bay DRI Development Order, the density for the western peninsula may be viewed as zero. No evidence suggests what density the western peninsula may have arguably been accorded by a former comprehensive plan or zoning. However, it is possible to read Recommendation 6 as intending to incorporate the density given the western peninsula by the Plan, so Petitioner has not proved to the exclusion of fair debate that the density designation is inconsistent with Recommendation 6. Petitioner has failed to prove that the density designation is inconsistent with FLUE Objective 3 because of the latter's ineffectiveness. FLUE Objective 3 defers meaningful action to land development regulations and provides no upon real objective upon which an inconsistency determination could be based. Petitioner has failed to prove to the exclusion of fair debate that the Plan is inconsistent with the criterion of an objective to coordinate coastal densities with the local hurricane evacuation plan. FLUE Objective 4 and Policy 1 under Objective 4 address this criterion. Petitioner has proved to the exclusion of fair debate that the Plan does not coordinate with the Spoonbill Bay DRI Development Order. As noted above, the density designation is consistent with Recommendation 6 of Neighborhood 12.04 only because it is assumed that the increased densities prohibited by Recommendation 6 are measured from the point of view of a former plan or former zoning, rather than the zero density accorded the western peninsula by the Development Order. In such a case, Recommendation 6 fails to coordinate with the Development Order. As noted above, the Data and Analysis fails to discuss why the Plan designates ten units per acre for the western peninsula when the Development Order prohibited any development. In effect, the Plan ignores the Development Order, and the resulting inconsistency is material in light of the impact of such a high density upon the natural resources of the peninsula and the public safety of future residents. However, the preceding two paragraphs are relevant only to consideration of the issue whether the density designation is supported by data and analysis. For reasons set forth in Conclusions of Law Paragraph 55, Rule 9J-5.006(3)(b)6., on which Petitioner relies, does not require an objective to coordinate with an DRI. Petitioner has failed to prove to the exclusion of fair debate that the Plan is inconsistent with the criteria of a policy to protect environmentally sensitive land and an objective to protect, conserve, or enhance remaining coastal wetlands, living marine resources, coastal barriers, and wildlife habitat. These criteria are addressed by Coastal Goals 2, 4, and 5 and their objectives, as well as PFE Goal 4, which is to "[p]revent. . . flood damage and improve. . . surface water quality." Petitioner has failed to prove to the exclusion of fair debate that the Plan is inconsistent with the criterion of an objective to direct population concentrations away from accurately defined coastal high hazard areas. For the reasons noted above, Petitioner has failed to prove that the Plan inaccurately defines the Coastal High Hazard Area for Bradenton, In the absence of such evidence, the Recreational/Conservation designation effectively addresses this criterion. Petitioner has failed to prove to the exclusion of fair debate that the Plan is inconsistent with the criteria of an objective to encourage land uses that are consistent with the community's character and future land use and a policy to provide for the compatibility of adjacent land uses. The FLUE Goal, FLUE Objective 1, and Housing Policy 1 under Objective 1 address these criteria. Petitioner has failed to prove to the exclusion of fair debate that the Plan is inconsistent with the criterion of an objective to maintain or reduce hurricane evacuation times between the barrier island and mainland. Coastal Goal 6 and Objective 1 address this criterion, as do FLUE Objective 4 and Coastal Goals 1 and 6, although less directly. Petitioner has proved to the exclusion of fair debate that the Plan is inconsistent with the provisions of the State Plan, construed as a whole. The density designation given the western peninsula of Perico Island conflicts with various provisions of the State Plan designed to protect water, coastal and marine resources, and to promote efficient land uses compatible with land and water resources. Stormwater Provisions Petitioner has proved to the exclusion of fair debate that the stormwater provisions of the Plan are internally inconsistent with Plan provisions concerning water quality protection and improvement. Coastal Goals 2 and 5 protect water quality. Goal 2 is to improve surface water quality. Objective 2 under Goal 2 is to reduce pollutant loads reaching waterways from urban stormwater. Goal 5 is to use coastal areas so as to preserve natural systems. The stormwater provisions are inconsistent with the above-cited provisions protecting water quality because the level of service standard contains a serious loophole. PFE Goal 4, Objective 1, Policy 2 completely undermines the drainage level of service standard by providing that its applicability to "various types and sizes of private development" shall be as set forth in land development regulations adopted by December 1, 1989. For the reasons set forth in Footnote 15 above, relegating to land development regulations substantial provisions required by law to included in a plan is ineffective for reasons involving public participation and notice, compliance review, and enforceability. In effect, the applicability of the drainage level of service standard is subject to land development regulations. The evidence is insufficient to prove to the exclusion of fair debate the inefficacy of the stormwater provisions based on stormwater projects included in the Capital Improvements Schedule. The Data and Analysis discloses that Wares Creek has suffered most extensively from untreated stormwater runoff. However, Table 4 in the Capital Improvements Element discloses that most, if not all, of the scheduled stormwater projects will affect the Wares Creek drainage basin, as defined in the map of Storm Drainage Areas on page 208 of the Plan. 16/ For the reasons set forth in the preceding paragraph, Petitioner has failed to prove to the exclusion of fair debate that the Plan is inconsistent with the criterion of including in the Capital Improvements Schedule projects necessary to achieve treatment of stormwater sufficient to meet relevant water quality standards. Petitioner has proved to the exclusion of fair debate that the Plan is inconsistent with the criterion of a policy demonstrating how the local government will coordinate with the SWIM Plan, especially as to the latter's requirement that all stormwater discharge comply with relevant water quality standards. The Plan's drainage level of service standard, which is seriously undermined in the manner set forth above, is further hampered by the failure of the standard to include post- development water quality standards. As noted in the SWIM Plan data and analysis, the water quality of stormwater runoff is a key factor in preserving the health of the Outstanding Florida Waters that surround Perico Island and in restoring the health of other nearby waters. Due to the failure of the Plan submitted into evidence to contain as an appendix the Comprehensive Stormwater Management Study, 1981, Petitioner has failed to prove to the exclusion of fair debate that the scheduled capital improvements concerning stormwater projects fail to implement the SWIM Plan. In addition, the SWIM Plan does not generally impose project deadlines for various capital improvements. Petitioner has proved to the exclusion of fair debate that the stormwater provisions of the Plan are inconsistent with the provisions of the State Plan, construed as a whole. The failure to incorporate into the Plan an effective level of service standard for post-development runoff rate for all developments and the failure to incorporate any level of service standard for post-development runoff water quality are inconsistent with the above-cited provisions of the State Plan. Historic Provisions Petitioner has failed to prove to the exclusion of fair debate that the Historic Element is inconsistent with the criterion of supporting data and analysis; the Historic goal is internally inconsistent with the Historic objectives and policies; or the Historic provisions are inconsistent with the criteria that objectives be measurable and policies describe how programs and activities will achieve the goals. None of the Historic provisions contradicts any of the Data and Analysis concerning historic resources. The Historic objectives and policies are in no way inconsistent with the Historic goal of preservation. The Historic objectives are measurable, and the policies describe how programs and activities will achieve the goals. Miscellaneous Provisions Petitioner has failed to prove to the exclusion of fair debate that the Plan is inconsistent with the criterion of establishing a level of service standard for recreational facilities. Recreation Objective 3 and Policy 1 establish a level of service standard for recreation by acreage. Policy 2 addresses the facilities that must be constructed for each park used to satisfy the recreational level of service standard. Petitioner has failed to prove to the exclusion of fair debate that the Plan is inconsistent with the criterion of including in the Schedule of Capital Improvements projects necessary to achieve a level of service D for roads. No roads for which Bradenton is fiscally responsible are predicted to attain a level of service standard more congested than D during the planning timeframe.
Recommendation Based on the foregoing, it is hereby RECOMMENDED that the Department of Community Affairs submit the Recommended Order to the Administration Commission for entry of a final order determining that Bradenton's plan is not in compliance for the reasons set forth above. ENTERED this 13th day of February, 1992, in Tallahassee, Florida. ROBERT E. MEALE Hearing Officer Division of Administrative Hearings The DeSoto Building 1230 Apalachee Parkway Tallahassee, FL 32399-1550 (904) 488-9675 Filed with the Clerk of the Division of Administrative Hearings this 13th day of February, 1992.
The Issue The issue to be determined in these consolidated cases is whether the U.S. Army Corps of Engineers (“Corps”) and the City of Sarasota (“City”) (sometimes referred to as “the Applicants”) are entitled to the proposed joint coastal permit, public easement, and sovereign submerged lands use authorization (referred to collectively as “the Permit”) from the Department of Environmental Protection (“DEP”) and the Trustees of the Internal Improvement Trust Fund to dredge sand from Big Sarasota Pass and its ebb shoal and place the sand on the shoreline of Lido Key.
Findings Of Fact The Parties Petitioner Siesta Key Association, Inc. is a Florida Not for Profit Corporation, with its principal place of business in Sarasota. The organization has approximately 1,425 members and represents the interests of those who use and enjoy Siesta Key’s beach and waters. A substantial number of its members have substantial interests in the use of the beach and adjacent waters. Petitioner Michael S. Holderness is a resident and property owner on Siesta Key. Mr. Holderness has substantial interests in the protection of his property and the use of the beach at Siesta Key and adjacent waters. Petitioner Save Our Siesta Sands 2, Inc. is a Florida Not For Profit Corporation, with its principal place of business in Sarasota. The organization has over 700 members and was formed in opposition to the current dredging proposal. A substantial number of its members have substantial interests in the use of the beach at Siesta Key and adjacent waters. Petitioners Peter van Roekens and Diane Erne are residents and property owners on Siesta Key. They have substantial interests in the protection of their properties and the use of the beach at Siesta Key and adjacent waters. Respondent City of Sarasota is an incorporated municipality in Sarasota County. It is a co-applicant for the Permit. Respondent Corps is the federal agency responsible for the Lido Key Hurricane and Storm Damage Reduction Project first authorized by Congress in 1970. Under this Project, the Corps has conducted periodic maintenance, inlet dredging, surveys, and bypassing to protect Lido Key’s shoreline. The Corps is a co-applicant for the Permit. Respondent DEP is the Florida agency having the power and duty to protect Florida’s air and water resources and to administer and enforce the provisions of chapters 161, 373, and 403, Florida Statutes, and rules promulgated thereunder in Titles 62 and 62B of the Florida Administrative Code, which pertain to the permitting of construction activities in the coastal zone and in surface waters of the state. DEP acts as staff to the Board of Trustees of the Internal Improvement Trust Fund. Intervenor Lido Key Residents Association is a Florida Not for Profit Corporation incorporated in 1980 and with its principal place of business in Sarasota. The organization represents the interests of regular users of Lido Key Beach. A substantial number of its members have substantial interests in the use of the beach at Lido Key and adjacent waters. The Project Area Lido Key is a 2.6-mile-long, manmade barrier island constructed in the 1920s, located on the Gulf of Mexico and within the City of Sarasota. North of Lido Key is New Pass, a navigation channel that separates Lido Key from Longboat Key. South of Lido Key is Big Sarasota Pass and the ebb shoal of the pass. Further south is Siesta Key, a natural barrier island. Sediment Transport In the project area, sand generally drifts along the various shorelines from north to south. There can be sand drift to the north during some storm events, currents, and tides, but the net sand drift is to the south. It is sometimes called “downdrift.” Whatever downdrift conditions existed 100 years ago, they were substantially modified by the creation of Lido Key. For decades, the shoreline of Lido Key has been eroding. Since 1964, the Corps has periodically dredged New Pass to renourish the shoreline of Lido Key. The City has also used offshore sand to renourish Lido Key. These renourishment projects have not prevented relatively rapid erosion of the shoreline. A 2.4-mile-long segment of the shoreline of Lido Key has been designated by DEP as “critically eroded.” The Big Sarasota Pass ebb shoal has been growing and now has a volume of about 23 million cubic yards (“cy”) of sand. The growth of the ebb shoal is attributable to the renourishment projects that have placed over a million cy of sand on Lido Key and Longboat Key. The growth of the ebb shoal has likely been a factor in the southward migration of the main ebb channel of Big Sarasota Pass, closer to the northern shoreline of Siesta Key. Most of the west-facing shoreline at Siesta Key has experienced significant accretion. It is unusually wide for a Florida beach. It was named the best (“#1”) beach in the United States by “Dr. Beach,” Dr. Steven Leatherman, for 2011 and 2017. The Project The federally-authorized Lido Key Hurricane and Storm Damage Reduction Project includes the use of New Pass as a supplemental sand source for renourishing Lido Key. However, the use of New Pass is the subject of separate DEP permitting. The project at issue in this proceeding only involves the renourishment of Lido Key and is named “Lido Key Beach Renourishment and Groins.” The Applicants conducted a study of the ebb shoal to determine whether it could be used as a permanent sand source to renourish Lido Key. The study consisted of an environmental feasibility study and an inlet management program for Big Sarasota Pass and New Pass with alternative solutions. The application for the Permit was a response to this study. The proposed sand source or borrow areas are three dredge “cuts.” Cuts B and D are within the ebb shoal. Cut C extends through the ebb shoal and partly into Big Sarasota Pass. Cut C generally follows an existing “flood marginal channel.” The sand from the cuts would be placed along the central and southern 1.6 miles of Lido Key to fill a beach “template.” The design width of the renourished beach would be 80 feet. The initial placement would be wider than 80 feet to account for erosion. The Permit would have a duration of 15 years. The Applicants’ intent is to initially place 950,000 cy of sand on Lido Key. After the initial renourishment, sand would be dredged from one or more of the three designated cuts about every five years to replace the sand that eroded away, and would probably be on the scale of about 500,000 cy. The numerical modeling of the proposed project assumed the removal of up to 1.3 million cy of sand from the three cuts. One of DEP’s witnesses testified that the Permit authorizes the removal of up to 1.732 million cy of sand. The record does not support that testimony. The Applicants did not model the effects of dredging 1.732 million cy of sand from the ebb shoal and pass. There is insufficient evidence in the record to support an authorization to remove more than 1.3 million cy of sand. Although the total volume of sand in the three cuts is 1.732 million cy, it is reasonable for the dimensions of the cuts and the proposed easement that is based on these dimensions to contain more material than is authorized to be removed, so as to provide a margin to account for less-than-perfect dredging operations. Therefore, it is found that the Permit authorizes up to 1.3 million cy of sand to be removed from the designated borrow areas. The findings of fact and conclusions of law in this Recommended Order that address the expected impacts of the proposed project are based on this finding. The Permit also authorizes the construction of two rubble mound groins at the southern end of Lido Key to stabilize the beach and lengthen the time between renourishment events. The groins are designed to be semi-permeable so that they “leak” sand. There are no seagrasses in the renourishment area and mostly scattered and thin patches of seagrass near the dredge cuts. The Permit requires mitigation for the potential direct impacts to 1.68 acres of seagrasses. To offset these impacts, the Applicants propose to create 2.9 acres of seagrass habitat. The seagrass habitat would be established at the Rookery at Perico Seagrass Mitigation Basin in Manatee County, about 16 miles north of Big Sarasota Pass. The Permit incorporates the recommendations of the Florida Fish and Wildlife Conservation Commission regarding protections for turtles, nesting shorebirds, and manatees. The Permit requires regular monitoring to assess the effects of the project, and requires appropriate modifications if the project does not meet performance expectations. Project Engineering The Corps’ engineering analysis involved three elements: evaluating the historical context and the human influences on the regional system, developing a sediment budget, and using numerical modeling to analyze erosion and accretion trends near the project site. A principal objective of the engineering design for the borrow areas, sand placement, and groins was to avoid adverse effects on downdrift, especially downdrift to Siesta Key. The Corps developed a sediment budget for the “no action” and post-project scenarios. A sediment budget is a tool used to account for the sediment entering and leaving a geographic study area. The sediment budgets developed by the Corps are based on sound science and they are reliable for the purposes for which they were used. The post-project sediment budget shows there would be minimal or no loss of sediment transport to Siesta Key. Petitioners did not prepare a sediment budget to support their theory of adverse impact to Siesta Key. Petitioners object to the engineering materials in the Permit application because they were not certified by a Florida registered professional engineer. DEP does not require a Florida professional engineer’s certification for engineering work submitted by the Corps. As explained in the Conclusions of Law, Florida cannot impose licensing conditions on federal engineers. Ebb Shoal Equilibrium Petitioners’ witness, Dr. Walton, developed a formula to estimate ebb shoal volume equilibrium, or the size that an ebb shoal will tend to reach and maintain, taking into account bathymetry, wave energy, tides, adjacent shorelines, and related factors. In an article entitled “Use of Outer Bars of Inlets as Sources of Beach Nourishment Material,” Dr. Walton calculated the ebb shoal equilibrium volume for the Big Sarasota Pass ebb shoal as between 6 and 10 million cy of sand. The ebb shoal has been growing and is now about 23 million cy of sand, which is well in excess of its probable equilibrium volume. The volume of sand proposed to be removed from the ebb shoal is only about six percent of the overall ebb shoal volume. Dr. Walton’s study of the use of ebb shoals as sand sources for renourishment projects supports the efficacy of the proposed project. Modeling Morphological Trends The Corps used a combined hydrodynamic and sediment transport computer model called the Coastal Modeling System, Version 4 (“CMS”) to analyze the probable effects of the proposed project. The CMS model was specifically developed to represent tidal inlet processes. It has been used by the Corps to analyze a number of coastal projects. Dr. Walton opined that the CMS model was inappropriate for analyzing this project because it is a two-dimensional model that is incapable of accounting for all types of currents and waves. However, a two-dimensional model is appropriate for a shallow and well-mixed system like Big Sarasota Pass. Dr. Walton’s lack of experience with the CMS model and with any three-dimensional sediment transport model reduced the weight of his testimony on this point. Petitioners contend that the CMS model was not properly calibrated or verified. Calibration involves adjustments to a model so that its predictions are in line with known conditions. Verification is the test of a model’s ability to predict a different set of known conditions. For calibrating the hydrodynamic portion of the model, the Corps used measurements of water levels and currents collected in 2006. The model showed a 90-percent correlation with water surface elevation and 87-percent correlation to velocity. Dr. Walton believes a model should exhibit a 95-percent correlation for calibration. However, that opinion is not generally accepted in the modeling community. Model verification, as described by Dr. Walton, is generally desirable for all types of modeling, but not always practical for some types of modeling. A second set of field data is not always available or practical to produce for a verification step. In this case, there was only one set of sea floor elevations available for verification of the CMS model. It is the practice of DEP in the permitting process to accept and consider sediment transport modeling results that have not been verified in the manner described by Dr. Walton. The Corps described a second calibration of the CMS model, or “test of model skill,” as an evaluation of how well the CMS model’s sediment transport predictions (morphological changes) compared to Light Detection and Ranging (“LIDAR”) data collected in 2004. The CMS model successfully reproduced the patterns of erosion and sediment deposition within the area of focus. Petitioners’ expert, Dr. Luther, testified that, over the model domain, the CMS model predictions differed substantially from LIDAR data and believes the discrepancies between the model’s predictions and the LIDAR data make the model’s predictions unreliable. Modeling sediment transport is a relatively new tool for evaluating the potential impacts of a beach renourishment project. Renourishment projects have been planned, permitted, and carried out for decades without the use of sediment transport models. Now, modeling is being used to add information to the decision-making process. The modeling does not replace other information, such as historical data, surveys, and sediment budgets, which were heretofore used without modeling to make permit decisions. Sediment transport is a complex process involving many highly variable influences. It is difficult to predict where all the grains of sand will go. Sediment transport modeling has not advanced to the point which allows it to predict with precision the topography of the sea floor at thousands of LIDAR points. However, the CMS model is still useful to coastal engineers for describing expected trends of accretion and erosion in areas of interest. This was demonstrated by the model’s accurate replication of known features of the Big Sarasota Pass and ebb shoal, such as the flood marginal channels and the bypassing bars. The CMS model’s ability to predict morphological trends assisted the Applicants and DEP to compare the expected impacts associated with alternative borrow locations on the ebb shoal and pass, wave characteristics, and sediment transport pathways. Together with other data and analyses, the results of the CMS model support a finding that the proposed dredging and renourishment would not cause significant adverse impacts. The Applicants extensively analyzed sediment transport pathways and the effects of alternative borrow areas on sediment transport to Siesta Key. Petitioners’ hypothesis is not supported by engineering studies of equivalent weight. The more persuasive evidence indicates that sediment transport to downdrift beaches would not be reduced and might even be increased because sediment now locked in the ebb shoal would reenter the sediment transport pathways. In addition, the proposed dredging may halt the southward migration of the main ebb channel of Big Sarasota Pass, and thereby reduce erosive forces on the interior shoreline of north Siesta Key. Wave Energy Petitioners assert that the proposed dredging would result in increased wave energy on Siesta Key because the diminished ebb shoal would no longer serve as a natural buffer against wave energy from storms. They conducted no studies or calculations to support this assertion. Because the proposed dredging would remove a small percentage of the total ebb shoal volume, the ebb shoal would remain a protective barrier for Siesta Key. Wave energy reaching the shorelines along Big Sarasota Pass or within Sarasota Bay would continue to be substantially reduced by the ebb shoal. The predicted increase in wave energy that would occur as a result of the project could increase the choppiness of waters, but would not materially increase the potential for wave-related erosion. Petitioners conducted no studies and made no calculations of their own to support their allegation that the project would significantly increase the potential for damage to property or structures on Siesta Key due to increased wave energy. To the extent that Petitioners’ expert coastal engineer opined otherwise, it was an educated guess and insufficient to rebut the Applicants’ prima facie case on the subject of wave energy. Groins Petitioners contend that the two proposed groins would adversely impact the beaches of Siesta Key because the groins would capture sand that would otherwise drift south and benefit Siesta Key. However, the preponderance of the evidence shows the groins would not extend into or obstruct the sand “stream” waterward of the renourished beach. The historic use of groins to capture downdrift resulted in adverse impacts to adjacent beaches. However, the use of groins in conjunction with beach renourishment to stabilize a renourished beach and without obstructing downdrift is an accepted practice in coastal engineering. The proposed groins would not obstruct longshore sediment transport and, therefore, would not interfere with downdrift to Siesta Key. Public Interest - General Section 373.414(1) requires an applicant to provide reasonable assurance that state water quality standards will not be violated, and reasonable assurance that a proposed activity is not contrary to the public interest. However, if the proposed activity significantly degrades or is within an Outstanding Florida Water (“OFW”), the applicant must provide reasonable assurance that the proposed activity will be clearly in the public interest. Sarasota Bay, including Big Sarasota Pass and portions of Lido Key, have been designated as an OFW. Therefore, the Applicants must demonstrate that the proposed project is clearly in the public interest. In determining whether an activity is clearly in the public interest, section 373.414(1)(a) requires DEP to consider and balance seven factors: Whether the activity will adversely affect the public health, safety, or welfare or the property of others; Whether the activity will adversely affect the conservation of fish and wildlife, including endangered or threatened species, or their habitats; Whether the activity will adversely affect navigation or the flow of water or cause harmful erosion or shoaling; Whether the activity will adversely affect the fishing or recreational values or marine productivity in the vicinity of the activity; Whether the activity will be of a temporary or permanent nature; Whether the activity will adversely affect or will enhance significant historical and archaeological resources under the provisions of section 267.061; and The current condition and relative value of functions being performed by areas affected by the proposed activity. DEP determined that the project is clearly in the public interest because it would improve public safety by providing protection to Lido Key upland structures from storm damage and flooding, protect and enhance wildlife habitat, and provide beach-related recreational opportunities; and it would create these public benefits without causing adverse impacts. Public Interest - Safety Petitioners contend that the proposed project would adversely affect public health, safety, welfare, or the property of others because it would interrupt downdrift and substantially reduce the storm protection provided by the ebb shoal. As found above, the preponderance of the evidence does not support this contention. Public Interest - Conservation of Fish and Wildlife Petitioners contend that the proposed project would adversely affect the conservation of fish and wildlife, including endangered or threatened species. The Permit application materials provided evidence that the proposed project would have no effects, or only minimal temporary effects, on water quality, temperature, salinity, nutrients, turbidity, habitat, and other environmental factors. That was sufficient as a prima facie showing that the project would not adversely affect the conservation of fish and wildlife because, if environmental factors are not changed, it logically follows that there should be no adverse impacts to fish and wildlife. Therefore, as explained in the Conclusions of Law, the burden shifted to Petitioners to present evidence to show that adverse effects to fish and wildlife would occur. It was not enough for Petitioners to simply contend that certain fish species were not adequately addressed in the application materials. With the exception of Dr. Gilmore’s field investigation related to the spotted seatrout, Petitioners conducted no studies or field work of their own to support their allegations of adverse impacts to fish and wildlife. Dr. Gilmore discovered that spotted seatrout were spawning in Big Sarasota Pass. Such spawning sites are not common, are used repeatedly, and are important to the conservation of the species. Spotted seatrout spawn from April through September. The record does not show that the Florida Fish and Wildlife Conservation Commission, the U.S. Fish and Wildlife Service, or the National Marine Fisheries Service were aware that Big Sarasota Pass was a spawning area for spotted seatrout, or considered this fact when commenting on the project. The spotted seatrout is not a threatened or endangered species, but DEP is required to consider and prevent adverse impacts to non-listed fish species, as well as recreational fishing and marine productivity. If the proposed project would destroy a spotted seatrout spawning area, that is a strong negative in the balancing of public interest factors. The Applicants do not propose mitigation for adverse impacts to spotted seatrout spawning. Seagrass sites close to the spawning area are used by post-larval spotted seatrout for refuge. The likely seagrass nursery sites for seatrout spawning in Big Sarasota Pass are depicted in SOSS2 Exhibit 77. The proposed seagrass mitigation at the Perico Rookery Seagrass Mitigation Basin, over 16 miles away, would not offset a loss of this refuge function because it is not suitable as a refuge for post-larval spotted seatrout. The spawning season for spotted seatrout occurs during the same months as turtle nesting season, and DEP argued that the turtle protection conditions in the Permit to limit lighting and prohibit nighttime work, would also prevent adverse impacts to the spotted seatrout. However, spotted seatrout spawning is also threatened by turbidity and sedimentation in the spawning area and adjacent seagrasses. The spotted seatrout spawning area is in the area where dredge Cut B is located. If Cut B were dredged during the spawning season, it would likely disrupt or destroy the spawning site. Reasonable assurance that the proposed project would not disrupt or destroy the spawning site requires that Cut B not be dredged during the spawning season. Seagrasses that are likely to provide refuge to post- larval seatrout are near the most eastern 1,200 feet of Cut C. Reasonable assurance that the proposed project would not disrupt or destroy the refuge function requires that the most eastern 1,200 feet of cut C not be dredged during the spawning season. In summary, the proposed project would adversely affect the conservation of fish and wildlife unless dredging was restricted during the spotted seatrout spawning season, as described above. Public Interest – Navigation, Flow of Water, and Erosion Petitioners contend that the proposed project would adversely affect navigation, the flow of water, and would cause harmful erosion to Siesta Key, but Petitioners conducted no studies or calculations to support this assertion. The preponderance of the evidence shows that no such adverse impacts would occur. Public Interest – Recreational Values Petitioners contend that the proposed project would adversely affect fisheries and associated recreation because of harm to spotted seatrout and other fish species. As found above, the preponderance of the evidence shows the project would adversely affect the spotted seatrout, an important recreational fish species, unless dredging was restricted during the spawning season. Public Interest - Value of Functions Petitioners contend that the proposed project would adversely affect the current condition and relative value of functions being performed by areas affected by the proposed project because dynamic inlet system would be disrupted. As found above, the preponderance of the evidence shows the project would not adversely affect the coastal system. However, it would adversely affect the spotted seatrout spawning and refuge functions provided by Big Sarasota Pass unless dredging was restricted during the spawning season. Mitigation If a balancing of the public interest factors in section 373.414(1)(a) results in a determination that a proposed project is not in the public interest, section 373.414(1)(b) provides that DEP must consider mitigation offered to offset the adverse impacts. Although the Perico Rookery at Seagrass Mitigation Basin is within the OFW and the same drainage basin, it does not fully offset the adverse impacts likely to be caused by the proposed project. The mitigation would not offset the loss of spotted seatrout spawning and refuge functions. The mitigation for the loss of spotted seatrout spawning and refuge functions is unnecessary if the impacts are avoided by restricting dredging during the spawning season as described above. Design Modifications Petitioners contend that the Applicants did not evaluate the alternative of taking sand from offshore borrow areas for the renourishment. The record shows otherwise. Furthermore, as explained in the Conclusions of Law, the Applicants were not required to address design modifications other than alternative locations for taking sand from the ebb shoal and Big Sarasota Pass. Consistency with the Coastal Zone Management Program Petitioners contend that DEP failed to properly review the Permit for consistency with the Florida Coastal Zone Management Program (“FCZMP”), because DEP failed to obtain an affirmative statement from Sarasota County that the proposed project is consistent with the Sarasota County Comprehensive Plan. The State Clearinghouse is an office within DEP that coordinates the review of coastal permit applications by numerous agencies for consistency with the FCZMP. It is the practice of the State Clearinghouse to treat a lack of comment by an agency as a determination of consistency by the agency. With respect to this particular project, the State Clearinghouse provided a copy of the joint coastal permit application to the Southwest Florida Regional Planning Council (“SWFRPC”) for comments regarding consistency with local government comprehensive plans. SWFRPC submitted no comments. In a letter dated June 26, 2015, the State Clearinghouse reported to the Corps that “at this stage, the proposed federal action is consistent with the [FCZMP].” In a written “peer review” of the proposed project produced by the Sarasota Environmental Planning Department in October 2015, some concerns were expressed, but no mention was made of inconsistency with the Sarasota County Comprehensive Plan. Sarasota County sent a letter to DEP, dated August 24, 2016, in which it requested that the Corps prepare an Environmental Impact Statement (“EIS”) for the project. Sarasota County did not indicate in its letter to DEP that the proposed project is inconsistent with any policy of the Sarasota County Comprehensive Plan. Petitioners assert that the proposed project would be inconsistent with an environmental policy of the Sarasota County Comprehensive Plan that Petitioners interpret as prohibiting the proposed dredging. The record contains no evidence that Sarasota County believes the proposed project is inconsistent with this particular policy or any other policy of its comprehensive plan.
Recommendation Based on the foregoing Findings of Fact and Conclusions of Law, it is RECOMMENDED that DEP issue a final order approving the proposed agency actions, but only if the joint coastal permit is modified to prohibit dredging operations in Cut B and the most eastern 1,200 feet of Cut C during April through September. If this modification is not made, it is recommended that the proposed agency actions be DENIED; and The joint coastal permit be modified to clarify that it authorizes the removal of up to 1.3 million cy of sand. DONE AND ENTERED this 8th day of May, 2018, in Tallahassee, Leon County, Florida. S BRAM D. E. CANTER Administrative Law Judge Division of Administrative Hearings The DeSoto Building 1230 Apalachee Parkway Tallahassee, Florida 32399-3060 (850) 488-9675 Fax Filing (850) 921-6847 www.doah.state.fl.us Filed with the Clerk of the Division of Administrative Hearings this 8th day of May, 2018. COPIES FURNISHED: Kirk Sanders White, Esquire Florida Department of Environmental Protection Mail Station 35 3900 Commonwealth Boulevard Tallahassee, Florida 32399-3000 (eServed) Kent Safriet, Esquire Hopping Green & Sams, P.A. Post Office Box 6526 Tallahassee, Florida 32314 (eServed) Alexandrea Davis Shaw, Esquire City of Sarasota Room 100A 1565 1st Street Sarasota, Florida 34236 John R. Herin, Jr., Esquire Gray Robinson, P.A. Suite 1000 401 East Las Olas Boulevard Fort Lauderdale, Florida 33301 (eServed) Eric P. Summa U.S. Army Corps of Engineers Post Office Box 4970 Jacksonville, Florida 32232 Martha Collins, Esquire Collins Law Group 1110 North Florida Avenue Tampa, Florida 33602 (eServed) Thomas W. Reese, Esquire 2951 61st Avenue South St. Petersburg, Florida 33712-4539 (eServed) Richard Green, Esquire Lewis, Longman & Walker, P.A. Suite 501-S 100 Second Avenue South St. Petersburg, Florida 33701 (eServed) Kevin S. Hennessy, Esquire Lewis, Longman & Walker, P.A. Suite 501-S 100 Second Avenue South St. Petersburg, Florida 33701 (eServed) Christopher Lambert, Esquire United States Army Corps of Engineers 701 San Marco Boulevard Jacksonville, Florida 32207 (eServed) Lea Crandall, Agency Clerk Department of Environmental Protection Douglas Building, Mail Station 35 3900 Commonwealth Boulevard Tallahassee, Florida 32399-3000 (eServed) Noah Valenstein, Secretary Department of Environmental Protection Douglas Building 3900 Commonwealth Boulevard Tallahassee, Florida 32399-3000 (eServed) Robert A. Williams, General Counsel Department of Environmental Protection Legal Department, Suite 1051-J Douglas Building, Mail Station 35 3900 Commonwealth Boulevard Tallahassee, Florida 32399-3000 (eServed)
The Issue The issue is whether to approve the City of Gulf Breeze's (City's) application for a Consolidated Wetland Resource Permit and Sovereign Submerged Lands Authorization to conduct a restoration project in Pensacola Bay.
Findings Of Fact Background This dispute involves a challenge by Petitioners to the third phase of a restoration project by the City designed to preserve the Island and protect its historical resources. The project site is located in sovereign submerged lands adjacent to the Island on the southwest side of the Highway 98 Bay Bridge which traverses Pensacola Bay connecting the Cities of Gulf Breeze and Pensacola. The Island is not a true island, but has always been connected to the mainland by a strip of land referred to as an isthmus, which meets the shoreline at Lot 36 of an older subdivision known as the First Addition to Casablanca Parcel No. 1 and platted almost sixty years ago. The isthmus juts out from Lot 36 into Pensacola Bay in a northwesterly direction for several hundred feet before making a 90-degree turn to the southwest where the Island then runs roughly parallel to the shoreline for around a half mile. See Joint Ex. 5-7, 14, and The Island, isthmus, and shoreline form the boundary around a small body of water known as Gilmore Bayou, an ecologically important and pristine salt marsh area. According to aerial photographs, at its widest point, the Island appears to be no more than a few hundred feet wide. Petitioners reside at Lot 37, which is just northeast of the isthmus on the shoreline. The rear part of Lot 37 faces Pensacola Bay and the City of Pensacola to the northwest. Lots 36, 35, and 34 (running to the southwest along the shoreline and facing Gilmore Bayou), are owned by Patricia Moreland, Robert Ozburn, and Intervenor Paul Tamburro, respectively, all of whom testified at the final hearing. Except for Petitioners, the project is supported by virtually all of the residents of the area as well as numerous civic organizations. See Joint Ex. 33. On July 14, 2008, the City filed with the Department its Joint Application for Works in the Waters of Florida, which would allow the City to complete the third phase of the project by (a) planting native submerged vegetation over approximately three acres of sovereign submerged lands, and (b) placing approximately 16,000 cubic yards of fill material and planting native emergent vegetation to stabilize the fill material on sovereign submerged lands at the north end of the Island. See Joint Ex. 3. The Department has authority under chapter 373, Florida Statutes, and Florida Administrative Code chapter 18-21 to approve the application. After an extensive review of the application, on August 9, 2010, the Department issued a Consolidated Notice of Intent to Issue Wetland Resource Permit and Consent to Use Sovereign Submerged Lands, which authorized the proposed project. See Joint Ex. 4. The proprietary authorization (letter of consent) was issued under the authority of rule 18- 21.005(1)(c), which identifies a number of activities that qualify for a letter of consent. In this case, because of the range of proposed activities, the project could qualify for a letter of consent under subparagraphs 8., 15., and 16. of the rule. On September 1, 2010, Petitioners filed their petition challenging the proposed agency action. While their initial pleading raised a number of issues, and cited two rules as a basis for reversing the agency action, these allegations have been substantially narrowed over the course of the proceeding and are now limited to the following: whether the project constitutes management activities associated with the protection of a historic site, thus qualifying for a letter of consent under rule 18-21.005(1)(c)16.; and whether the project unreasonably restricts or infringes upon their riparian rights of navigation, boating, swimming, and view, as proscribed by rule 18-21.004(3)(c). They also question whether Intervenor has standing to participate, but that issue is not dispositive of the primary issues in this case. Petitioners do not contest the issuance of a Wetland Resource Permit. Finally, Respondents and Intervenor question whether Petitioners have standing to initiate this action. The Project Site The project is located on sovereign submerged lands adjacent to the Island, a "naturally occurring sandy beach," as that term is contemplated in rule 18-21.005(1)(c)8. This is true even though portions of the "sandy beach" have eroded over time. The City owns the entirety of the Island. See Joint Ex. 14 and 15. This was not disputed by Petitioners. The Island is a public park, natural preserve, and historic site that is owned and maintained by the City exclusively for public use. Deeds by which the property was conveyed to the City require that it be forever used as a natural preserve and maintained in its natural state. See Joint Ex. 14 and 15. The Island and the area immediately adjacent thereto have a long and significant history dating back to the 1700's. Throughout the 1700's and 1800's, various portions of the Island were used as a careening facility for the repair and maintenance of large vessels. A marine railway was also built. In the late 1800's, a quarantine station was constructed on the Island where people who had contracted yellow fever were isolated. A cemetery exists upon the Island containing the remains of many who perished from the yellow fever epidemic. Also, there were many shipwrecks at the Island, of which some of the remains still exist. Accordingly, there are historic resources and artifacts such as shipwrecks and human remains on and around the Island. The Island has sustained significant erosion over the past 70 years. The northeast shoreline has eroded some 450 to 500 feet during that period of time. There has been a significant loss of vegetation and land mass. Without protection, the Island is in a perilous condition and subject to a permanent breach. The peat bog underlying the Island is vital to the stability of the Island and has been greatly damaged. It requires protective measures, such as those contemplated by the proposed project in order to assure its preservation. Due to the effects of hurricanes and storms, the erosion has substantially increased during the past decade. The erosion has caused the unearthing of and damage to historic artifacts and the salt marsh in Gilmore Bayou. There are clearly visible remnants of the former marine railway on the Island, which are being weakened by current weather events and require protection in order to preserve them. Caskets from the cemetery as well as human bone remains have been unearthed and additional damage will occur without protective restoration efforts. If the erosion continues, there will be more damage to the historic artifacts and the salt marsh will be destroyed. The Project To prevent further erosion and to protect the Island and Gilmore Bayou, the City has applied to the Department for three separate phases of a project to stabilize the shoreline. The first two phases of the project involved the construction of an artificial reef breakwater and the planting of shoreline vegetation. See Joint Exhibit 7a. They have already been approved by the Department and are no longer in issue. The first and second phases were challenged by Petitioners but the cases were eventually settled. See Case No. 09-4870, which involved the second phase. The third phase of the project is being conducted primarily for the maintenance of essentially natural conditions and for the propagation of fish and wildlife. This phase can be described as follows: restoration or nourishment of a naturally occurring sandy beach as contemplated by rule 18-21.005(1)(c)8.; habitat restoration or enhancement as contemplated by rule 18-21.005(1)(c)15.; management activity associated with protection of a park as contemplated by rule 18-21.005(1)(c)16.; management activity associated with protection of a preserve as contemplated by rule 18-21.005(1)(c)16.; management activity associated with protection of a historic site as contemplated by rule 18-21.005(1)(c)16.; and management activity associated with protection of habitat restoration or enhancement as contemplated by rule 18- 21.005(1)(c)16. While the project implicates each of the above provisions, the application and proposed agency action indicate that the letter of consent is granted on the theory that the project is associated with protection of historic sites. See Joint Ex. 4. The third phase is also designed to minimize or eliminate adverse impacts on fish and wildlife habitats and other naturally occurring resources. The project consists of the placement of 16,000 cubic yards of fill material in the area between the existing artificial oyster reef and the shoreline to restore and replace conditions that previously existed. The fill will consist of beach compatible sand that will be approximately six inches to a foot above mean high water. This phase also involves the planting of appropriate native wetland vegetation in the fill area, which will help stabilize the fill. The planting of vegetation in the third phase is separate and distinct from the plantings authorized in the second phase of the project. The project is needed in order to prevent further damage to a public park; public preserve; threatened, endangered, or special concern species of vegetation/habitat; and historic artifacts. These protection efforts were requested and recommended by the Florida Department of State. Petitioners contest only the propriety of the fill materials and the planting of the emergent stabilizing grasses on the fill. The fill portion of the project is located a significant distance from Petitioners' property. The closest portion of the project is estimated to be at least 550 feet from Petitioners' property, while the bulk of the project will take place between some 750 to 1,200 feet from their property. The Proposed Vegetation Planting In the third phase of the project, the City proposes to plant and establish emergent grasses (those that grow in water but partially pierce the surface) and sea grasses, all of which are appropriate native wetland vegetation on the Island. The proposed emergent grasses are Spartina alterniflora (also known as smooth cordgrass) and Juncus roemerianus (also known as black needle rush), which will be used for stabilization of wetlands. The proposed submerged seagrasses are Halodule wrightii (a type of shoal grass) and Ruppia maritime (a type of widgeon grass), which will help stabilize the fill. The smooth cordgrass is native to the Island. It will be planted in the fill area to prevent the fill from eroding. It is expected that once they mature, the height of the plants will not exceed two and one-half feet. Due to the water depth in the area, the shoreline slope, the sediment supply, and the wave action, the smooth cordgrass will not spread outside the proposed project area. Also, it will not interfere with navigation, boating, swimming, fishing, or view. The vegetation will, however, help fishing in the area. The black needle rush is also native to the Island. It will only grow to approximately two and one-half feet in height due to stressful conditions caused by the salt content in the water and wave action. It will not spread beyond the proposed project area and will not interfere with navigation, boating, swimming, fishing, or view. Like the smooth cordgrass, it will enhance fishing in the area. Both Halodule wrightii and Ruppia maritime are native to the Island. Both have slow growth rates, which when coupled with the "high energetics of the system," will hinder their ability to spread outside the project area. Neither seagrass will hinder navigation, boating, swimming, fishing, or view. They will afford a greater opportunity for snorkeling, recreation, and fishing; they will serve as a nursery habitat for finfish and shellfish; they will increase the habitat value of the area; and they will improve water quality. Petitioners submitted no evidence to contradict these findings. They also failed to submit any evidence that the fill material or grasses would spread into any riparian area that might be appurtenant to their Lot 37. The above findings are reinforced by the results of a separate project known as Project Greenshores located across Pensacola Bay from the Island. Project Greenshores involved the restoration of wetlands using dredge material to restore islands that are then protected by the construction of a breakwater and are stabilized by the planting of the same grasses that are proposed for the Island project. The two projects are in relatively close proximity to each other and have essentially the same environment. One difference, however, is that Project Greenshores receives a small source of sediment from stormwater outfalls, which means that it has a higher chance of grasses growing than does the Island. Even with the increased sediment, the grasses at that project have not spread beyond the project area, they have not interfered with navigation, boating, swimming, view, or fishing, and they have enhanced fishing in the area. Historical Artifacts Petitioners contend that the project does not qualify for a letter of consent under rule 18-21.005(1)(c)16. That provision authorizes the Department, acting on behalf of the Board of Trustees of the Internal Improvement Trust Fund, to issue a letter of consent for "management activities associated with . . . historical sites . . . provided there is no permanent preemption by structures or exclusion of the general public." As noted above, the Island has a long and significant history dating back to the early 1700's and there are historic resources and artifacts on the Island. See Finding of Fact 10, supra. When there is an archeological site issue in a permit, the Department typically relies on information from the Division of Historical Resources of the Department of State. See Fla. Admin. Code R. 18-21.004(2)(c)("reports by other agencies with related statutory, management, or regulatory authority may be considered in evaluating specific requests to use sovereignty lands"). Here, the Department relied on information from that agency, which indicates that there are archeological resources at the project site. The Department of State also recommended placing fill over the artifacts to protect them, which will be accomplished by the proposed fill. In addition, the Department relied upon information contained in a survey conducted by Mr. Empie, a registered professional surveyor, to generally show where those artifacts are located. See Joint Exhibit 5, also referred to as the Empie survey. The evidence supports a finding that the project is for management activities associated with historical sites. The record shows that there is strong public support for the project. See Joint Ex. 33. Although many of the artifacts will be covered by the fill, the fill will actually protect them from damage, destruction, theft, and removal. By protecting them, future generations will be able to enjoy the artifacts. No "structures," as that term is defined in rule 18- 21.005(1)(c)16., are part of the project. Therefore, the project will not cause permanent preemption by structures. Contrary to Petitioners' assertion, the project will not exclude the general public from the fill area. The City contemplates that other activities, such as underwater snorkeling, will encourage the public to utilize the project site. The evidence supports a finding that the project qualifies for a letter of consent under this rule. Riparian Lines The Empie survey provides a reasonable depiction of the various riparian lines in the areas adjacent to the proposed project. See Joint Ex. 5. A professional surveyor with the Division of State Lands, Mr. Maddox, agreed that it was a reasonable depiction of the angle of the riparian lines and a "fair distribution of riparian areas," including that of Lot 37. The only property owner adjacent to the Island is Patricia Moreland, who owns Lot 36 and has resided on that parcel since 1956. As noted above, the isthmus meets the northwest boundary line of Lot 36. By executing a Letter of Concurrence, Ms. Moreland conferred upon the City all rights, both proprietary and riparian, that she has with respect to Lot See Joint Ex. 16. Petitioners contend that they own riparian rights appurtenant to their Lot 37, which is to the east of Lot 36. The City and Intervenor dispute this claim and contend that Lot 37 does not adjoin any navigable water and thus there are no riparian rights appurtenant to Lot 37. Assuming arguendo that Lot 37 adjoins Pensacola Bay, it is still separated from the project site by riparian areas appurtenant to the Moreland property (Lot 36) as well as the riparian areas appurtenant to the City property, i.e., the Island and isthmus. The Empie survey, which reasonably depicts the riparian lines in the project area, shows the project site as being approximately 300 feet inside the existing breakwater, which is shown as being no closer than 48.9 feet away from the westernmost riparian line appurtenant to Lot 37. See Joint Ex. The primary portion of the fill site is located around 370 feet from the closest point of the western riparian line appurtenant to Lot 37. Id. No portion of the project is located within 25 feet of the Lot 37 riparian line. Id. Petitioners presented no evidence disputing the riparian areas identified on the Empie survey or otherwise identifying the areas of riparian rights appurtenant to their property. While they engaged the services of Mr. Barrett, a professional land surveyor to prepare a boundary survey, the purpose of the survey was to show that Lot 37 adjoins Pensacola Bay, rather than depicting the riparian areas appurtenant to that lot. See Petitioners' Ex. 1. Infringement on Riparian Rights Rule 18-21.004(3)(c) requires that "activities [in submerged lands] must be designed and conducted in a manner that will not unreasonably restrict or infringe upon the riparian rights of adjacent upland property owners." (emphasis added) Petitioners contend that, even though they do not routinely use their riparian rights, the project will restrict or infringe upon their riparian rights of boating, swimming, navigation, and view. To make this determination, they assert that the appropriate test under the rule is mere infringement, and not "unreasonable" infringement; however, this interpretation is contrary to the plain wording in the rule. The main living floor of Petitioners' residence is approximately 50 feet above sea level. The emergent grasses will be located no closer than 500 feet from the edge of Lot 37 and 600 feet from their residence and are expected to grow only to a height of no more than two and one-half feet. The concern that the grasses will impair Petitioners' view is without merit. Although Dr. Cope initially believed that fill or grass would be placed or planted "all the way up to and abutting our lot 37," this interpretation of the City's plans was incorrect. A photograph taken from his back yard indicated that he could view the northeastern corner of the Island where new vegetation or fill might be placed, but the photograph depicted an area outside of the Lot 37 riparian area. See Petitioners' Ex. 18. While Dr. Cope initially stated that the new emergent grass would "clearly degrade the view from both the house and the shoreline," he later acknowledged that the project would not have any effect upon his view of Lot 37's riparian areas. There are a boathouse and dock in the waters behind Petitioners' house. However, Petitioners submitted no evidence to support their suggestion that the project might cause the water behind Lot 37 to become more shallow and adversely affect boating and navigation. Contrary evidence by the Department and City was unrefuted. Finally, Dr. Cope stated at hearing that he has never been swimming in Gilmore Bayou or Pensacola Bay and has no intention of doing so. His wife offered no evidence that she ever intends to swim in those waters. In summary, the activities undertaken in the project area will not unreasonably restrict or infringe upon Petitioners' riparian rights of swimming, boating, navigation, or view within the meaning of rule 18-21.004(3)(c). Petitioners' Standing Respondents and Intervenor contend that Petitioners lack standing to bring this action for two reasons: that they do not own Lot 37 individually but rather as trustees, and the petition was not filed in that capacity; and that Lot 37 does not adjoin navigable waters. See § 253.141(1), Fla. Stat. ("[r]iparian rights are those incident to land bordering upon navigable waters"). As described by the City's real estate expert, in June 2010, or before the instant petition in this case was filed, the Copes executed two deeds for estate planning purposes, which resulted in "legal title [being] owned part by Dr. and Ms. Cope as to one-half life estate and for Ms. Cope as to one-half for her life estate [and] then the remainder interest is vested in the trustees [of the D. Nathan Cope or Cynthia Russell Cope revocable trust agreements] for the remainder interests." Put in plainer language, this meant that the ownership of Lot 37 is now divided as follows: an undivided 50 percent is owned by the wife as to a life estate and by the wife's revocable trust as to the remainder interest, and the other undivided 50 percent is owned by the wife and husband as to a life estate for the husband's lifetime and by the husband's revocable trust as to the remainder interest. Therefore, there are four entities or persons with an ownership interest in the property: Dr. Cope, Mrs. Cope, Dr. Cope's trust, and Mrs. Cope's trust. The City presented expert testimony regarding the chain of title of Lot 37, beginning in June 1952 when the subdivision was first platted, and running through June 2010, when Petitioners conveyed the property to themselves as trustees of two revocable trusts. According to the expert, the subdivision plat in 1952 reflects a narrow strip of property (described as a hiatus strip) separating the entire subdivision, including Lot 37, from the waters of Gilmore Bayou, Pensacola Bay, and Woodland Lake, a nearby body of water. The strip was a park that was dedicated to the public. See Joint Ex. 1. In 1962, the developer conveyed by quit claim deed the entire strip to the record title holder of each lot in the subdivision. At that time, Lot 37 was owned by the Blaylocks. The expert found that each conveyance of Lot 37 that occurred after 1962, up to and including the Copes' purchase of the property in February 2008, did not include the hiatus parcel. Therefore, he opined that title in the strip property continues to remain with the Blaylocks. Besides his title search, the expert further corroborated this opinion by referring to a topographic survey of Lot 37 prepared in June 2005, see Joint Ex. 2a; a title insurance policy on Lot 37 issued in 2008 when the Copes purchased the property that specifically excludes title insurance for the hiatus parcel; and a recent Santa Rosa County tax bill describing the property without the hiatus parcel. In response, Petitioners contend that the hiatus strip never existed or the 1952 plat is invalid because it failed to comply with section 177.08, Florida Statutes (1951), which required that "all land within the boundaries of the plat must be accounted for either by blocks, out lots, parks, streets, alleys or excepted parcels." Because a dispute over the exact boundary lines of Lot 37 exists, this issue must be resolved in the appropriate circuit court. See § 26.012(2)(g). For purposes of deciding the merits of this case, however, it is unnecessary that this determination be made. Intervenor's Standing Dr. Tamburro currently resides on Lot 34, which faces Gilmore Bayou, and jointly owns the property with his wife. He uses the Bayou to boat and for other recreational purposes. He also uses the Island to swim, walk, and boat. The preservation of the Island is important to him since it serves as a barrier island in protecting his home during storm events. Although Dr. Tamburro's wife did not join in his petition to intervene (but appeared as his counsel), he still has a recognized ownership interest in the property.1
Recommendation Based on the foregoing Findings of Fact and Conclusions of Law, it is RECOMMENDED that the Department of Environmental Protection enter a final order approving the City's application for a Wetland Resource Permit and Letter of Consent to Use Sovereign Submerged Lands. DONE AND ENTERED this 20th day of April, 2011, in Tallahassee, Leon County, Florida. S D. R. ALEXANDER Administrative Law Judge Division of Administrative Hearings The DeSoto Building 1230 Apalachee Parkway Tallahassee, Florida 32399-3060 (850) 488-9675 Fax Filing (850) 921-6847 www.doah.state.fl.us Filed with the Clerk of the Division of Administrative Hearings this 20th day of April, 2011.
The Issue The issue is whether Petitioner's after-the-fact modification application for construction activities seaward of the coastal construction control line in New Smyrna Beach, Florida, should be approved.
Findings Of Fact Based upon all of the evidence, the following findings of fact are determined: In 1984, Petitioner, Thomas R. Sweeney, purchased a home at 5917 South Atlantic Drive, New Smyrna Beach, Florida. At that time, the home was approximately 3,000 square feet in size. The home sits seaward of the coastal construction control line (CCCL) and thus any construction activities on the premises require the issuance of a CCCL permit from Respondent, Department of Environmental Protection (DEP). In 1987, Petitioner constructed a first floor porch, second story addition, and wooden deck at the site without first applying for and obtaining a CCCL permit from the Department of Natural Resources, which was subsequently merged with DEP. After the construction was completed, Petitioner submitted an after-the-fact application for a CCCL permit for those structures. Before being issued Permit Number VO-423, Petitioner was required to pay an administrative fine. Among other things, Permit VO-423 approved an already constructed wooden deck on the eastern side of the home which approximated 840 square feet in size. Petitioner was also given approval for a wooden walkway with stairs that provided access to the beach. On June 1, 1995, Petitioner filed a second CCCL application with DEP to add a 20-foot first and second story addition with a deck to the south side of the home. After reviewing the application, on November 9, 1995, DEP issued CCCL Permit Number VO-627 authorizing the scope of work identified in the permit application documents. Notwithstanding the limited amount of work authorized by the permit, Petitioner constructed a third story addition to his home. He also removed the original wooden deck on the eastern side of the home, and he constructed spread footers and a foundation on top of the rock revetment for a new and much larger deck. The new deck is approximately 2,100 square feet, or more than 1,200 square feet larger than the original permitted deck. In its present state, the home is approximately 5,600 square feet, and the existing eastern deck is larger than any permitted deck on any other single-family home in Volusia County. On September 9, 1996, DEP discovered the third story addition and the much larger wooden deck with appurtenant structures. Presumedly at the behest of DEP, on November 22, 1996, Petitioner submitted an application for an after-the-fact modification of CCCL Permit Number VO-627 to authorize the previously completed, unauthorized work. On April 23, 1997, DEP issued CCCL Permit Number VO-627 After-the-Fact. The permit approved the third-story addition to the home together with a 10-foot wide wooden deck on the seaward side of the entire third story and a 12-foot wide wooden deck on the landward side of the third story. DEP denied, however, authorization for Petitioner's new wooden deck on the first floor with a tiki hut and sundeck on the ground those structures violated Rule 62B-33.005(4)(e), Florida Administrative Code. That rule requires that any new construction seaward of the CCCL "minimize the potential for wind and waterborne missiles during a storm." The issuance of the proposed agency action prompted Petitioner to initiate this proceeding. On November 3, 1997, DEP entered a Final Order directing Petitioner to pay a fine because he illegally constructed structures seaward of the CCCL. The order was never appealed, and thus the time to challenge the order has elapsed. As of the date of hearing, Petitioner had not paid the fine, and a statutory lien has been placed on the property. The Storm Surge Elevation at this site for a 100-year storm event is 10.7 feet N.G.V.D. The Breaking Wave Crest- Elevation for a 100-year storm event at this site is 14.9 feet N.G.V.D. Part of the new eastern deck is located below an elevation of 14.9 feet N.G.V.D. The builder who constructed the additions, Edward Robinson, characterized them as "above average to superior" in quality. To minimize the possibility of the deck washing away during a storm event, he used the "best" nails, bolts, and concrete available. In addition, the new decking was rested upon concrete footers for support. The footers, however, are on top of a rock revetment, and Robinson conceded that such footers are not as stable as a pile foundation. Petitioner used coquina rock (with a low unit weight) for his revetment. It was established that the rocks on which the footers rest are not permanent, and they can shift during a large storm event. In fact, shifting can occur even during a ten-year storm, and there will be a total failure of the revetment during a thirty-year storm event. Once the stones move, an erosion process begins, and the deck will fail. The accompanying high winds will then lift the wooden debris in an airborne fashion. Depending on the strength of the storm, the airborne debris will be a threat not only to Petitioner, but also to his neighbors. Therefore, it is found that the existing construction for the eastern deck does not minimize the potential for wind and waterborne missiles during a storm, and it thus violates Rule 62B-33.005(4)(e), Florida Administrative Code, as alleged in the proposed agency action denying in part the permit.
Recommendation Based on the foregoing Findings of Fact and Conclusions of Law, it is RECOMMENDED that the Department of Environmental Protection enter a Final Order denying Petitioner's application for an after-the-fact amended CCCL permit to construct an expanded eastern deck with a tiki hut and sun deck on his property at 5917 South Atlantic Avenue, New Smyrna Beach, Florida, and approving the application for the structures previously authorized by the Department in its Final Order issued on April 24, 1997. DONE AND ENTERED this 11th day of May, 1998, in Tallahassee, Leon County, Florida. DONALD R. ALEXANDER Administrative Law Judge Division of Administrative Hearings The DeSoto Building 1230 Apalachee Parkway Tallahassee, Florida 32399-3060 (850) 488-9675 SUNCOM 278-9675 Fax Filing (850) 921-6847 Filed with the Clerk of the Division of Administrative Hearings this 11th day of May, 1998. COPIES FURNISHED: Kathy Carter, Agency Clerk Department of Environmental Protection 3900 Commonwealth Boulevard Mail Station 35 Tallahassee, Florida 32399-3000 Thomas H. Dale, Esquire Post Office Box 14 Orlando, Florida 32802 Thomas I. Mayton, Esquire Department of Environmental Protection 3900 Commonwealth Boulevard Mail Station 35 Tallahassee, Florida 32399-3000 F. Perry Odom, Esquire Department of Environmental Protection 3900 Commonwealth Boulevard Tallahassee, Florida 32399-3000
The Issue The issue for determination is whether Petitioners are eligible for a permit, pursuant to Section 161.053, Florida Statutes, for construction seaward of the Coastal Construction Control Line in Broward County, Florida.
Findings Of Fact On November 30, 1993, Vander Ploeg and Associates, Inc., on behalf of Paul Leto, Richard Meyer, and Berta Anderes (Petitioners) submitted an application to the Florida Department of Environmental Protection (Respondent) for a permit to perform construction on their property seaward of the Broward County Coastal Construction Control Line. Respondent deemed their application complete on April 18, 1994. Petitioners proposed construction will be seaward of the Coastal Construction Control Line. The proposed construction will occur on two adjacent lots in Broward County. Petitioner Leto is the owner of one of the lots described as Lot 19, Block 196, Hollywood Central Beach, Plat Book 4, Page 20, Public Records of Broward County. Petitioners Meyer and Anderes are the owners of the other lot described as Lot 20, Block 196, Hollywood Central Beach, Plat Book 4, Page 20, Public Records of Broward County. Petitioner Leto purchased his lot in September 1992 and Petitioners Meyer and Anderes purchased their lot in March 1993. The lots were platted in or around the 1920's. Both lots are seaward of the seasonal high water line, on a sandy beach with no frontal dune structure. They are bordered by the Atlantic Ocean on the eastern most side and by a roadway (Surf Road) which is immediately adjacent to the lots on the western most side and landward of the lots. Approximately 200 feet north of the lots is an existing structure and approximately 800 feet south of this first existing structure is another existing structure. Petitioners topographical survey, which was submitted to Respondent in December 1993, showed that Lots 19 and 20, each measured 40 feet in a shore parallel direction and 80 feet in a shore normal direction, i.e., perpendicular to the shoreline. The proposed structure will be located directly on the sandy beach. The City of Hollywood, Florida has granted Petitioners a variance. Further, the proposed construction complies with the rules, zoning regulations, and ordinances of the City of Hollywood. Petitioners' application requests a permit for the construction of a single-family residence on the lots, which will house two families. However, the proposed construction is for a duplex, not a single-family residence. Petitioners are willing, and agreeable, to changing the design of the proposed structure to comply with Respondent's specifications for a single- family residence. Additionally, the proposed construction includes a riprap which will also be located on the sandy beach. A riprap is typically used for protective armoring. No structure presently exists for the riprap to protect. Furthermore, the riprap proposed by Petitioners is not adequately designed as a coastal protection structure, and if the proposed single-family residence is modified in accordance with Respondent's specifications, the proposed modified single-family residence would not be eligible for coastal armoring. The riprap structure is not an integral part of the structural design. Petitioners are willing, and agreeable, to eliminating the riprap structure. No other issues exist as to the structural integrity of the design of the proposed project. The lots on which the proposed structure will be located are a part of the beach-dune system. The natural function of the beach provides protection to upland property. The lots on which the proposed structure will be located are subject to normal storm-induced erosion. Tide and wave forces will impact the proposed structure during storms of minor intensity, including five-year storms. The proposed structure will induce greater erosion on the lots as a result of scour due to the interaction of the storm waves and currents with the proposed structure. During the storm, the normal storm-induced erosion combined with the scour erosion will form a breach or depression in the subject property. In turn, the upland property will be exposed to greater tide and wave forces, increasing the risk of erosion and damage to the upland property. The subject lots and surrounding properties have been subjected to unnatural forces which have added to the erosion. The Port Everglades inlet has inhibited the natural downdrift of sand. The City of Hollywood's beach maintenance division has been regularly pushing sand seaward and in the process, breaking down natural forming cliffs. Even though these unnatural forces are capable of being eliminated, the normal storm-induced erosion and the scour erosion would still exists. The existing developed structures to the north and south of the subject lots appear to create a reasonably uniform line of construction. However, the developed structures have been unduly affected by erosion. The proposed structure will be located within this line of construction. During a major storm along the shoreline, waves remove sand from the beach and dune area and deposit the sand in an offshore bar. After the major storm, a recovery of the beach and dunes takes place. Normal wave activity carries the sand from the offshore bar back to the beach, and the sand is then carried landward by winds and is caught and trapped by dune vegetation; thereby reforming a dune. Constructing the structure as proposed will not locate the structure a sufficient distance landward of the beach-dune system. As a result, the proposed structure will interrupt natural fluctuation in the shoreline and not preserve the natural recovery following the storm-induced erosion. The cumulative impact on the beach-dune system by the proposed structure would be severe, i.e., the effects on the beach-dune system by repeating this same proposed structure along the subject shoreline would be severe. There would be structure-induced scour and general degradation of the beach-dune system. Additionally, the recovery potential of the subject area following a major storm event would be threatened. Over the years, the beach of the subject property has been subjected to a re-nourishment project consisting of pumping sand from offshore. This method of re-nourishment may have negatively impacted the sand bar system immediately offshore affecting the hindrance of erosion. A sand bar system immediately offshore softens wave action on the shore and aids in inhibiting erosion. The proposed structure will hinder lateral public beach access. Currently, lateral beach access exists along the beach between the existing northern developed property and the existing southern developed property. The proposed structure will be located on the sandy beach, and the seaward face of the proposed structure will be within approximately one foot of the wet sand beach. At times, the proposed structure will be surrounded by water on at least three sides. No alternative beach access would be available. The proposed riprap will also be located on the sandy beach and will further hinder lateral public beach access. 2/ Loggerhead turtles, which are nesting marine turtles, engage in nesting activities along the stretch of beach where the subject property is located. They are a threatened species, i. e., close to extension. Although they do not nest every year, the turtles usually provide several nests in a single year. Typically, one hundred eggs comprise a turtle nest. In 1992, approximately 2,221 loggerhead turtle nests were in Broward County, with 22 of these nests located within 1,000 feet of the subject property. Turtle nesting efforts have been observed in the beach area of the subject property. One nest was found within the subject property. Structures located on the sandy beach interfere with marine turtle nesting habits. If female turtles make contact with the structures, they often abort nesting attempts, which results in false crawls. Repetitive false crawls harms successful nesting, which may cause malformed egg chambers, impacting the successful incubation of the nest. Also, interaction with a structure can cause injury or death to a female turtle attempting to nest. Additionally, urbanization activity and lighting on the beach deter nesting. A loss of marine turtle nesting habitat will result if the proposed structure is constructed. Also, armoring, such as the proposed riprap, can result in nests being placed more seaward. 3/ Consequently, the nests would be threatened with tidal inundation, which would affect the mortality of the nest itself. As one nest has been located within the subject property, at least one nest or crawl per year would be affected by the proposed structure. Within 30 years, the proposed structure will be seaward of the seasonal high water line. The location of the proposed structure is seaward of the 30-year erosion projection for the subject property. Beach Defense Fund, Inc. (Intervenor) presented no evidence to show that its interest is different than the public at large and that it has substantial interest separate and apart from the public.
Recommendation Based on the foregoing Findings of Fact and Conclusions of Law, it is RECOMMENDED that the Department of Environmental Protection enter a final order denying the application of Paul Leto, Richard Meyer, and Berta Anderes for a permit, pursuant to Section 161.053, Florida Statutes, for construction seaward of the Coastal Construction Control Line in Broward County, Florida. DONE AND ENTERED this 31st day of May, 1996, in Tallahassee, Leon County, Florida. ERROL H. POWELL, Hearing Officer Division of Administrative Hearings The DeSoto Building 1230 Apalachee Parkway Tallahassee, Florida 32399-1550 (904) 488-9675 Filed with the Clerk of the Division of Administrative Hearings this 31st day of May, 1996.
The Issue The issue is whether to approve Steven A. Walker's application for a coastal construction control line (CCCL) permit authorizing him to conduct certain construction activities at 100 Park Avenue, Anna Maria, Florida.
Findings Of Fact Based upon all of the evidence, the following findings of fact are determined: History of the Proceeding Since 2005, Petitioner has owned property at 104 Park Avenue, Anna Maria, Sarasota County, Florida. The parcel fronts on the Gulf of Mexico and is adjacent to property owned by the Stephen A. Walker Land Trust (Land Trust) located at 100 Park Avenue. The Trustee of the Land Trust is Stephen A. Walker, who is the applicant in this proceeding. On March 5, 2009, Mr. Walker filed an application with the Department for a permit authorizing the construction of "a new single family residence with a pool, driveway and multiple structures" seaward of the CCCL on his parcel. See Joint Exhibit 11. The application was accompanied by a letter from the City Planner, B. Alan Garrett, indicating that the proposed activity "does not contravene the City of Anna Maria local setback and pervious coverage requirements of the zoning code provisions." See Joint Exhibit 3. On June 26, 2009, the Department, through its Bureau of Beaches and Coastal Systems, issued a Final Order granting the application subject to certain general and special conditions. See Joint Exhibit 47. A Notice to Proceed with the construction was issued the same date. See Joint Exhibit 46. Separate written notice of the Department's proposed action was also served on both Petitioner and his attorney. See Joint Exhibits 49 and 50. On July 22, 2009, Petitioner filed his Petition with the Department contesting the proposed agency action. See Joint Exhibit 51. As grounds, Petitioner contended generally that the environmental permitting requirements under Florida Administrative Code Rule 62B-33.0052 had not been met, and that the proposed activity violated both the City's Plan and the zoning code. Id. Evidence regarding the latter allegations was later excluded as being irrelevant. See Order dated March 12, 2010. At hearing, counsel for Petitioner represented that he was no longer alleging that the application did not qualify for a permit under the environmental permitting requirements of the rule. However, he continued to assert that the proposed construction will violate the City's Plan and zoning code. A suit in circuit court has been filed seeking an adjudication of those claims and apparently is still pending. See Friday v. City of Anna Maria, Case No. 2010-CA2369 (12th Cir., Manatee Cty Fla.). Permitting Criteria The general permitting requirements for issuance of a CCCL permit are found in Rule 62B-33.005. There is no dispute that these criteria have been satisfied. Rule 62B-33.008 contains the permit application requirements and procedures. Paragraph (3)(d) of the rule provides that an application for a CCCL permit shall contain the following information: Written evidence, provided by the local governmental entity having jurisdiction over the activity, that the proposed activity, as submitted to the Bureau, does not contravene local setback requirements or zoning codes. Joint Exhibit 3 is a letter dated February 2009 authored by B. Alan Garrett, City Planner, who states that he had reviewed the application and plans filed with him on February 2, 2009, and that the proposed construction "does not contravene the City of Anna Maria local setback and pervious coverage requirements of the zoning code provisions." This letter satisfies the requirement of the rule.
Recommendation Based on the foregoing Findings of Fact and Conclusions of Law, it is RECOMMENDED that the Department of Environmental Protection enter a final order granting the application of Stephen A. Walker, Trustee, for a coastal construction control line permit authorizing certain activities seaward of the CCCL at his property in Anna Maria, Florida. DONE AND ENTERED this 24th day of May, 2010, in Tallahassee, Leon County, Florida. S D. R. ALEXANDER Administrative Law Judge Division of Administrative Hearings The DeSoto Building 1230 Apalachee Parkway Tallahassee, Florida 32399-3060 (850) 488-9675 Fax Filing (850) 921-6847 www.doah.state.fl.us Filed with the Clerk of the Division of Administrative Hearings this 24th day of May, 2010.
