The Issue At issue in this proceeding is what costs, if any, are recoverable by petitioner as a consequence of its successful prosecution of an appeal from the agency's final order heretofore rendered in the above-styled matter.
Findings Of Fact Background On January 14, 1988, respondent, Key Biscayne Limited partnership, formerly known as Biscayne Beach Hotel Association, Ltd. (the "Hotel") , filed an application with Respondent, Department of Natural Resources (DNR), for a coastal construction control line (CCCL) permit authorizing it to conduct construction activities seaward of the Dade County CCCL on Key Biscayne, Florida. As proposed, the Hotel, which currently owns the Sonesta Beach Hotel on Key Biscayne, sought authorization to construct a nine-story 124-unit habitable addition and a one-story non habitable addition, with understructure parking, to its existing facility. Incident to such construction, the Hotel also sought authorization to construct a deck and jacuzz-type hot tub south of the addition, and authorization to excavate approximately 1,400 cubic yards of fill for the pile foundation and caps, and to deposit such fill seaward of the CCCL. Excavation for the foundation would extend a maximum of 177 feet seaward of the CCCL and placement of the excavated material would extend a maximum of 300 feet seaward of the CCCL. On August 11, 1988, DNR issued a notice of intent to approve the Hotel's application and to is sue a CCCL permit subject to the following special conditions: The issuance of the permit placard shall be withheld pending staff receipt and approval of: Two sets of specifications and final certified construction plans accurately dimensioned with elevation referenced to NGVD. Details of the foundation of the 9-story and single- story addition, pile/pile cap/column connections, column/floor slab and roof slab connections, cantilevered balconies, garage floor slab, breakaway walls, storm drainage and domestic waste disposal, and fences shall be included in the plans. Two sets of certified dimensioned site plans showing the location of the control line, existing sea grape trees, the placement of excavated material seaward of the control line, and species of salt-resistant vegetation. The site plans shall be subject to review and acceptance by the Bureau staff. Evidence that written notice has been recorded in the deed covenants and restrictions for the subject property that: The construction of any future rigid coastal protection structures on the property shall be prohibited. The deed covenants and restrictions shall be recorded in the public records of Dade County. Such deed covenants and restrictions shall be enforceable and shall not be altered unless approved by the Department of Natural Resources. The use of gravel or other similar materials or structures with the potential for becoming aerodynamically propelled missiles shall not be included in the construction of the roof. Salt-resistant vegetation such as sea oats, sea grape, panic grass, salt jointgrass, and/or other approved salt- resistant species shall be planted on the fill area. In addition, the permittee shall irrigate and apply fertilizer as appropriate for the particular species planted until the vegetation is established. A 75 percent survival rate of the vegetations shall be ensured and replanting shall be conducted until a 75 percent overall survival rate is attained and until any sizeable barren portions of the area are covered. The excavated fill material to be placed on the beach shall consist of material compatible in grain size and coloration as the native beach sand and shall come from a source located landward of the coastal construction control line. The main structure of the addition shall not extend further seaward than the projected line of the existing retaining wall located seaward of the existing swimming pool. Petitioner, Key Biscayne Council (the "Council"), filed a timely protest of DNR's action. Essentially, the Council contended that the location of the proposed construction would be seaward of the 30-year seasonal high-water line and, therefore, prohibited by Section 161.053(6)(b), Florida Statues; that the proposed construction would adversely impact the beach-dune system and adjacent properties; that construction of similar projects along the coast would have a significant cumulative impact resulting in the general degradation of the beach or dune system along that segment of shoreline; and that the proposed construction failed to comply with the setback requirements or zoning or building codes of Dade County. The Key Biscayne Council In Its petition for formal hearing, the Council alleged that it was a not-for-profit Florida corporation which had, as one of its purposes, the preservation of the environment of Key Biscayne, including its beaches. The proof at hearing failed, however, to demonstrate that the Council enjoyed corporate status but, rather, demonstrated that it was an association formed in November 1987 to give the residents of Key Biscayne a more effective voice on matters of local interest, including the preservation of the environment of Key Biscayne. The Council is governed by nine individuals who are residents of Key Biscayne. These individuals are elected to their positions by the resident members of the association, who are also registered voters in Dade County. 4/ The Council meets at least once each month, and its meetings are open to the public. The agenda for each meeting is published in the local Key Biscayne newspaper, The Islander, the week before each meeting. Of particular interest to the Council is the preservation and protection of the beaches of Key Biscayne which form an important part of that community's and the Council members' lifestyle. To date, the Council has been a motivating force behind the enactment of Dade County Ordinance No. 89-23 discussed infra, which established the CCCL as the mandatory setback line for new construction on Key Biscayne, as well as efforts to fund a cleanup of the beaches, to establish a vegetation dune system, and to protect the sea turtle population. Here, by unanimous vote of the Council, it elected to contest the propriety of DNR's proposal to approve the Hotel's application to construct the proposed additions seaward of the CCCL. Key Biscayne and the surrounding topography Key Biscayne is the southernmost barrier island in what is now a chain of barrier islands extending southward from Miami Beach. Historically, Miami Beach was connected to some extent with Virginia Key, which lies to the north across Bear's Cut from Key Biscayne. In 1835, however, a hurricane struck the area, breached whatever connection existed between Miami Beach and Virginia Key, and formed what is now known as Norris Cut. The topography of the area was further altered in 1905 when construction of Government Cut, the navigational channel for the Port of Miami, was begun. Construction of that cut severed the southern tip from Miami Beach, and formed what is now known as Fisher Island. By 1927, a jetty had been constructed on the north side of Government Cut that created an effective barrier to any along shore sediment transport to the south. Over time the channel in Government Cut was deepened and jetties on its north and south sides extended. Today, the channel is 42 feet deep and extends two miles into the ocean. The north jetty extends 3,000 feet into the ocean, and the south jetty extends 2,750 feet into the ocean. Key Biscayne, which lies to the south of Government Cut and the other islands, is a sand island, roughly "drum-stick" in shape, formed on a limestone base, with elevations ranging from 5 1/2 to 6 1/2 feet. The northern and southern portions of its eastern shore are dominated by Crandon Park and Cape Florida State park, respectively, with development concentrated in the central portion of the island. It is along this central part of the island that the Sonesta Beach Hotel exists, and where the proposed construction is to occur. Immediately north of the existing hotel lies the Silver Sands Hotel and Sand Dollar Restaurant. To the south of the hotel lies the Sheraton Beach Hotel and Beach Club and, further south, the Key Biscayne Hotel and Villas. 5/ Although Key Biscayne is generally subject to mild weather conditions and a low energy environment, it has been subjected to erosion along its eastern shore, with the more severe erosion occurring along the central portion of its shoreline. Seaward of the northern and southern portions of its eastern shore, sand shoals exist which tend to dampen the force of wave energy that would otherwise be exerted against that stretch of coast line. The center of the island is not, however, accorded similar protection and the consequent concentration of wave energy causes sand to be transported from the center of the island to its outer ends. As a result, the central portion of the island, where the subject development is proposed, has historically eroded at a faster rate than the north or south ends of the island. In September 1984, as a consequence of the severe erosion suffered to the eastern shore of Key Biscayne, Dade County was authorized to place over 411,000 cubic yards of sand along approximately 10,000 feet of shoreline on Key Biscayne, and to construct a terminal structure at the south end of the island. The beach was restored by hydraulically pumping sand onto the beach from an offshore dredge and then redistributing the sand with a bulldozer. The resulting beach is characterized as "plan form," and is expected to assume a natural profile over time by responding to the natural forces of wind and waves. The fill pipes which were used to pump sand onto the beach were removed from the area of the Sonesta Beach Hotel on July 3, 1987, and the reprofiling or redistribution of sand in that area was completed around July 20, 1987. On September 26, 1987, the renourishment project was certified complete. The 30-year erosion projection Section 161.053(6)(b) Florida Statutes, provides that DNR may not issue a permit for construction seaward of the CCCL, except for certain specific structures not pertinent to this case, if the structure is "proposed for a location which, based on the department's projections of erosion in the area, will be seaward of the seasonal high-water line within 30 years after the date of application for such permit." The "seasonal high-water line" is a creature of statute, and is defined by Section 161.053(6)(a), Florida Statues, as "the line formed by the intersection of the rising shore and the elevation of 150 percent of the local mean tidal range above local mean high-water." Here, the seasonal high-water line, which is established as an elevation, calculates to approximately 5.4 feet NGVD, and according to the survey dated August 1, 1987, which was submitted with the Hotel's application, currently derives a line that is approximately 375 feet seaward of the proposed construction. To establish the 30-year erosion projection, DNR proposes to horizontally shift the profile which was depicted on such survey in a landward direction a distance equal to the expected erosion rate over a 30-year period. Ordinarily, DNR would calculate a 30-year erosion projection based on historic erosion rates, referred to as "horizontal change rates" in Rule 16B- 33.024, Florida Administrative Code, by reviewing two or more historical surveys taken over a period of time, and measuring the amount of shoreline recession that had occurred during that period. From that figure, an erosion rate would be derived by dividing the number of years which elapsed over the period of record chosen into the amount of shoreline recession that occurred during that period. The result would be the historic erosion rate which, when multiplied by 30, would establish the location of the 30-year seasonal high-water line. However, where, as here, the beach as been renourished, consideration of the effect and performance of such project must also be considered in making the 30- year erosion projection. Rule 16B-33.024(3)(e), Florida Administrative Code. Accordingly, to determine the expected location of the seasonal high-water line in 30 years in this case, it is necessary to establish a historical shoreline change rate and to evaluate the effect and performance of the beach renourishment project. To establish an appropriate historical erosion rate for the subject site, consideration must be given to both the tidal datum relied upon to obtain the rates, and the time period selected as the period of record for analysis of historic shoreline change rates. With regard to tidal datums, the Department's rule provides that horizontal shoreline change rate values may be obtained from one of several available tidal datums, including mean high-water, mean sea level, and mean low-water. Rule 16B-33.024(3)(a), Florida Administrative Code. However, the preferred and more reliable tidal datum to use in assessing historic erosion rates is the line of mean high-water. The time period used in calculating the historic shoreline change rate is required by DNR's rule to extend from the date of the field work for the applicant's survey, which was submitted as part of the application, to the earliest date for which reliable information is available. Rule 16R- 33.024(3)(b) Florida Administrative Code. The historic shoreline change rate analysis should generally include data from points 3,000 feet on either side of the proposed construction, with the change rate for each point averaged for the time period chosen. Rule 16R-33.024(3)(g), Florida Administrative Code. In the event that coastal or shoreline protection structures exist which have influenced the shoreline data for any of the reference points, such influence must be addressed, and if such influence renders the data unreliable the rate data obtained from that point during the period of influence must be rejected. 6/ Rule 16B-33.024(3)(c), Florida Administrative Code. Historic shoreline change rates for the subject project are properly determined by reference to DNR reference monuments R-101 to R-106, located on Key Biscayne. Monument R-104 is the closest monument to the project site, lying approximately 180 to 200 feet south of the site, with the project lying between monuments R-103 and R-104. To facilitate an accurate determination of historic shoreline change rates, DNR has created the Beaches and Shores Growth Management Data Base (DNR Data Base), which consists of data from primary source maps from various governmental agencies, including the United States Coastal and Geodetic Survey, National Ocean Survey, and United States Geologic Survey. These maps have been digitized relative to the DNR monuments, which are located along- the coast at- approximately 1,000-foot intervals, and the resulting data is used to assess shoreline changes over time. Inherent in these shoreline changes are the effects of natural forces on the shoreline, such as wind, wave height, and temperature. Pertinent to this case, the surveys available in the DNR Data Base prior to 1989 were those of 1851, 1919, 1927, 1935, 1945, and 1962. In or about February 1989, DNR contracted with Florida State University to redigitize maps of Key Biscayne. As a consequence, the accuracy of existing data was enhanced and a new survey, the 1913 United States Coastal and Geodetic Survey Map, was added to the DNR Data Base. The addition of the 1913 survey to the DNR Data Base is significant to this case, since the proof demonstrates that the data derived from the 1919 survey is unreliable and should be disregarded. Accordingly, the surveys that may be reasonably relied on in this case are those of 1851, 1913, 1927, 1935, 1945, and 1962. In selecting the appropriate period to determine the historic change rate in this case, several factors should be considered. First, in 1926 a hurricane, which came very close to Key Biscayne, resulted in severe damage to the beach. This storm was reported as at least a 100-year storm event, and is the major storm of record for the area. The 1926 storm, as a naturally occurring event, should be taken into consideration in arriving at an historic erosion rate, but should not be allowed to bias the data. Accordingly, any survey immediately preceding it should not ordinarily be used as a starting point for determining an historic erosion rate, because it would overestimate the historic change rate. Similarly, the immediate post-storm survey of 1927 should not be used as the starting point for determining the historic change rate, since this data would overestimate the effects of the post-storm rebound (accretion), but ignore the erosion caused by the 1926 storm and artificially lower the erosion rate. Finally, the 1962 survey should be the most recent survey used to establish an historic erosion rate, since it marks the end of the predevelopment phase of the study. In the mid-1960's, shoreline structures (seawalls) were erected along portions of the coast, and a beach renourishment project was carried out at Crandon Park in 1969 resulting in filling at DNR Monument R-101. These events render post 1962 data unreliable in assessing an historic change rate. Here, the proof demonstrates that the appropriate time period for analyzing the historic change rate is 1851 to 1962. Based on an analysis of the historic change data for such period, the appropriate historic erosion rate for the project site is -2.3 feet per year. In reaching the foregoing conclusion, the Council's contention that pre-1919 survey data should be rejected in deriving an historic change rate because the construction of Government Cut had, by 1927, interrupted a littoral supply of sand in the neighborhood of 200,000 to 400,000 cubic yards of sand to the south has not been overlooked. However, the more credible proof demonstrates that the littoral transport of sand along this area of Florida's coast is approximately 10,000 cubic yards per year, and that little of that sand ever reached Key Biscayne. Accordingly, the construction of Government Cut had little, if any, impact on Key Biscayne. Also, notable to this conclusion is the fact that an analysis of the historic change rate from 1913 to 1962 calculates an historic erosion rate of -2.5 feet per year, an insignificant difference from that calculated for the period of 1851 to 1962, and the existence of an erosional trend at the central portion of Key Biscayne prior to the construction of Government Cut. Following the establishment of an historic erosion rate, the next step in assessing the expected location of the seasonal high-water line in 30 years in situations where, as here, the beach has been renourished, is a consideration of the effect and performance of such renourishment project. The importance of this analysis cannot be gainsaid, since a beach nourishment project may behave differently than the natural beach, as the nourishment may erode faster or slower than the natural beach or it may accrete. Factors which may cause a beach nourishment project to behave differently than the natural beach include project design, such as the length and width of the project, the seaward slope of the fill material, and the nature of the fill material; and, natural and manmade factors, such as offshore shoals, jetties, and breakwaters. The length and width of a project is very significant in terms of how long the project will remain in place. A project which is short in length will have a tendency to erode at a faster rate than a long project or the natural beach. This loss, referred to as "end losses" or "spreading-out losses," is not necessarily a loss of material from the system, but rather a redistribution of the sediment to the outer edges of the nourishment project. These spreading-out losses are caused by the project's exposure to waves that occur from offshore. As a nourishment project is exposed to waves, it reacts to the force of those waves by spreading out in an alongshore direction, resulting in a reduction in the overall width of the project. A longer project, such as the nourishment project in the existent case, will erode from the ends more slowly than a small project and, consequently, maintain its width and life for a greater period of time. The seaward slope of the nourished beach will also affect the project's performance. When a nourishment project is constructed, the seaward slope of the beach may initially be steeper than the slope which existed prior to nourishment, and may be irregular in shape compared to the natural shoreline. During the slope adjustment process, gravity and waves act on the shoreline to create a more natural slope and shape. During this process, the upland portion of the beach, as well as any irregularities in the shoreline, will experience shoreline recession, with the material being redistributed along shore and offshore. This adjustment process, and the effects it will have on the project's performance, may extend over several years after nourishment is completed. The grain size of the material used in the nourishment project can also affect the performance of the project. If the sediments used to construct the nourishment project are essentially of the same grain size and quality of the sediments which existed on the natural beach, then the nourished beach can be expected to perform, after initial slope adjustment, in much the same manner as the natural beach.. Natural features or manmade structures which may affect the performance of the nourishment project include the shoreline and offshore characteristics of the area that can increase or slow the rate at which the material may otherwise erode, or a groin or natural feature that would tend to confine the project and prevent or minimize spreading-out losses. Here, the nourishment project is a long project, approximately 10,000 feet in length. This factor will contribute favorably to the project's longevity. The material used in the nourishment project is very similar to that which existed on the natural beach. Therefore, after initial slope adjustment, the nourished beach should perform in a manner similar to the natural beach. Finally, the portion of the beach fronting the hotel is bordered to the north and south by areas which are historically stable or accreting. This factor should stabilize the ends of the project, and reduce the alongshore spread which would otherwise occur. In sum, after the slope and shoreline have adjusted to a natural profile and shape, the nourishment project should perform in a manner very similar to the pre-nourishment beach. While the nourishment project should ultimately perform similar to the pre-nourished beach, little time has elapsed since completion of the project for slope and shoreline adjustment or to demonstrate stabilization. Here, the nourished beach was profiled by man (bulldozers), with the reprofiling in she area of the hotel being completed around July 20, 1987. The Hotel submitted its application for the subject permit on January 14, 1988, together with a survey of the area dated August 1, 1987. Based on this survey, DNR proposes to establish the 30-year seasonal high-water line by horizontally shifting the profile depicted on the survey in a landward direction. To predict the performance of the beach nourishment over time, the Hotel offered the results of an analytical computer model run by Dr. Robert Dean, an expert in coastal and oceanographic engineering and coastal processes. That model predicts spreading-out losses," and considers site specific factors that will affect the nourishment project, including pre-existing shoreline conditions, size and quality of the beach fill, volume, length of the project, conditions at the end of the fill, and the affect of wave forces on the coast. The wave data relied upon by Dr. Dean to drive his model was derived from a wave gauge located just north of Government Cut. The wave characteristics at Key Biscayne are, however, dissimilar to those experienced off Miami Beach due to the wave damping characteristics of the offshore area of Key Biscayne. While dissimilar, Dr. Dean opined that the data from Miami Beach could be reliably used as a conservative estimate of the force of waves at Key Biscayne, and that his model would, thereby, present a worst case scenario or prediction of spreading-out loss of sediment on the nourished beach. Based on such analysis, Dr. Dean predicted that shoreline recession on the nourished beach, attributable to spreading-out losses, would amount to 28 feet over the next 30 years, most of which would occur in the early years of the project. When combined with the historic change rate of -2.3 feet per year for 30 years, Dr. Dean calculates that 97 feet of erosion will occur at the subject site over a 30-year period, and that at the end of that period the proposed addition will be 102 feet landward of the seasonal high-water line. DNR also made an erosion projection to predict the performance of the beach nourishment over time. In its analysis, DNR relied on monitoring data Dade County had gathered regarding the performance of the project. Such data measured, at various monuments, the amount of accretion or erosion that had occurred within the first 6 months of the project, and the amount of accretion or erosion that had occurred over the next 12 months of the project. The data was not, however, complete for all monuments within 3,000 feet of the hotel, and was otherwise unpersuasive for reasons hereinafter discussed. In performing its analysis, DNR chose to focus on one monument, PL-5- DC, which is located 200 feet north of the hotel. The data at that monument showed that within the first six months the mean high-water line (MHWL) had receded 22 feet, and that over the next 12 months it had receded an additional 10 feet. Assuming a constant rate of erosion based on those two time points, DNR concluded that initial slope adjustment or stabilization would occur within four years, and that shoreline recession on the nourished beach over that 4-year period would amount to -41.6 feet. When combined with an historic change rate of -2.3 feet for the next 26 years, DNR's methodology calculates that 101.4 feet of erosion will occur at the subject site over a 30-year period, and that at the end of that period the proposed addition will be 99 feet landward of the seasonal high-water line. 7/ While Dr. Dean's model and DNR's analysis of Dade County data may yield similar results, neither methodology is, under the circumstances of this case, persuasive proof of how the nourishment project will perform or where the 30-year seasonal high-water line will be located. Here, the proof demonstrates that Key Biscayne enjoys a low-energy environment, and that the only force of significance ordinarily exerted along its coast occurs during the winter months when northeasters impact its shoreline. It is this wave energy that would, under normal circumstances, mold or adjust the seaward slope and shoreline of the nourishment project until it reached a more natural slope and shoreline, and after which the rate of erosion would be consistent with the historic change rate. However, since completion of the nourishment project, Key Biscayne has enjoyed unusually mild weather conditions, and the usual winter storms have not occurred. Consequently, the nourishment project has yet to be subjected to the forces of nature which can be reasonably expected to ultimately mold or adjust its seaward slope and shoreline. DNR's conclusion that the nourishment project will reach stability within four years, based on its analysis of the meager data provided by Dade County, is simply unpersuasive. That data, which appears on page 6 of DNR's exhibit 5, showed that at monument PL-5-DC the MHWL had receded 22 feet in the first six months of project existence and 10 feet over the course of the next 12 months. Based solely on these two measurements, DNR calculated a straight line decreasing rate of erosion to conclude that within four years the project would erode at the historic change rate. DNR's methodology and assumption, based on only two points of measure within the first 18 months of project existence, is not credible or persuasive proof of how the nourishment project will perform, and is rendered even less persuasive In view of the mild weather that affected Key Biscayne during such time period. Dr. Dean's opinion, based on his analytical computer model, which assessed shoreline recession on the nourished beach attributable to spreading- out losses, is likewise unpersuasive proof of how the nourishment project will perform. While Dr. Dean considered spreading-out losses and the historic change rate in reaching his conclusion, he failed to address offshore losses of sediment that will occur as the seaward slope of the project adjusts to a more natural profile. Here, the proof demonstrates that the seaward slope was constructed much more steeply than the natural slope, and that in the first 18 months of project existence significant quantities of fill have been lost offshore. At monument PL-5-DC the slope remains steep. Notably, while Dr. Dean calculated a spreading-out loss for the life of the project of 28 feet under what he termed a worse case scenario of wave height, the MHWL at the nourishment project has already receded 32 feet, under mild weather conditions, in the first 18 months of existence. Compared with Dr. Dean's and DNR's conclusions, the Army Corps of Engineers (Corps), which designed the nourishment project, calculated a loss rate of approximately 22,000 cubic yards of fill each year. Should the project perform consistent with the Corps' estimate of project life, it will have receded to the Dade County erosion control line within 10 years, and over the course of the next 20 years to a point such that the proposed addition would lie seaward of the 30-year seasonal high-water line. Under the circumstances of this case, a calculation of the probable location of the 30-year seasonable high-water line, based on the Corps' estimate of the performance of the nourishment project, is more compelling than that of Dr. Dean or DNR. 8/ Impact on the beach and dune system Where, as here, construction is proposed seaward of the CCCL, Section 161.053(5)(a)3, Florida Statutes, requires DNR to consider the potential impacts which the location of the proposed structures or activities may have on the beach-dune system. That system includes the beach, the dunes, and the overwash areas, which are interrelated by the sediment erosion and accretion process. 9/ DNR's analysis of potential impacts to the beach-dune system includes both short-term and long-term impacts of proposed construction. Short-term impacts are those which may arise during construction of a project and are often a concern in sensitive areas, such as those areas characterized by natural dune features and dune-stabilizing vegetation. Long-term impacts of a project may include increased flooding caused by a lowering of dunes and increased erosion caused by a lowering of dunes or by a net loss of sand from the beach-dune system. Impact to the beach-dune system can also be caused by increased pedestrian traffic associated with the construction of a major habitable structure. Pedestrian-caused impacts are, however, a potential concern only in areas where there are dune features and stabilizing vegetation which could be destroyed. In the absence, of these dune features, pedestrian traffic has no significant impact to the beach-dune system. Here, the site of the proposed construction does not have any prominent dune features or stabilizing dune features or stabilizing dune vegetation. In fact, the site is the present location of an asphalt parking lot, which extends 40 feet seaward of the footprint of the proposed construction. Construction of the project will not result in any net excavation of material. Since dunes will not be lowered and there will be no net loss of material, there will be no increased flooding or erosion caused by the project. Under such circumstances, the proof demonstrates that there will be no long-term or short-term impacts to the beach-dune system occasioned by the project. Adverse cumulative impact on the beach-dune system Section 161.053(5)(a)3, Florida Statutes, also requires DNR to assess the potential cumulative impacts to the beach-dune system that may be caused by construction seaward of the CCCL. Here, the proof demonstrates that the proposed project, either singularly or in combination with other existing or similar projects, would not have any adverse impact to the beach-dune system. Impact on adjacent property Construction activities proposed for a location seaward of the CCCL are also analyzed by DNR to assess their impact on adjacent properties. Rule 16B-33.007(2), Florida Administrative Code. Such analysis includes a determination of whether construction activities will be confined on-site; whether a lowering of dunes will occur such that increased flooding on adjacent property could occur; whether elevations on the proposed construction site will be lowered such that flooding of adjacent property could occur; and whether proposed construction, in the event of a major storm event, would potentially increase erosion on adjacent property. Here, the proof demonstrates that construction activities will be confined on site, there will be no lowering of the dunes or elevations, and that there will be no net excavation of materials such that any increased risk of flooding or erosion could occur to either the project site or to adjacent properties. Interference with public beach access One purpose of CCCL permitting is to preserve public beach access. Sections 161.053(1) and (5)(e), Florida Statutes. "Public access" is defined as "the public's right to laterally traverse the sandy beaches of this state where such access exists on or after July 1, 1987." Section 161.021(1), Florida Statutes. The public presently does not have east-west access to the beach at the Sonesta Beach Hotel, and is not entitled to such access by law. The Hotel does not propose to hinder existing north-south (shore parallel/lateral) beach access, and the proposed project would not impede such access until the seasonal high-water line receded to the project. 10/ While the project might limit lateral access at times once the seasonal high-water line recedes, such impact would be de minimis in the instant case since construction of the project would not be seaward of existing structures on the Hotel's property. Compliance with local zoning requirements In order for a permit application to be deemed complete, an applicant must provide DNR with written evidence, provided by the appropriate local governmental-agency having jurisdiction over the activity, that the proposed development does not contravene local setback requirements or zoning or building codes. Rule 16B-33.008(2)(c), Florida Administrative Code. By letter dated February 10, 1988, the Hotel submitted to DNR a letter from Metropolitan Dade County's Department of Building and Zoning which indicated that the site plan for the proposed project was consistent with existent regulations. On April 21, 1988, DNR deemed the Hotel's application complete. While not contesting the consistency of the proposed project with local regulations at the time the Hotel's application was deemed complete, the Council contends that subsequent events have rendered its proposal inconsistent with such regulations. In this regard, the proof demonstrates that the Hotel received site plan approval for the proposed addition from Dade County in November 1988, but that its application for a bull ding permit was denied and returned to the Hotel for further action. To date the Hotel has not sought to further process such application with the County. On April 4, 1989, Dade County enacted Ordinance No. 89-23, effective April 14, 1989, relating to construction seaward of the CCCL on Key Biscayne. Pertinent to this case, the ordinance prohibits the new construction of major habitual structures and severely restricts the construction of nonhabitable structures seaward of the CCCL, absent a variance. At hearing, no proof was offered that any portion of the proposed project would qualify for a variance, or that the nonhabitable portion of the project complied with the requirements of the new ordinance. 11/
Recommendation Based on the foregoing findings of fact and conclusions of law, it is RECOMMENDED that a final order be entered denying the Hotel's application to construct and excavate seaward of the CCCL. DONE AND ENTERED in Tallahassee, Leon County, Florida, this 5th day of September 1989. WILLIAM J. KENDRICK Hearing Officer Division of Administrative Hearings The DeSoto Building 1230 Apalachee Parkway Tallahassee, Florida 32399-1550 (904) 488-9675 Filed with the Clerk of the Division of Administrative Hearings this 5th day of September, 1989.
The Issue The issue in the case is whether the Town of Beverly Beach's Comprehensive Plan Amendment 03-1, initially adopted by Ordinance 2003-ORD-6 and amended by Ordinance 2004-ORD-6, is "in compliance," as required by Section 163.3184, Florida Statutes (2004).
Findings Of Fact The Department is the state land planning agency and has authority to administer and enforce the Local Government Comprehensive Planning and Land Development Regulation Act, Chapter 163, Part II, Florida Statutes (2004). One of the Department's duties under the Act is to review proposed amendments to local government comprehensive plans to determine whether the amendments are in compliance with the Act. The Town of Beverly Beach is a small municipality in Flagler County, Florida, and has the duty and authority to adopt a local government comprehensive plan pursuant to Chapter 163, Florida Statutes (2004), and to amend the plan from time to time. In June 2002, the Town proposed to amend its Future Land Use Map (FLUM) to change some of the land uses within the 37-acre Shelter Cove Planned Unit Development (PUD). The Shelter Cove PUD was the subject of an earlier lawsuit in the circuit court for Flagler County brought by the owners and developers of the property after the Town denied their PUD application. In 2002, the court entered judgment against the Town and ordered the Town to approve the PUD application. In its order, the court included a statement that the Shelter Cove PUD was consistent with the Beverly Beach Comprehensive Plan. The purpose of the plan amendment proposed in June 2002 was to re-designate 14.25 acres from Conservation/Spoil Area to Low Density Residential, 0.75 acres of Conservation/Spoil Area to Medium Density Residential, and 8.25 acres of Low Density Residential to Medium Density Residential. The proposed amendment was transmitted to the Department for compliance review. In its July 2003 ORC Report, the Department set forth four objections to the proposed amendment: 1) increased density in a Coastal High Hazard Area; 2) no traffic impact analysis regarding emergency evacuation; 3) inadequate potable water and sanitary sewer services; and 4) unsuitability for development because of saltwater marsh and potential use by threatened and endangered animal species. The Town made changes to the proposed amendment to address the Department's objections and adopted Plan Amendment 03-1 on October 6, 2003. One significant change made by the Town was to reduce the size of the land affected by the amendment from 23.25 acres to 14.5 acres. The stated purpose of the revised amendment was to deal exclusively with the spoil areas within the Shelter Cove PUD; to convert them from Conservation to Low Density Residential. The Department was not satisfied with the changes made by the Town and on November 17, 2003, it issued a Statement of Intent To Find The Comprehensive Plan Amendment Not In Compliance. This statement did not reassert the four objections of the ORC Report, but identified only two reasons for its determination that Plan Amendment 03-1 was not in compliance: 1) increased density in a Coastal High Hazard Area that would increase evacuation clearance times and 2) inadequate sanitary sewer facilities based on the denial of the utility's permit renewal by the Department of Environmental Protection (DEP). The Department recommended remedial actions that would bring Plan Amendment 03-1 into compliance. Thereafter, the Department and Town entered into a compliance agreement to identify remedial actions by the Town that would bring the plan amendment into compliance. Pursuant to the agreement, the Town adopted remedial measures in Ordinance 2004-ORD-6 (the Remedial Ordinance) that caused the Department to determine that the plan amendment was in compliance. The Remedial Ordinance (with additions and deletions as indicated in the ordinance) states in pertinent part: Limiting Density on the 14.5-acre amendment site & Hurricane Evacuation Plan Future Land Use Element: contains policies controlling the density and intensity of development (both residential and non- residential) in the Town of Beverly Beach. Policy A.1.1.9 The Low Density Residential (LDR) land use (up to 5 dwelling units/acre) shall be applied to 14.5 acres of upland spoil sites in the Shelter Cove development as shown in Exhibit A, not to exceed a total gross density of 28 residential units. In addition to the provisions described in Policy 1.1.4, the following provisions shall apply to the Shelter Cove Development: Residential land use for the Shelter Cove Planned Unit Development(PUD)shall be limited to a maximum of 115 dwelling units. The Town of Beverly Beach shall not issue a permit or certificate of occupancy until the Building Official certifies the required public facilities and services will be provided consistent with Chapter 9J-5, Florida Administrative Code (see Policy A.1.1.1). * * * Policy A.1.1.10 No later than December 2005, Beverly Beach shall revise its comprehensive plan to update the goals, objectives and policies and future land use map series and transmit such revisions to the Department of Community Affairs. The updated plan shall reflect changes to Chapter 163, Florida Statutes, and Rule 9J-5, Florida Administrative Code, since the plan went into effect in 1991. This revision shall be based on a planning period through Year 2015, with current and forecasted conditions and satisfy data and analysis requirements. * * * Revise policies under Objective D.2.1, Beverly Beach Comprehensive Plan regarding the provision of potable water and sanitary sewer Public Infrastructure/Facilities Element: refers to the protection of water quality by specific policies that require deficiencies in wastewater treatment facilities be corrected in accordance with DEP requirements. Objective D.2.1 By December 31, 1992 December 31, 2005, the Town shall require that existing deficiencies in the wastewater treatment package plants owned by Surfside Utilities operated by Ocean City Utilities be corrected in accordance with FDER Department of Environmental Protection [DEP] requirements. Policy D.2.1.1 As the Town does not own the wastewater treatment plants nor has operational control over the same, the Town shall formalize a coordination committee to include the owner/operator of Surfside Utilities Ocean City Utilities, the members of the Town Commission, members of the Flagler County Board of County Commissioners or their appointee, members of the City of Flagler Beach Commission or their appointee, and FDER the Department of Environmental Protection [DEP] and any other identified stakeholder in the Town. Policy D.2.1.2 The Town shall use the coordination committee to address the deficiencies in the wastewater plants, to set priorities for upgrading and replacing components of the plants, and to request FDER the Department of Environmental Protection [DEP]to increase and enforce their regulations requiring periodic monitoring and maintenance of package treatment plants. Policy D.1.2.3 The Town shall use the coordination committee to investigate the feasibility of assuming operational responsibility of the wastewater treatment system by another entity. Applying the five dwelling units per acre density allowed in the Low Density Residential category to 14.5 acres would generate 72.5 units. However, as indicated above, the Remedial Ordinance also restricted the total allowable dwelling units in the 14.5 acres to 28 units. The 28 units coincide with the site plan for the Shelter Cove PUD that was the subject of the circuit court judgment. The site plan called for 28 single- family lots in the former spoil areas. Charles Osbourne, Bernard Knight, and Mary Jo Knight were residents of the Town of Beverly Beach when the Town adopted Plan Amendment 03-1. They intervened against the Town in the original proceedings initiated by the Department. Following the Department's determination that the plan amendment had been brought into compliance by the Remedial Ordinance, they filed an Amended Petition to Intervene and were realigned as the Petitioners. On some date between the filing of their original petition in this case and the date of the final hearing, Petitioners Bernard Knight and Mary Jo Knight moved out of Beverly Beach. They are no longer residents of the Town. In their Amended Petition to Intervene, the Petitioners assert that the Remedial Ordinance did not resolve all the problems originally identified by the Department's ORC Report, and Plan Amendment 03-1 is still not in compliance. The Petitioners' objections to the amendment fall into three categories: insufficient and inaccurate data and analysis, insufficient legal description for the lands affected by the plan amendment, and inadequate wastewater services available for the increased density resulting from the amendment. These three categories will be used to organize the findings of fact that follow. Data and Analysis/Maps The Petitioners assert that the maps used for Plan Amendment 03-1 and the Remedial Amendment are not the official maps currently contained in the Beverly Beach Comprehensive Plan. They contend the unofficial maps contained errors that caused some of the area designated as Conservation/Saltwater Marsh to be included in the 14.5 acres re-designated Low Density Residential. At the hearing, the Petitioners also attempted to show that maps used by the Town with Plan Amendment 03-1 were not consistent with the Beverly Beach FLUM with regard to the depiction of saltwater marsh areas outside the 14.5 acres affected by the plan amendment. Whether such discrepancies exist is not a relevant inquiry for determining whether Plan Amendment 03-1 is in compliance. A 1997 report regarding threatened and endangered animal species, prepared by Lotspeich and Associates for the developer of the Shelter Cove PUD, includes a statement that there are 10.3 acres of spoil on the 37-acre PUD site. That figure is inconsistent with the Town's claim that the lands affected by Plan Amendment 03-1 consist of 14.5 acres of spoil. Lindsay Haga, a regional planner with the Northeast Florida Regional Planning Council (Council), made the determination that there are 14.5 acres of spoil area. Because the Town does not have a professional planning staff, the Council was providing planning services to the Town under contract. Ms. Haga worked on Plan Amendment 03-1 on behalf of the Town. Ms. Haga obtained a mapping of the land uses within the Shelter Cove PUD from information maintained by the St. Johns River Water Management District (District). The land use categories are based on the Future Land Use Classification Categorization System, and were applied by the District using aerial photography. Using professional software called "ArcView," Ms. Haga derived the size of the various land uses mapped within the Shelter Cove PUD by the District. The software calculated the size of the spoil areas as 14.5 acres. According to Ms. Haga, planners use this method "100 percent" of the time to delineate land uses on future land use maps. Ms. Haga was called as a witness by the Petitioners and by Beverly Beach and testified at length on direct and cross-examination on how she determined the size of the spoil areas. Nevertheless, some ambiguity remains as to whether the size and position of the spoil areas designated in the official Town FLUM are the same as their size and position as delineated by Ms. Haga for Plan Amendment 03-1 using information from the St Johns River Water Management District. The Town and the Department seem to suggest in their joint post-hearing submittal that the size and position of the spoil areas on the FLUM can be "cleaned up" or re-drawn using more site-specific information presented at the final hearing. The implication is that, if the Town's FLUM delineated less than 14.5 acres as Conservation/Spoil Area, but better data is presented at the hearing to show that the spoil areas actually cover 14.5 acres, the FLUM delineation can be ignored or treated as if did cover 14.5 acres. The redrawing of land uses as they are depicted on an adopted FLUM is arguably beyond the authority granted to the Department in Chapter 163. That issue need not be decided on this record, however, because the more credible and persuasive evidence shows there were no material changes to the size and position of the spoil areas in Plan Amendment 03-1, and no saltwater marsh was re-designated as Low Density Residential. Data and Analysis/Topographic Information The Petitioners assert that topographic data used by the Town was flawed and did not accurately reflect that much of the Shelter Cove PUD is within the 100-year floodplain. For example, the June 2002 Transmittal Packet sent to the Department included a statement that, "According to FEMA the 100 year floodplain is confined to the saltwater marsh areas located adjacent to the Intracoastal Waterway." At the hearing, the Town admitted that some of topographic information was inaccurate and described it as a "scrivener's error." The parties stipulated to the introduction into evidence of topographic information that indicates a portion of the 14.5 acres affected by Plan Amendment 03-1 lies within the 100-year floodplain. The Petitioners have not shown how the inclusion of inaccurate topographic in the data and analysis causes Plan Amendment 03-1 to be not in compliance; or, put another way, the Petitioners have not shown how the accurate topographic information proves Plan Amendment 03-1 will be inconsistent with the Beverly Beach Comprehensive Plan or applicable state laws and regulations. The Beverly Beach Comprehensive Plan does not prohibit Low Density Residential uses in the 100-year floodplain. Data and Analysis/Clustering The Petitioners contend that the data and analysis was flawed because it included a reference to the possibility of clustering dwelling units to avoid adverse impacts to areas unsuitable for development, but the Town has no regulations that allow for or address clustering. Neither the Amended Petition to Intervene nor the evidence presented by the Petitioners makes clear how this alleged error causes Plan Amendment 03-1 to be not in compliance. Any alleged error must relate to the 14.5 acres affected by the amendment. The Petitioners did not show that clustering of dwelling units is planned or necessary on the 14.5 acres. Data and Analysis/Scrub Jays The Petitioners contend that the data and analysis is insufficient because it fails to describe and account for the current use of the site by the Florida scrub jay, a bird listed as threatened by the Florida Fish and Wildlife Conservation Commission and the United States Fish and Wildlife Service. The Town and Department stipulated that scrub jays have been seen on the property. Charles Osbourne and Gail Duggins, a birdwatcher, testified that they have seen scrub jays in the Shelter Cove PUD area on several occasions. They marked Petitioners' Exhibit 15 to indicate eight specific sites within the PUD where they had observed scrub jays. None of the marked sites are located on the 14.5 acres affected by Plan Amendment 03-1. Lotspeich and Associates conducted a scrub jay survey on the 37-acre Shelter Cove PUD in 1997. They observed no scrub jays on the 14.5 acres that will be affected by Plan Amendment 03-1. In the written report of the survey, Lotspeich and Associates concluded that, "no jays reside on-site nor did any birds react as though they were defending territory which extended onto the property." Following a second survey in 2002, Lotspeich and Associates reached the same conclusion that the property "is unlikely to support a resident Florida scrub jay population." The observations of scrub jays made by Mr. Osbourne and Ms. Duggins do not contradict the conclusions of the Lotspeich and Associates reports. Mr. Osbourne and Ms. Duggins did not offer an opinion (and no foundation was laid for their competence to offer such an opinion) that scrub jays reside on the 14.5 acres affected by Plan Amendment 03-1. The Department's ORC Report stated that the originally-proposed amendment was not consistent with Policy E 1.4.3 of the Town's comprehensive plan which calls for the Town to obtain information from appropriate agencies concerning the known locations of listed plant and animal species. The Department recommended in the ORC Report that the Town conduct a survey for gopher tortoises and other listed species. The Department's objection about listed species, however, was not included its subsequent Statement of Intent to Find The Comprehensive Plan Amendment Not in Compliance. The Town had available to it, as part of the data and analysis to support Plan Amendment 03-1 and the Remedial Amendment, the Lotspeich and Associates reports prepared for the United States Fish and Wildlife Service. The reports convey the results of Lotspeich and Associates' surveys of the Shelter Cove PUD property for gopher tortoises, scrub jays and other listed species. It is likely to be the best information available since it is a site-specific, scientific study. The Petitioners did not show that better data were available or that the Lotspeich and Associates reports are flawed. In fact, the Lotspeich and Associates reports were exhibits offered by the Petitioners. Policy E.1.4.3 of the Beverly Beach Comprehensive Plan directs the Town to adopt land development regulations that provide protections for known listed species. Land development regulations are the usual and appropriate tools for applying specific protective measures to specific development proposals. No regulations have yet been adopted by the Town to protect listed species. Listed species are not left unprotected from development activities in the Town, however, since there are both state and federal laws to protect listed species and their habitats. Data and Analysis/Beach Access The Petitioners contend that the data and analysis was insufficient because it indicated that there are five locations in the Town where the public can gain access to the beach, but the Petitioners allege there are only two public beach walkovers that qualify under the Beverly Beach Comprehensive Plan. The beach access issue relates to the Town's recreational level of service standard adopted in the Recreation and Open Space Element of the Beverly Beach Comprehensive Plan. Policy F.1.1.1 specifies that the adopted level of service standard is "Five publicly-owned beach access facilities." The Petitioners apparently believe that the easements acquired by the Town that provide for public beach access across private property do not qualify as publicly-owned beach access facilities as contemplated by the Beverly Beach Comprehensive Plan. The term "publicly-owned beach access facilities" is not defined in the Recreation and Open Space Element, but one can find a statement at page F-2 that, "Access points and parking areas are support facilities for public owned beaches." Therefore, the Town considers an access point, without any man- made structures, to be a "facility." Furthermore, the comprehensive plan, itself, includes a map that depicts the location of the five public beach access points. It must be assumed that these access points met the Town's intent and meaning. By raising the issue of whether the data and analysis for Plan Amendment 03-1 is accurate in referring to the existence of five public beach access points, the Petitioners are collaterally attacking the existing comprehensive plan. Stephen Emmett, the mayor of Beverly Beach, stated that the five public beach access points depicted in the Beverly Beach Comprehensive Plan, as well as a new sixth beach access point, are currently maintained by the Town. Description of the Land Affected The Petitioners alleged in their Amended Petition to Intervene that the Town did not have an adequate legal description for the lands affected by the plan amendment. The issue was not raised in the Petitioners' Pre-Hearing Statement. When the Department objected to the Petitioners' presentation of evidence on this issue because it was not raised in their Pre- Hearing Statement, the Petitioners voluntarily withdrew the issue. Sanitary Sewer Services The Petitioners contend that sanitary sewer services are not adequate for the increased residential density that would result from Plan Amendment 03-1. The Beverly Beach Wastewater Treatment Facility is operated by Ocean City Utilities. Ocean City's application to renew the permit for the facility was denied by DEP in September 2003 because the facility was not in compliance with several DEP regulations. As a result of the denial of Ocean City's permit renewal application, DEP would not allow new customers to connect to the Beverly Beach Wastewater Treatment Facility, including the Shelter Cove PUD. DEP subsequently approved the connection of the Shelter Cove PUD wastewater collection system to the Beverly Beach Wastewater Treatment Facility. Permitting problems associated with the treatment plant was one reason for the Department's objection to the originally proposed plan amendment and the Department's subsequent determination that Plan Amendment 03-1 was not in compliance. No evidence was presented to show that Ocean City Utilities has corrected the deficiencies in the wastewater treatment plant or has obtained a renewal permit from DEP. Nevertheless, the Department determined that Plan Amendment 03-1 is in compliance based on the changes to the Beverly Beach Comprehensive Plan called for in the compliance agreement and adopted in the Remedial Ordinance. Objective D.2.1 of the Beverly Beach Comprehensive Plan was amended to require that existing deficiencies in the wastewater treatment plant be corrected by December 31, 2005. Policies D.2.1.1, D.2.1.2, D.2.1.3 were amended to re-constitute and re-energize a coordination committee to address the deficiencies in the wastewater plant and the feasibility of giving operational responsibility to another entity (such as Flagler County). In addition, the Remedial Ordinance amended Policy A.1.19 of the Beverly Beach Comprehensive Plan to prohibit the Town from issuing a permit or certificate of occupancy for the Shelter Cove PUD "until the Building Official certifies the required public facilities and services will be provided consistent with Chapter 9J-5, Florida Administrative Code." No dispute was raised about the available capacity of the Beverly Beach Wastewater Treatment Facility to serve the Shelter Cove PUD.
Recommendation Based on the foregoing Findings of Fact and Conclusions of Law, it is RECOMMENDED that the Department of Community Affairs enter a final order determining that the Town of Beverly Beach Plan Amendment 03-1, and Remedial Ordinance 2004-ORD-6, are "in compliance" as defined in Chapter 163, Part II, Florida Statutes (2004). DONE AND ENTERED this 29th day of August, 2005, 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 SUNCOM 278-9675 Fax Filing (850) 921-6847 www.doah.state.fl.us Filed with the Clerk of the Division of Administrative Hearings this 29th day of August, 2005. COPIES FURNISHED: Shaw P. Stiller, Esquire Department of Community Affairs 2555 Shumard Oak Boulevard Tallahassee, Florida 32399-2100 Sidney F. Ansbacher, Esquire Upchurch, Bailey and Upchurch, P.A. Post Office Box 3007 St. Augustine, Florida 32085-3007 Robert J. Riggio, Esquire Riggio & Mitchell, P.A. 400 South Palmetto Avenue Daytona Beach, Florida 32114 Thaddeus Cohen, Secretary Department of Community Affairs 2555 Shumard Oak Boulevard, Suite 100 Tallahassee, Florida 32399-2100 Heidi Hughes, General Counsel Department of Community Affairs 2555 Shumard Oak Boulevard, Suite 325 Tallahassee, Florida 32399-2100
The Issue Did Respondent, Robert Skidmore, III, violate section 112.313(6), Florida Statutes (2011),1/ by using his position as county commissioner to ask a county staff member to approve a zoning application for Beach Road Boutique? Did Mr. Skidmore violate section 112.313(6) by asking a county employee to look for and selectively enforce code violations against J.J.'s Restaurant?
Findings Of Fact Based on the oral and documentary evidence presented at the final hearing and on the entire record of this proceeding, the following Findings of Fact are made: At all times relevant to this proceeding, Mr. Skidmore was a Charlotte County commissioner. Beach Road Boutique Zoning Scott and Jill Hemmes, constituents of Mr. Skidmore, owned a business known as Beach Road Boutique in Charlotte County. They sought to obtain a state alcoholic beverage sales license. In order to obtain a license, the applicant must demonstrate local zoning approval. Charlotte County Commission employees enforce and apply zoning regulations in the county. Erin Mullen-Travis is the licensing manager for Charlotte County Planning and Development. During 2011, she was the code compliance and licensing manager. Ms. Mullen-Travis has worked for Charlotte County over 26 years. One of Ms. Mullen-Travis's duties as code compliance and licensing manager was the review and approval of the zoning requirements on applications of establishments wanting alcoholic beverage licenses. Ms. Mullen-Travis first denied the zoning application of Beach Road Boutique on February 17, 2011. Mr. and Ms. Hemmes sought Mr. Skidmore's assistance getting approval for their zoning application. Mr. Skidmore called Ms. Mullen-Travis about the application. Mr. Skidmore told Ms. Mullen-Travis that he had some nice people in his office and that he needed help getting zoning approval for them. In her 26 years of employment with Charlotte County, Mr. Skidmore was the only county commissioner who had ever directly sought her assistance with constituent matters. Other commissioners had always gone through the chain-of-command. He identified the applicant, and Ms. Mullen-Travis explained why the zoning had not been approved. Ms. Mullen-Travis felt intimidated by Mr. Skidmore. Mr. Skidmore, however, did not threaten Ms. Mullen-Travis or explicitly offer any reward available to him because of his position as county commissioner. He did, however, implicitly offer a reward, if she helped the Hemmes. It is common knowledge in Charlotte County that Ms. Mullen-Travis is a NASCAR fan. Among other things, she drives a car with Dale Earnhardt and NASCAR badges and decals. During the call, Mr. Skidmore asked Ms. Mullen-Travis about her affinity for NASCAR. He also offered to get her an autographed photo of Rusty Wallace (a NASCAR driver) and tickets to a race. He told her that he had gone to school with Rusty Wallace's son. This is true. And Ms. Mullen-Travis could not have known it without Mr. Skidmore telling her. Given the context, Ms. Mullen-Travis accurately considered that the tickets and photo were offered in exchange for her approval of the application to the benefit of the Hemmes. Also, the call was made in Mr. Skidmore's official capacity. Charlotte County has a Home Rule Charter (Charter). Section 2.3(A)(1) of the Charter makes the county administrator responsible for all administrative matters and operations. Section 2.3(C)(1) states: "Except for purposes of inquiry and information, the members of the board of county commissioners shall not interfere with the performance of the duties of any employee of the county who is under the direct or indirect supervision of the county administration." Also, the long-established practice was for commissioners to only contact agency directors. Mr. Skidmore's call to Ms. Mullen-Travis was contrary to the Charlotte County Charter and the practice under it. Therefore, it was not an authorized act pursuant to his duties or authorities as a county commissioner. Mr. Skidmore and Ms. Mullen-Travis were the only participants in the call. He denies the conversation. Ms. Mullen-Travis's account is more credible. This is based upon her contemporaneous communications about the call, the common recollection of all witnesses of a NASCAR component to the conversation, the fact that she could not otherwise have known Mr. Skidmore went to school with Rusty Wallace's son, the relative personal interests of the witnesses in the outcome of the proceeding, and the demeanor of the witnesses, particularly of Mr. Skidmore's. Shonna Jenkins worked as a contractor licensing investigator for Charlotte County for a little over seven years. She held that position in 2011 and reported to Ms. Mullen-Travis. Mr. Skidmore had obtained Ms. Jenkins cell phone number. He had a practice of calling her directly to check on contractor licensing matters. He also contacted Ms. Jenkins to ask her to approve the Beach Road Boutique zoning application. J.J.'s Restaurant After a meeting held on March 3, 2011, Mr. Skidmore flagged Ms. Jenkins down in the parking lot. He asked her to "do him a favor," and "go shut them [J.J.'s Restaurant] down. I want them out of this f**ing town." Mr. Skidmore wanted Ms. Jenkins to find code violations for J.J.'s Restaurant. Mr. Skidmore said that he would make sure that Ms. Jenkins got a pay raise or a pay grade increase for this. Either the ex-boyfriend or ex-husband of Mr. Skidmore's wife and father of her child had an interest in J.J.'s Restaurant. There was conflict between the two families. Mr. Skidmore had also requested the Charlotte County director of Growth Management, Jeff Ruggieri, to take code enforcement actions against J.J.'s Restaurant. Ms. Jenkins was intimidated and feared her job with the county was in jeopardy if she did not do as Mr. Skidmore asked. Ms. Jenkins reported the conversation to Ms. Mullen-Travis and Joanna Colburn, a licensing investigator, immediately afterwards. Ms. Jenkins was visibly upset and shocked. She also contemporaneously documented the incident. Ms. Jenkins is and has been frank about her dislike for Mr. Skidmore. This hostility, as well as the mental and emotional difficulties Ms. Jenkins suffered as a result of her employment and dealings with Mr. Skidmore, does not undermine her testimony. In light of the witnesses' demeanor and corroborating evidence, her testimony is credible. In addition, although evidence established Ms. Jenkins was taking several medications, the record does not indicate that the medications in any way affect a person's memory or veracity. Mr. Skidmore's requests to Ms. Jenkins and Mr. Ruggieri to act against J.J.'s Restaurant were in violation of the Charlotte County Charter and, therefore, not authorized acts pursuant to his duties or responsibilities as a county commissioner.
Recommendation Based on the foregoing Findings of Fact and Conclusions of Law, it is RECOMMENDED that a final order and public report be entered finding that Respondent, Robert Skidmore, III, twice violated section 112.313(6) and that he be fined $5,000 for each violation for a total of $10,000, together with public censure and reprimand. DONE AND ENTERED this 27th day of February, 2015, in Tallahassee, Leon County, Florida. S JOHN D. C. NEWTON, II 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 27th day of February, 2015.
The Issue The issues for determination are: (1)whether Respondent violated Section 112.313(7)(a), Florida Statutes; (2) whether Respondent violated Article II, Section 8, Florida Constitution; and (3) if so, what penalty should be imposed.
Findings Of Fact At all times pertinent to this proceeding, and since November 1994, Kenneth Sattler (Respondent), served as a Commissioner on the St. Lucie County Board of Commissioners (Board of Commissioners). The Board of Commissioners also acts as the St. Lucie County Port and Airport Authority (St. Lucie Airport Authority). Accordingly, at all times relevant to this proceeding, Respondent was also a member of the St. Lucie Airport Authority. As a St. Lucie County Commissioner and a member of the St. Lucie Airport Authority, Respondent was subject to the requirements of Part III, Chapter 112, Florida Statutes, the Code of Ethics for Public Officers and Employees. Respondent first met Maurice Warren at an Elks Club function in early 1995. At this initial meeting, Mr. Warren mentioned to Respondent that he had a business proposition, but did not specify the nature of the business or any details related thereto. In or about June 1995, Mr. Warren met with Respondent and disclosed to him information about his proposed business venture. Mr. Warren told Respondent about Civil Aviation Academy, Inc. (CAA), a company that he had formed, and about his plans to establish a flight school. Moreover, Mr. Warren discussed the possibility of locating the school at the St. Lucie Airport. Later in the summer of 1995, Respondent met with Mr. Warren and Thomas B. Furse, a colleague of Mr. Warren, to discuss their plans to locate the proposed flight school at the St. Lucie County Airport. Respondent was particularly impressed with Mr. Furse's presentation of CAA's proposal for a flight school and believed that such a project would be good for the economy of St. Lucie County. In the summer of 1995, when the meetings between Respondent and Mr. Warren took place, CAA had developed a business plan. However, at that time, CAA was not a legal entity and appeared to have no substantial assets. CAA was incorporated by the Secretary of State on October 5, 1995. Prior to building and operating a flight school at the St. Lucie County Airport, CAA had to comply with the requirements of the St. Lucie Airport Authority. The conceptual lease was a preliminary requirement for obtaining a lease to operate at the St. Lucie County Airport. Recognizing this, in or about August 1995, CAA took steps to secure a conceptual lease by applying to the St. Lucie Airport Authority. On August 22, 1995, the Board of Commissioners granted approval for CAA to be given a conceptual lease. The conceptual lease, valid for a year, was set to expire on August 22, 1996. Respondent was not present at the August 22, 1995 meeting and did not participate in the vote. According to the conceptual lease, CAA was to "establish a full service fixed base operation on airport property." Moreover, under the terms and conditions of the conceptual lease, CAA was required to: (1) make a nonrefundable deposit of five percent of the monthly lease payment to the St. Lucie Airport Authority; (2) survey the property which was the subject of the conceptual lease; (3) develop a site plan for the property; and (4) submit the site plan to the St. Lucie County Planning and Zoning Board. Once these conditions were met, the St. Lucie Airport Authority was obligated to issue a lease to CAA. An integral part of CAA's plan to establish and operate a flight school at the St. Lucie County Airport involved purchasing an already existing flight school. At some point, CAA sought to purchase Pro-Flite, an accredited and established flight school, located in Vero Beach, Florida. Mr. Warren believed that by purchasing an accredited and established school, CAA could begin operating its flight school much sooner. At the time CAA was attempting to purchase Pro-Flite, CAA was aware that Pro-Flite had existing leases at the Vero Beach Airport, some of which extended to 2017. Moreover, CAA anticipated that the flight school initially would continue to operate from the Vero Beach location. However, if successful in its negotiations to purchase Pro-Flite, CAA fully expected that it would move Pro-Flite's operations to the St. Lucie County Airport as soon as was practical Respondent became involved with CAA on September 21, 1995, when he gave Mr. Warren $5,000 cash as seed money for CAA. Respondent believed that at least part of the funds would be used to cover the travel expenses of a person from whom CAA was seeking financial backing. Also, part of Respondent's $5,000 was used to pay all or part of the $3,267 deposit that CAA was required to pay the St. Lucie Airport Authority under the terms of the conceptual lease. In exchange for the $5,000 that Respondent gave to Mr. Warren, Mr. Warren gave Respondent a promissory note with a face amount of $5,000. The promissory note, given to Respondent by Mr. Warren on September 21 or 22, 1995, listed the borrower as CAA and was signed by Maurice Warren. Under the terms of the promissory note, Respondent would be repaid the $5,000, at an interest rate of nine percent, on September 22, 2000. Although the face amount of the promissory note was $5,000, the value of the note between September and December of 1995, is unknown. However, as of April 1996, it was determined that the promissory note had no value. In addition to the promissory note that Mr. Warren gave Respondent, Mr. Warren offered and wanted to give Respondent 500 shares of CAA stock. In response to the offer of stock in CAA, Respondent told Mr. Warren that he did not want shares of CAA stock and further indicated that this might create a conflict of interest. On September 25, 1995, Respondent obtained a power of attorney from Margaret Mansfield, the mother of his late first wife. The durable general power of attorney authorized Respondent to act for Ms. Mansfield and in her "name, place, and stead." On the date that the power of attorney was executed, Ms. Mansfield was eighty-three years old and resided in Respondent's home. Ms. Mansfield had lived with Respondent since 1977. At some point, Respondent asked Margaret Mansfield if she wanted shares of the CAA stock. According to Respondent, Ms. Mansfield told Respondent to "do what he wanted." Subsequently, Respondent asked Mr. Warren to issue the 500 shares of stock in his ex-mother-in-law's name. Mr. Warren complied with the Respondent's request. Pursuant to the aforementioned power of attorney, Respondent signed Ms. Mansfield's name on the November 16, 1995, CAA "Stockholders Agreement" and on the December 22, 1995, CAA "Stock Subscription Agreement." Ms. Mansfield was never personally involved in either of these transactions or any other business of CAA. On December 12, 1995, at the end of a meeting of the Board of Commissioners, Respondent announced that a gentleman by the name of Maurice Warren had been in attendance at the meeting, but had left after a couple of hours. Respondent mentioned that Mr. Warren was associated with the flight school being planned for the St. Lucie County Airport and then urged other commissioners to be supportive of the project. The particular issue being addressed at that time involved a request Mr. Warren recently had made to individual commissioners concerning the proposed flight school. Mr. Warren apparently had invited commissioners to come to the St. Lucie County Airport on December 18, 1995, for his public announcement regarding the flight school. At no time during the December 12, 1995, meeting of the Board of Commissioners did Respondent indicate that he was involved with Mr. Warren, CAA, and/or the proposed flight school. In or about March 1996, Respondent learned that CAA had been unable to obtain the financial support that it needed to establish its proposed flight school. At about this time, Mr. Warren contacted Respondent and asked him to assist CAA in purchasing Pro-Flite, a flight school located in Vero Beach, Florida. Respondent agreed to assist CAA in its effort to purchase Pro-Flite. In or about March 1996, when Respondent agreed to provide such assistance, he believed that CAA would be operating its proposed flight school in Vero Beach, Florida. Because Vero Beach is located in Indian River County, Respondent did not view his involvement with CAA as a "problem." On March 22, 1996, at a meeting of the CAA Board of Directors, Respondent was appointed to the CAA Board of Directors and also elected to serve as secretary of the CAA Board. Respondent was present at this meeting. When Respondent became a director and the secretary of CAA, CAA's conceptual lease remained in effect and the company was moving forward with its attempt to obtain a lease. Moreover, during the time Respondent was a director and the secretary of CAA, CAA was taking steps to purchase Pro-Flite and to eventually move the flight school to St. Lucie County Airport. After being elected to the CAA Board of Directors, Respondent followed through on his promise to assist CAA in its efforts to acquire Pro-Flite. In this regard, Respondent accompanied Mr. Warren on visits to the Pro-Flite facility in Vero Beach, Florida, and to financial institutions that might provide funds for the acquisition. On at least one occasion, Mr. Warren, Respondent and two other CAA investors went to Sun Bank to seek financing for the purchase of Pro-Flite. During this meeting, Respondent learned that only two people in attendance, Respondent and one of the other CAA investors, had sufficient assets to collateralize a loan in the amount necessary to purchase Pro-Flite. In or about April 1996, Respondent withdrew his support of CAA's proposed acquisition of Pro-Flite. The basis of Respondent's decision, as articulated in his April 19, 1996, letter to Mr. Warren, was because of Respondent's concerns about Mr. Warren's ability to provide leadership to CAA and his business practices. After withdrawing his support from CAA and its proposed acquisition of Pro-Flite, Respondent and another CAA investor formed another company. The newly formed company obtained a loan from a Vero Beach bank to keep Pro-Flite operating while the principals attempted to negotiate the purchase of the flight school. However, Respondent's new company never purchased Pro- Flite. After Mr. Warren received Respondent's April 19, 1996, letter and learned of Respondent's forming a new company and attempting to purchase Pro-Flite, the relationship between the two men became acrimonious. Although Respondent left CAA and withdrew his support of the Pro-Flite purchase, CAA's conceptual lease remained in effect. In or about May 1996, CAA apparently determined that it needed additional time in which to meet the conditions set out in the conceptual lease and, thus, requested that its conceptual lease be extended to December 1, 1996. At its May 14, 1996 meeting, the St. Lucie Airport Authority considered and approved CAA's request for an extension. Respondent abstained from voting on CAA's extension request, and stated that the reason for his abstaining was that he had previously been associated with CAA. On June 10, 1996, Respondent filed a Memorandum of Voting Conflict regarding the CAA extension request. While the conceptual lease was in effect, Curtis King, Director of the St. Lucie County Airport, went to Respondent and told him that CAA was "running behind" in complying with the conditions set forth in the conceptual lease and asked Respondent if CAA "could speed this up." After indicating that there was a possibility that CAA would be unable to meet the deadlines, Respondent asked Mr. King whether CAA might receive a refund of its "nonrefundable" deposit of $3,267 paid pursuant to the terms of the conceptual lease. Respondent then indicated to Mr. King that he had money invested in CAA.
Recommendation Based upon the foregoing Findings of Fact and Conclusions of Law, it is recommended that a Final Order and Public Report be entered finding that the Respondent, Kenneth Sattler, violated Section 112.313(7)(a), Florida Statutes; imposing a civil penalty of $4,100; and issuing a public censure and reprimand. DONE AND ENTERED this 27th day of July, 1998, in Tallahassee, Leon County, Florida. CAROLYN S. HOLIFIELD Administrative Law Judge Division of Administrative Hearings The DeSoto Building 1230 Apalachee Parkway Tallahassee, Florida 32399-1550 (850) 488-9675 SUNCOM 278-9675 Fax Filing (850) 921-6847 Filed with the Clerk of the Division of Administrative Hearings this 27th day of July, 1998. COPIES FURNISHED: Eric S. Scott Assistant Attorney General Office of the Attorney General The Capitol, Plaza Level 01 Tallahassee, Florida 32399-1050 Robert Watson, Esquire 3601 Southeast Ocean Boulevard Sewalls Point Stuart, Florida 34996 Bonnie Williams, Executive Director Commission on Ethics 2822 Remington Green Circle Suite 101 Post Office Drawer 15709 Tallahassee, Florida 32317-5709 Kerrie Stillman Commission on Ethics 2822 Remington Green Circle Suite 101 Post Office Drawer 15709 Tallahassee, Florida 32317-5709
The Issue This case concerns proposed amendments to Respondent's Rule 16N-22.009, The issues for determination are, 1) whether Petitioner has standing to challenge the proposed amendments, and 2) whether the amendments are an invalid exercise of delegated legislative authority. More specifically, the following issues are raised by the pleadings and presentation of the parties: Whether the rule amendments exceed the agency's grant of authority by creating a "no entry" or "motorboat prohibited zone", and by extending that zone into the right of way of the Intracoastal Waterway Channel. Whether the agency materially failed to follow rulemaking procedures prescribed by Section 120.54, F.S., by substantially revising the proposed amendments after a challenge had been filed, and by preparing an inadequate economic impact statement; and Whether the amendments are arbitrary and capricious because they are unnecessary or unrelated to manatee protection.
Findings Of Fact Petitioner, Gerald M. Ward, is a registered engineer residing in Riviera Beach, Palm Beach County, Florida. He owns a 30-foot Columbia sailboat, with motor power. He uses the boat for recreational purposes exclusively. Since 1973, the boat has been berthed at Old Ship Marina, within the slow speed zone of the existing rule, but approximately one mile outside of the proposed motorboats prohibited zone. Petitioner does not live on, nor own any real property abutting the proposed motorboat prohibited zone. Since 1979, Rule 16N-22.009, F.A.C. has provided two speed zones for operation of motor boats between November 15 and March 31 in Palm Beach County: an idle speed zone in all waters within one-half mile of the discharge of the Florida Power and Light Riviera Beach Power Plant, including the Intracoastal Waterway; and a slow speed zone for all inland waters lying between one-half mile and one and one-half miles of the power plant discharge, including the Intracoastal Waterway. These zones are within Lake Worth, the body of water between West Palm Beach and Palm Beach and extending both north and south. The changes proposed for Rule 16N-22.009, F.A.C., would create a third zone, "motorboats prohibited", in a much smaller area within the current idle speed zone, and in and immediately adjacent to the power plant discharge canal. The full text of the Department of Natural Resources (DNR) proposed rule was published in the Florida Administrative Weekly, Volume 15, No. 38, September 22, 1989, as follows: 16N-22.009 Palm Beach County Zones Amended. For the purpose of regulating the speed and operation of motorboat traffic between the dates of November 15 and March 31 of each year, the Palm Beach County zones are amended as follows: IDLE SPEED ZONE-All waters lying within one-half mile of the discharge of the Florida Power and Light Riviera Beach Power Plant including the Intracoastal Waterway, except those waters posted as a "Motorboats Prohibited Zone" as described in paragraph (c) below. (c) MOTORBOATS PROHIBITED ZONE - All waters lying within Lake Worth, commencing at a point exactly 300 feet north of the Riviera Beach Power Plant discharge canal and easterly to within 100 feet of the westernmost boundary of the Intracoastal Waterway, lying within Township 42 South and Range 43 East, running southerly to a point exactly 300 feet south of the abovementioned discharge canal and easterly to the westernmost boundary of the Intracoastal Waterway lying within Township 43 South and Range 43 East. The precise boundaries and effective period of the zone will be posted each year between November 15 and March 31 (see accompanying map for exact locations). (Emphasis in original denotes new text). No map was published. Sometime between September 22nd and October 16, 1989, DNR staff realized that the description of the proposed zone was defective. It failed to "close", and therefore did not adequately describe the area. At the public hearing on the proposed rule amendments, on October 16, 1989, Department staff person, Karen Lewis announced the need to make a technical change to the proposed amendments; she provided the attendees a copy of the revised description and a map depicting the zone. These changes were incorporated into the record of the rulemaking proceedings. On November 3, 1989, the DNR, Division of Law Enforcement, published a "notice of change" in the Florida Administrative Weekly, Volume 15, No. 44. The notice affected several other rules establishing zones in other counties, and the following text was published for proposed Rule 16N-22.009, F.A.C.: * * * 2. For proposed rule 16N-22.009, Palm Beach County Zones the word "amended" has been deleted from the title, and subsection (1)(c) has been corrected to read as follows: (c) MOTORBOATS PROHIBITED ZONE - All waters lying within Lake Worth, commencing at a point exactly 300 feet north of the northeast corner of the Riviera Beach Power Plant discharge canal, thence easterly to a point 100 feet west of the western boundary of the Intracoastal Waterway channel, lying within Township 42 South and Range 43 East; thence running southerly parallel to and 100 feet west of the western boundary of the Intracoastal Waterway channel for a distance of 700 feet to a point within Township 43 South and Range 43 East; thence westerly to the shoreline to a point 300 feet south of the southeast corner of the discharge canal; thence northerly 300 feet to the southeast corner of the discharge canal; thence westerly 150 feet, northerly 100 feet, and easterly 150 feet to the northeast corner of the discharge canal (inclusive of the entire waterbody comprising the Riviera Beach Power Plant discharge canal); thence northerly 300 feet to the point of origin. The precise boundaries and effective period of the zone will be posted each year between November 15 and March 31. The words "(see accompanying map for exact locations)" have been removed from subsection (1)(c). * * * A map depicting the three zones in Lake Worth was published at page 5144 of the Nov. 3rd Florida Administrative Weekly. The Intracoastal Waterway is a federal Corps of Engineers project extending the Atlantic coast length of Florida. In Palm Beach County the waterway consists of a main channel approximately 125 feet wide with 187.5 feet of right of way on each side. The waterway runs north and south in the waters of Lake Worth, hugging the mainland coast, east of Riviera Beach. The waterway is regulated by the Florida Inland Navigation District (FIND). An easement for maintenance of the project was granted by Chapter 13664, Laws of Florida (1929), and by a conveyance from the Trustees of the Internal Improvement Trust Fund to the United States, dated June 8, 1942. Petitioner has suggested, but failed to prove, that FIND has withheld necessary permission for DNR to establish its zone within a portion of the right of way. Maintenance or repair of a property owner's facilities is exempt from the prohibition of the motorboat prohibited zone. Rule 16N-22.003(3), F.A.C. The Department has received no objection nor written comment from the U.S. Army Corps of Engineers and U.S. Coast Guard, and its comment from FIND was simply that the draft map was inconsistent with the text of the September 22, 1989 version of the proposed rule. The Department has consistently intended that the zone extend into the right of way, but not into the waters of the Florida Intracoastal Waterway channel. The revised description of the boundaries of the zone, published on November 3rd, plainly effectuates that intent. There are no marinas in the area of the proposed motorboat prohibited zone. There is an existing dock owned by the U.S. Coast Guard within the zone, but arrangements have been made with the Coast Guard regarding their non-use of the dock during the posted months. The proposed zone is a very small area within an already limited speed zone. There is ample room for motorboats to navigate east of the zone, within the right of way, in the channel of the Intracoastal Waterway, and in the wide waters of Lake Worth lying east of the waterway. The proposed motorboat prohibited zone will not interfere with navigation or boats engaged in interstate commerce. The zone will be marked by signs installed by the department during the relevant months. While the exact type of marker has not been established, they will be obvious to boaters and will be easily removed by department staff. The increase in signs will not automatically increase boating accidents. In the record there are two versions of an economic impact statement accompanying the proposed rule. They do not materially differ; the revised version simply provides an expanded narrative without altering the estimated costs or the underlying conclusions. The Department estimates the cost of signs to be approximately $125.00 each, for four; and an additional $320.00 each for the pilings, for a total quantifiable cost of $1780.00. This is for signs to be attached to a piling structure. The department is currently investigating the possibility of using buoys which would be cheaper to install and remove. The $1780.00 is a one-time cost and the department anticipates that installation and removal each year will be routinely accomplished by existing field staff who are already working in that area. The zone will be enforced by the Florida Marine Patrol who already enforces the existing zones. Any associated increase in law enforcement costs will be absorbed into the existing operating budget. No small nor minority businesses are operating in the area within the proposed zone and no evidence was presented to disprove the department's estimate of no cost to those groups or to competition and open market for employment or to persons directly affected by the proposed action. The stated purpose of the proposed rule is for ". . . regulating the speed and operation of motorboat traffic to needed protection for the Florida manatee." (Notice of proposed rulemaking published in the Florida Administrative Weekly, Volume 15, No. 38, September 22, 1989.) The manatee is an endangered species, one of the original species identified in the Federal Endangered Species Act. Its estimated population is approximately 1,200 for the entire United States; many of whom are found in the waters of Florida. In 1978, the Florida Legislature passed the Manatee Sanctuary Act declaring the state to be a refuge and sanctuary for manatees. The act has also been amended at least three times since 1978, giving the department additional authority to protect the species. Motorboats kill, maim and disturb manatees. In the past five years there has been an 85 percent increase in the incidents of manatee deaths from collision with vessels. In 1988, 133 manatees were found dead in Florida; 43 were determined to have been killed by boats. In 1989, those figures had both been surpassed at the time of the hearing in this case. Since 1978, there have been 12 boat-related manatee deaths in Palm Beach County, including two deaths in 1988. No deaths have been observed this year. Manatees congregate in the winter months in the Florida Power and Light Riviera Beach power plant discharge canal and surrounding waters. The warm waters there are a refuge. Each year their numbers fluctuate according to the weather conditions. In warmer years fewer numbers are observed, and the totals range from a maximum one-day count of 60 in 1983-84, to 277 in 1987-88. The proposed rule is reasonably expected to fulfill the purpose of protecting the manatee. Prohibiting motorboat traffic in the limited area immediately in and surrounding the discharge canal will not only prevent deaths and harassment in that area, but will also keep the motorboats from scattering the animals into the busier, highly trafficked area further east and in the channel of the Intracoastal Waterway.
Findings Of Fact Permitting History This development was originally known as North Largo Yacht Club and was owned and developed originally by the Largo Brand Corporation. That developer and this development received Development of Regional Impact approval from the county commission of Monroe County in accordance with Chapter 380, Florida Statutes in 1974. In 1975 that developer received various permits and water quality certifications authorizing construction of the "Atlantic Marina" (the existing marina) from both the Florida Board of Trustees of the Internal Improvement Trust Fund and the United States Army Corps of Engineers. The marina was ultimately constructed and no further governmental approvals are required for the present Respondents to make full use of the existing marina which has an authorized boat capacity of 363 boat slips, which are situated around long piers extending from the shore of the marina basin out into the marina basin. Sometime after construction of the marina, the mortgagee, through foreclosure, obtained title to the property from Largo Brand Corporation which has since dissolved, ultimately conveying it to City National Bank as trustee under a Florida land trust. City National Bank filed the present application in its original form but in February, 1984, conveyed the property to Port Bougainville, Inc. and Port Bougainville Enterprises, Inc., the present Applicant/Respondent who succeeded City National Bank as the real parties in interest prosecuting the present permit application, as modified. The permit application as it presently exists is the result of various modifications suggested by the Department of Environmental Regulation and agreed to by the present Applicant/Respondents, which had the effect of causing the Department to change its position from one of denial of the permit to one of approval, by issuance of a Notice of Intent to grant the permit in June of 1984. The Applicant/Respondent's original decision to apply for the new permit was based upon aesthetic considerations and a desire to redesign and change the theme of the development and the marina itself. It is thus proposed that the boat-mooring facilities be moved to the periphery of the basin and the piers or docks extending out into the basin be removed. This would create an open body of water in the basin, more in keeping with the "Mediterranean Village Harbor" theme of the entire development. The original application filed in early 1984, called for realignment of the docks rather than removal, and the creation of various baylets or inlets along the access canal and contained no proposal for shoaling the existing boat basin. The Department used this original proposal as a basis for its Intent to Deny the Permit Application since it considered those modifications unacceptable in terms of the likelihood that it might degrade water quality or at least not improve the ambient water quality then existing in the marina basin and entrance canal. The Respondents acceded to the demands of the Department, employed additional consultants and redesigned the project, including the creation of a sophisticated hydrographic model by which, and through which, the Respondents ultimately proposed (with the Department's agreement) to revise the application as follows: Shoal the entire basin and canal system to no more than -6 Ft. mean low water; widen and sculpt the access canal on the west side and install solid flow baffles on the east side so as to create a sinusoidal or curving configuration in the canal to improve mixing of the water in the canal and basin system; remove the existing docks and construct new docks around the periphery of the basin so as to provide a decreased number of boat slips and capacity for a total of 311 boats; install one bubble screen surrounding the fueling facilities to contain oil and fuel spills and another at the entrance of the access canal where it opens into the Garden Cove Channel so as to prevent organic materials from outside the canal and basin system from being carried into it with tidal currents and wind; installation of "batter boards" along the length of the waterward or easterly and southeasterly side of the access canal so as to protect the mangroves along that side of the canal from the effects of wake energy caused by boats. After further "free-form" review, investigation and negotiation, the Department required, and the Respondents agreed to make the following additional modifications to the marina development plan: Shoal the north end of the basin to -4 ft. mean low water; slightly reconfigure the access canal and install an additional wave baffle on the eastern periphery of the canal in order to improve circulation in the western portion of the boat basin; relocate the proposed fueling facilities more toward the rearward center of the basin in order to further isolate them from the outstanding Florida waters lying at the outward, "seaward" end of the project; provide funds necessary to more adequately mark the Garden Cove Channel in accordance with the requirements specified by the Department of Natural Resources so as to further ensure that boat traffic and possible propeller damage could be prevented to the marine grassbeds and other marine life on either side of the Garden Cove Channel; install tidal level gauges at the mouth of the Garden Cove Channel which would show boaters wishing to use the channel and access canal the current, minimum depths prevalent in the channel and canal; grant to the Department a "conservation easement" binding upon the Respondent which would provide the following: That no hydraulic connection be made from any of the upland lakes on the Respondent's property to the marina, to the canal, to the channel or any other state waters; an agreement not to employ boat lifts that would require a dredge and fill permit from the Department; an agreement not to apply for additional permits so as to increase the number of boat slips in the marina beyond the 311 presently proposed; to develop a reef management plan in conjunction with the Florida Audubon Society to include educational programs for the public as well as underwriting the installation of mooring buoys and adequate channel markers in the John Pennekamp Reef Park, the Outstanding Florida Waters (OFW) involved in this proceeding. During the time of construction of the proposed marina modifications, the entire marina will be closed and isolated from the waters of Garden Cove by the installation of a dam at the entrance to the marina access canal where it opens into Garden Cove. The dam will remain in place until turbidity resulting from the dredging, filling and construction has settled and the waters in the marina have achieved the turbidity standards required by the Department and its rules contained in Chapter 17 3, Florida Administrative Code. All the proposed modification work will be performed landward of the surveyed mean high water line. Additionally, a storm drainage system will be installed which will prevent any stormwater runoff from being deposited into the marina harbor. The stormwater runoff will be routed away from the harbor through the use of a reverse gradient around the periphery of the harbor and runoff from the adjacent real estate development will be thus routed away from the harbor into grass swales to be collected into holding areas for filtration. Ambient Water Quality in the Marina and Garden Cove Respondents tendered Dr. Earl Rich, a professor of Biology at the University of Miami as an expert in ecology and he was accepted without objection. Since 1974 he has conducted extensive studies with attendant sampling, observation and water quality monitoring in the Port Bougainville Marina. Beginning in 1983 he also performed certain chemical analyses on the water samples from the marina. Photographs taken underwater in the marina basin were adduced and placed in evidence, as were the results of the observations and tests. It was thus established that there is a dense growth of macroalgae in the marina at a depth of about six feet, although at the nine-foot level there is much less such growth. Concomitantly, the deeper holes in the marina basin exhibit a low dissolved oxygen reading and are largely responsible for the frequently occurring, low dissolved oxygen reading in the marina system that is lower than acceptable standards embodied in Chapter 17-3, Florida Administrative Code. Garden Cove itself is a shallow embayment open toward the Atlantic Ocean in a generally easterly direction, characterized by a rocky or coarse sediment bottom substrate. It is characteristic of this area that organic materials such as seaweeds and the like, are transported by currents and winds into Garden Cove from other marine areas. The underwater vegetation in Garden Cove is lush. There are extensive shallow-water marine grass beds. These vegetated areas support a large population of marine animals and fish. Dissolved oxygen is, of course, essential to the metabolism of these organisms. The two primary means for oxygen to enter the water are as a result of photosynthetic activity of marine plants and through oxygen entering the surface waters through waves and wind action, with that surface water being distributed and mixed so as to disburse the action throughout the water column. The term biochemical oxygen demand or BOD, refers to the rate at which organisms use oxygen in the water. If there are many active photosynthetic organisms, as in Garden Cove, the production of oxygen during the day, as for instance by the seagrasses in the cove, exceeds the BOD of the plant and animal community in the water body, in which case the plants contribute excess oxygen to the air. During hours of darkness, plant and animal communities in the water body will continue to consume oxygen although there will be no photosynthesis to contribute oxygen. Therefore, in an underwater community rich in plant and animal life, such as Garden Cove, the dissolved oxygen level is typically higher during the daylight hours and BOD readings will be decreased during the night, reaching a low level during the early morning hours. Frequently, dissolved oxygen readings in Garden Cove are below state standards for waters of the State under natural conditions. These low DO readings occur commonly in Garden Cove during conditions of calm wind. Indeed, Dr. Rich has measured dissolved oxygen in Garden Cove below the four-part per million state standard even before the present marina and canal were ever constructed. Since the opening of the marina there have been times when the DO readings in Garden Cove have been lower than those inside the marina itself. Hydrodynamics of the Modified Marina The proposal by the permit applicant calls for widening the access channel into the marina to approximately 130 feet by excavating upland on the western bank of the canal. The access canal will then be reconfigured during the excavation into a winding or curving fashion. That adjustment, along with the solid flow baffles to be installed on the eastern bank of the canal, will set up a winding or sinusoidal flow of tidal currents. The sinusoidal flow will induce secondary helical currents that will move water repeatedly from the top to the bottom of the canal and then back, thereby significantly improving the mixing action. The improved mixing of the waters in the canal and marina will serve two purposes: It will disperse any pollutants so as to reduce pollutant concentrations. It will disperse the oxygen introduced into the surface waters by wave and wind throughout the water column. Dr. Bent Christensen is Chairman of the University of Florida Hydraulics Lab. Using knowledge gained in hydrographic modeling as a result of work he performed in carrying out a "Sea Grant study" under the auspices of the University of Florida, Dr. Christensen designed a computer model of the proposed Port Bougainville marina and access canal by which, in turn, he designed the winding access canal which will emulate nature in producing a turnover of water induced by current velocities and canal configuration, rather than by temperature differences in water. The computer model takes into account tidal flows and wind-induced velocities which are important to mixing of water within the system. Using this model, Dr. Christensen was able to redesign the marina canal so as to improve water quality within that system as well as improving the quality of water leaving the system into Garden Cove. Drs. Lee and Van de Kreeke are ocean engineers who testified as expert witnesses on behalf of Petitioners. They sought to dispute Dr. Christensen's conclusion that the redesign would improve DO levels within the marina based upon their independent determination that a different design would increase flushing times for the system. Flushing, however, is a simplistic way of analyzing water quality. Flushing analysis assumes that the only means to improve water quality is to replace water within the system with water from outside the system. The Christensen model and the resulting proposed design of the marina and canal, on the other hand, improves water quality through internal mixing action. The proposed design actually reduces flushing time, but more importantly, maximizes dispersion of water within the system and along with it, dissolved oxygen. The design introduces dissolved oxygen throughout the water column in the system through internal mixing because of the sinusoidal configuration of the canal and the helical currents the canal configuration sets up. The concentration of pollutants measured by the State Water Quality Standards are, in turn, reduced through the same hydrodynamics. Dr. Van de Kreeke admitted that a key ingredient in his model was the assumption he had regarding BOD in the system, but he had no idea what the BOD extant in the Port Bougainville system might be. He also admitted that his calculations did not take into consideration the factor of wind mixing of the waters in the system and acknowledged that wind can and does play an important role in flushing and mixing the waters in marinas. Finally, Dr. Van de Kreeke admitted that he could not fully analyze Dr. Christensen's assumptions in arriving at his model and design because he did not have the information Dr. Christensen relied upon. Thus, Dr. Christensen's model and design is accepted as more credible than that of Drs. Van de Kreeke and Lee. That model and design establishes that the quality of water exiting the marina into the Outstanding Florida Waters in Garden Cove will be improved by the modifications proposed to be constructed in the marina. Impact on Benthic Communities The northerly end of the marina basin will be sloped from -6 feet to - 4 feet. This widening and shallowing of the marina basin and access channel will have the affect of promoting the growth, regrowth and welfare of the benthic communities in the waters in the marina and access canal by providing greater light penetration to the bottom of the marina. The widening will have the effect of causing a greater portion of the marina bottom to be lighted during the day since at the present time, the bank and surrounding trees shade the marina basin for substantial portions of the day. The increased light penetration will result in more photosynthetic activity by the plant life in the marina and canal such that increased amounts of oxygen will be produced enhancing the dissolved oxygen levels of the marina waters. In that connection, the Respondents' expert, Dr. Rich, has examined a number of marinas and observed very healthy benthic communities in marina harbors more densely populated with boats than will be the proposed marina. Another significant improvement in the ecological status of the present marina will be the placing of a bubble screen device across the mouth of the entrance canal. This will have the effect of preventing floating organic materials such as sargassum, from entering the marina. Marinas typically experience problems related to dissolved oxygen levels in their waters because of an accumulation of floating organic material which tends to settle to the bottom creating excessive biochemical oxygen demand in their decomposition process, thus resulting in decreased dissolved oxygen levels. Thus, the bubble screen will aide in decreasing BOD. Likewise, a bubble screen device is proposed to be placed around the fueling facilities in the rearward portion of the marina basin so as to prevent the spread of pollutants such as spilled oils, greases and fuels, which may occur during routine fueling operations from time to time. Inasmuch as the modifications have been shown to cause some improvement in the dissolved oxygen level in the waters of the marina basin and access canal, it has been demonstrated that the modifications will not interfere with the conservation of marine wildlife and other natural resources. The bodies of water consisting of the marina, the access canal and Garden Cove, at the present time support a diverse marine community that can be expected to continue to flourish. Neither will the proposed activity destroy any oyster or clam beds, as none have been shown to exist in these waters. Dr. Rich has monitored waterways and offshore waters at a nearby, comparable marina, The Ocean Reef Club, for approximately ten years. He has discerned no noticeable impact on the benthic communities within that marina from a very heavy boat traffic during that period of time. The boats using The Ocean Reef Club Marina are typically larger than will use the Port Bougainville facility and boats of over 100 feet in length commonly use The Ocean Reef Club. In terms of impact on offshore benthic communities, he has observed no visible impact by the heavy amount of boat traffic using The Ocean Reef Marina from the standpoint of comparison of the experience with that marina, in terms of biological impacts, with the marina configuration proposed by the Applicant/Respondents. In short, the proposed marina configuration as contrasted to the existing permitted marina, represents an improvement because of the increased surface area providing increased oxygen exchange through wave and wind action, the shoaling which will also be beneficial to dissolved oxygen levels because of its enhancement of photosynthetic processes, and because of the proposed marina management steps designed to prevent floating organic material from entering the marina. Thus, the modified design was shown to provide a meaningful improvement in general ecological conditions within the marina and hence, in the offshore waters of Garden Cove with which the marina waters exchange and mix. Water Quality Dr. Eugene Corcoran is Professor Emeritus of the Rosensteel School of Marine and Atmospheric Sciences. He is a marine chemist and performed a chemical analyses of the samples taken for the water quality report presented by Respondents and in evidence as Respondent's Exhibit 17. Dr. Corcoran also performed the analyses for the ongoing water sampling program conducted by Dr. Renate Skinner, an expert witness for Petitioners. The Petitioners accepted Dr. Corcoran as an expert witness without objection. The proposed marina modifications involved in this permitting application were thus shown to cause no violations of the state standards for dissolved oxygen. The Rio Palenque Water Quality Study in evidence indeed documented a number of instances where dissolved oxygen fell below the state minimum standards of four parts per million in the present marina. Once the modifications are completed there still may be instances when dissolved oxygen falls below that standard, but this can be attributed to natural phenomenon and the same relatively low levels of dissolved oxygen below state standards have been observed in the offshore waters of Garden Cove itself, which is an Outstanding Florida Water. Significantly, however, it was established that concentrations of dissolved oxygen will likely increase as a result of these modifications, the inducement of the helical flow and consequent vertical mixing, the widening of the entrance canal and the shoaling of the bottoms in the marina basin and canal, as well as the measures to be taken to reduce the deposition of organic materials in the marina basin and canal. The only water quality criteria placed in contention by the Petitioners and Intervenors were dissolved oxygen and copper. Although a number of Petitioners' witnesses were qualified to address the impacts of water quality on different marine organisms, only Dr. Curry was qualified as an expert in water quality. Dr. Curry's chief concern was with dissolved oxygen, which is based on the Rio Palenque Study showing present low values for dissolved oxygen in the marina as it now exists. Dr. Curry did not establish that the proposed modifications to the marina would themselves cause dissolved oxygen violations and although he testified in great detail concerning his attempt to compute the amount of copper that might be given off by the bottom paint of boats in the modified marina, he was unable to render an opinion that the modifications would increase copper levels in the waters in the marina. He acknowledged that his calculations were based on the assumption that all the boats in the marina would be using copper anti-fouling paints and his calculations took into account an assumption that all boats in the marina would have been painted within the last six months as a base datum for his calculations. Additionally, he did not take into account dispersion ratio associated with the hydrodynamic forces present in the modified marina. Dr. Curry admitted that he had never studied copper levels in a marina environment and was unable to explain the chemical effects on water quality of copper anti-fouling paints on boats. In all his sampling, he only found one instance of a violation of the Chapter 17-3 copper standard and that occurred within only a few millimeters of the hull of a newly-painted boat. Other fallacies involved in Dr. Curry's analysis, concern the interaction of seawater with copper bottom paint. Since seawater has a high level of carbonates, copper is immediately complexed with organic compounds such as amino acids. These organic complexes are soluble in seawater and indeed, serve as important nutrients to phytoplankton and other beneficial marine organisms. Thus, that portion of the total complex copper precipitated from the water as well as that portion taken up as nutrients would not be included in any concentrations of copper measured in the water column. Additionally, Dr. Curry's computations did not take into account the dispersion of copper concentrations due to mixing or flushing, which has a direct beneficial effect on reducing concentration of copper and other pollutants in the water column. Thus, Dr. Curry's computations are deemed immaterial, inasmuch as he effectively admits that the modifications to the marina would not be detrimental to water quality. The proposed modifications will not lower ambient water quality or significantly degrade the waters in the adjacent John Pennekamp Park, Outstanding Florida Waters. Since it has been established that the marina modifications will likely improve water quality within the marina, logically, the water quality in the park to some degree might be slightly improved, since those waters exchange with the waters in the marina. There will be no increase in concentrations of any pollutants emanating from the Port Bougainville Marina as a result of the proposed modifications. Improved Marking of Garden Cove Channel The Applicant/Respondents are required to provide improved navigational markers in the Garden Cove Channel, pursuant to an amended development order. Additionally, they have agreed to provide additional channel markers delineating the channel from the entrance of the existing marina to the Garden Cove Channel proper. With regard to the Garden Cove Channel, the Respondents proposed to move certain existing channel markers to more clearly identify that channel, which would make certain portions narrower and thereby eliminate boat passage over some shallow areas populated with marine grasses which presently lie within the marked channel. The Respondents also propose to add two more sets of channel markers at the seaward end of Garden Cove Channel, so that boats exiting the channel heading for the open sea will avoid certain shallow marine grass areas. The reason for this is to avoid possible damage to valuable marine grass beds and habitat which might be caused by prop wash of boats crossing over them, as well as actual contact and scouring by propellers or potential grounding of boats navigating these areas. Witness Balfe for the Respondents has personally sounded the entire length of the access canal and Garden Cove Channel. His soundings are admitted in evidence as Respondent's Exhibit 19 and are unrefuted. It was established therefore, that the bottom configuration of that access channel is basically flat or level with only minor irregularities of less than a foot. There are no rock outcroppings or other obstructions which would reduce the controlling depth below -4 feet. Approximately 12 times per year however, during "spring tides", the ambient water depths in Garden Cove could be expected to go below -4 feet mean low water. During these times the tide will be approximately 6 to 8 inches below that normal depth. Perhaps 25 times per year the tide is 5 or 6 inches below that mean low depth. The tide gauge which will be installed will alleviate possible propeller scouring or grounding damage to grass beds and marine habitat, especially during those abnormally low tides, by providing boat operators a current, up-to-date reading on the depths in the channel. Contributions to Park Management Plan and Marina Management Plan The Applicant/Respondents have agreed to a permit condition requiring a financial commitment to assist in the management of the John Pennekamp Park so as to minimize the adverse impacts of human use of the park. This commitment includes the provision of $75,000 to finance a study and preparation of a management plan for the John Pennekamp Coral Reef State Park and Key Largo National Marine Sanctuary, which would include study of the feasibility of inaugurating an entry permit system for the park, a testing and certification program for commercial dive boat operators, possible zoning of the park to allow recovery of the park coral reefs and other resources from the impacts of human visitors, locating central mooring buoys so that visitors' boats could be moored in one restricted area to avoid damage to the delicate coral reefs, and more adequately marking the boundaries of the park. Additionally, the Respondents propose to provide $50,000 for the acquisition of anchor buoys to be placed in selected areas of the park and to provide funds to finance a survey to more adequately identify the boundaries of the park. In order to more adequately protect water quality in the marina itself, the Respondents will inaugurate a marina management program which will include the installation of a sewage pump-out station and a pump-out station for motor oils and lubricants for boats. In addition to the two bubble curtains mentioned above, the Respondents will install containment booms and absorption mats and will permanently maintain a boat equipped with absorption mats and suction equipment for fuel or oil spill removal. The marina will prohibit persons living aboard boats, to prevent attendant sewage effluent problems, and will prohibit maintenance of boats, including painting and oil changes, while boats are in the water. This program will be monitored by an environmental protection officer employed by the condominium association under the auspices of the Respondents. Many of these marina management provisions are already requirements of the Port Bougainville 1982 development order referenced above. Management of Inland Lakes Although the use and management of the inland lakes on the Respondents' property is not directly involved in this permit application proceeding, the Respondents' overall development plan encompassed by the development order anticipates that at a future time a boat lift will be installed on upland so as to allow boats to be transferred from the inland lakes into the marina for access to marine waters. The lakes themselves, however, will not be open to the marina or to outside waters. The inland lakes are anticipated to provide dockage for approximately 200 boats, with restrictions against boats exceeding 20 feet in length and boats powered by combustion engines. The Respondents expect that the inland lakes will be primarily used by small boats such as canoes or sailboats. Dry storage for boats will be maintained on an upland site, for which a DER permit is not required. Neither is a permit for a boat transfer facility required since it would not involve dredging, filling or construction over water. The use of a boat lift, although it itself is not an issue before the Hearing Officer in this proceeding, would involve the potential of 200 or more boats using the marina in addition to those for which the marina is designed. This could occasion substantially greater risk for oil, grease and fuel spills and other potential damage to the water quality within the marina and damage to the marine habitat, grass beds and so forth within the marina, the access canal and the adjacent areas in Garden Cove. Accordingly, the conservation easement which the Respondents have agreed to provide the department as a condition to the grant of this permit should be amended to add a further condition on a grant of this permit so as to preclude placement of boats from the inland lakes into this marina or its access canal. Such a restriction would comport with the proposed uses of the inland lakes established by Mr. Scharenberg, the Respondent's principal. Boating Impacts Boat traffic in the Garden Cove Channel area is significant, with heaviest traffic occurring on the weekends when approximately two to three hundred boats navigate that channel. The boats presently using Garden Cove Channel come from a number of nearby marinas, small fishing docks and dry storage areas, as well as from a marked navigational channel called North Creek that provides access to the Garden Cove area and the Atlantic Ocean from Largo Sound. A small canal cuts through Key Largo into Largo Sound and provides access for boats in the Black Water Sound and other areas on the west side of Key Largo to the Garden Cove area and the Atlantic. The Port Bougainville Marina is expected to attract a mix of boats typical for such a marina, with the majority consisting of boats ranging from 27 to 35 feet in length. Approximately 20 percent of the boats will likely be in the 40-foot range. Larger boats may also use the marina, particularly those with a shallow draft, and "shoal draft" sailboats of 35 to 40 feet can safely navigate in and out of the marina. The marina, as it would be modified, would permit use of boats with a draft of up to three and one-half feet, although deeper draft boats could use the marina by timing arrivals and departures for the high tide, which is a common mode of operation by boat operators in the Florida Keys and other marine areas. The Port Bougainville Marina will contribute approximately 30 to 50 boats to the Garden Cove boat traffic on an average weekend out of the possible 311 boats in the harbor as it is proposed to be constructed. There will be a lesser number of boat arrivals and departures during the weekdays. The primary users of boats in and out of the marina will be people who own condominiums in the attendant real estate development. Temporary visitors, not owning boats moored in the marina, would typically use the dive charter boats and other rental boats in the surrounding areas, such as at the Ocean Reef facility. The existing marina which is already permitted and can be fully used at the present time from a legal standpoint, could accommodate the same reduced number and sizes of boats as the proposed modified marina by simply removing some of the present docks and finger piers. The Respondents propose to maintain approximately 20 slips for boats which are not owned by condominium unit owners, and they anticipate operating six to seven deep-sea charter boats as well as five smaller skiff-type charter boats, and perhaps as many as two dive charter boats with additional demands for charters to be serviced by charter boats in the surrounding areas. Boating adverse impacts on the marine benthic communities inside and outside of the marina will be minimized by the construction configuration of the marina and boat slips, the shoaling and widening of the marina basin and canal, and the channel marking and tidal gauging provisions proposed by the Applicant/Respondents. These safety arrangements would be further enhanced by the above-mentioned restriction on the placing of boats into the waters of the marina and canal from the inland lakes. The configuration of the proposed modified marina and the shoaling will have a beneficial effect in rendering use by extremely large boats, which might cause propeller, wake or grounding damage to the marine benthic communities unlikely because of the inaccessibility caused by the intentional shoaling. Coral Reef Impacts Dr. Peter Glynn is a qualified expert in marine ecology and was accepted as an expert witness in that area with particular emphasis, through his long specialization, in the ecology of corals and coral reefs. He has researched the effects of sediments, herbicides, pesticides, oxygen levels, temperature, salinity, tidal effects and oil pollution on corals. He testified as a rebuttal witness addressing concerns raised by Petitioners' and Intervenor's witnesses with regard to boat traffic, attendant turbidity and possible synergistic effects on coral reefs caused by oils, greases, low oxygen levels and turbidity. Dr. Glynn has studied corals in many areas of the world including the Caribbean and the Florida Keys. The coral reefs in Florida are similar to those in the Caribbean area and belong to the same "biogeographic province." He has dived in and examined the Garden Cove area and found four species of small reef building corals in Garden Cove. These were found in the vicinity of a shipwreck near the channel entrance to Garden Cove and the remainder of the corals observed in Garden Cove were in the bottom of the boat channel running through Garden Cove. There were no corals observed on the grass flats and in shallower areas of Garden Cove. The corals occurring in the boat channel are in isolated colonies of less than a foot in diameter. The Petitioners and Intervenors attempted to raise the possibility of synergistic adverse effects on corals posed by combinations of oils, oxygen levels, temperatures and sedimentation or similar impacts. It was not shown how or at what concentration turbidity might combine with various oxygen levels, temperatures or degrees of light penetration to produce such effects, however. The only type of synergistic effects on corals Drs. Glynn and Corcoran have observed is that between oils and pesticides. Although this effect has been demonstrated in another study area far removed from the Florida Keys, no such pesticide and oil synergistic impact has been observed in the Florida Keys area, chiefly because it is not an agricultural area characterized by significant use of pesticides. Likewise it was not established that suspended sediments in the Garden Cove area could have an adverse effect on corals by reducing light penetration. In tropical areas such as the Keys, light penetration is often saturating or in greater quantities than are really needed for healthy coral growth and indeed, many corals in these areas have pigments that naturally shield them from excess light because these coral species actually can suffer from too much light penetration. Additionally, Dr. Glynn has observed good coral reef health and growth in areas that are highly turbid. It was not established that an increase of sedimentation deposit on corals will necessarily have an adverse impact, particularly because most corals can accept a substantial amount of fine-grain sediment deposition without adverse effect. The manner in which the proposed marina modifications will be accomplished will minimize sedimentation at any rate since the canal will be dammed off from Garden Cove until all work is completed and all sedimentation within the marina and marina access canal has subsided to levels compatible with the state standards for turbidity. In any event, there is no evidence that boat traffic in Garden Cove at the present time influences the distribution and health of live coral, particularly since the main coral abundance in Garden Cove occurs in the heavily-used boat channel at the present time. Likewise, Dr. Glynn established that sediments from any increase in boat traffic in Garden Cove will not likely drift out on the offshore reef tract and be deposited on the reefs to their detriment in any event, since the fine sediments occurring in Hawk Channel and in Garden Cove, are largely precluded from deposition on the offshore reefs because the waters over the reef tract offshore have very different physical characteristics. That is, there is distinct interface between the inshore and oceanic waters caused by the strong wave assault and current action near the reefs, which precludes the fine sediments from the inshore areas remaining in the area of the reefs. Finally, any increase in the number of people visiting the Pennekamp Park attributable to use of the modified marina will not inevitably lead to degradation of the reefs. By way of comparison, studies of Kaneoi Bay in Hawaii where a major pollutant source from human sewage caused degradation of the coral reefs, showed that when sewage effluent was subsequently directed away from the reefs, the reefs rejuvenated and repopulated and are now used extensively for recreational activities without observable biological degradation. These studies are consistent with studies Dr. Glynn referenced with regard to Biscayne Bay National Park, which have shown no significant degradation occasioned by human visitation of the reefs in that park. Those studies have not shown a significant difference between the health of the "controlled reefs" and the reefs which are allowed to be used for recreational purposes. It was thus not established that there will be any degradation of the corals in the near-shore areas of Garden Cove nor in the offshore reef areas occasioned by any increased boat traffic resulting from the modification of the marina. Indeed, it was not demonstrated that the mere modification of the marina, which will actually accommodate fewer boats than are presently permitted, will cause any increase in present boat traffic at all. Dr. Glynn, in the course of his teaching and studies in the field of marine ecology has become familiar with the causes and effects of Ciguatera toxin in marine environments. He recently participated in the study of possible Ciguatera toxin at the grounding site of the freighter Wildwood on Molasses Reef, some miles distant from the marina site. All cases reported of such harmful concentrations of this toxin have originated from open water, outer coral reef environments, and not from near shore areas such as those involved in this case, where seagrasses and mangroves are the dominant marine communities. Ciguatera toxin organisms require clear open ocean water with strong currents and well-developed coral reefs which are found offshore in the Keys and not in the near-shore mangrove-type environments. The cause of Ciguatera is a concentration of toxin in the food chain. Although the bacteria that cause Ciguatera Toxin in fish, and resulting harmful effects in humans, occur everywhere in marine waters, the bacteria are not a hazard because generally, conditions are not appropriate for the bacteria to multiply. The two main species of dinoflagellates, that have been associated with causing Ciguatera poisoning do not occur in an environment such as the Port Bougainville Marina. They are typically concentrated in larger fish such as snapper, grouper and barracudas which cause problems when they are eaten by people. These species are not generally found in the inshore mangrove and grassbed areas such as are involved in the case at bar. Thus, the concerns expressed by Petitioner's witnesses concerning the possibility of Ciguatera poisoning occurring because of possible damage to corals and coral death caused by the dredge and fill operations, and boat operation associated with the marina and Garden Cove are, in reality, only unsubstantiated speculation.
Recommendation Having considered the foregoing Findings of Fact, Conclusions of Law, the evidence of record, the candor and demeanor of the witnesses and the pleadings and arguments of the parties, it is, RECOMMENDED: That the State of Florida, Department of Environmental Regulation, issue the requested permit subject to the conditions incorporated in the agreement or "conservation easement" executed between the Department and the Respondents with the further condition added to that conservation easement such that the deposition of boats from the inland lakes system into the marina and its access canal be prohibited. DONE and ENTERED this 9th day of April, 1985 in Tallahassee, Florida. P. MICHAEL RUFF 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 9th day of April, 1985. COPIES FURNISHED: Elizabeth J. Rickenbacker, Esquire 10500 Southwest 108th Avenue Miami, Florida 33176 Michael F. Chenoweth, Esquire 522 Southwest Third Avenue Miami, Florida 33130 Douglas H. MacLaughlin, Esquire Department of Environmental Regulation 2600 Blair Stone Road Tallahassee, Florida 32301 Michael Egan, Esquire, Robert Apgar, Esquire Post Office Box 1386 Tallahassee, Florida 32302 Victoria Tschinkel, Secretary Department of Environmental Regulation 2600 Blair Stone Road Tallahassee, Florida 32301 ================================================================= AGENCY FINAL ORDER ================================================================= BEFORE THE STATE OF FLORIDA DEPARTMENT OF ENVIRONMENTAL REGULATION SIERRA CLUB: UPPER KEYS CITIZENS ASSOCIATION, INC., a non-profit Florida corporation; PAMELA BERYL PIERCE, and FRIENDS OF THE EVERGLADES, INC., a non-profit Florida corporation, Petitioners, and DOAH CASE NOS. 84-2364 84-2365 FRIENDS OF THE EVERGLADES, INC., 84-2385 a non-profit Florida corporation; 84-2827 THE FLORIDA DIVISION OF IZAAK (Not consolidated) WALTON LEAGUE OF AMERICA, INC., a non-profit Florida corporation; UPPER KEYS CITIZENS ASSOCIATION, INC., a non-profit Florida corporation, Intervenor-Petitioners, vs. STATE OF FLORIDA DEPARTMENT OF ENVIRONMENTAL REGULATION, and PORT BOUGAINVILLE ASSOCIATES, LTD. a Florida limited partnership, and PORT BOUGAINVILLE ENTERPRISE, INC. a Florida corporation, Respondents. /
