Findings Of Fact Petitioner, Roland Peterson, is the owner of Lots 4, 5 and 6, Block 7, Vilano Beach, in an unincorporated area of St. Johns County, Florida. Vilano Beach lies just eastward of the City of St. Augustine, Florida, and north of St. Augustine Inlet. The three lots are adjacent to each other. By applications dated June 7, 1985 petitioner sought the issuance of three coastal construction control line permits by respondent, Department of Natural Resources, Division of Beaches and Shores (Division), to authorize construction seaward of the coastal construction control line or setback line on Lots 4, 5 and 6. More specifically, petitioner sought approval to construct a beach-side snack bar with associated beach walkover, driveway and attached decks on Lot 4, and single family residences with associated dune walkover; driveway and attached decks on Lots 5 and 6. These applications were assigned Application Numbers SJ 220, SJ 221 and SJ 222 by the Division. They were deemed to be complete on August 6, 1985. After evaluating the three applications, the Division formulated recommendations to deny the requested permits. These recommendations were adopted by the Governor and Cabinet sitting as head of the agency at its November 5, 1985 meeting. Notice of such intended action was previously forwarded to petitioner on October 23, 1985. Said notice prompted the instant proceeding. As grounds for denying the permits the Division concluded that the three projects were located seaward of the seasonal high- water line and were therefore prohibited by a law, the projects lay in an area "highly vulnerable" to a major storm; and the cumulative impact of locating these and other structures further seaward could be expected to adversely impact the beach and dune system of the Vilano Beach area. The parties have stipulated that the Division has properly calculated the seasonal high water line in the questioned area, and that petitioner's three projects lie seaward of that line. The parties have also stipulated that the three projects lie seaward of the frontal dune within the meaning of Subsection 161.053t6)(a)1., Florida Statutes (1985).
Recommendation Based on the foregoing findings of fact and conclusions of law, it is RECOMMENDED that application numbers SJ 220, SJ 221 and SJ 222 filed by Roland Peterson to construct various structures on Lots 4, 5 and 6, Block 7, Vilano Beach in St. Johns County, Florida, be DENIED. DONE and ORDERED this 14th day of May, 1986, in Tallahassee, Florida. DONALD R. ALEXANDER, Hearing Officer Division of Administrative Hearings The Oakland Building 2009 Apalachee Parkway Tallahassee, Florida 32399 (904) 488-9675 Filed with the Clerk of the Division of Administrative Hearings this 14th day of May, 1986.
The Issue Whether or not the proposed amendments to Respondent's Rules 18-21.003 and 18-21.004, Florida Administrative Code, comply with Section 120.54, Florida Statutes, or is otherwise an invalid exercise of delegated legislative authority. Specifically, the following issues are raised by the pleadings and presentation of the parties: a) Whether the proposed rule amendments exceed the Respondent's grant of authority by placing a moratorium on the issuance of requests to use sovereign submerged lands adjacent to coastal islands, as more specifically defined by the rule; b) Whether Respondent failed to materially follow rulemaking procedures as prescribed by Section 120.54, Florida Statutes in preparation of the economic impact statement; c) Whether the amendments are arbitrary and capricious because they are unnecessary and are unrelated to the administration and management of sovereign submerged lands; d) Whether the proposed amendments contained terms and definitions which are vague and ambiguous, because the terms as defined are not ascertainable; e) Whether the proposed amendments effectuate a "taking" of Petitioner's property; and f) Whether the claims of Petitioner's Andrews, Depot Key and Lost Tree that the Board of Trustees are estopped from promulgating the proposed amendments are without merit. Additionally, Respondent raised the issue of whether the Petitioners had standing to bring the subject rule challenge.
Findings Of Fact The Board of Trustees of the Internal Improvement Trust Fund (Trustees) holds state land in trust for the use and benefit of the people of the State of Florida, pursuant to Section 7, Article II, and Section 11, Article X of the State Constitution. The Division of State Lands within the Department of Natural Resources (DNR) performs all staff duties and functions related to acquisition, administration and disposition of state lands, title to which is or will be vested in the Trustees pursuant to Section 253.002, Florida Statutes. The Trustees are vested and charged with the acquisition, administration, management, control, supervision, conservation, protection and disposition of all lands owned by, or which may inure to, the State or any of its agencies, departments, boards, or commissions, except for certain exceptions contained in Section 253.03(1), Florida Statutes. Among lands vested in the Trustees are all tidal lands and all lands covered by shallow waters of the ocean or gulf or bays or lagoons thereof, and all lands owned by the state covered by freshwater (i.e., sovereign submerged lands). The Trustees are authorized to administer all state-owned lands and are responsible for creating an overall and comprehensive plan of development concerning acquisition, management, and disposition of state-owned lands so as to insure maximum benefit and use. To accomplish this mandate, the Trustees are empowered to adopt all necessary rules and regulations pursuant to Section 253.03(7)(a), Florida Statutes. Currently, the administration and management of sovereign submerged lands is governed by the provisions of Chapters 18-18, 18-20 and 18-21, Florida Administrative Code. Pursuant to rules contained therein, the Trustees may approve the following types of uses of sovereign submerged lands: a) Consents of use, b) Easements, c) Management Agreements, d) Use Agreements and e) Leases. On June 27, 1989, the Trustees were asked to consider approving the issuance of a 5-year sovereign submerged land lease for the construction of a 42-slip private residential docking facility located adjacent to Atsena Otie Key, an island located off the coast of Cedar Key, which would serve a proposed upland development. Approval of that lease would, if granted, preempt over 14,500 sq. ft. of sovereign submerged lands. Under pertinent rules in place when the Trustees considered the Atsena Otie Key request, Trustees' staff recommended that they approve the requested use. However, based on written public opposition to the approval of that request, the Trustees, during the subject Cabinet meeting, heard from eight persons appeared who urged denial of the requested use maintaining that the proposed project was not in the public interest. Based on public opposition and the concerns raised, the Trustees rejected staff's recommendation and unanimously deferred action on the Atsena Otie lease request. Additionally, the Trustees directed the Division of State Lands to compile a report of what types of federal and state protection of coastal islands currently existed. The Trustees thereafter commissioned its to pull together their authority and promulgate a rule enunciating common standards for application on barrier islands. Treasurer Gallagher moved to have the DNR develop rules for the trustees to follow when making decisions regarding development on coastal islands which was to be presented to the Trustees at the August 22, 1989 Cabinet meeting. Based on the Trustees desire to develop a more clearly enunciated policy of what the state would allow its lands adjacent to coastal islands to be used for in the future and to put the public on notice as to what they could expect the Trustees to permit in terms of the use of sovereign submerged lands adjacent to coastal islands and to also provide its staff with guidance as to how they would analyze requests prior to submitting them for consideration, the proposed rule here under challenge was promulgated to put in place a statewide policy regarding development of undeveloped coastal islands. In addition, the Trustees were concerned about issues being raised as to the use of sovereign submerged lands to facilitate coastal island development which was not being adequately addressed by the local governments comprehensive planning processes. The next developmental stage of the coastal island policy was agendaed at the August 22, 1989 Cabinet meeting. At that meeting, staff presented a report entitled, "Analysis Of Existing Policy And Programs Affecting Florida's Coastal Resources." That report summarized and analyzed the existing federal and state programs affecting Florida's coastal islands. It is noted that there existed no single state or federal program with sufficient standards and authority to adequately protect and manage the entire beaches, dunes, back barriers and wetland systems of Florida's coastal islands. Likewise, there was no easy accessible resource data base or model criteria to assist local and state agencies in the planning, management and regulation of coastal island development and protection. The findings in that report triggered the Trustees to approve a temporary moratorium on authorizations for the use of sovereign submerged lands that would facilitate development of currently unbridged, undeveloped coastal islands until such time as the Trustees could adopt a policy for considering such requests. At that meeting, the Trustees invited public comment before taking action on staff's recommendations. Following public discussions, the Trustees unanimously accepted the staff's report and a temporary moratorium was placed on authorizations for use of sovereign submerged lands that would facilitate development of currently unbridged, undeveloped coastal islands until DNR's Division of State Lands could propose a comprehensive policy for such requests. Following approval of the staff's report and recommendations, the Trustees reconsidered the Atsena Otie Key request for authorization to construct the 42-slip docking facility and the Trustees approved the lease request but made the approval subject to several amendments including a reduction in size from a 42-slip to a 25-slip private residential docking facility. The Trustees next addressed the developing coastal island policy at the December 19, 1989 Cabinet meeting. At that meeting, the Trustees deferred voting on staff's recommendation that they adopt an interim policy governing the use of sovereign submerged lands adjacent to unbridged coastal islands until the February 1990 Cabinet meeting. At the February 6, 1990 Cabinet meeting, following a lengthy public discussion, the Trustees again deferred action on adoption of the interim policy until they more fully reviewed the issues surrounding the emerging policy at a Cabinet workshop. During that meeting, the Trustees were advised by opponents to their policy about the potential environmental impacts that would arise if the policies were implemented and developers were forced to seek alternative means of providing sewer, water and electricity to their developments. After listing to those concerns, the Trustees considered the opponents position but retained their position of restricting the use of sovereign lands. At the conclusion of the discussion, the Trustees voted unanimously to defer action for 90 days until a Cabinet level workshop could be held to delineate the issues regarding the use of sovereign lands to facilitate upland development and to define the extent of the Trustees' jurisdiction and authorization to proceed. During the March 12, 1990 Cabinet workshop, the Trustees received input on their emerging coastal island policy from the Department of Environmental Regulation (DER), the Department of Community Affairs (DCA) and both the Governor's coastal resources Interagency Management Committee (IMC) and the Citizen's Advisory Committee (CAC). 1/ As a result of the workshop at the May 8, 1990 Cabinet meeting, the Trustees directed the staff to develop recommendations for continuing the moratorium and to develop a plan for identifying specific islands that would be protected under the policy. Staff was also directed to work with the DCA to secure funding to complete the inventory and compile data on natural resource values, as a potential land use/development status and development potential on all unbridged coastal islands. At the May 8, 1990 meeting, several of Petitioners voiced opposition to the moratorium but spoke in support of the agency proceeding with rulemaking. Following comments from the public, the Trustees voted to approve and extend the moratorium imposed on August 22, 1989, and for staff to begin rulemaking immediately to begin development of an interim policy until a comprehensive policy and rules governing coastal islands could be adopted by the Board of Trustees. Staff was also directed to work with relevant agencies including the DCA, the coastal resources IMC, and the CAC to develop a definition of coastal islands and undeveloped coastal islands and to give reasonable consideration to development of a comprehensive plan which would be compatible with the Coastal Barrier Resources Act (CBRA). Also, during that meeting, staff was directed to work with the DCA, the IMC and the CAC to develop definitions of "coastal island" and "undeveloped coastal island". The Trustees reiterated the directions to staff to give reasonable consideration to the comprehensive plans of coastal communities and that the policy be compatible with CBRA. The first draft was to be presented to the Trustees in June and a final form of the proposed rule was to be presented at the Trustee's second meeting in September. The Trustees directed staff to include, at a minimum, all unbridged, undeveloped coastal islands units contained within CBRA and all unbridged undeveloped coastal islands within aquatic preserves. The rule was to also address islands which were heavily developed at one end and totally undeveloped at the other. Finally, the staff was to consider the local government's comprehensive plans for coastal communities. At the June 12, 1990 Cabinet meeting, the Trustees were asked to adopt the draft rule prepared. The Trustees after considering the draft, authorized staff to proceed with rulemaking by publishing the rule in the Florida Administrative Weekly and conducting at least three public meetings. On August 31, 1990, DNR received petitions challenging the proposed rules and the moratorium. The petitions raised several issues regarding the proposed rule which had been voiced at the public hearings. In response to those issues, DNR staff sought authority to make amendments to the proposed rule. A report outlining the status of the rule and the revisions were presented to the Trustees at the October 9, 1990 Cabinet meeting. At that meeting, the Trustees accepted the status report including the revision to the amendment to Rules 18-21.003 and 18-21.004, Florida Administrative Code, and authorization to proceed was given to revise the proposed rule. At the October 23, 1990 Cabinet meeting, staff presented the revised proposed rule to the Trustees and requested authorization to formally withdraw the originally proposed rule and to give notice of revision on the instant rule for adoption. An outline explaining the revisions were included within the report. At that meeting, the Trustees approved staff's recommendation to withdraw the original rule and allow the CAC and the IMC to be afforded an opportunity to review the revised rule. On November 11, 1990, the IMC held a public meeting on the revised rule at which time the Trustees received comments, both pro and con, to the revised rule. As a result of those comments, modifications were suggested to the revised rule. At the December 18, 1990 Cabinet meeting, the Trustees authorized staff to withdraw the original proposed amendments and to provide notice of the withdrawal in the Florida Administrative Weekly. As a result of the Trustees consideration of the modification to the rule recommended by the IMC, the following amendment was made to Section 18-21.004(1)(h)(1), Florida Administrative Code: The application is for the purpose of obtaining authorization for a use which was included in a development project which has undergone development of regional impact review and a final development order has been issued pursuant to Chapter 380, Florida Statutes as of the effective date of this rule, and is otherwise permitted by and consistent with the provisions of Rule Chapters 18-18, 18-20, and 18-21, Florida Administrative Code provided, however, that in the case of a substantial deviation to said development order, no authorization of use may be granted for any use that was not included in the original order. Additionally, staff amended the definition of "coastal island segment" to be consistent with CBRA and to provide that if an island segment had an overall density of less than one structure per 5 acres of fastland as of the effective date of the rule, that it be included within the operation of the revised rule. Prior to approval, opponents of the proposed rule engaged the Trustees in a discussion about whether the local government's comprehensive plan process adequately addressed the Trustees' concerns about the protection of natural resources. Following consideration of that discussion, the Trustees made no modification to their policy. The Trustees thereafter voted to continue the moratorium until adoption of the proposed coastal island rule. On August 2, 1991, the Trustees published notice in the Florida Administrative Weekly, Volume 17, No. 31, of their intention to adopt the proposed rule amendments to Rules 18-21.003 and 18-21.004, Florida Administrative Code. As specific authority, Sections 253.03(7) and 258.43(1), Florida Statutes was referenced. On August 31, 1991, Petitioners herein filed challenges, with the Division of Administrative Hearings, to the proposed rule amendments. On September 12, 1991, staff presented the Trustees with a status report regarding the proposed rule in view of the pending challenges. At that meeting, the Trustees reaffirmed their desire to protect undeveloped coastal islands and their adjacent natural resources and directed staff to defend the proposed rule against challenges. In support of this position, the Trustees reaffirmed their desire to curtail development of undeveloped barrier islands as development of such islands poses threats to the natural resources and coastal marine environment and their stated desire to protect those resources. In Section 18-21.003, Florida Administrative Code entitled, "Definitions", was amended by the Trustees' adoption of its coastal island policy to include four new definitions: "Coastal Island", "Fastland", "Undeveloped Coastal Island" and "Undeveloped Coastal Island Segment." The DNR's Office of Marine and Program Planning primarily developed the definitions included in the rule. George Schmahl, an employee at DNR for approximately two years who was accepted herein as an expert in the fields of biology, coastal ecology and coastal resource management, was assigned the task of coordinating the drafting of the definitions. Mr. Schmahl received his guidance for the development of the necessary definitions from the Trustees at the May 8, 1990 staff meeting. The initial draft of the definitional section of the rule contained only the terms "coastal island" and "undeveloped coastal island." Thereafter, the draft was expanded to include definitions for the terms "fastland" and "undeveloped coastal island segment." The definitions were presented to the Trustees for consideration at the June 12, 1991 Cabinet meeting, at which time the Trustees approved staff's draft and directed them to proceed with the rulemaking process. The rule defines "coastal island" as: coastline geological feature lying above mean high water that is completely separated from the coastal mainland by marine or estuarine waters, including those parcels of land which become insular due to natural causes, and is composed of any substraint material, including spoil material. This specifically includes, in addition to exposed coastal island; All islands within aquatic preserves except for Lake Jackson, Rainbow River, Lake Weir and Wekiva River aquatic preserves; and Other islands within confined or semi-confined marine or estuarine waters with an open connection to the Atlantic Ocean or Gulf of Mexico such as bays, lagoons, or inlets. Except for coastal islands within the specified aquatic preserves, it does not include islands or portions of islands within rivers leading into marine and estuarine waters more than one mile upstream of a line drawn at the river mouth from headland to headland. The nucleus for the definition of "coastal island" was derived from the existing definition of "coastal barrier island" found at Section 161.54, Florida Statutes. Schmahl modified the definition in Chapter 161 to take into consideration the phrase as defined by CBRA, and be further modified it to encompass virtually all islands within Florida's coastline. Spoil islands were included in the definition of "coastal island" because the definition of "coastal barrier island" in Chapter 161 specifically includes islands created from spoil disposal. Schmahl opined that "an island so far as the impacts to state lands and the benefits of islands in terms of protection to landward aquatic habitats and mainland ... it didn't matter what the composition of the island ... the issues were the same." Schmahl excluded islands more than one mile upstream from the mouth of a river because the rule was not intended to include, within its operations, islands that occur in river and lake systems within the interior portion of the state. Thus, by excluding islands more than one mile upstream from the mouth of the river, the rule would primarily capture those islands located in close proximity to Florida's coastline. Schmahl explained the choice of one mile upstream as the point at which to connect a line drawn at the river mouth from headland to headland after rejecting other forms of measurements, such as the water salinity or the extent of the tidal influence in the river system, because such methods were difficult to implement and the choice provided a standardized form of measurement which could be objectively applied. A section within the definition of "coastal island" was added to insure that the rule encompassed all islands within aquatic preserves except those islands within freshwater preserves. The freshwater aquatic preserves listed in the rule were identified as islands within freshwater preserves by reviewing aerial maps and excluding any islands located entirely within freshwater aquatic preserve systems. The rule defines the term "fastland" as: That portion of a coastal island above the upper limit of tidal wetland vegetation or if such vegetation is not present, that portion of the island above the mean high water line. Fastland is a common term which is defined in Webster's Third International Unabridged Dictionary as "high and dry land or land above the range of the tides." The term was included within the federal legislation implementing CBRA and was therefore, included within the rule to comply with the Trustees' direction that the definitions be compatible with CBRA's legislation. The term "fastland" was defined to determine whether a particular unabridged island met the definitions for "undeveloped coastal island" and "undeveloped coastal island segment." The rule defines "undeveloped coastal island" as: coastal island not directly or indirectly connected to the mainland by a bridge suitable for automobile traffic, and which has an overall density of less than one structure per five acres of fastland as of December 18, 1990. For the purpose of this definition, a structure means a wall and roofed habitable structure that is principally above ground and affixed to a permanent foundation with a projected ground area exceeding 200 square feet and constructed in conformance with all applicable legal requirements. For the purpose of determining density, facilities such as docks, groins, utility poles and pipelines are not counted as structures. The term "undeveloped coastal island" was primarily derived from definitions used by the Department of Interior Legislation implementing CBRA and is in keeping with the Trustees' instruction that the rule definitions be compatible with CBRA. Likewise, the density threshold of one man-made structure per five acres was taken directly from CBRA's implementing legislation. The term "undeveloped coastal island segment" is defined as: [A]n unbridged coastal island with an overall density of greater than or equal to one structure per five acres of fastland, a segment or portion of the island which either is at least one-quarter mile in linear shoreline length or comprises a minimum of 25% of the total fastland of the island and which consist of less than one structure per five acres of fastland as of December 18, 1990. A segment boundary shall be contiguous with a line drawn from the shore at the point of the outermost structure within a developed area to intersect each shoreline, then continue laterally along the sinuosity of each shoreline until another developed area is encountered or the end of the island is reached. See "undeveloped coastal island" for the definition of a structure. This phrase was included as a result of specific input from the IMC who convinced the Trustees of the importance of protecting large undeveloped areas of island when one or more portions of the islands were developed. In keeping with instructions received from the Trustees and relying on his professional experience, Schmahl also relied on a review of the following documents in developing the rules definitional sections: Coastal Barrier Resources Act, Public Law 97-348, 16 USC, Section 3500; and the Executive Summary of the Report of Congress on the Coastal Barrier Resources System. Section 18-21.004, Florida Administrative Code, entitled "Management Policies, Standards and Criteria," was amended by the Trustees' adoption of the coastal island policy to include four exceptions to the application of the rule. The Division of State Lands drafted language for this section under the direction of the Division's Director who viewed the rule's purpose as a means to modify the moratorium which had been opposed as the Trustees developed and refined the coastal island policy. The rule was to serve as an interim device until a multi-agency comprehensive policy could be developed to address development of and protection of coastal islands and their adjacent resources. The Trustees policy is reflected in language of Section 18-21.004(h), Florida Administrative Code, which provides: No application to use sovereignty, submerged land adjacent to or surrounding an unbridged, undeveloped coastal island or undeveloped island segment may be approved by the Board of Trustees unless it meets the following criteria... . The remaining section codify exceptions to the moratorium which had been defined over the approximate 18-month development stage that the policy underwent. Exception (1), contained in 18-21.004, states: The application is for the purpose of obtaining authorization for a use which was included in a development project that has undergone development of regional impact review and a final development order has been issued pursuant to Chapter 380, Florida Statutes, as of the effective date of this rule and is otherwise permitted by and consistent with the provisions of Rule Chapters 18-18, 18-20 or 18-21, Florida Administrative Code, as applicable, provided, however, that in the case of a substantial deviation to said development order, no authorization of use may be granted for any use that was not included in the original order. The rationale for the exception was premised on the fact that if a project had undergone DRI review, both regional and state agencies had had an opportunity to participate in review of the development. Therefore, such proposed projects had undergone a higher level of review as to the propriety and continuity with development plans than would have otherwise occurred had the review been conducted only at the local level. Thus, the exception was a way of lending credence to this state's policy of encouraging developers to use the DRI review process. The second exception to the Trustees coastal island policy states: The proposed facility is limited to a 2-slip private residential dock that complies with the standards set forth in Section 18-20.004(5)(b), Florida Administrative Code and the upland parcel to which the facility will be attached was not created by platting or subdividing after December 18, 1990. However, as an alternative to multiple private residential docks, the Board may authorize a private docking facility of more than 2-slips if it determines that such a facility would result in greater environmental protection for sovereignty submerged land resources than multiple individual docks, and provided the facility complies with all of the applicable standards. The number of slips associated with such a facility shall not exceed the number of slips which would have been authorized as individual docks. This exception recognized that under certain circumstances a person could construct a dock on their property. However, the intent was to provide notice that as to those purchasers of waterfront property on a coastal island within the definition of the rule after the December 18, 1990, date would be on notice that they would not be permitted to construct a single-family dock and will therefore have no reasonable expectation to receive one. The Trustees recognized that riparian owners have a right to access their property but that such does not extend to a statutory right to construct a dock. The third exception which addresses the provision of utility services provides: With respect to applications to use sovereignty submerged lands for the provision of public utility services, such services were in place as of December 18, 1990, and the requested usage of sovereignty, submerged land will not result in a upgrade of capacity or will not serve additional customers on a unbridged, undeveloped coastal island or undeveloped coastal island segment. Applications may be approved under this provision only to allow the maintenance or repair of existing utility lines, or as necessary to maintain public safety as ordered by the Public Service Commission. The purpose of that exception was to provide notice to the utility companies that if utility service already existed on an island, and it became necessary for the company to work on lines either to repair or maintain existing service, the rule would not prohibit such activity. The purpose was one of protecting some sovereign submerged resources and not facilitate development by use of sovereign lands, and that utility companies would be prohibited from using sovereign lands to serve additional customers or to upgrade existing service. The final exception to the Trustees' policy states: The proposed use is for the purpose of allowing access, for public purposes, to publicly owned uplands or submerged lands for recreation, research, conservation, mosquito control or restoration activities only, at the discretion of the Board, and is otherwise consistent with the provisions of Rule Chapters 18-18, 18-20, or 18-21, Florida Administrative Code. This exception was developed to allay concerns that the state had acquired a number of coastal islands pursuant to its "Save Our Coast Program" for public recreation which would be subject to the moratorium and therefore not used and the exceptions made clear that the use of coastal islands for public purposes and for the general public's enjoyment, remained in tact. Development of the Economic Impact Statement Pursuant to Section 120.54(2)(b), Florida Statutes, each agency shall provide information on its proposed action by preparing a detailed Economic Impact Statement (EIS) which shall include an estimate of the cost to the agency of the implementation of the proposed action, including the estimated amount of paperwork; an estimate of the cost or the economic benefit to all persons directly affected by the proposed action; an estimate of the impact of the proposed action on competition and the open market for employment, if applicable; a detailed statement of the data and method used in making each of the above estimates; and an analysis of the impact on small business as defined in the Florida Small and Minority Business Assistance Act of 1985. DNR prepared an EIS which was included with the proposed rule amendments that contained estimates of the cost to the agency of the implementation of the proposed action including the estimated amount of paperwork; of the cost of the economic benefit to all persons directly affected by the proposed action; of the impact of the proposed action on competition in the open market for employment; of the data and method used in making each of the above estimates; and contained an analysis of the impact on small business as defined in the Florida Small and Minority Business Assistance Act of 1985. The EIS was prepared for DNR by Ed Wood, a senior management analyst, with the Division of State Lands. He is coordinator for rule development at the Division and is responsible for the budget and personnel functions for the Division. He holds a master's degree in education and administration with a specialty in school finance and a bachelor's degree in business administration. He has prepared similar EIS's and received a primer from staff on the agency's rationale for proposing the subject rule. Wood read the draft EIS prepared by Dr. Bell, an economist for the Department, who was hired to assist in the preparation of the EIS. Wood consulted with DNR staff regarding information received at public hearings from citizens possibly affected by the proposed rule in order to assess public opinion about the rule prior to undertaking the paths of development of the EIS. Wood relied heavily on the Department of State's document entitled, "Guide to Rules Promulgation Under The Florida Administrative Procedures Act" dated November 1986, which included examples of EISs. Based on his familiarity with the Division's budget and personnel functions, he is infinitely familiar with cost and both paperwork and manpower necessary to implement the proposed action which would be affected by the proposed rules. At the time Wood consulted with Department staff, there were only six applications pending out of an estimated 867 coastal islands. Based on an inadequate sample of potentially affected parties, Wood did not rely on them as a basis for determination of economic impact, as such would have been speculative. Those portions of Dr. Bell's EIS which were relevant were adopted and utilized heavily by Wood in preparation of the EIS. Likewise, irrelevant portions including analysis of benefits from storm protection, hazard avoidance and shoreline protection, none of which are under the Division's jurisdiction were excluded. The Division fully considered all impacts that were capable of being considered based on the information which was furnished and which was reliable. Estimates of the impact on the action of competition and the over-market for employment were taken verbatim from Dr. Bell's draft EIS. The criteria utilized and adopted from Dr. Bell's draft EIS were sufficiently documented to be utilized and therefore was in fact utilized by Wood in the subject EIS. The information relied upon by Wood in preparation of the EIS was included in the statement of data and methods used. At the time of Wood's preparation of the EIS, there were no pending applications for marinas on affected islands and therefore any impact in that area was deleted as being mere speculation. Finally, as to those estimates of the various impacts which were indeterminate, they were stated as such and Wood failed to speculate as to such costs. Facts Relevant to Petitioner's Depot Key Joint Venture Partnership and George Rex Andrews After being deferred by the Board at its June 27, 1989 meeting, the Andrews lease application for the multi-slip docking facility was Item 22 on the Board's agenda for the August 22, 1989 meeting. Item 21 on the agenda was for recommendation for approval of a moratorium on authorizations for use of sovereignty, submerged land that would facilitate development of unbridged, undeveloped coastal islands. Based on the staff's recommendation in favor of the moratorium, the Andrews lease application was recommended for withdrawal. The Board first approved the lease after amending it to allow 25 slips and approved the moratorium. In April 1991, George Rex Andrews and Verna Andrews Woodlief transferred title to Atsena Otie to the Depot Key Joint Venture to obtain financial resources to develop Atsena Otie in accordance with the approved development plan. The development plans for Atsena Otie include an electrical transmission line to be laid between the town of Cedar Key and Atsena Otie. An easement for the utility transmission line will be required from the Board of Trustees. The proposed rule amendments will prohibit the Trustees from granting the easement necessary for the utility transmission line. Petitioners Andrews and Depot Key Joint Venture argue that the marketability of the lots at Atsena Otie will be greatly reduced if they are unable to obtain the easement required for the utility transmission line. Facts Relevant to Petitioner Lost Tree Village Corporation Lost Tree owns undeveloped islands within the Indian River in Indian River County, Florida, which are unbridged, not served by public or private utilities and which were not platted or subdivided prior to December 18, 1990. Lost Tree has preliminary development plans for a residential development and a golf course on seven of its islands. Other islands which have large areas of wetlands will not be developed but would be part of an overall environmental enhancement and preservation plan. Lost Tree's proposed plan of development will require approval for the use of sovereign, submerged lands. The proposed rule would prohibit a bridge to the island across sovereign submerged lands, the extension of utilities, and docks on the islands. Facts Relevant to Petitioners Munz, Watrous and Broderick Thomas Munz - Burgess Island Thomas Munz is the majority owner of a corporation, Burgess Island Associates, which owns an island known as Burgess of Little Bokeelia Island in Pine Island Sound, Lee County, Florida; the minority interest owners are Munz' wife and children. The island is over 100 acres in size of which about 26 acres is uplands. The applicable local zoning will limit development of the island to 27 units. Munz' development plans for the islands offer a total of 27 homes on the island including any of the four existing structures which continue to be used as residents; some of which may be converted to an office and a museum. The existing residences are served by septic tanks and obtain potable water through a combination of wells and cisterns. The island was not platted or subdivided as of December 18, 1990. Variances have been sought from some local zoning regulations relating to road widths and other development standards, which request was in process as of October 18, 1991. There are currently four docks serving the island. As no bridge will be constructed, plans are to provide a dock for each lot for access, although physical restrictions may require some lots to share a common dock. Authorization for such docks will be needed from the Trustees. Sewage treatment is to be by septic tanks. Potable water would be provided through wells and a Reverse Osmosis (RO) system--either individual RO plants or a central system. Permits necessary for water withdrawal, treatment and distribution systems had been applied for as of October 1991, including a consumptive use permit from the South Florida Water Management District (SFWMD); and an industrial discharge permit from DER; and a water plant and distribution system permit from HRS. A surface water management permit from SFWMD was also being sought. Sufficient electrical facilities are in place to meet the needs of the proposed development. Electricity in the form of an overhead utility line from Pine Island which is submerged for a portion of its route to go underneath a channel. Petitioners urge that the marketability and value of the lots on Little Bokeelia Island would decrease without the availability of individual docks for prospective lot owners. Petitioners urge that a distant, central dock is impractical. Ted Watrous - Buck Key Ted Watrous is the majority owner of a parcel of property, approximately 100 acres in size, on an unbridged island known as Buck Key and Pine Island South. The island is approximately 325 acres in size, the remainder of which is owned by the federal government and the Sanibel-Captiva Conservation Foundation. The island is not connected by bridge to any other land mask, nor is the island platted, subdivided, or currently served by any utilities. Watrous plans to develop 28 to 30 single-family homes on a portion of Buck Key; current local land use regulations would allow up to 35 or 36 single-family residences. Primary plans are for 20 of those lots to be waterfront with individual docks. Buck Key is separated from Captiva Island by a channel approximately 500 ft. wide and which gradually slopes to a depth of approximately 8 ft. Access to Buck Key would be by boat from Captiva Island, which is bridged to the mainland through Sanibel Island. Watrous' plans for the Buck Key development include electric utility lines and telephone cable from Captiva Island. The alternative energy source available is diesel generators. Sewage treatment would be handled on-site via septic tanks. The proposed rule would allow Watrous a single two-slip dock for his parcel which he contends would be impractical and would lower his selling price for the lots due to the limited access which would be occasioned by the two-slip dock for the development. Roger Broderick - Chino Island Roger Broderick is the owner of Chino Island, a 55 acre island located in Pine Island Sound. The island is unbridged or proposed to be bridged to another island and is not currently served by utilities. Broderick plans to develop up to 15 single-family residences on the southernmost 15 acres of the island in two phases, the first phase consisting of 10 homes. The northern portion of the island will be maintained in its natural state except that as a condition of a DER permit for the installation of a subaqueous utility line to the island. An existing man-made berm around the perimeter of the northern portion of the island would be removed to improve the flushing in the area and promote reestablishment of mangroves and other native vegetation. Exotic or nuisance vegetation species such as Brazilian pepper and Australian pine would also be removed as a condition of that permit. Broderick desires to live on the island in addition to developing homesites for sale. A majority of the island including wetlands is proposed to be placed under a conservation easement in perpetuity. Of the southern portion of the island where homes are proposed to be located, a man-made canal exist in the interior of the island with direct deep- water access to Pine Island Sound. It is anticipated that individual docks to serve the residential lots will be constructed in the canal on privately owned submerged lands so no Trustee authorization would be needed to construct docking facilities. Broderick has received authorization for many aspects of his development specifically SFWMD has approved a surface water management permit for control of stormwater runoff. Broderick proposes to provide water to residences with a well and a distribution system; SFWMD has issued a withdrawal permit for the water and HRS has issued a permit for the distribution system. Broderick proposes to provide electricity to the island with a submerged utility cable. The cable would be installed by supersaturating the bottoms with water to create a trench then immediately laying the cable in the trench and allowing settlements to settle in over the cable. Both DER and the U.S. Army Corps of Engineers have issued dredge and fill permits for the installation of the subaqueous line. DER investigated the alignment of the submerged utility line and determined that its impacts would be insignificant. A portion of the submerged utility line is co-located in the maintenance channel of an existing easement for an overhead utility line issued by the Trustees to the Lee County Rural Electric Cooperative for an electric utility line running from Pine Island to Sanibel Island. An application has been submitted to the Trustees for the submerged line covering both the co- located portion of the line and the spur necessary to run to Chino from the existing corridor. As of the final hearing, that application was not complete. Broderick urges that he has explored the possibility of alternative means of providing electricity and determined that the cost would be prohibitive and the alternatives would be inconvenient, unreliable, adversely affecting the marketability of the lots. Lee County has issued a final development order for the project, authorizing commencement of construction of the infrastructure and housepads. Lee County has found the development consistent with its comprehensive plan. Sewage treatment will be provided by individual treatment systems that will disinfect the effluent prior to discharge to a drainfield; the septic tank system is not the typical design and was specifically designed to avoid impacting shellfish harvesting areas.
The Issue Petitioners challenged the Department of Environmental Protection's (Department) preliminary Final Order, alleging that Petitioners committed the "unauthorized clearing and destruction of dunes and dune vegetation for the purposes of constructing a roadway seaward of the coastal construction control line [(CCCL)] without benefit of a permit." The ultimate issue is whether the work Petitioners performed was seaward of the CCCL, and if it was, whether there was a violation of Amended Permit FR-563 and Section 161.053(2), Florida Statutes.
Findings Of Fact Parties Petitioner, Ben Withers, Inc., is a Florida corporation doing business in the State of Florida. Petitioner, Ben Withers, is the President and owner of Ben Withers, Inc., and a resident of Panacea, Florida. (Henceforth, Ben Withers and Ben Withers, Inc., are referred to collectively as "Mr. Withers," unless otherwise noted.) Mr. Withers is a licensed general contractor. The Department is the executive agency of the State of Florida operating pursuant to, among others, Chapter 161, Florida Statutes, and Chapter 62, Florida Administrative Code. Pursuant to Chapter 161, Florida Statutes, the Department administers the CCCL program for construction activities seaward of the CCCL. Coastal Construction Control Line Program The Department's Bureau of Beaches and Wetland Resources regulates construction and excavation activities seaward of the CCCL. The Department is responsible for determining and setting the CCCLs. The CCCL is a scientifically established line pursuant to Section 161.053, Florida Statutes. By definition, the CCCL "defines that portion of the beach-dune system subject to severe fluctuations based on a one-hundred-year storm surge, storm waves, or other predictable weather conditions." Rule 62B-33.002(13), Florida Administrative Code. Construction and excavation activity seaward of the CCCL is regulated by Section 161.053, Florida Statutes, and Rule 62B- 33, Florida Administrative Code. Mr. Withers admitted that he is aware of Department rules regarding beaches and coastal construction and is also aware that excavation seaward of the CCCL requires a permit unless it is otherwise exempt, and that he had this knowledge prior to the present case. Accessing the Pepper Project Site Under Amended Permit FR-563 Dog Island is a barrier island south of and about three miles off the coast of Franklin County, Florida. The island is approximately eight miles in length. There is no bridge to the island. The Pepper project site is on the far western end of the island. The Gulf of Mexico borders the island on the south and St. George Sound borders the island to the north. The most common way to access the Pepper site with any vehicle carrying equipment and materials, would be to use a boat or barge to a marina area (Tyson's Harbor) near the center of the island, or a private dock, and then traverse west down the middle of the island or down the beach itself, or a combination of the two. The Easy Street Easement is an easement area for a roadway running east and west through Dog Island. The parties agree that Easy Street and the Easy Street Easement are the same. The Easy Street Easement had been an unpaved roadway years before; part of the roadway was still visible in May 2001, and other parts had been covered with vegetation. There are portions of Easy Street and Easy Way east of the cul-de-sac which are visible roadways. See, e.g., Department Exhibit 13. Additionally, parts of Easy Street are seaward of the Department's CCCL (e.g., in the narrows area which is west of the cul-de-sac) and other parts are landward of the CCCL. See, e.g., Finding of Fact 29. Pursuant to its statutory duty, in 1996, the Department set the reference monuments R-158-R-160 for the CCCL on the west end of Dog Island. These monuments are in the narrows area of the island and run west to east. The CCCL is not visible on the ground. A surveyor is needed to locate the line. The alleged violation in this case was committed between R-158 and R-160, part of the narrows area. The Easy Street Easement on Dog Island runs both north and south from The Nature Conservancy cul-de-sac and then runs westerly to the west end of Dog Island. The CCCL Permits On October 21, 1999, the Department issued Permit FR-563 to Leonard Pepper, the property owner, for the construction of a single–family dwelling and for structures associated with the dwelling on the west end of Dog Island. Permit FR-563 contained Standard Permit Conditions that required in part: (1)(a) all construction or activity for which the permit was granted be carried out in accordance with the plans and specifications which were approved by the Department as a part of the permit; (1)(b) all construction or activity authorized under the permit shall be conducted using extreme care to prevent any adverse impacts to the beach and dune system; and (1)(g) existing beach and dune topography and vegetation shall not be disturbed except as expressly authorized in the permit. Permit FR-563 did not authorize the start of construction until a construction access plan to the Pepper project site was approved, in order to minimize impacts to the beach and dune system. On October 16, 2000, Amended Permit FR-563 was issued with a Notice to Proceed Withheld. The Amended Permit also contained Special Condition 1.5 which required the submittal and approval of "[a] construction access plan showing the route and timing for bringing equipment and materials to the site, in order to minimize impacts to the beach and dune system." The Department was concerned about the manner in which equipment and materials would be brought to the project site without causing further harm to the system. Amended Permit FR-563 did not expressly or implicitly authorize excavation or grading seaward of the CCCL in any area on Dog Island off of the project site and footprint of the house. In late 2000, Mr. Withers became involved with the Pepper project after Amended Permit FR-563 (with the Notice to Proceed Withheld) was issued on October 16, 2000. Part of Mr. Withers' job responsibility was to prepare and submit a construction access plan to the Department for approval. The Department does not normally require an access plan because most job sites are located in areas with established roads for ingress and egress. Here, there was no established road to and from the project site. The access plan was necessary in order to determine how Mr. Withers would transport equipment and materials to the Pepper project site on the west end of Dog Island due to the site's remote location and the absence of an established roadway to the site. Mr. Withers expected that materials and heavy equipment, including cranes, would be off-loaded at Tyson's Harbor, located approximately in the middle of Dog Island, and transported by vehicle to the project site along the access plan route. He expected to only transport pilings using the beach access route. On March 15, 2001, Mr. Withers submitted an access plan which described the route Mr. Withers would traverse by vehicle with construction equipment and materials. See Endnote 1. The Easy Street Easement starts at the east end of the island as an established roadway. Proceeding in a westerly direction, Easy Street comes to a dead-end at a cul-de-sac landward of the CCCL. The access plan authorized Mr. Withers to access the job site using part the Easy Street/Easy Street Easement (starting on the east end of the island) going north from The Nature Conservancy cul-de-sac, then heading in a westerly direction just south of the Ausley house (west of R-158 and just landward of the CCCL) and across the narrows area and continuing in a westerly direction along the northern shoreline and in southerly direction toward R-154. The access plan then authorized Mr. Withers to proceed in a westerly direction over the middle portion of the west-end of the island, then in a southerly direction toward the project site.1 The access plan showed a route both landward and seaward of the CCCL along the narrows area. See Department Exhibit 4- orange line then blue line after the orange circle on the west-end of the island. As described by Mr. McNeal of the Department, the access route is seaward, for the most part, of the CCCL from R-157 to R- 159 (running west to east) and landward of the CCCL east of R-159. The Department described the damaged area of 5,305.6 square feet (Department Exhibit 11A, insert "B") caused by Mr. Withers as east of R-159 and seaward of the CCCL and south of the access plan route. See also Finding of Fact 35. However, it appears that a portion of Easy Street, between R-159 and R-160, is seaward of the CCCL. Compare Department Exhibit 12 with Department Exhibits 4, 11A, and 13. During a pre-hearing deposition, Mr. Withers marked in pink the route he took through a portion of the narrows area which coincides with the portion of Easy Street between the approximate locations of R-159 and R-160, depicted on Department Exhibit 12. See Finding of Fact 43. (Mr. Withers had the Easy Street Easement staked prior to doing any work on Dog Island. See Findings of Fact 33-35.) The damaged area appears to coincide with this portion of Easy Street, and seaward of the CCCL. See Department Exhibit 11A. The access plan authorized Mr. Withers to drive (vehicular traffic) his equipment over the easement following the route depicted on the access plan until he arrived at the project site. See Endnote 1. The Department expected that travel along the access route would cause minimal and temporary damage or destruction to the topography, so the plan was considered acceptable. The access plan did not authorize excavation of a roadway within the route, including the narrows area, nor did it contemplate any other activity over or around a dune other than what might occur as a result of driving.2 The Department understood that Mr. Withers would be driving daily over the access plan route to the project site. The Department assumed that trucks would be used to transport equipment and materials. The Department did not differentiate among vehicles which could be used, including large trucks. On April 11, 2001, the Department issued a Notice to Proceed to Mr. Pepper to begin construction of his single-family dwelling in accordance with Amended Permit FR-563. The access plan is part of the Amended permit. Shortly after the Notice to Proceed was issued, The Nature Conservancy advised the Department of concerns it had with the access plan. As a result, on April 24, 2001, there was a meeting in Apalachicola, Florida, convened by the Department and attended by other interested governmental entities and private persons, including Mr. Withers. The purpose of the meeting was explore other possible ways and means of access by Mr. Withers to the Pepper project site.3 No resolution was reached during the meeting and the access plan previously approved by the Department remained effective. The previously issued Notice to Proceed was also in effect. The Violations Mr. Withers hired Kenneth Greenwood of Garlick Environmental Associates to perform a threatened/endangered species inspection, plant and animal, on an approximately 30-foot wide strip on the Easy Street Easement (approximately 1,800 feet) being utilized in Mr. Withers' access plan and within the narrows area. See Department Exhibit 13-yellow markings. On May 2, 2001, Mr. Greenwood performed the inspection within the easement that Mr. Withers had staked out by a land surveyor, approximately 15 feet on either side of the stakes. He found no threatened/endangered species. (The CCCL was not staked by Mr. Withers because, according to Mr. Withers, the Department did not ask him to locate the CCCL with stakes.) The access route depicted by Mr. McNeal in orange on Department Exhibit 4, which runs east of R-159, is similar to the description of the staked areas east of R-159, described by Mr. Greenwood and marked in yellow on Department Exhibit 13. See Findings of Fact 28-29. Both areas are landward of the CCCL. However, the 5,305.6 square foot damaged area is east of R-159 and is seaward of the CCCL. Mr. Greenwood described the area where he performed his investigation as being "relatively undisturbed," "relatively stable," having no vehicle tracks, and he stated that there were areas of bare sand as well as areas of "natural beach dune vegetation." He described the area as "relatively flat with some small amounts of mounding." The pictures taken by Mr. Greenwood within the staked easement on May 2, 2001, as part of his investigation, do not depict any vehicle tracks. After Mr. Greenwood completed his investigation on May 2, 2001, he observed Mr. Withers landward of the CCCL on a front-end loader and north of the cul-de-sac, proceeding west along the Easy Street Easement scraping off the top layer of soil and heading in a westward direction. Mr. Greenwood believed that the activity performed by Mr. Withers at this time was consistent with unpaved, road construction. According to Mr. Greenwood, the width of the scraped area appeared to be approximately the width of the bucket on Mr. Withers' front-end loader. Mr. Withers stated that he was doing minor grading landward of the CCCL with a John Deere 310-E front-end loader tractor when Mr. Greenwood was present on May 2, 2001. This tractor had a front bucket (approximately seven to eight feet wide) and a backhoe for excavating dirt on the back-end. Mr. Withers described the work which he performed when Mr. Greenwood was present as moving out and smoothing off the top of the sand landward of the CCCL in order for his equipment to get through. Mr. Withers also stated that he made areas in the easement seaward of the CCCL smooth by using the bottom of the bucket of his front-end loader to move sand around. Mr. Withers mentioned that he was very concerned that he needed to have the pathway he was utilizing in the access plan marked and smoothed off and fairly level. He believed the access plan authorized him to smooth off the areas on the access route. Mr. Withers stated that he had to have the access path level because he was bringing a self-propelled, 25-ton crane down the access path and they are top heavy and can get off balance, topple over, or get stuck. Mr. Withers described two types of work that he performed in the Easy Street Easement as: 1) clearing landward of the CCCL that required scooping and moving dirt, and 2) smoothing several areas seaward of the CCCL, just east of R-158 to around R- 160. An area of excavation damage seven feet seaward of the CCCL (beginning approximately 130 feet east of R-158) and an area 41 feet seaward of the CCCL (beginning at R-159, continuing east approximately 500 feet) are located within the area Mr. Withers stated he did some "smoothing off areas," again, east of R-158 and continuing east toward, but west, of R-160. Mr. Withers believed that Amended Permit FR-563 allowed him to use the Easy Street Easement in the access plan "to do . . . whatever was necessary and . . . needed to get [his] equipment, access [his] equipment down to the job site." He also admitted smoothing the areas. Mr. Withers also stated that Amended Permit FR-563 granted him permission to access the west end of Dog Island. Therefore, there was no need for him to locate the CCCL. Mr. Withers referred to the easement in the access plan as turning into a good pathway after he smoothed the areas. Mr. Withers stated that it was his "intention to gain access to the west end of Dog Island through a legal easement and an existing roadway" and that he wanted to utilize it. Mr. Withers testified "that he knew a lot of roads on Dog Island crossed seaward of the [CCCL]" in response to questioning whether he knew at the time of his performing work on the easement, whether or not the Easy Street Easement crossed seaward of the CCCL. He knew he was going to be traversing "fairly close" to the CCCL. Mr. Withers stated he did not knowingly violate the conditions of the Amended Permit. Mr. Withers was aware of the Department's permit requirements for work seaward of the CCCL when he performed his access work in the easement on Dog Island. However, Mr. Withers never had a survey done to figure out where the CCCL was located. Notice of the Alleged Violations Around May 2, 2001, the Department received a complaint that excavation was occurring seaward of the CCCL on Dog Island in the narrows area of the Easy Street Easement. On May 4, 2001, John A. Poppel, William Fokes, and Phil Sanders went to Dog Island on behalf of the Department to investigate the complaint of excavation in the narrows area seaward of the CCCL. On May 4, 2001, Mr. Poppel performed a survey of the narrows area and located the CCCL. He located monuments R-158- R-160. Department Exhibit 11. As a product of his survey, Mr. Poppel was able to depict the newly excavated roadway or pathway in relation to the CCCL. Mr. Poppel calculated that one area of damage was seven feet seaward of the CCCL and consisted of 503.8 square feet of damage and a second area of damage was 41 feet seaward of the CCCL and consisted of 5,305.6 square feet of damage. These square foot areas represent only the disturbed areas seaward of the CCCL, not the entire area between the CCCL and the Gulf of Mexico. Both areas of damage are within the area where Mr. Withers stated that he smoothed out the sand. As part of the May 4, 2001, investigation, William Fokes, an Engineer I with the Department, took photographs of the damaged areas and prepared an inspection report. Mr. Fokes' report indicates that an approximately 11-foot wide roadway or pathway had been cleared by excavation with the most seaward extent of the road being about 40 feet seaward of the CCCL. In addition, the report states that small dunes and beach vegetation had been destroyed. Mr. Fokes described the damage as excavation or grading done by some kind of machine, which cut and uprooted vegetation and pushed sand to the side as it leveled the ground. Mr. Fokes testified that the damage did not appear to be caused by merely traversing the area. Mr. Sanders, an engineer with the Department, processes CCCL permit applications and supervises Mr. Fokes, a field engineer. On May 4, 2001, Mr. Sanders observed the narrows area in question and confirmed that it looked like a "graded road" in that "[i]t appeared in the road bed that vegetation was gone and had been pushed out to the side, graded away," and that there was "excavation" seaward of the CCCL. Mr. Sanders stated that this activity did not comply with the approved access plan. On May 7, 2001, a Notice of Violation was issued to Mr. Withers for the "the unauthorized clearing and destruction of dunes and native vegetation for the purpose of constructing a roadway seaward of the coastal construction control line." Mr. Greenwood's photographs taken May 2, 2001, when compared with Mr. Fokes' photographs taken May 4, 2001, show that no discernable roadway or pathway was present landward or seaward of the CCCL in the narrows area at the time of Mr. Greenwood's inspection on May 2, 2001. This is evident when comparing Mr. Greenwood's photograph, Exhibit 15a, taken on May 2, 2001, with Department Exhibit 16g taken on May 4, 2001--the roadway or pathway present in the May 4, 2001, photo is absent in the May 2, 2001, photograph, and the vegetation has been removed from part of the area. Comparing Mr. Greenwood's photograph, Department Exhibit 15b, taken May 2, 2001, with Department Exhibits 16c and d, taken on May 4, 2001, also shows that the roadway or pathway was not present on the narrows portion of the Easy Street Easement at the time of Mr. Greenwood's inspection. The previously mentioned pictures, which were used for a comparison, were taken by two different people on separate dates, and from approximately the same locations. Also, Department Exhibit 16j was taken 250 feet east of R-159 and within the narrows area, facing east which shows clearing approximately 40 feet seaward of the CCCL. On May 14, 2001, at the request of the Department, Ken Jones, a principal engineer with Post Buckey et al., performed a damage assessment of the narrows portion of the Easy Street Easement which was seaward of the CCCL. Mr. Jones has a bachelor's degree in civil engineering and a master's degree in physical oceanography. Mr. Jones was familiar with the narrows area having been to Dog Island for recreation during the past 20 years and as a Dog Island property owner for the last three years. Mr. Jones described the narrows area as relatively flat and located between the St. George Sound to the north and the Gulf of Mexico beaches to the south. Between these two areas, the land is undulating sand and fairly consistent vegetation. At the time of Mr. Jones' damage assessment, he determined that a road had been cut through the vegetative portion of the dune of the narrows. Mr. Jones observed cut roots and a majority of the vegetation destroyed. Mr. Jones stated it appeared that the damage was caused by a vehicle with a blade on the front. The result was the road sat down in the sand approximately four to six inches. Mr. Jones stated that the work appeared to have been recent because distinct edges were still present. Mr. Jones took photographs and compiled an inspection report as part of his damage assessment. Mr. Jones testified that the damage "was pretty consistent from both landward and seaward of the [CCCL]." The pictures labeled Department Exhibits 18a1 and 18a2 depict a level pathway or roadway barren of vegetation seaward of the CCCL. Department Exhibit 18a4 is a photograph of a typical vegetated dune. Mr. Jones took this picture in order to have a general idea of what the vegetation coverage was in order to get an idea from a cost-estimating perspective. Mr. Jones's cost estimate for repairing the damage to the narrows area seaward of the CCCL, was approximately $7,500.00.4 Mr. Jones calculated the $7,500.00 by making an estimate of what it would cost to buy coastal vegetation, and by estimating what it would cost to employ laborers to hand rake the sand back into position and to plant the vegetation. Administrative Fine and Damages Jim Martinello, an environmental manager in charge of enforcement and compliance with the Bureau, used Mr. Jones' damage assessment estimate for informational purposes in assessing the damages amount for the narrows area. Mr. Martinello calculated the administrative fine and damages in accordance with Section 161.054, Florida Statues, and Rules 62B-54.002 and 62B-54.003, Florida Administrative Code. Rule 62B-54.002, Florida Administrative Code, provides that the Department shall assess fines for willful violations of, or refusing to comply with, for example, Section 161.053, Florida Statutes, and the fine should be sufficient to ensure immediate and continued compliance. In determining the actual fine within the range, the Department shall consider the offender's past violations, if any, and other aggravating or mitigating circumstances. Aggravating circumstances include prior knowledge of rules. Mitigating circumstances may be considered. Id. Mr. Withers had knowledge prior to the issuance of Amended Permit FR-563 of Department rules regarding permit requirements for construction activities seaward of the CCCL. On October 4, 1996, Mr. Withers, on behalf of Ben Withers Construction Company, was issued a warning letter for possible unauthorized construction seaward of the CCCL. This matter was resolved by entering into a consent order. On October 29, 1997, Mr. Withers, on behalf of Ben Withers Construction Company, was issued a warning letter for possible permit violation seaward of the CCCL. On November 13, 1997, Mr. Withers was issued a warning letter for possible unauthorized construction seaward of the CCCL. On October 27, 2000, Mr. Withers wrote a letter to Mr. McNeal indicating that he believed that the Easy Street Easement on Dog Island heading south from The Nature Conservancy cul-de- sac, then west to the west end of Dog Island, is landward of the CCCL and, therefore, no permit was necessary to reopen and use the easement, but he would have a surveyor establish the control line prior to work commencing. On November 7, 2000, Phil Sanders replied by letter to Mr. Withers' October 27, 2000 letter, in which Mr. Sanders reminded Mr. Withers of the pertinent rules and laws and suggested that Mr. Withers have the CCCL surveyed. On December 20, 2000, Mr. Martinello sent Mr. Withers an advisory letter informing him that the area he traversed (on July 2000) on the south route of the Easy Street Easement from the cul- de-sac on Dog Island was considered to be a dune as defined by Rule 62B-33.002, Florida Administrative Code. However, Mr. Martinello further advised that the Department did not take any action because "the traversing [did not] cause any substantial damage, it was minimal damage." In regard to the present case, it is more than a fair inference that Mr. Withers had specific knowledge of the CCCL and the Department's laws and rules, and that he knew excavation was not authorized seaward of the CCCL. The information in the prior Findings of Fact was used by the Department, and specifically Mr. Martinello, to determine that the harm to the beach resource or potential harm was major, and the administrative fine assessed was $7,500.00. However, part of Mr. Martinello's determination was predicated on Mr. Jones' assessment that the site one narrows violation was approximately 700 feet in length when, in fact, the area was approximately 500 feet in length, which explains in part the disparity between a 9,800 square foot area and the proven 5,305.6 square foot area. See Finding of Fact 78 and Endnote 4. Even the additional amount of damage of 503.8 square feet for the site two narrows area, when viewed in the aggregate, is significantly less than Mr. Jones' assessment of damages by square feet. (Mr. Martinello used the Jones' assessment as a guideline. Mr. Martinello says that the mistake did not alter his decision, although he was unaware of the mistake until the final hearing. He also says that Mr. Jones recommended a higher damage amount than the $5,000.00 assessed by the Department in its preliminary Final Order. He did--$7,500.00 for 9,800 square feet of damage.) Grossly negligent or knowing violations of statutes and Department rules regarding coastal construction seaward of the CCCL, which result "in harm to sovereignty lands seaward of mean high water or to beaches, shores, or coastal or beach-dune system(s), including animal, plant or aquatic life thereon," shall be considered in determining damages. Rule 62B-54.003(1), Florida Administrative Code. Rule 62B-54.003(2), Florida Administrative Code, provides that a damage amount greater than the minimum amounts may be assessed to ensure, immediate and continued compliance and the Department may consider, e.g., the need for restoration and the damaged ecological resource. The Department determined that the violation was knowing based on the factors mentioned above. The Department also considered the need for restoration and the damage to ecological resources and whether the amount would ensure immediate and continued compliance. Id. The Department determined that there was harm to the resource and that it was major and knowing. The Department proposed to assess the minimum damage amount of $5,000.00. On January 11, 2002, the Department entered a preliminary Final Order for the unauthorized grading and destruction of dunes and dune vegetation seaward of the control line for the purpose of constructing a roadway. The amount assessed in the Final Order was $12,500.00, $7,500.00 in administrative fines and $5,000.00 in damages, as described above. As noted, there has been harm to the beach area resource seaward of the CCCL and the Department proved the need for restoration and the damage to the ecological resource. In mitigation, Mr. Withers' construction access plan was approved by the Department. The Department knew that Mr. Withers intended to use the access route, which ran seaward of the CCCL from approximately R-157 to R-159 (except for a small portion between R-158 and R-159) in the narrows area; that Mr. Withers planned to transport equipment and materials by truck using the access route and necessarily would traverse seaward of the CCCL; and that he would continuously use the access route until the project was completed. The actual damaged area is less than originally determined by Mr. Jones, thus the need for restoration reduced. Mr. Jones, without the benefit of a survey, estimated the total cost to restore the damaged area of 9,800 square feet to be approximately $7,500.00. The total square feet of damage proven in this proceeding is 5,809.4 square feet in the narrows area and the Department is requesting $12,500.00 in fines and damages. Based on an approximate ratio of square feet and dollars needed to restore, a damage assessment in the amount of $4,500.00 is appropriate. Balancing the aggravating and mitigating circumstances, a fine of $3,500.00 is appropriate.
Recommendation Based on the foregoing Findings of Fact and Conclusions of Law, it is recommended that a final order be rendered as follows: That a final order be issued adopting this Recommended Order; and Within 30 days of a final order being effective, Petitioners shall pay a fine of $3,500.00 and $4,500.00 in damages with the total amount of $8,000.00, to the Department of Environmental Protection. DONE AND ENTERED this 9th day of January, 2003, in Tallahassee, Leon County, Florida. CHARLES A. STAMPELOS Administrative Law Judge Division of Administrative Hearings The DeSoto Building 1230 Apalachee Parkway Tallahassee, FL 32399-3060 (850) 488-9675 SUNCOM 278-9675 Fax filing (850) 921-6847 www.doah.state.fl.us Filed with the Clerk of the Division of Administrative Hearings this 9th day of January, 2003.
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 in this case is whether a proposed activity by Cayo Costa Island Partnership is exempt from permitting.
Findings Of Fact Cayo Costa Island is a bridgeless barrier island situated between Gasparilla Island to the north and Captiva Island to the south. East of Cayo Costa Island is Pine Island, and east of Pine Island is Cape Coral. In the 1960s, Travis Gresham subdivided and commenced development of a portion of Cayo Costa Island. Development included the dredging of canals. Eventually, one or more plat maps were recorded in the public records of Lee County, so that warranty deeds for residential lots referred to such recorded plat maps. There is also a subdivision sales plat map, which may not have been recorded. Not all of the land was subdivided into lots. The sales plat map reserves a considerable amount of land and canals for future development. One of the reserved areas is to the east of the subdivided lots. The location of the proposed dock is in the extreme southwest corner of this unplatted area. The dock would be located at the western end of a relatively wide manmade canal, which measures 2000 feet long and 105 feet wide. The east end of the canal terminates in Pine Island Sound. Petitioner and her late husband purchased from Mr. Gresham lot 16 in block 1 over 30 years ago, and they moved onto the island almost 20 years ago. The lot does not abut the canal, nor the upland adjacent to the subject dock. She has permanently resided on the island continuously since 1976. In 1984, she and her husband conveyed their property by warranty deed to the State of Florida, reserving a life estate. Petitioner's husband and some friends constructed the subject dock at the end of the canal in September 1978. A couple of years later, another nearby resident named Carl Noah substantially enlarged the dock. On March 16, 1993, Mr. Noah conveyed by warranty deed his real property to Paul Faust. At the same time, Mr. Noah gave Mr. Faust a quitclaim deed for "boat docks constructed by [Mr. Noah] to be used with the [residential] structure." After purchasing the property from Mr. Noah, Mr. Faust was contacted by Petitioner, who told him that she had previously owned the dock and that Mr. Noah had shared it with her. Mr. Faust agreed to share the dock with her, for as long as he owned it. There are no recorded easements concerning the use of the dock. On the sales plat map, the west end of the canal is clearly separated from the subdivided area by a road, which is named Harbor Drive. However, Harbor Drive was never constructed and there is no physical evidence of the proposed road. Petitioner's late husband and his friends who helped build the dock mistakenly believed that the west end of the canal terminated at Harbor Drive. Undoubtedly, other persons were similarly confused, including the property assessor, who had never assessed the property that separates the west end of the canal from Harbor Drive. However, in May 1993, Noel Andress, one of the partners of Cayo Costa Island Partnership, obtained a warranty deed from Mr. Gresham for a triangular- shaped piece of land running north just to the existing dock from the intersection of Harbor Drive and an actual road known as La Costa Drive. Mr. Andress quitclaimed the triangular-shaped parcel, which is described by metes and bounds, to Cayo Costa Island Partnership on January 13, 1994. After Mr. Andress acquired the triangular-shaped parcel, he directed his attorney to write Petitioner and Mr. Faust and inform them to remove their personal property from the real property that Mr. Andress had recently acquired. Mr. Faust is contesting this matter in court. Unfortunately, the record does not include the application or applications submitted by Cayo Costa Island Partnership. Mr. Andress testified that he submitted an application in February or March of 1993. The proposed dock, which would replace the dock built by Mr. Sellars and Mr. Noah, would serve a single family. The proposed dock would consist of two sections: a 5' by 92' main section and a 6' by 10' walkway to the upland area. Thus, the total area of the dock would be 520 square feet. The application reportedly provides that Cayo Costa Island Partnership would use turbidity barriers during construction. The location of a 92-foot dock running parallel to the end of a 2000- foot long undeveloped canal presents no impediment to navigation. There is no reason to infer an adverse impact to flood control or, as long as turbidity barriers are used, a violation of water quality standards. By letter dated June 15, 1994, the Department of Environmental Protection acknowledged receipt of the application, as well as additional drawings and documents submitted on April 8, 1994. Based on these materials, the letter states that the proposed project "appears to qualify as an activity which is exempt from the need for a Department wetland resource permit under Florida Administrative Code Rule 17-312.050(1)(h)."
Recommendation Based on the foregoing, it is hereby RECOMMENDED that the Department of Environmental Protection enter a final order dismissing the petition of Petitioner. ENTERED on November 22, 1994, in Tallahassee, Florida. ROBERT E. MEALE 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 on November 22, 1994. APPENDIX Rulings on Petitioner's Proposed Findings A-C: rejected as not findings of fact. A1: rejected as not finding of fact and irrelevant, except for last sentence, which is adopted or adopted in substance. A2-end: rejected as irrelevant, recitation of evidence, subordinate, and unsupported by the appropriate weight of the evidence. Rulings on Cayo Costa's Proposed Findings 1-10: adopted or adopted in substance. 11-12: rejected as subordinate. 13-15: adopted or adopted in substance. 16-23: rejected as subordinate, recitation of testimony, and unnecessary. 24-31: adopted or adopted in substance. 32-33: rejected as irrelevant. COPIES FURNISHED: Virginia B. Wetherell, Secretary Department of Environmental Protection Twin Towers Office Building 2600 Blair Stone Road Tallahassee, FL 32399-2400 Kenneth Plante, General Counsel Department of Environmental Protection Twin Towers Office Building 2600 Blair Stone Road Tallahassee, FL 32399-2400 Barbara Mathews Trescott Pepper Law Firm 1505 S.E. 40th St. Cape Coral, FL 33904 Mary F. Smallwood Ruden, Barnett P.O. Box 10888 Tallahassee, FL 32302 John Chaves Department of Environmental Protection Twin Towers Office Building 2600 Blair Stone Road Tallahassee, FL 32399-2400
Findings Of Fact Marvel O. Warren and his brother Dan own a parcel of beachfront property in Walton County, south of State Road 30A (SR30A) near Seagrove Beach. Like Mr. Warren, the other intervenors own beachfront in the area, which lies in County Commission District Five. In 1954, before the Warrens built their house landward of the dunes, no road ran toward the beach from SR30A. Construction traffic to the house site beat down a path, however. In Walton County, each county commissioner is responsible, within the district he represents, for road maintenance and, on existing county right-of- way, for construction of new roads. DNR's Exhibit No., 7; Testimony of Owens. Expenditures in excess of $500 for materials beyond what the county has stockpiled require approval by the full commission, however. Testimony of Owens. FIRST ROAD BUILT Albert Gavin of Freeport was county commissioner for District Five when, in 1958 or 1959, he caused a red clay road to be built from SR30A southerly along the eastern edge of the Warren property over sand dunes and onto the beach to within 20 or 30 feet of the water's edge. During Mr. Gavin's tenure, the county owned a borrow pit and kept no records of how much clay was placed where. (No records of the quantity of clay deposited on the beach at any time were offered in evidence at the hearing.) Fishermen used the road to launch boats into the Gulf of Mexico. Except for any portion that may have extended onto sovereignty land, the road lay on county-owned right-of-way. UPLAND SEGMENT PERMANENT The clay road landward of the sand dunes leading along the eastern edge of the Warren property to SR30A (the upland road) has been consistently maintained and in existence since it was originally built. The upland road ends at the bluff line, which is practically congruent with the coastal construction control line at that point on the coast. DNR's Exhibit No. 4; Testimony of Hill. At some time between 1960 and 1969, also landward of the subsequently established coastal construction control line, a clay parking lot was built adjacent to the upland road. BEACH SEGMENTS EVANESCENT Whenever clay has been placed on the beach, seaward of the crest of the landwardmost sand dune, the gulf has washed it away. Many clay roads at the site did not last the summer. Virtually no clay deposit has lasted longer than a full year. One attempt after another to construct a clay road seaward of the sand dunes (the beach segment) has failed. Witnesses testified that the sun bleached the red clay and that wind covered it with white sand but wave action has been the clay's principal nemesis. When Harold C. Lucas was commissioner for District Five from March, 1968, to January, 1969, no clay was deposited on the beach and there was no beach segment. Except for three months in 1975 when Van Ness R. Butler, Jr., of Grayton Beach, served as District Five's county commissioner, Conley Martin of Portland represented the district from 1969 to 1976. As county commissioners, both of these men directed clay to be placed on the beach at various times. COASTAL CONSTRUCTION CONTROL LINE ESTABLISHED A beach segment was in existence at the time the coastal construction control line was established, and recorded, on June 4, 1975, although the beach segment that then existed went straight from the foot of the sand dune toward the edge of the gulf, instead of veering east like the new; longer beach segment built last September. THEN EXISTING ROAD DESTROYED, REPLACED In September of 1975, Hurricane Eloise removed not only the beach segment of the road but much of the beach, including the dunes themselves. As road foreman for District Five at the time, Robert N. Budreau used a road grader and other equipment to fill a large hole between the Warren house and the sand dune and to cover over broken toilets and other debris with a mixture of sand and yellow clay. After the filling, a roadway was constructed with the same sand and clay mix, extending about 25 feet seaward of the dunes along a line perpendicular to the gulf shore. REPLACEMENT ROAD RECLAIMED BY ELEMENTS In 1976, Freddie M. Bishop was elected county commissioner for District Five. After the beach segment built by Mr. Budreau washed out, at least one constituent, Gene Wesley, asked Mr. Bishop to replace it, but Mr. Bishop broke with sisyphean tradition, and declined to place any clay on the beach, or otherwise attempt to reconstruct or replace the beach segment. By the time petitioner McLean succeeded Bishop as commissioner for District Five, the beach segment had been completely obliterated. The end of the upland road continued, however, to be one of some half-dozen points of access for four-wheel drive vehicles to Walton County's gulf beaches. Commissioner Bishop did cause two truckloads of oyster shells to be deposited on the "hump" of the landward sea dune, on or near the bluff line. NEW BEACH SEGMENT In response to constituents' requests, Mr. McLean ordered a new road built. He caused clay and gravel to be placed and compacted seaward of the coastal construction control line by county workmen and machinery, including some "borrowed" for the purpose from colleagues on the Walton County Commission. Built without a DNR permit in September of 1981, this new beach segment extends 180 feet seaward of the coastal construction control line and takes an unprecedented veer to the east. The only preexisting foundation for the new beach segment was the beach itself. Like Commissioner Anderson, Commissioner W. F. Miles "lent" county trucks he had charge of to respondent McLean, but Mr. Miles did not know in advance that Mr. McLean intended to use them to build a road on the beach. Commissioners Matthews, Miles, and Owens were aware of the existence of the coastal construction control line in Walton County and, in a general way, of DNR permitting requirements and procedures, including the fact that the County Commission itself acts on certain coastal construction applications. Commissioners Anderson and McLean did not testify on these matters. DNR has issued no permit for anything like the new beach segment at any time since the coastal construction control line wad established. DNR has no record of any inquiry concerning the new beach segment by or on behalf of petitioners McLean or Walton County, before the new beach segment was built. There was no showing that Mr. McLean sought legal advice before ordering construction of the new beach segment. Paragraphs 1 through 8 of DNR's "Final Order," as amended at the final hearing and set forth above, have been established by stipulation of the parties. The hearing officer has had the benefit of posthearing submissions, including proposed findings of fact, filed by all parties. Proposed findings have been adopted, in substance, where relevant, except when unsupported by appropriate evidence.
Recommendation Upon consideration of the following, it is RECOMMENDED: That DNR order petitioner Walton County to remove the new beach segment seaward of the Walton County Coastal Construction Control Line within 30 days of entry of a final order. That DNR remove the new beach segment seaward of the Walton County Coastal Construction Control Line itself, in the event of petitioner Walton County's noncompliance with the final order; and take steps to recover the cost from petitioner Walton County. That DNR impose no civil or administrative fine against petitioner W. L. "Billy" McLean. DONE AND ENTERED this 30th day of July, 1982, in Tallahassee, Florida. ROBERT T. BENTON, II Hearing Officer Division of Administrative Hearings The Oakland Building 2009 Apalachee Parkway Tallahassee, Florida 32301 (904) 488-9675 Filed with the Clerk of the Division of Administrative Hearings this 30th day of July, 1982. COPIES FURNISHED: George Ralph Miller, Esquire Post Office Box 687 DeFuniak Springs, Florida 32433 W. Dennis Brannon, Esquire Post Office Box 1503 Fort Walton Beach, Florida 32549 Deborah A. Getzoff, Esquire Department of Natural Resources 3900 Commonwealth Boulevard Tallahassee, Florida 32303 M. Stephen Turner, Esquire Post Office Drawer 591 Tallahassee, Florida 32303 Elton J. Gissendanner Executive Director Department of Natural Resources 3900 Commonwealth Boulevard Tallahassee, Florida 32303
