Findings Of Fact Petitioner is the state land planning agency charged with the responsibility to administer the provisions of Chapter 380, Florida Statutes, and the regulations promulgated thereunder. Petitioner has the authority to appeal to the Florida Land and Water Adjudicatory Commission any development order issued in an area of critical state concern. Monroe County is a political subdivision of the State of Florida, and is responsible for issuing development orders for development in Monroe County. Monroe County issued the development order that is the subject of this appeal. Respondent, Bruce Schmitt, is the owner of real property known as Section 15, Township 66, Range 32, Sombrero Beach Road and Tingler Lane - 88 Tingler Lane, Vaca Key Bright, Florida. Most of Monroe County, including the subject property, is within the Florida Keys Area of Critical State Concern, as designated under Sections 380.05 and 380.0552, Florida Statutes. On May 25, 1993, Monroe County issued building permit number 9320003962 to Bruce A. Schmitt, Owner, and Marathon Woodworking, General Contractor, authorizing the construction of a 4 feet X 140 feet wooden dock with a 4 feet x 40 feet terminus. The site of the permitted dock is on an open water shoreline. Running parallel to this shoreline is a channel that is greater than four feet in depth at mean low tide and is greater than twenty feet in width. The permitted dock will terminate at the edge of that channel in an area that is at least four feet deep at mean low tide and more than 20 feet in width. There are no hard coral bottoms found in the area where the dock will terminate. In the vicinity where Mr. Schmitt proposes to construct his dock, there is a channel that is perpendicular to the shoreline that intersects with the channel that is parallel to the shoreline. This perpendicular channel leads out to deep water. The channel providing access to deep water crosses an area of shallow water, which is an area of flats that is referred to by the Department as a shoal. The water depth of this area at mean low tide ranges between 3.0 and 3.5 feet. The channel running parallel to the shoreline and the channel leading out to deep water are not marked. Boats that use this area traditionally have used the channel that is parallel to the shoreline to access the channel in front of Mr. Schmitt's property that leads to deep water. These boats thereafter access deep water by crossing the area of flats that is referred to by the Department as a shoal. While it was established that boats cannot navigate around the shoal, the dimensions of the shoal were not established. Natural shallow water marine communities, such as seagrasses, exist in the waters in the navigation route for boats that will use the permitted dock. Sea grass beds play an important role in water quality maintenance in the Keys through filtration and nutrient uptake and serve as nursery habitats for fisheries. The cumulative impact of the operation of propeller- driven boats in the Keys results in damage and destruction to shallow water marine communities, such as sea grass beds, through prop dredging. There is evidence of considerable prop dredging of the sea grass beds in the shallow waters offshore of the subject property. Boats have been known to run aground in the flats off Mr. Schmitt's property. Any boat using the permitted dock will have to cross shallow waters with seagrass with water depths of less than four feet at mean low tide. Pursuant to the provisions of Sections 380.05 and 380.0552, Florida Statutes, Monroe County has adopted a comprehensive plan which complies with the Principles for Guiding Development found at Section 380.0552(7), Florida Statutes. Section 380.0552(7), Florida Statutes, requires Monroe County land development regulations to comply with certain principles for guiding development, including the following: (b) to protect shoreline and marine resources, including mangroves, coral reef formations, wetlands, fish and wildlife and their habitat. * * * (e) to limit the adverse impacts of development on the quality of water throughout the Florida Keys . . . Monroe County's Comprehensive Plan, which has been approved by the Department and by the Administration Commission, is implemented, in part, through its adopted land development regulations, codified in Chapters 6 and 9.5, Monroe County Code. Section 9.5-345(m) (2), Monroe County Code, provides as follows: (2) All structures on any submerged lands and mangroves shall be designed, located, and con- structed such that: * * * No structure shall be located on submerged land which is vegetated with seagrasses except as is necessary to reach waters at least four (4) feet below mean low levels for docking facilities; No docking facilities shall be developed at any site unless a minimum channel of twenty (20) feet in width where a mean low water depth of at least minus four (4) feet exists. Section 9.5-4(W-1), Monroe County Code, provides as follows: (W-1) "water at least four (4) feet below mean sea level at mean low tide" means locations that will not have a significant adverse impact on off- shore resources of particular importance. For the purposes of this definition, "off-shore resources of particular importance" shall mean hard coral bottoms, habitat of state or federal threatened and endangered species, shallow water areas with natural marine communities with depths at mean low tide of less than four (4) feet, and all designated aquatic preserves under Florida Statutes, Section 258.39 et seq. Section 2.104, Nearshore Waters, Monroe County Comprehensive Plan, Volume II, Future Land Use Element, provides as follows: The Florida Keys are dependent on nearshore water quality for their environmental and economic integrity. The heart of the Florida Keys economy, the means by which Monroe County exists as a civil and social institution, is based on its unique oceanic character. If nearshore water quality is not maintained, then quality of life and the economy of Monroe County will be directly and immediately impacted. OBJECTIVES 1. To protect, maintain, and where appropriate, to improve the quality of nearshore waters in Monroe County. POLICIES 1. To prohibit land use that directly or indirectly degrades nearshore water quality. * * * To prohibit the development of water dependent facilities, including marinas, at locations that would involve significant degradation of the biological character of submerged lands. To limit the locations of water-dependent facilities at locations that will not have a significant adverse impact on off-shore resources of particular importance. For the purposes of this policy, off-shore resources of particular importance shall mean hard coral bottoms, habitat of state or federal threatened or endangered species, shallow water areas with natural marine communities with depths at mean low tide of less than four (4) feet, and all designated aquatic preserves under Florida Statutes, section 258.39 et seq. There are no channel markers to deep water in the area of the permitted dock that have been approved by the Department of Environmental Protection. There was a dispute in the evidence as to whether marking the channel that has served this area as the access route to deep waters would be appropriate and whether such marking would create a navigational hazard. The conflict in the evidence presented is resolved by concluding that the marking of the channel that serves as the navigation access route for boats that will use the permitted dock is appropriate, will aid navigation, and will not create a navigation hazard. This conclusion is reached, in part, because the channel is well defined by its long-term use and connects with the channel that is parallel to the shoreline at a known point.
Recommendation Based on the foregoing Findings of Fact and Conclusions of Law, it is RECOMMENDED that the Florida Land and Water Adjudicatory Commission enter a final order which conditionally denies Building Permit Number 9320003962, but which authorizes Monroe County to issue that permit once the access channel to deep water has been properly marked and approved by the Department of Environmental Protection. DONE AND ENTERED this 25th day of October, 1994, in Tallahassee, Leon County, Florida. CLAUDE B. ARRINGTON 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 25th day of October, 1994.
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. /
The Issue At issue was whether Petitioner should be granted a permit from the Respondent, Department of Environmental Regulation, to excavate material in front of the Petitioner's seawall in Naples Bay, Collier County, Florida. The Petitioner owns a residential homesite lot in the Royal Harbor Subdivision in Naples, Florida. Royal Harbor is a waterfront oriented residential community devoted to single family residences; each residence either has waterfront' on Naples Bay or through a network of interior canals which provide navigational access to Naples Bay. All lots are bordered by concrete seawalls. The Concrete seawall bordering the Petitioner's property does not Immediately abut the water, but has an amounts of earth between the seawall and the water's edge, somewhat resembling a beach. It is this earth the Petitioner wishes to remove so that he may have his seawall abut the water which would facilitate the launching of a vessel from his property. Presently, it does not appear that the Petitioner could keep a boat at his property without building a lengthy dock from his seawall into Naples Bay. The Department of Environmental Regulation opposes the application in that it claims the excavation of this material would destroy an oyster bar which exists in front of the Petitioner's property and would eliminate an ecologically significant area. From the exhibits presented at the hearing and after consideration of the testimony, it appears that in the entire Royal Harbor development only the Petitioner's property lacks having the bay waters abut the seawall. The Petitioner's property is approximately one quarter mile from the channel in Naples Bay which is a low energy water body. That is to say, wave action does not become extremely forceful in this area because of the protected nature of the waterway. The Department of Environmental Regulation in part opposes the permit because they state to remove the berm from in front of the seawall would expose the seawall to direct wave energy which would cause turbidity within the waters. No direct evidence was presented that wee the seawalls in Naples Bay are in direct contact with the water that this ill fact does cause increased turbidity and therefore this testimony is rejected by this Hearing Officer as being merely speculative. On the other hand, the Petitioner made no showing that the project would actually be in the public interest except to show that the area in question was a relatively small area. Witnesses for the Department of Environmental Regulation stated that were this berm removed and the area converted to a shallow submerged bay bottom, oysters and marine vegetation would eventually propagate here, particularly if the bottom was excavated with a smooth contour. It is difficult to imagine after listening to all the testimony in this case how the granting of this permit would have a measurable environmental Impact. It would appear to this Hearing Officer that there could be some benefit to water quality from the granting of this permit by somewhat restoring Naples Bay to its original condition. Testimony was received that the entire Royal Harbor development was man-made and the removal of this fill would, in some slight degree, remove fill material that had been previously placed within the waters of Naples Bay. Testimony was also received from Mr. Thomas Provenzano, District Supervisor of the Department of Environmental Regulation, that in his opinion it would be environmentally acceptable for the Petitioner to excavate this berm from within five (5) feet of the concrete seawall. This appears to be a reasonable disposition of this dispute. Whatever destructive force the waves of Naples Bay might have on an exposed vertical seawall would be minimized by leaving a five (5) foot berm seaward of that wall and would in no way interfere with the Petitioner's intended use of his land; reasonable navigational access to Naples Bay. It is, therefore, RECOMMENDED: The application be granted with the proviso that the Petitioner leave a five (5) foot berm between Naples Bay and his vertical seawall. DONE and ENTERED this 3rd day of November, 1976, in Tallahassee, Florida. KENNETH G. OERTEL, Director Division of Administrative Hearings Room 530, Carlton Building Tallahassee, Florida 32304 (904) 488-9675 COPIES FURNISHED: Carole Haughey, Esquire Department of Environmental Regulation 2552 Executive Center Circle, E. Montgomery Building Tallahassee, Florida 32301 Donald T. Frank, Esquire Suite A, U.S. Home Building 3174 E. Tamiami Trail Naples, Florida 33940 ================================================================= AGENCY FINAL ORDER ================================================================= STATE OF FLORIDA DEPARTMENT OF ENVIRONMENTAL REGULATION LYNN A. LUNDSTROM, Petitioner, vs. DOAH CASE NO. 76-1555 STATE OF FLORIDA DEPARTMENT OF ENVIRONMENTAL REGULATION, Respondent. /
The Issue Has the applicant, Grove Isle, Ltd. provided reasonable assurances and affirmatively demonstrated that its proposed marina is clearly in the public interest and will not lower the existing ambient water quality of Biscayne Bay, a designated outstanding Florida water?
Findings Of Fact On March 13, 1978 an application was made to DER for a water quality control permit to construct a wet-slip marina on the west side of Grove Isle, formerly known as Fair Isle and Sailboat Key. The original plan for the marina, which was initially objected to by the Department of Environmental Regulation, was modified to protect a bed of seagrasses extending about 30 feet wide in a band along the west side of the island. While the plans were being modified and consultations with other government permitting agencies were in progress, the application was "deactivated" from September 27, 1978 until March 30, 1979. As a result of its investigation and review, DER on October 23, 1979, issued a letter of intent to grant the permit to Grove Isle, Inc. The permit if granted, would allow the applicant to construct six concrete fixed piers, five "T" shaped, one "L" shaped, with a boat docking capacity of 90 pleasure boats. The piers will extend a maximum of 165 feet offshore from an existing concrete bulkhead. The width of the piers will be 8 feet from the bulkhead to a point 41 feet offshore, and then increased to a width of 10 feet. A sewage pump-out facility is also proposed. Attached to that letter of intent were the following conditions: Adequate control shall be taken during the construction so that turbidity levels outside a 50 foot radius of the work area do not exceed 50 J.C.U's, as per Section 24-11, of the Metropolitan Dade County Code. During construction, turbidity samples shall be collected at a mid-depth twice daily at a point 50 feet up stream and at a point 50 feet down stream from the work area. The contractor shall arrange to have turbidity sample results reported to him within one hour of collection. Turbidity monitoring reports shall be submitted weekly to DER and to the Metropolitan Dade County Environmental Resources Management (MDCERM) If turbidity exceeds 50 J.C.U's beyond a 50 foot radius of the work area, turbidity curtains shall be placed around the work area and MDCERM notified immediately. Turbidity samples shall be collected according to condition two above, no later than one hour after the installation of the turbidity curtain. It turbidity levels do not drop below 50 J.C.U's within one hour of installation of the curtain all construction shall be halted. Construction shall not be resumed until the contractor has received authorization from MDCERM. No live-a-board vessels (permanent or transient) shall be docked at this facility unless direct sewage pump-out connections are provided at each live-a-board slip. A permanent pump-out station shall be installed and maintained for further removal of sewage and waste from the vessels using this facility. Compliance with this requirement will entail the applicant's contacting the Plan Review Section of MDCERM for details concerning connection to an approved disposal system. Boat traffic in the shallow 30 foot wide dense seagrass area which parallels the shoreline shall be restricted by the placement of wood piles on 6 foot centers along the entire shoreline facing the marina. The channel from this marina to deeper water in Biscayne Bay shall be marked to prevent boats from straying into adjacent shallow areas. This will prevent habitat destruction. A chemical monitoring program shall be established to determine the effect of this marina on the water quality of this section of Biscayne Bay. Surface and mid-depth samples shall be collected at three points in the project area and at one background station. Parameters shall include, but not be limited to dissolved oxygen, pH, salinity, temperature, total coliform and fecal coliform and fecal streptococci bacteria, oil and grease, biochemical oxygen demand, and turbidity. Background samples shall be collected prior to construction and quarterly for a minimum of one year after 90 percent occupancy of the marina. In addition to the chemical monitoring program, a benthic community monitoring program is to be established. Samples of the benthic seagrass community within and adjacent to the project area are to be collected prior to construction and quarterly for a minimum of one year after 90 percent occupancy of the marina. Should either monitoring program detect dissimilar changes at its monitoring and control stations, DER and MDCERM shall be notified of the results. The monitoring programs shall be reviewed and approved by DER and MDCERM prior to implementation. Monitoring reports shall be submitted to DER and MDCERM and the United States Corps of Engineers on regular basis. Warning signs shall be posted in the marina area to advise marina users that manatees frequent the area and caution should be taken to avoid collisions with them. With the foregoing conditions imposed, the Department concluded that no significant immediate or long term negative biological impact is anticipated and state water quality standards should not be violated as a result of the proposed construction. Grove Isle, Inc., has agreed to comply with all the conditions established by the DER letter of intent to grant the permit. Grove Isle is a spoil bank in Biscayne Bay located approximately 700 feet east of the Florida mainland. It is linked to the mainland by a two-lane concrete bridge. The island is currently under development for a 510 unit condominium community with associated facilities such as a restaurant, hotel, and the proposed marina. The island is surrounded by a concrete bulkhead constructed many years ago. No changes in the bulkhead line are proposed. Grove Isle, Inc., proposes constructing the marina on concrete piles driven into the Bay bottom from a shallow draft barge. During construction there would be some turbidity caused from the disruption of the Bay sediment. This can however be adequately controlled by the use of turbidity curtains during construction. The construction will not require any dredging or filling. In the immediate marina site the most significant biota are a 30 foot wide bed of seagrasses. There are no other important biota because at one time the area was extensively dredged to create the island. There are no oyster or clam beds nearby. While lobsters may have once frequented the area, they too are no longer present. The water depth in the area ranges from 1 foot near the island bulkhead to 12 feet offshore to the west of the island. This particular seagrass bed consist primarily of turtle grass (thalassia, testudinum) with some Cuban Shoal Weed (Halodule, Wrightii). Protection for these grasses will be provided by a buffer zone between the island and the boat slips. The grassy zone will be bordered by a row of dolphin piles to exclude boat traffic. Because the grass requires sunlight for photosynthesis and therefore life, the six piers will have grated walkways where they pass over the grass. This will allow sunlight to reach below. In addition to the small grass bed on the west of the island there are extensive beds to the northeast, east and south of the island that extend several hundred yards from the island in water depths of three to ten feet. If boat traffic in the vicinity is markedly increased due to the existence of the marina, it is conceivable that the number of propeller scars in these shallow beds could increase. At the present time the beds are already traversed by boats, some of which are owned by Petitioner's members. There are already for example, approximately 50 crafts which operate from the nearby mainland or from Pelican Canal directly to the north of the island. Propeller scars take up to fifteen years to heal yet the number of scars in the Grove Isle area is insignificant and even a tripling of them from an additional 90 boats would still be de minimus. Potential damage to the seagrasses on the north side of the island will be minimized by the planned installation of navigation markers by Grove Isle. These markers will channel boats into water of a navigable depth and lessen the number of groundings and near groundings which cause the scarring. There is evidence that pleasure boats by their very existence and operation in the water are potential pollution sources. For instance, various maintenance chemicals such as anti-fouling bottom paint and wood cleaner have the ability, if used in sufficient quantity, to harm marine life. The fueling of engines and sewage discharge from boats are additional pollution sources. There was however, no showing that the location of up to 90 pleasure and sport fishing craft at the proposed marina site would in any way cause a degradation of water quality below the acceptable standards for Class III waters. At the present time, the marina site has adequate flushing to disburse those pollutants which may be generated by the marina operations. While a hydrographic survey was not requested by DER or provided by Grove Isle at the time the permit application was made, the testimony of Dr. Echternacht at the time of the Hearing provided adequate assurances respecting the hydrographic characteristics of the proposed site. The proposed marina will have no fueling or maintenance facilities. No live-a-board craft will be allowed at the marina. Both Mr. Wm. Cleare Filer and David A. Doheny live close to Grove Isle. Mr. Doheny's residence is on the mainland facing the proposed marina site and Mr. Filer's house is on Pelican Canal. They use the waters of Biscayne Bay around Grove Isle for recreation. If the quality of the water in the proposed marina site were lessened their substantial interest would be affected. Biscayne Bay is classified as a Class III water and is in the Biscayne Bay Aquatic Preserve. Careful considerations has been given to each of the proposed findings of fact submitted by the parties. To the extent that they are not contained in this Order, they are rejected as being either not supported by competent evidence or as immaterial and irrelevant to the issues determined here.
Recommendation Based on the foregoing Findings of Fact and Conclusions of Law, it is RECOMMENDED: That a Final Order be entered by the State of Florida, Department of Environmental Regulation, determining that the requested water quality control permit and certification be issued subject to the conditions contained in the Notice of Intent to Issue Permit and that the Relief requested by the Petitioners be denied and their Petitions be dismissed. DONE and ENTERED this 22nd day of February, 1980, in Tallahassee, Florida. MICHAEL P. DODSON Hearing Officer Division of Administrative Hearings Room 101, Collins Building Tallahassee, Florida 32301 (904) 488-9675 COPIES FURNISHED: David A. Doheny, Esquire 1111 South Bayshore Drive Miami, Florida 33131 Wm. Cleare Filer 3095 Northwest 7th Street Miami, Florida 33125 Joel Jaffer 2479 Southwest 13th Street Miami, Florida 33145 Randall E. Denker, Esquire Assistant General Counsel Department of Environmental Regulation 2600 Blair Stone Road Tallahassee, Florida 32301 Larry S. Stewart, Esquire Frates, Floyd, Pearson, Stewart, Richmond & Greer One Biscayne Tower 25th Floor Miami, Florida 33131 ================================================================= AGENCY FINAL ORDER ================================================================= STATE OF FLORIDA DEPARTMENT OF ENVIRONMENTAL REGULATION BAYSHORE HOMEOWNERS ASSOCIATION, INC., et al., Petitioner, vs. CASE NO. 79-2186 79-2324 STATE OF FLORIDA, 79-2354 DEPARTMENT OF ENVIRONMENTAL REGULATION, and GROVE ISLE, LIMITED, Respondent. /
The Issue Issues presented here concerned the entitlement of Respondent, Russell D. Horn, Sr., to be granted an environmental permit by Respondent, Department of Environmental Regulation, to build a boat stall on an existing dock in Putnam County, Florida. The boat stall's dimensions are ten feet wide by twenty feet deep and the construction would be on the St. Johns River.
Findings Of Fact On July 13, 1981, Russell D. Horn, Sr., who has a residence in Putnam County, Florida, bade application to the State of Florida, Department of Environmental Regulation, for the necessary permits to construct a boat stall ten feet wide by twenty feet deep at the site of an existing dock. A copy of the application may be found as Respondent Horn's Exhibit No. 2 admitted into evidence. The dock where Horn applied to build the boat slip is found in the St. Johns River, a navigable water body and waters of the State of Florida in Putnam County, Florida. The application form which was executed by Horn required him to indicate the name of adjacent property owners to the property at which the dock site was located, both upland and adjacent to the uplands. See Rule 17- 4.28(11)(c), Florida Administrative Code. To accomplish this task, the applicant utilized a sketch which he had been provided when he purchased his homesite in the area and indicated to the Department that the adjoining landowners were Milton Kilis and Robert Michal. In fact, Robert Michal was not an adjacent landowner. The adjacent landowner, Milton G. Kilis, wrote to advise the Department that he had no objection to the construction of the boat slip. This correspondence was dated September 11, 1981. A copy of that correspondence may be found as Respondent Department's Exhibit No. 3 admitted into evidence. After reviewing the initial application, additional information was requested by a document entitled "Completeness Summary" which was addressed from the Department to the Applicant Horn. A copy of this "Completeness Summary" requesting additional information may be found as Department's Exhibit No. 1 admitted into evidence. Through this summary, Horn was requested to provide written authorization from the dock owners. It was also requested that Respondent provide an affidavit of ownership of the upland property adjacent to the dock site. Horn received permission to construct from Frank Scussell and William A. Reaves, persons he understood to be the dock owners. See Respondent Horn's Exhibit No. 3 admitted into evidence. Horn misunderstood the question related to ownership of upland property and provided a mortgage deed with its attendant description of his home site property in Putnam County, which is at a different location from that of the upland property adjacent to the dock. A copy of that deed and other matters may be found as Respondent Horn's Exhibit No. 4 admitted into evidence. Department of Environmental Regulation reviewing authorities wrote on the "Completeness Summary" form, Respondent Department's Exhibit No. 1, indicating that the task of seeking written authorization from the dock owners had been achieved and that the affidavit of ownership of upland property owners was satisfactory. In fact, all adjacent property owners had not been notified of the pendency of the application request through the process of Horn's advising the Respondent agency of the names of all adjacent property owners to the uplands and the affidavit of ownership of the upland property owner at the dock site was not filed. During the review process, permission was given by the Department of the Army, Corps of Engineers, for the construction of the boat slip. A copy of this permission, by letter dated August 31, 1981, is Respondent Department's Exhibit No. 2, admitted into evidence. The Department of Environmental Regulation reviewed the permit application and prepared an application appraisal, which may be found as Respondent Department's Exhibit No. 5 admitted into evidence. The findings made by that application appraisal related to application review are found to be accurate. In particular the permit application appraisal indicated that the boat slip would be located at the waterward end of the existing dock structure, which existing dock structure accommodated four boats. The appraisal found that the project was located in South Putnam County in the town of Georgetown on the St. Johns River. The permit appraisal found that the project site would be located in the littoral zone of the river about one hundred feet waterward of the mean high water line. No littoral growth was seen at the depth of the proposed construction. Tapegrass, Mexican waterlily and cattail were present near the shore. Several large hardwood swamp trees were present at the shoreline. The project was found to be located in a Water Class III and adjacent waters were Class III according to the appraisal, no significant immediate or long-term adverse environmental impacts were to be expected to occur due to the completion of the boat slip. Horn was subsequently given a construction permit to add the boat stall to the existing dock. A copy of that permit may be found as Respondent Department's Exhibit No. 6 admitted into evidence. The only specific conditions related to that matter pertain to the necessity for the utilization of turbidity curtains throughout the project for purposes of containing the turbidity that might exceed State water quality standards, The permit was issued on September 22, 1981. After receiving the permit, sometime around October 20, 1981, Horn purchased the necessary lumber to construct the stall and on October 24, 1981, went to the dock site to begin the installation of pilings related to the construction of the boat stall. While placing the pilings on October 24, 1981, an adjoining property owner and Petitioner in this cause, Marshall Wolfe, stood on his dock, that is, Wolfe's dock, and hailed to Horn to stop building. Horn did not know Wolfe before that time and did not know that Wolfe, not Michal, was the adjacent property owner on that side of the dock. On October 28, 1981, Marshall Wolfe and his wife, Ann Wolfe, wrote to the Department in the person of G. Doug Dutton, Subdistrict Manager, and indicated that they were opposed to the issuance of the permit, which is under the number of the permit issued to Respondent, and requested a hearing on the question of the issuance. A copy of that correspondence may be found as Department's Exhibit No. 7 admitted into evidence. On the same date, October 28, 1981, Horn was contacted by the Department of Environmental Regulation and advised of the Wolfe complaint and Horn was told that he would receive a cease and desist order from the Department of Environmental Regulation. On October 30, 1981, Horn returned to the construction site and found four of his neighbors finishing the construction of the stall. In fact, the neighbors did conclude the construction and the boat slip remains in place. A cease and desist letter was mailed on November 2, 1981; however, this letter was not received by Horn immediately. Horn did subsequently learn of the contents of the letter some time in November or December, 1981. A copy of the cease and desist letter may be found as Respondent Department's Exhibit No. 8 admitted into evidence. On December 13, 1981, an attempt was made at the instigation of Department officials for the Petitioners and Respondent Horn to resolve the controversy. This effort was unsuccessful. As a consequence, a formal hearing was necessary in keeping with the request of the Department that the Division of Administrative Hearings conduct a Subsection 120.57(1), Florida Statutes, formal hearing. This request had been made on November 12, 1981, and an initial hearings had been scheduled for February 11, 1982, following consultation between the various parties and the Hearing Officer. At the initial hearing session on February 11, 1982, which was to be held in Palatka, Florida, counsel for Department indicated that the upland property was not owned by Horn and that easement rights to that property were unclear. In view of this fact the hearing was continued until the ostensible upland property owner could be notified of the pendency of the issuance of an environmental permit and be allowed to participate. Notification was subsequently provided by an Intent to Issue Statement, a copy of which may be found as Respondent Department's Exhibit No. 9 admitted into evidence. This notification was through the Department at the instigation of the Hearing Officer. The date of notification was February 12, 1982. An order was entered on March 17, 1982, which allowed the intervention of St. Johns Crescent Lakesites, Inc. into the proceedings and that party, in the person of its counsel, Lauren E. Merriam, III, Esquire, participated in the April 15, 1982 hearing. St. Johns Crescent Lakesites, Inc. is the owner of the upland property adjacent to the dock in which Horn had constructed the boat slip. No indication was given that any easement rights were ever granted by that corporation to grant access to the boat slip from the adjacent property. The overall dock area, in terms of square feet, is between 500 and 1000 square feet. Other than the permit application made by Horn, no other permission has been received by the Department to construct the other features of the dock. A further appraisal of the project site subsequent to the September 18, 1981, appraisal has been made. That appraisal was made by the field inspector for the Department. This appraisal by Melvin Rechtor agrees with the project appraisal made by the first field inspector, John Hendricks. The testimony of Melvin Rechtor on environmental impacts of the project are accepted as accurate. Rechtor's testimony established that the project would have an insignificant impact on water quality considerations and would not adversely affect the species or the conservation of fish, marine and wildlife or other natural resources. Rechtor's testimony established that there would be no unreasonable interference with waterward access of adjacent property owners. Rechtor's testimony also established that there would be no navigational hazard nor interference with fishing and swimming by persons using the river.
Findings Of Fact Based on the stipulations and admissions of the parties, on the exhibits received in evidence, and on the testimony of the witnesses at hearing, I make the following findings of fact. Facts admitted by all parties The water quality standards contained in Rule 17-3.111, Florida Administrative Code will not be violated by this project. There are no aquatic macrophytes located in the area of the proposed project. The proposed project is located within 500 feet of the incorporated municipality of Horseshoe Beach, Florida. The proposed project is located within Class II waters of the State not approved for shellfish harvesting. The project will not adversely affect the conservation of fish and wildlife, including endangered or threatened species, or their habitats. The proposed project will be of a permanent nature. The project will not adversely affect or will not enhance significant historical or acheological resources under the provisions of Section 267.061, Florida Statutes. The rest of the findings The Applicant, Dixie County, applied for a dredge and fill permit to construct a dock which would expand the existing public dock at Horseshoe Beach. In accordance with the revised plans dated October 23, 1986, the proposed facility would consist of a pier 6 feet wide and 120 feet long designed to accommodate six boat slips, each 30 feet wide and 40 feet long. The boundaries of the boat slips will be demarcated by pilings set 10 feet apart. Four of the boat slips would be primarily for the use of commercial fishing boats and commercial shrimping boats. The other two boat slips (the two slips closest to the land) would be reserved for the exclusive use of recreational and other small vessels. By adding a catwalk 3 or 4 feet wide down the middle of the two slips reserved for recreational vessels, the usefulness of those slips to recreational vessels would be greatly enhanced and the narrowness of the resulting slips would preclude their use by large vessels. Adding the two catwalks would be a minor addition to the proposed project which would greatly enhance the usefulness of the project and at the same time avoid the possibility that large vessels in the two slips closest to the land would impede ingress and egress at the nearby boat lift, boat fueling facility, and boat ramp. Adding a reasonable number of permanent trash or garbage containers would also enhance the usefulness of the proposed project and minimize the possibility of improper disposal of trash and garbage which is generated by the normal use of a dock by fishermen and boaters. The proposed project site is located in the Gulf of Mexico at Horseshoe Beach, Florida, and would extend into the waters of the Gulf, which is a tidally influenced water body adjacent to Dixie County, Florida. The water along the shoreline of the area is shallow for a considerable distance waterward, except where basins and channels have been dredged. The Horseshoe Beach area is relatively unpolluted. The existing public dock at Horseshoe Beach is used primarily by recreational vessels, but there is also extensive commercial fishing and Shrimping boat activity in the area. The project is located at the mouth of a canal with direct access to the Gulf. Several commercial fishhouses operate from the canal bank, which generates extensive commercial boat traffic past the proposed project site. Large numbers of commercial shrimp boats presently dock along the canal that ends near the proposed project site. The proposed project requires no dredging. The only filling required by the proposed project is the placement of pilings into the bottom of the Gulf of Mexico. Even though the plans do not specify whether concrete or wooden pilings will be used, this lack of specificity in the plans is irrelevant. Regardless of what types of pilings are used on this project, the filling activity will not violate the water quality criteria contained in Rule 17- 3.051(1), Florida Administrative Code. The placement of the pilings will not adversely affect the public health, safety, and welfare. Further, the proposed project will not adversely affect any property interests of the Petitioners within the scope of Chapter 403, Florida Statutes. The Gulf bottom in the area of the proposed project has already been disturbed. The presently existing suspension of particulate material in the water column, a natural occurrence in the area of the project, results in low visibility which means that seagrass beds and other marine vegetation, which provide shelter and detrital deposits for fish and other marine resources, will not grow. Coast Guard regulations prohibit commercial fishing vessels from depositing materials into the water within three miles of the coast line. Commercial fishing vessels must prominently display a sticker reciting that regulation and it is the practice of commercial fishing vessels operating in the vicinity of Horseshoe Beach to comply with this Coast Guard no discharge requirement by cleaning nets and scrubbing decks outside the three mile limit. It is not the practice of Commercial fishing vessels to deliberately discharge diesel fuel, fish parts or other material into the water while docked. Further, the limited number of commercial fishing vessels which could dock at the proposed facility at the same time cannot reasonably be expected to create discharges in amounts creating a nuisance, posing any danger to the public health safety or welfare, or violating the water quality criteria contained in Rule 17-3.051(1), Florida Statutes. Although small amounts of diesel fuel can become mixed with bilge water and be discharged by automatic bilge pumps while commercial fishing vessels are docked, there is no evidence that this would be in amounts Sufficient to create a nuisance or violate water quality criteria. To the contrary, notwithstanding a large amount of commercial boat traffic past the proposed site and notwithstanding the fact that large numbers of shrimp boats dock up the canal from the proposed site, the water in the area of the proposed site has remained relatively unpolluted. The proposed project will not affect the normal wind and wave action in the area of the proposed project. Such wind and wave action presently results in free exchange between the waters of the open Gulf and the waters near the shore. This free exchange of waters means that any pollutant discharges in the area of the proposed project will be diluted and rapidly dispersed into the Gulf of Mexico. There will be no measurable difference in the wind and wave action, or in the water exchange, after the proposed project is built. No harmful shoaling or erosion is expected to result from construction of the proposed project. Any docking structure extending out into the Gulf of Mexico will obviously have some effect on navigation in the area of the dock, but there is no evidence that the proposed dock will present a hazard to navigation or any significant interference with customary navigation patterns. The distance between the nearest channel marker and the waterward end of the proposed project is more than 200 feet. The angle of the proposed dock and its Spatial relation to the main Horseshoe Beach turning basin cause no impediment to navigation. The placement of Coast Guard Safety lights on the dock would minimize any potential for impeding navigation or posing a danger to the public health or safety during hours of darkness.
Recommendation Based on all of the foregoing, I recommend that the Department of Environmental Regulation issue a Final Order in this case granting the permit applied for by Dixie County. It is also recommended that the permit be made subject to the following additional conditions: That one or more Coast Guard safety lights be placed on the proposed expansion to the dock; That catwalks be added down the middle of the two most landward of the proposed boat slips; and That a reasonable number of trash or garbage receptacles be permanently located on the proposed expansion to the dock to minimize the possibility of trash and garbage being thrown overboard. DONE AND ENTERED this 30th day of October, 1987, at Tallahassee, Florida. MICHAEL M. PARRISH, Hearing Officer Division of Administrative Hearings The Oakland Building 2009 Apalachee Parkway Tallahassee, Florida 32399-1550 (904) 488-9675 Filed with the Clerk of the Division of Administrative Hearings this 30th day of October, 1987. APPENDIX TO RECOMMENDED ORDER, CASE NO. 86-1448 The following are my specific rulings on all of the proposed findings of fact submitted by all of the parties. The paragraph numbers referred to below are references to the paragraph numbers in the parties' respective proposed recommended orders. Ruling on findings proposed by the Petitioners: Paragraph 1: Accepted. Paragraph 2: Accepted. Paragraph 3: Accepted. Paragraph 4: First sentence is rejected as appearing to be more in the nature of an introduction to a discussion of legal issues than a proposed finding of fact. Second and third sentences are rejected as repetitious Paragraph 5: Entire paragraph rejected as unnecessary speculative generalizations in light of the other evidence in this case. Paragraph 6: Entire paragraph rejected as unnecessary speculative generalizations in light of the other evidence in this case. Paragraph 7: Rejected as contrary to the greater weight of the evidence. Paragraph 8: Entire paragraph is rejected as appearing to be more in the nature of an introduction to a discussion of legal issues than proposed findings of fact. Paragraph 9: Entire paragraph rejected as contrary to the greater weight of the evidence; construction of the dock may be expected to bring about some changes in the nature of the boat traffic in the immediate area, but nothing of the nature or magnitude suggested by these proposed findings. Paragraph 10: Rejected as contrary to the greater weight of the evidence. Paragraph 11: First sentence is rejected as contrary to the greater weight of the evidence. Second sentence is accepted in part and rejected in part. Rejected portion is irrelevant. Third sentence is rejected as irrelevant. Fourth Sentence is accepted. Fifth sentence is rejected as contrary to the greater weight of the evidence and as repetitious Sixth sentence is rejected as contrary to the greater weight of the evidence. Paragraph 12: Entire paragraph rejected as contrary to the greater weight of the evidence. Rulings on findings Proposed by the Respondent: Paragraph 1: Accepted. Paragraph 2: Accepted in substance. Paragraph 3: First two sentences accepted in substance. Last sentence rejected as irrelevant. Paragraph 4: Accepted. Paragraph 5: Accepted. Paragraph 6: Accepted. Paragraph 7: Rejected as unnecessary recitation of opposing party's contentions and not proposed finding of fact. Paragraph 8: Accepted in substance. Paragraph 9: Accepted in substance. Paragraph 10: Accepted. Paragraph 11: Accepted in substance. Paragraph 12: Accepted. Paragraph 13: First sentence accepted in substance. Second sentence accepted in part and rejected in part; rejected portion concerns riparian rights, which are irrelevant to whether this permit should be issued. Paragraph 14: Entire paragraph rejected as irrelevant. Paragraph 15: Accepted in substance. Paragraph 16: Accepted. Paragraph 17: Accepted in substance. COPIES FURNISHED: Frederick M. Bryant, Esquire Moore, Williams & Bryant, P.A. Post Office Box 1169 Tallahassee, Florida 32302 J. Doyle Thomas, Esquire County Attorney Post Office Box 339 Cross City, Florida 32628 Ann Cowles-Fewox, Legal Intern Twin Towers Office Building 2600 Blair Stone Road Tallahassee, Florida 32399-2400 Karen Brodeen, Esquire 2600 Blair Stone Road Tallahassee, Florida 32301 Dale Twachtmann, Secretary Twin Towers Office Building 2600 Blair Stone Road Tallahassee, Florida 32399-2400
Findings Of Fact Respondent/applicant, The Yachting Arcade (applicant), initiated this matter when it filed an amended application with respondent, Department of Environmental Regulation (DER), on April 27, 1984, seeking a permit authorizing the construction of a docking facility on the eastern shore of Bethel Creek in the City of Vero Beach, Florida.1 Specifically, applicant wished to construct a commercial shoreline dock 530 feet long and six feet wide with four access docks at various locations along the shoreline. The access docks would vary in size from thirteen to sixteen feet in length and from four to ten feet in width. The dock will be situated in front of a two-story commercial structure and parking lot on 1.14 acres owned by applicant which lies between Highway A-1-A and Bethel Creek. That structure will house a restaurant and other retail establishments. A city permit for the dock was previously issued on November 17, 1983, and remains in effect at this time. According to the parties, permit approval is also required from the Department of Natural Resources (DNR). However, DNR is awaiting action by DER before issuing or denying a permit. Bethel Creek is a relatively small navigable U-shaped dead-end canal connected to the Intracoastal Waterway in the Indian River in Indian River County, Florida. It is classified as a Class III water of the State. Because of continued development along the Creek, and poor flushing characteristics, the water has gradually deteriorated over the years. Most of its shoreline is bulkheaded in the vicinity of the proposed project, and it has a depth of around fifteen to twenty feet. The width of the Creek at the site of the project ranges from 120 to 195 feet and represents the most narrow part of the canal. The project is approximately one to two-tenths of a mile from the dead-end of the canal, and less than a half a mile from the opening at Indian River. In addition to applicant's commercial development, there are a number of single family residences on the Creek, a large condominium known as the Riverwalk Condominium, and eight townhouses at the deadend of the Creek. Other development may also exist but was not disclosed at hearing. There are a number of existing private docks with boats on the Creek including a four-dock marina at the end of the canal. Petitioner, Riverwalk Condominium Association, Inc., is an association of condominium owners who reside within 500 feet of the proposed activity. Under the proposal, applicant intends to limit the docking facilities to the private use of The Yachting Arcade." There will be no fuel or maintenance service for boats, and sewage disposal facilities and live-aboards will be prohibited. Shoreline improvement is to be accomplished by excavating an area landward of the dock, backfilling the area with sand and rubble, placing filter fabric over the backfill, laying sand and gravel over the fabric and revegetating the excavated/backfilled area with cordgrass and red mangroves. The theoretical capacity of the docking facility will depend on the size of the boats, but it will allow docking by up to twelve to fifteen boats of the fifty foot category at one time, or up to thirty-six smaller boats simultaneously. At the insistence of DER, the boats will be moored parallel to the Creek in an effort to not impede navigation. After receiving the original and amended applications, DER personnel made three on-site inspections of the property. These were conducted in January and May, 1984 and May,|1985. Although no water quality testing was performed, the Department found the Creek to be a viable habitat for various game and nongame species, including mullet, sheepshead, tarpon, snapper, manatees, great blue herons and egrets. The property along the shoreline was comprised of Australian pines, pepper trees and railroad vines until they were removed in June, 1985 by applicant. There has been severe erosion along the water front but this will diminish through revegetation and excavation of the bank. The construction of the dock will create only minor, short-term turbidity. The quality of the water within the Creek is now poor, but a vegetated shoreline, including mangroves, will assist in cleansing the water and improving its quality. Therefore, applicant has given reasonable assurances that the proposed project will not violate established water quality standards, or constitute a threat to marine life, wildlife or natural resources. According to agency rule an applicant must demonstrate that "the proposed project will not create a navigational hazard, or a serious impediment to navigation. . ." in the affected waters. Even though the dock will be built at the most narrow part of the creek, and may have as many as thirty-six boats moored at any one time, the agency expert concluded that no impediment to navigation would occur.2 However, testimony by residents on the Creek indicate that the actual navigable part of the stream is much smaller, and that boats are frequently "beached" because of the shallow nature of the waters. Since applicant will simultaneously allow as many as fifteen boats in the fifty-foot category, or thirty-six of a smaller variety, to traverse the Creek, there will be a serious impediment to navigation on the narrow navigable part of the Creek. Moreover, it will create a navigational hazard. A restriction on the number of boats to use applicant's dock at one time is not practical, and even DER omitted such a condition because of its inability to enforce this provision. Therefore, the criteria for issuance of a permit have not been met.
Recommendation Based on the foregoing findings of fact and conclusions of law, it is RECOMMENDED that the application of The Yachting Arcade for a permit to construct a shoreline dock on Bethel Creek in Indian River County, Florida be DENIED. DONE and ORDERED this 7th day of August, 1985, in Tallahassee, Florida. DONALD R. ALEXANDER Hearing Officer Division of Administrative Hearings The Oakland Building 2009 Apalachee Parkway Tallahassee, FL 32301 (904)488-9675 Filed with the Clerk of the Division of Administrative Hearings this 7th day of August, 1985.
Findings Of Fact Urbanek owns land in and adjacent to Town Lots 93 and 94, Highland Beach, in Section 28, Township 46 South, Range 43 East, Palm Beach County, Florida. The real estate in question is located on the eastern shore of the Intra-Coastal Waterway approximately 2,000 feet south of the mouth of the C-15 Canal. Urbanek seeks a permit under Chapters 403 and 253, Florida Statutes, and water quality certification under Public Law 92-500, to dredge approximately 24,500 square feet of shoreline and shallow nearshore area, while installing approximately 240 linear feet of bulkhead and ten mooring piles, and constructing a marginal dock and piers for the use of future residents. The application also includes filling approximately 60,000 square feet of tidally connected ditches and wetlands to allow the construction of a high density residential development. On January 19, 1976, DER received a short form application for a permit from Urbanek pursuant to Subsection 17-4.28 (4)(a), Florida Administrative Code. On March 10, 1976, Urbanek received from DER a request for additional information. This occurred 51 days after Urbanek's original application for permit. Urbanek forwarded the requested additional information to DER on April 22, 1976, and April 30, 1976. On May 12, 1976, DER notified Urbanek that the project must be submitted using standard permitting procedures along with the incorporation of certain recommendations made by DER's field inspector. On June 9, 1976, Urbanek was notified by DER that his application had been forwarded to Tallahassee with a recommendation for denial on two grounds. First, that the application did not meet the criteria for short form applications and second, that the proposed project would eliminate valuable submerged and wetland habitats. On July 27, 1976, Urbanek was notified by DER's Tallahassee office that his application was received on January 1976, and that the application was incomplete. The notification requested additional information. On September 22, 1976, DER notified Urbanek that processing of his application was discontinued because required data was not sent by Urbanek to DER. Urbanek was further advised that processing of the application," would be continued upon receipt of the necessary information. On January 20, 1977, Urbanek submitted another modified permit application to DER. On February 28, 1977, DER sent Urbanek notice of receipt of the application once again requesting additional information be submitted. On March 4, 1977, Urbanek forwarded the requested information to DER. On April 1, -1977, DER forwarded to Urbanek its notice of intent to deny and the proposed order of denial of the permit application. On April 15, 1977, Urbanek petitioned DER for a hearing pursuant to the provisions of Section 120.57, Florida Statutes. The area of the project, prior to the turn of the century, was a fresh water wetland. However, salt water intrusion from the permanent opening of the Boca Inlet in south Palm Beach County in the early 1900's paved the way for colonization of mangroves in the Spanish River Basin, now the Intra-Coastal Waterway. As the human population increased in Palm Beach County, the mangroves were destroyed in order to afford living spaces. As a result, approximately 77 percent of the mangroves in Palm Beach County have been removed. One of the last remaining mangrove areas in southern Palm Beach County is located on a strip of land which borders the eastern side of the Intra-Coastal Waterway. The applicant's project site represents a portion of that strip. The project site fronts 230 feet-of the Intra-Coastal Waterway and extends approximately 670 feet eastward to State Road A1A. The property is intersected by three mosquito control ditches which run perpendicular to the Intra-Coastal Waterway but do not connect with it, and by six lateral ditches which extend from north to south and adjoin the property to the south. The project site is thus divided into eighteen parcels of land or "islands" and a fringing shoreline area. A survey conducted on October 13, 1977, and October 18, 1977, revealed the emergent areas between the ditches to be vegetated by mostly white mangroves, with canopies ranging from fifteen to forty-five feet in height. Numerous white and red mangrove seedlings plus a few scattered black mangrove seedlings indicate that the area may be changing from a predominantly white mangrove to a mixed mangrove community throughout the project site. Batis and Sesuvium were found and Australian Pines and Brazilian Pepper were observed only in areas where spoil from dredging activities was placed on the emergent area. There are approximately seven to eight thousand trees, including seedlings, in the project area. The mangrove system at the project site was characterized as a very productive system by Dr. G. Alex Marsh, an expert in Estuarine Ecology, who testified for DER. Dr. Arnold Banner of the United States Fish and Wildlife Service concurred with Dr. Marsh that the eradication of the productive system would result in the removal of a significant source of food and habitat. The evidence shows that a wetland habitat such as the project site affords approximately 535 pounds of fishing products per year with a dollar value of $8,000 per acre to the public. Petitioner argues that it would be in the public interest to bulkhead and fill the subject property because rodents would be eliminated, trash and debris would no longer collect on the property and that further erosion of the property would be prevented. However, Urbanek has failed to establish with substantial competent evidence that there actually exists a rodent problem on the subject property. The evidence does establish that trash and debris collect among the root system of the vegetation and that severe erosion has occurred on the property from wave action created by vessels moving through the Intra- Coastal Waterway. Urbanek has failed to establish with substantial competent evidence that the proposed project will not degrade water quality, cause violation of water quality standards or criteria or cause pollution. In fact, no evidence was submitted whatsoever by Urbanek which would tend to prove any of these three preconditions to the granting of the requested permit. Nonetheless, DER's failure to act on the permit application within the time limits prescribed by Subsection 120.60 (2), Florida Statutes, as amended in 1976, mandates the issuance of the requested permit.
Findings Of Fact Petitioner is the state land planning agency charged with the responsibility to administer the provisions of Chapter 380, Florida Statutes, and the regulations promulgated thereunder. Petitioner has the authority to appeal to the Florida Land and Water Adjudicatory Commission any development order issued in an area of critical state concern. The appeal in the instant proceeding was timely. Monroe County is a political subdivision of the State of Florida and is responsible for issuing development orders for development in unincorporated Monroe County. Monroe County issued the development order that is the subject of this appeal. Respondents, Mortimer and Gay Hall, are the owners of real property known as Lots 60 and 61, Block 19, Breeze Swept Beach Estates on Ramrod Key in unincorporated Monroe County. The Halls have constructed a single family dwelling on that property, but the building permit for the construction of the dwelling is not at issue in this proceeding. Most of Monroe County, including the subject property, is within the Florida Keys Area of Critical State Concern as designated under Sections 380.05 and 380.0552, Florida Statutes. On January 21, 1992, Monroe County issued the subject building permit, Permit Number 9010001679, to Mortimer and Gay Hall as owners and Pierce Construction and Builders as contractor. The subject permit would be subject to certain conditions imposed by the Florida Department of Natural Resources (DNR). As permitted, the use of the structure would be limited to swimming and recreation. Boating, or the mooring of boats, would not be permitted. By letter dated December 17, 1991, DNR authorized the project subject to certain conditions and limitations, and provided, in pertinent part, as follows: Mort and Gay Hall are hereby authorized to proceed with the construction of a swim platform as proposed This authorization is specifically conditioned upon the following: * * * The structure shall be used only for passive recreational activities such as swimming and fishing. Mooring of vessels at the facility either on a temporary or permanent basis is strictly prohibited. The platform and walkway shall be elevated four feet above mhw [mean high water]. Handrails at a height of four feet shall be installed along the walkway and around the platform. Handrails shall be two feet above the platform deck. Install at least three "NO MOORING" signs along the perimeter of the platform. Install a ladder on the waterward terminus of the platform for water access. The application submitted by the Halls to Monroe County that resulted in the subject permit incorporated the DNR conditions and described the project as follows: Applicant wishes to install a wooden swim platform (20 ft. length x 8 ft. width) and a wooden elevated access walkway (25 ft. length x 4 ft. width) to access this platform; for the purpose of using the channel cut for swimming activities at their existing single family residence. Monroe County's comprehensive plan, which has been approved by the Petitioner and by the Administration Commission, is implemented through its adopted land development regulations, codified in Chapter 9.5, Monroe County Code. Section 9.5-345(m)(2), Monroe County Code, referred to as the four foot rule, provides as follows: (2) All structures on any submerged lands and mangroves shall be designed, located and constructed such that: * * * No structure shall be located on submerged land which is vegetated with sea grasses except as is necessary to reach waters at least four (4) feet below mean low level for docking facilities; No docking facility shall be developed at any site unless a minimum channel of twenty (20) feet in width where a mean low water depth of at least minus four (4) feet exists; Section 2.104, Nearshore Waters, Monroe County Comprehensive Plan, Volume II, Future Land Use Element, provides, in pertinent part, as follows: The Florida Keys are dependent on nearshore water quality for their environmental and economic integrity. The heart of the Florida Keys economy, the means by which Monroe County exists as a civil and social institution, is based on its unique oceanic character. If nearshore water quality is not maintained, then quality of life and the economy of Monroe County will be directly and immediately impacted. OBJECTIVES 1. To protect, maintain and, where appropriate, to improve the quality of nearshore waters in Monroe County. * * * POLICIES 1. To prohibit land use that directly or indirectly degrade nearshore water quality. * * * To prohibit the development of water dependent facilities, including marinas, at locations that would involve significant degradation of the biological character of submerged lands. To limit the location of water-dependent facilities at locations that will not have a significant adverse impact on off-shore resources of particular importance. For the purposes of this policy, off-shore resources of particular importance shall mean hard coral bottoms, habitat of state or federal threatened and endangered species, shallow water areas with natural marine communities with depths at mean low tide of less than four (4) feet, and all designated aquatic preserves under Florida Statutes section 258.39 et seq. By Final Judgment entered June 7, 1991, the Honorable Richard G. Payne, Judge of the Circuit Court of the Sixteenth Judicial Circuit, in and for Monroe County, Florida, ruled in Stanton v. Monroe County, Case No. 91-20-035- CA-18, that Monroe County's four foot rule does not apply to swimming piers, concluding, in pertinent part, as follows at page five of the Final Judgment: 5. To the extent that the County's Comprehensive Plan and Land Development Regulations fail to provide for swimming piers ... the court finds that it is unreasonable to treat such piers as if they were docks at which boats are to be moored. Pursuant to the judicial review authority of Chapter 163, Fla. Stat., the court declares ... [the four foot rule] inapplicable to piers at which boats are not to be moored. The County has adequate judicial remedies, including injunction, to prevent the use of such piers, including the subject pier, for the mooring of boats. Despite the Stanton ruling, supra, Monroe County has interpreted the four foot rule as being applicable to swimming piers such as the one the Halls wish to construct. Monroe County's long-standing interpretation of the four foot rule would not prohibit the permit because of the minimal effect such construction would have on the nearshore waters. Since 1986, Monroe County has adopted an interpretation of Section 9.5-345(m)(2), Monroe County Code, and of Section 2.104, Nearshore Waters, Monroe County Comprehensive Plan, Volume II, Future Land Use Element, that would permit the construction of the subject project. That interpretation permits the development of docks in subdivisions that were under development in 1986 if there is at least four feet of water at the terminal point of the dock at mean low tide. The structure that is the subject of this proceeding is in a subdivision that was under development prior to 1986 and would, if permitted, terminate in a channel more than 20 feet wide with water at least six feet deep at mean low tide. Monroe County's interpretation of the four foot rule is that the rule was intended to restrict the development of boating access facilities in new, undeveloped subdivisions and to regulate proposed expansion of existing marinas and the development of new marinas. Monroe County considers the subject application by the Halls to meet all of its permitting criteria. The structure will be constructed in a dredged area of adequate size for swimming. Access to the structure by boat is unlikely because the swimming area is surrounded by a reef and hard bottom that is extremely shallow, even at high tide. At low tide much of this surrounding area is above water, and the deepest area of water is approximately six inches. At high tide, the water depth of the surrounding area ranges from approximately four inches to approximately eighteen inches. On the waterward side of the surrounding area, the water depths are less than four feet. Petitioner's concern is that boats will moor at the structure regardless of the restrictions on the permit and that these boats will cause degradation to the nearshore waters while crossing to deep water. Benthic communities exist in the waters between the Halls's property and deep water, such as rock-hard bottom, sea grasses, algae, and hard coral. Turtles, manatees, sharks, stingrays, eagle rays, snapper, pink shrimp, mullet, and other marine animals populate those waters. Sea grass beds play an important role in water quality maintenance in the Keys through filtration, nutrient uptake, stabilization of the bottom, and as a habitat for commercially important species. One cannot reach deep water by boat from the Halls's property without crossing areas in which the water depth is less than four feet at low tide. Petitioner speculates that prop dredging, and the resulting damage to seagrass beds and shallow water marine communities, would result if one were to attempt to navigate these shallow waters by a propeller powered boat. Petitioner's concern is premised on the unwarranted assumptions that the structure will be illegally used at some point in the future by boats. Petitioner has failed to establish that this concern justifies denial of the permit. Petitioner did not establish that damage would be done to the environment by swimming in the area of the proposed swimming platform. Respondents presented evidence that several similar projects were permitted at approximately the same time as the Halls's permit without Petitioner filing an appeal. This evidence was insufficient to establish that Petitioner should be estopped to appeal the subject permit, that Petitioner engaged in selective enforcement of its regulatory power, or that Petitioner otherwise brought the subject appeal for an inappropriate purpose.
Recommendation Based on the foregoing findings of fact and conclusions of law, it is recommended that the Florida Land and Water Adjudicatory Commission enter a final order affirming Monroe County's decision to issue building permit number 9010001679, and dismissing the appeal filed by the Department of Community Affairs. DONE AND ENTERED this 26th day of January, 1993, in Tallahassee, Leon County, Florida. CLAUDE B. ARRINGTON 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 26th day of January, 1993. APPENDIX TO RECOMMENDED ORDER, CASE NO. 92-2958DRI The following rulings are made on the proposed findings of fact submitted on behalf of Petitioner. The proposed findings of fact in paragraphs 1, 2, 3, 4, 5, 6, 7, 8, 9, 10, and 14 are adopted in material part by the Recommended Order. The proposed findings of fact in the first sentence of paragraph 11, 12, 13, and 16 are subordinate to the findings made. The proposed findings of fact in paragraph 15 are rejected as being unnecessary to the conclusions reached because the use of the platform is limited. The testimony by Robert L. Herman as to the purpose and interpretation of the four foot rule by Monroe County is found to be a more persuasive than Mr. Metcalf's testimony. The following rulings are made on the proposed findings of fact submitted on behalf of Respondents. The proposed findings of fact in paragraphs 1, 2, 3,4, and 8 are adopted in material part by the Recommended Order. The proposed findings of fact in paragraphs 5 and 6 are rejected as being subordinate to the findings made. The proposed findings of fact in paragraph 8 are rejected as being unnecessary to the conclusions reached. COPIES FURNISHED: Lucky T. Osho, Esquire David Jordan, Esquire Department of Community Affairs 2740 Centerview Drive Tallahassee, Florida 32399-2100 Theodore W. Herzog, Esquire Theodore W. Herzog, P.A. 209 Duval Street Key West, Florida 33040 Linda Loomis Shelley, Secretary Department of Community Affairs 2740 Centerview Drive Tallahassee, Florida 32399-2100 G. Steven Pfeiffer, General Counsel Department of Community Affairs 2740 Centerview Drive Tallahassee, Florida 32399-2100 James T. Hendrick, Esquire Attorney for Monroe County Post Office Box 1117 Key West, Florida 33040 Carolyn Dekle, Director South Florida Regional Planning Council 3400 Hollywood Boulevard Suite 140 Hollywood, Florida 33021 Pierce Construction and Builders Route 4, Box 319 Summerland Key, Florida 33042 Bob Herman, Herb Rabin, Lorenzo Aghemo, Pat McNeese Monroe County Growth Management Division Public Service Building, Wing III 5100 Junior College Road West Stock Island Key West, Florida 33040 William R. Kynoch, Deputy Director Florida Land and Water Adj. Commission Executive Officer of the Governor 311 Carlton Building Tallahassee, Florida 32301
