The Issue Whether Petitioner is entitled to a consent to use sovereign submerged lands.
Findings Of Fact MBRRC filed an application for an environmental resource permit and authorization to use sovereign submerged lands located in the Biscayne Bay Aquatic Preserve (BBAP). This application sought approval to construct two finger piers and to install twelve mooring pilings for the benefit of a private yacht club. The application was filed with the Department for review on October 20, 1995. The Petitioner’s property is located on Hibiscus Island, a man-made island within the BBAP, and is accessed by boat. The island is primarily used for residential purposes. Petitioner’s facility is the only commercial docking facility on the island. Petitioner owns approximately 140 feet along the waterfront with its property line extending 20 feet seaward of the upland property. It has an existing dock which is approximately 10 feet wide that runs the length of, and parallel to, the seawall along its waterfront. The proposed finger piers would extend waterward and perpendicular to the existing dock from its ends. This extension proposes to use approximately 16 feet into the sovereign submerged land at the ends and would also allow the installation of 12 mooring pilings between the piers. The ultimate purpose of the installation is to allow perpendicular docking. At all times material to this case the Department has considered the proposed construction to be a new facility subject to the requirements of Section 258.397(3)(a), Florida Statutes, and Rule 18-18.006(3), Florida Administrative Code. No existing structures at the site would qualify the applicant for the type of lease proposed. The Petitioner annually hosts numerous fishing and social events at its club facility. Participants typically “raft” vessels together in order to gain access to the shore. Historically this process has moored vessels parallel to the existing dock/seawall. This “rafting” would not necessarily be eliminated by the addition of the proposed finger piers. Petitioner seeks to expand the docking facility as requested in order to provide better ingress and egress to its property. It contends that fishing and boating in the BBAP will be enhanced by such improvements. Petitioner maintains its property is being treated differently than others; however, policies used by the Department in this instance are applicable to all areas of the BBAP. By letter dated February 6, 1996, the Department advised the Petitioner that staff would recommend denial of the application. That letter advised Petitioner of the “extreme hardship” test found in Rule 18-18.006(3), Florida Administrative Code as well as Section 258.397(3)(a), Florida Statutes. The letter noted that this standard was “at best very difficult to demonstrate” and advised Petitioner of the “public interest” requirement also set forth by rule and statute. “Self-imposed circumstances” as used in the applicable rule has been construed to include circumstances where the applicant seeks to improve existing boat access, to increase the number of docking slips, and to enhance the upland property. The Board of Trustees of the Internal Improvement Trust Fund (Board of Trustees) has determined that the construction of single-family docks meets the “extreme hardship” test because single-family docks are considered to be the lowest impact use available on sovereign submerged land. It is deemed appropriate to allow a qualified right of ingress and egress to the upland owner. The Petitioner’s proposal is not a public project or a public necessity. Petitioner currently has ingress and egress to its upland property. The Petitioner’s property is a nonconforming use in a residential area. The term “property owners in the area” has been construed to mean the BBAP. The proposed project is not unique to the applicant, and the burden to the applicant is shared by other property owners in the BBAP. The proposed project would provide additional access to an upland property owner who already has boat access to the waterway. Neither the project site nor the island on which it is located are unique as other properties of a similar nature are within the BBAP. In order to establish that a proposed project is “in the public interest,” applicants are required to demonstrate that the activity would improve either public recreation, water quality, fish hatcheries, or other matters of public interest. In this instance, Petitioner did not submit a written proposal to support the public interest requirement during the application process. Consequently, DEP has not assessed such proposal for its quantity or quality. Petitioner relies on its improved boating access to support a claim of enhancement to public recreation. As to water quality, fish hatcheries, or other matters of public interest, the proposed project would adversely affect seagrasses and other environmental resources by shading. Although the installation of mooring pilings would provide some environmental benefit, those benefits would not be quantifiable and would be offset by increased shading from the project. Other proposals submitted by Petitioner incidental to its Dade County permit application are insufficient in detail and scope to show the public interest requirement would be met. The proposed project is located in an area that is intermediate between the most sensitive and least sensitive sites, for the purpose of manatee protection. The proposed project would have an adverse environmental impact on manatee protection since it creates additional docking slips and additional boat traffic. The proposed project would result in environmental costs through the loss of resources and increased turbidity. The proposed project would provide no quantifiable economic benefit to the public, but would provide some economic cost in the loss of habitat and food source for fisheries. The proposed project would provide no social benefits different from those presently provided by the existing facility. The benefit of the proposed project is merely enhancement of the Petitioner’s current use at a cost of lost fisheries, increased danger to manatees, and increased turbidity.
Recommendation Based on the foregoing, RECOMMENDED: That the Department of Environmental Protection enter a final order denying Petitioner’s request for authorization to lease sovereign submerged land. DONE AND ORDERED in Tallahassee, Leon County, Florida, this 31st day of March 1997. J. D. PARRISH Administrative Law Judge Division of Administrative Hearings The DeSoto Building 1230 Apalachee Parkway Tallahassee, Florida 32399-3060 (904) 488-9675 SUNCOM 278-9675 Fax Filing (904) 921-6847 Filed with the Clerk of the Division of Administrative Hearings this 31st day of March 1997. COPIES FURNISHED: Stephen E. Tunstall, Esquire Stephen E. Tunstall, P.A. 2701 Southwest LeJeune Road Suite 410 Coral Gables, Florida 33134 Jeffrey Brown, Esquire Department of Environmental Protection 3900 Commonwealth Boulevard Tallahassee, Florida 32399-3000 Kathy Carter, Agency Clerk Office of the General Counsel Department of Environmental Protection, Mail Stop 35 3900 Commonwealth Boulevard Tallahassee, Florida 32399-3000 Perry Odom General Counsel Department of Environmental Protection 3900 Commonwealth Boulevard Tallahassee, Florida 32399-3000
The Issue The issue to be determined is whether the applicants, William Guererro and Christina Bang, a/k/a Christina Guerrero (Applicants), are entitled to issuance of a Consolidated Environmental Resource Permit and State Lands Approvals for various structures on the Applicants’ property at 58458 Overseas Highway, Marathon, Florida.
Findings Of Fact The Parties Petitioners Bernard Spinrad and Marian Spinrad are the owners of adjoining parcels of property with the addresses of 58418 and 58420 Overseas Highway, Marathon, Florida. They acquired the property in December 2001. They recently completed construction of two residential structures on the properties. The structure at 58418 Overseas Highway is currently listed for sale. The structure at 58420 Overseas Highway is a vacation rental property. Neither structure is Petitioners’ permanent residence. The DEP is the state agency with the power and duty to regulate activities in waters of the state pursuant to chapter 373, Florida Statutes. The DEP also serves as staff to the Board of Trustees of the Internal Improvement Trust Fund (“Board of Trustees”) to review and act on activities on state sovereignty submerged lands under chapter 253. The Applicants, are the owners of adjoining parcels of property with the address of 58478 Overseas Highway, Marathon, Florida (the Property). They purchased the Property in June 2010. The structures that are the subject of the Permit are to be constructed near or waterward of the shoreline of the Property. The Property The Property is located on Grassy Key, an island in the middle Florida Keys, within limits of the city of Marathon, Monroe County, Florida. U.S. Highway 1 passes through Grassy Key. The Property -- as is that of Petitioners -- is situated between U.S. Highway 1 and the open waters of the Atlantic Ocean. In the early part of the 20th century, a portion of Grassy Key was platted as the Crains Subdivision. The properties owned by Applicants and Petitioners are within the Crains Subdivision. During the periods of time directly relevant hereto, the Property has been owned by Burgess Levine, who owned the property during the period prior to the October 2006, landfall of Hurricane Wilma until June 2010, and by Applicants, who have owned the Property since June, 2010. Grassy Key Grassy Key is three-miles long, and has 6800 feet of beaches, none of which are designated as critically eroded. The island fronts the Atlantic Ocean to the east, and the more protected waters of Florida Bay to the west. The waters along the Atlantic Ocean shoreline of Grassy Key in the area at issue are shallow, with an extremely flat bottom having a very gradual slope of approximately 1 to 30, meaning there is a one foot vertical change over 30 horizontal feet. The mean tide range at the Property is about 1.7 feet. Under normal conditions, the stretch of Grassy Key at issue is fairly characterized as a zero-wave energy shoreline. Waves break well offshore and there is negligible wave energy propagating beyond that point. What shoreline energy exists is produced by small tide currents and wind-shear on the water surface that moves water along the shoreline. The direction of the water movement is dependent on tides and wind direction, with the predominant direction being from north to south. Erosive and other significant changes to the shoreline of Grassy Key, including that stretch fronting the Property, are event driven, meaning when there is a coastal storm that causes a rise in the water level, substantially higher than the astronomical tide, waves can propagate onto the shoreline of Grassy Key. The wind and waves can come from virtually any direction depending on the storm. A storm of greater intensity will create higher energy-wave conditions. Although storm conditions may only occur over 1 to 3 percent of a given year, with the rest of the year having zero-wave energy, on average the coastline may be considered to be of moderate-wave energy. The beach sediment along the Grassy Key shoreline in all areas pertinent hereto consists of calcareous material, made up of the breakdown of corals and coralling algae, with a significant fraction of other detrital marine material. The upper beaches of Grassy Key, including that on the Property, generally consist of coarse, calcareous sand with a small fraction of calcareous silt-size particles. The inter-tidal areas along Grassy Key consist of predominantly fine calcareous sand, with a greater fraction of calcareous silt. Extending out into the nearshore area all along Grassy Key, including that fronting the properties owned by Petitioners and Applicants, the sediment becomes a very fine calcareous sand, with a greater fraction of the material being calcareous silts and clays, and with a substantial amount of organic mud of a marine origin, classified as Islamorada muck. Since at least the 1970s, one wading in the nearshore waters along Grassy Key could expect to sink into the surface muck to a depth of anywhere from six inches to two feet. The depth of muck becomes less as one moves further out and approaches the offshore Thalassia beds. Although some areas offer more resistance than others, it is routine to experience difficulty in walking and wading along the coast of Grassy Key because of the high percentage of clays and silts in the substrate. The band of muck narrows as one proceeds towards the northern stretches of Grassy Key, until one reaches the furthest areas to the northeast where the nearshore transitions to exposed rock and hard bottom. The surface muck that exists in the nearshore waters of Grassy Key, having a sizable component of decaying organic material, gives off an odor of hydrogen sulfide when disturbed that some find to be unpleasant. The odor is a naturally- occurring condition of the sediment, and is common in mucky areas all around the southern coasts of Florida. The suggestion that the shoreline in the vicinity of the Petitioners’ property, and that of Applicants, was a naturally occurring white, sandy beach is contrary to the greater weight of the evidence. To the extent the shoreline at Petitioners’ property may have been temporarily altered by the overwash from Hurricane Wilma as discussed herein, Petitioners’ own post-Wilma man-made efforts at beach stabilization, or the redistribution of sediments occasioned by Hurricanes Isaac and Sandy in 2012, the evidence demonstrates the “mucky” condition described herein to be more consistent with the natural and long-standing conditions of Grassy Key. Thus, as Grassy Key exists in the present time, one may expect to encounter six inches to two feet of loose muck anywhere along the nearshore area. Close to shore of Grassy Key are scattered beds of Halodule, a species of seagrass that tends to emerge and grow in shallow waters. The growth of Halodule is influenced by the nature of the sediments, the salinity temperature, and clarity of the water. Storm events have a significant effect on its growth. Given its transient nature, Halodule may vary in any given area from nonexistent, to spotty, to well-established beds. As one moves further offshore, the Halodule transitions to large, continuous beds of Thalassia. Thalassia grows in deeper water, and is common to a depth of about 12 feet. Being deeper and less affected by storm energy, the line of the Thalassia beds off of Grassy Key has not substantially changed over time. As wind and waves come across the grass beds, and as tides ebb and flow, grass blades are cropped. The amount of grass varies seasonally to a degree. The cropped and dislodged seagrasses, along with other organic material entrained therein, are naturally carried by the tides and wind and stranded along the shoreline. The stranded material is known as wrack, and the line of stranded material is known as the wrack line. Grassy Key is well known for the large seagrass wracks that pile up on the shoreline. A wrack line is a normal and natural occurrence in marine environments like that of Grassy Key, and can be a good indicator of the upper edge of the water action at a particular time. The cropping and dislodging of seagrass is accentuated during major or minor storm events. During Hurricane Rita in 2005, a very large seagrass wrack was blown onto the shoreline of Grassy Key. It was subsequently blown back out to sea by the overwash from Hurricane Wilma. The decomposition of the seagrass and other organic materials creates a significant odor that is not uncommon. That odor of decomposing material is well-recognized as being associated with Grassy Key. Areas along the shoreline of Grassy Key have been used by sea turtles for nesting. However, the nature of the substrate in the area of the Property is not optimal for nesting. Generally, sea turtles require a nesting site with 15 to 20 inches of sand above the water table so as to allow them to dig a suitably deep and dry cavity for their eggs. The natural substrate along the section of Grassy Key at issue is coarser and more difficult to dig into, and does not have the depth of sand for the best chance of a successful nest. Despite the nature of the substrate, Petitioner testified as to her observation of turtle nests along her property in each year from 2006 through 2010. Since the SW Groin, the Mid-bulkhead, and the NE Groin were all in existence and functioning during that period, with work to the SW Groin having been completed by 2008, the preponderance of the evidence demonstrates that those structures have no effect on the success or failure of sea turtles to nest along the property. To the extent nesting has been disrupted since 2011, the most logical inference that can be drawn from the evidence is that such disruption is the result of the Mid-Jetty Extension, which is slated for removal under the terms of the Permit. The preponderance of the evidence demonstrates that the structures and activities authorized by the Permit will have no adverse effect on sea turtles. Hurricane Wilma In October, 2005, Grassy Key was pounded by Hurricane Wilma. The storm passed to the north, and created a substantial storm surge that moved from west to east across Grassy Key. The storm surge created a “ridge and runnel” effect on the Atlantic facing shoreline, with the channelization of the storm tide flow creating erosion and gullies on upland shore-adjacent properties. The storm surge and flooding across Grassy Key caused substantial wash-outs of sand; transported a large volume of sandy, upland sediments into the nearshore waters of the Atlantic Ocean; and created washover “fans” of material along the shoreline of Grassy Key. The effects of the Hurricane Wilma storm surge manifested just north of the Property, became substantial at the Property, and continued south down the shoreline for a considerable distance. At the Property, sand was pushed from 50 to 100 feet waterward from the existing shoreline, and a substantial runout was created running parallel and north of the SW Jetty. The sand pushed into the water buried everything in its path, including seagrasses. In short, the post-Wilma shoreline from the Property south along Grassy Key was left in a completely disrupted state. The nearshore waters fronting the properties owned by Petitioners and Applicants were affected by the deposition of sandy, upland sediments, which temporarily created areas of substantially harder-packed sediment. Over time, as the shoreline equilibrated and the sandy sediment distributed through a broader area, more typical shoreline conditions returned. The photographic evidence demonstrates that the Mid- bulkhead and the SW jetty structures were impacted by the Hurricane Wilma storm surge. In addition, the sandy area between the mid-bulkhead and the SW jetty was pushed seaward from its previous location. The scars from Hurricane Wilma remain evident through the most recent aerial photographs received in evidence. It is visually apparent that seagrass, though reappearing in patches, has not reestablished in the nearshore areas along the affected shoreline of Grassy Key -- including the areas in front of the Property and the property owned by Petitioners -- to the extent that it existed prior to the storm. Post-Wilma Activities When Hurricane Wilma hit, the Property was owned by Burgess Lea Levine. Not long after Hurricane Wilma, Ms. Levine shored up the SW Jetty, and performed work in the “beach” area between the mid-bulkhead and the SW jetty. The photographic evidence also supports a finding that the rock outline of the Mid-jetty was reestablished to its pre-Wilma configuration. The repairs to the SW Jetty resulted in a structure that is virtually indistinguishable in size and shape to the SW Jetty as it presently exists. The wrack line at the beach area after it was “worked” following the passage of Wilma, shows the area in which work was done to be generally consistent with -- though slightly seaward of -- the 2005 post-Wilma shoreline. In 2008, Ms. Levine applied for a series of exemptions and for consent of use for state-owned lands for “shoreline repair, replace earthen ramp with a concrete ramp, repair wood deck, replace mooring piles & maintenance dredge existing channel w/in Atlantic Ocean.” On September 19, 2008, the DEP issued a regulatory authorization and proprietary submerged land approval. The Rights of Affected Parties that accompanied the September 19, 2008, notice provided that “[t]his letter acknowledges that the proposed activity is exempt from ERP permitting requirements” and that “this determination shall expire after one year.” The notice of Rights of Affected Parties did not apply to the proprietary authorization. At some time after issuance of the regulatory authorization, Ms. Burgess initiated additional work to repair the SW Jetty. The photographic evidence, which is persuasive, indicates that the work on the SW Jetty, including the concrete cap, was complete by the end of 2008. When Applicants purchased the Property, the determination of exemption issued in 2008 had, by application of the notice of Rights of Affected Parties, expired. Shortly after the Applicants purchased the property, they had the existing family home demolished. Applicants intend to construct a winter vacation home for their personal use on the property. 2012 Storms In August and October 2012, Grassy Key was subject to event-driven conditions as a result of the passage of Hurricanes Isaac and Sandy. Those storms redistributed large areas of sediments that had been moved offshore by the effects of Hurricane Wilma. The Proposed Permit The February 20, 2013, Permit provides that the structures described herein do not require the issuance of an Environmental Resource Permit, subject to the criteria and conditions in Florida Administrative Code Rule 40E-4.051. The Permit provides that the boat ramp is eligible to use the general permit in Florida Administrative Code Rule 62-330.417, the repair and replacement of the dock is exempt pursuant to section 403.813(1)(b), Florida Statutes, the maintenance dredging of the Channel is exempt pursuant to section 403.813(1)(f), and that the repair and replacement of the NW Jetty, the SW Jetty, and the Mid-bulkhead are exempt because the structures are “historic in nature and pre-dates Department regulations.” In addition to the regulatory authorizations, the Permit granted proprietary authorization by Letter of Consent for the dock pursuant to Florida Administrative Code Rule 18- 21.005(1)(c)4., and for the Channel, the NW Jetty, the SW Jetty, and the Mid-bulkhead pursuant to rule 18-21.005(1)(c)7. The Permit established the mean high-water line as that existing in 1974 and depicted on the “Richmond Survey.” Proprietary authorization for the boat ramp was determined to be unnecessary due to its location above the mean high-water line. Finally, proprietary authorization for the “Sandy Area” or beach between the Mid-bulkhead and SW Jetty was granted by Letter of Consent pursuant to rule 18-21.005(1). On September 20, 2013, the DEP filed a Notice of Additional Grounds for Exemption Determination, in which it found each of the structures subject to the regulatory review to “have only minimal or insignificant individual or cumulative adverse impacts on water resources” and to thus be exempt from the need to obtain an Environmental Resource Permit pursuant to section 373.406(6), Florida Statutes. On December 12, 2013, Applicants filed a Notice of Filing Proposed Changes to the Pending Agency Action in which they agreed to certain additional conditions, and which referenced the October 1, 2013, repeal of rule 40E-4.051, and its replacement by the “Statewide ERP rules.” For purposes of this de novo proceeding, the proposed Permit at issue includes the February 20, 2013, Permit; the September 20, 2013, Notice of Additional Grounds for Exemption Determination; and the December 12, 2013, Notice of Filing Proposed Changes to the Pending Agency Action. The Proposed Structures Groins There has been some confusion relating to the names of the structures that are subject to the proposed Permit. Two of the structures are referred to as jetties, the NE Jetty and the SW Jetty, and the middle structure is referred to as the Mid- bulkhead. A jetty is a navigation structure that is constructed at a barrier inlet. Its purpose is to stabilize the inlet and prevent shoaling by “jetting” current and wave-driven sand further offshore, such that the offshore bar is moved into deep enough water to allow navigation in and out of the tidal inlet, and allowing the tidal current between the ocean and the receiving body of water to keep the inlet scoured and open. There are 48 jetties on the open coast of Florida, none of which are in the Florida Keys. A groin is a structure designed for shore protection purposes. A groin is typically aligned perpendicular to the shoreline, or “shore normal.” The structures identified in the Permit as the NE Jetty and the SW Jetty are clearly groins, and not jetties. The mid-bulkhead is a groin, generally for shore confinement, with a channel-facing bulkhead. For purposes of continuity, the structures will be identified by the names given them in the Permit. Since there is negligible wave energy along the shoreline normal conditions, the groins have little or no day- to-day effect on longshore transport. Under storm conditions, the structures affect longshore transport, as evidenced by accretional “fillets,” and function as shoreline protection and confinement structures. The rock groins provide shelter, habitat and structure for corals, sponges, lobster, and fish in the area. The preponderance of the evidence demonstrates that the groins authorized by the Permit will have no adverse effect on fish and wildlife resources. NE Jetty The NE Jetty was originally constructed in the early 1960s, likely concurrent with the dredging of the navigational channel. The quality of the aerial photographs of the period make it difficult to tell if the NE Jetty was a loosely-placed rock embankment or a more well-designed and constructed structure. However, the fillet of sand accreted to the north of the Channel demonstrates that the jetty was in existence and functioning as a shore-protection structure. By the 1970s, the NE Jetty had become overwhelmed by longshore sediment transport from the northeast. Sediment overtopped the NE Jetty and filled in the landward reaches of the Channel. At that point, ability of the NE Jetty to perform as a shore protection structure was compromised to the point that it could no longer hold the shoreline out of the basin or the landward portion of the Channel. The Mid-bulkhead became the dominant structural control over the shoreline and started to accrete the shoreline to the northeast. At some time between 1977 and 1981, the Channel was maintenance dredged pursuant to a permit issued by the Department of Environmental Regulation, DEP’s predecessor agency. The NE Jetty appeared on the plans for the maintenance dredging. Thus, the most reasonable inference that can be drawn from the evidence is that the NE Jetty was repaired and restored in conjunction with the approved maintenance dredging. By 1981, the NE Jetty had been restored as the dominant shore protection structure north of the Channel, and a fillet of accreted material had been reestablished. The aerial photographs from that period are not sufficiently distinct to determine the precise size, shape, and configuration of the NE Jetty at that time. However, there is no evidence of additional work having been performed on the NE Jetty between 1981 and 1985. By 1985, the NE Jetty existed in substantially the size, shape, and configuration as it existed at the time of Hurricane Wilma. Between 1981 and the 2005 arrival of Hurricane Wilma, the evidence is convincing that the NE Jetty was holding up the shoreline to the northeast and preventing sediment from filling in the upper reaches of the Channel. Although the evidence suggests that the NE Jetty had, by 2005, begun to show its age, the continuous presence of an accretional fillet demonstrates that it continued to serve its function as a shore-protection structure. Although the NE Jetty suffered damage from Hurricane Wilma, it continued to perform its shoreline protection function. Aerial photographs taken in 2009 and 2011 show a relatively distinct structure with a well-defined accretional fillet. Thus, the greater weight of the evidence demonstrates that, at the time of its repair in May 2011, the NE Jetty was a functional groin. The NE Jetty, as repaired in 2011, is of substantially the same size, shape, and location as the structure depicted in aerial photographs taken in 1985, 2009, and early 2011. Although the elevation of the structure was increased over its pre-repair elevation, the increase was that reasonably necessary to prevent the function of the structure from being compromised by the effects of age and weather. The work performed on the NE Jetty, consisting of new rock laid on top of the existing rock, constituted repair and maintenance of the existing structure. Since 2005, and at the present time, the shoreline north of the NE Jetty has reached a state of equilibrium and stability, and is not expected to change significantly from its current condition. The preponderance of the competent, substantial evidence demonstrates that the effect of the NE Jetty on the shoreline and water resources of Grassy Key in the vicinity of the properties owned by Applicants and Petitioners is minimal and insignificant. The sand and sediment accreted to the north of the NE Jetty since 1981 is in the range of 250 square feet. SW Jetty The aerial photographs from 19647/ demonstrate that some form of structure then existed at the location of the current SW Jetty. The structure is indistinct due to what appears to be sidecast material from a small channel in front of the property to the immediate south of the Property. By 1971, the SW Jetty had become more distinct. From that time forward, the SW Jetty, and its accompanying fillet of accreted material, appears in roughly the size and shape of the structure as it appeared immediately prior to the arrival of Hurricane Wilma. The SW Jetty was heavily impacted by Hurricane Wilma. The overwash from the storm created a substantial runout alongside the SW Jetty, and the post-storm aerials suggest that the jetty boulders were undermined and shifted from their more uniform 2003 appearance. Immediately after Hurricane Wilma, the owner of the Property commenced restoration and repair activities. As part of the activities, the SW Jetty was repaired with the addition of boulders, which were often three feet and every now and then as much as four feet across. The boulders, being irregularly shaped, could not be stacked like Legos®, so the repairs were not neatly within the precise pre-Wilma footprint. However, the repaired SW Jetty was substantially in the length and location as existed prior to Hurricane Wilma, though it may have had a slightly wider cross-section. By 2007, the work on the SW Jetty was complete, and it had assumed its present appearance with the addition of a concrete cap. Its appearance -- i.e. length, width, and location -- in 2007 and 2008 was not dissimilar from its appearance in 2003. As repaired, the SW Jetty effectively constitutes the same structure that it has been since its initial construction. From a coastal engineering perspective, the work that was performed on the SW Jetty, consisting generally of new rock laid on top of the existing rock, constituted repair and maintenance of the existing structure. Dr. Lin testified that between 1974 and 2011, the area to the southwest of the southwest jetty was “about equalized,” though it was “accreting a little bit.” Thus, the effect of the SW Jetty on the shoreline of Grassy Key in the vicinity of the properties owned by Applicants and Petitioners from 1974 to 2011 was minimal and insignificant. Dr. Lin testified that, since 2011, the same area had eroded. The only substantive shoreline change that logically accounts for that subsequent erosion is the Mid-bulkhead extension, which is slated for removal under the terms of the proposed Permit. Petitioner testified that she observed no adverse effects from activities on the Property until after February 2011.8/ Since work on the SW Jetty was complete by no later than 2008, Petitioner’s testimony supports a finding that the SW Jetty has had no measurable effect on the water resources in the vicinity of the properties owned by Applicants and Petitioners. The preponderance of the competent, substantial evidence demonstrates that the effect of the SW Jetty on the shoreline and water resources of Grassy Key in the vicinity of the properties owned by Applicants and Petitioners is minimal and insignificant. Mid-bulkhead The structure of the Mid-bulkhead first appeared as part of the sidecast material from the excavation of the navigation channel in 1964. It coalesced into a defined but smaller and more rudimentary structure in the 1971-1972 time period. At that time, it was acting as the predominant shore protection structure due to the overtopping of the NE Jetty with sediment, which also filled in the landward reaches of the Channel. By 1981, after the maintenance dredging of the Channel, the Mid-bulkhead had assumed substantially the size, shape, and location that it has currently. The Mid-bulkhead has a navigation function of protecting the landward extent of the Channel from the collapse of adjacent sand and sediment, and a shore protection and compartmentalization function. Those functions have been consistent since 1981. The Mid-bulkhead appears to have been subjected to the overwash of sand and sediment from Hurricane Wilma, though it maintained its shape and form. The outline of the Mid-bulkhead appears to be more well-defined after the initial post-Wilma repairs. In any event, the configuration and size of the Mid-bulkhead is substantially the same as it had been since 1981. At some point, the interior section of the Mid- bulkhead was topped with soil that is inconsistent with that naturally occurring in the area. That fill was confined, and brought the Mid-bulkhead to a more even grade with the rock outline, but could have had no measurable effect on the shoreline and water resources of Grassy Key in the vicinity of the properties owned by Applicants and Petitioners. The preponderance of the competent, substantial evidence demonstrates that the effect of the Mid-bulkhead is minimal and insignificant. Channel In 1961, the Department of the Army authorized dredging of a navigation channel at the Property. The approved channel was to be 700 feet long, 30 feet wide, and to a depth of five feet below mean low water. The Florida Trustees of the Internal Improvement Fund issued a letter of no objection. By 1964, the Channel that is the subject of this proceeding had been dredged, though not to the 700-foot length approved. Rather, the Channel was dredged to a length of approximately 290 feet. Much, if not all of the dredge spoil was sidecast, creating a rock structure alongside the Channel. Measurements taken during the course of this proceeding demonstrate that the initial dredging resulted in near vertical side slopes, which shows that the bailing of the bedrock was accomplished to the limits. The width of the Channel is from 28 feet to 32 feet wide, which is within an acceptable tolerance of the 30-foot approved width. In 1976, the then-owner of the Property sought a permit from the DEP’s predecessor, the Department of Environmental Regulation, to maintenance dredge the Channel to a dimension of 290 feet long and 30 feet wide, to a depth of minus 8-feet mean high water, and to construct a new rock jetty to extend 230 feet waterward from the existing terminus of the NE Jetty. Given the mean tide range of 1.7 feet at the Property, the depth of the proposed dredging would have been minus 6.3 feet mean low water, or 1.3 feet deeper than originally approved. The permit drawings depict the existing NE Jetty, the Channel boundary, the outline of the Mid-bulkhead, and the sidecast rock structure alongside the southern side of the Channel. The permit was denied. In 1977, the owner of the property reapplied for a permit to maintenance dredge the Channel to a dimension of 290 feet long and 30 feet wide, and to a depth of minus 4.0 feet below mean low water nearshore to minus 6 feet below mean low water at the waterward end. The proposal to construct an extension of the NE Jetty was deleted. The permit was issued, and a severance fee for the dredged material was paid based on a projected 700 cubic yards of material removed. The permit drawings and photographs depict the existing NE Jetty, the nearshore Channel boundary, and the general outline of the Mid- bulkhead. By 1981, aerial photographs demonstrate that the maintenance dredging of the Channel was complete, the NE Jetty was in place and functioning to protect the shoreline as evidenced by the accretional fillet, and the Mid-bulkhead had assumed its approximate current shape and configuration. Although the Channel has varied in depth over the years since the maintenance dredging and Hurricane Wilma, the greater weight of the evidence, including photographic evidence, indicates that the Channel was well-defined and remained navigable during that period. The Channel is an open-water exposed channel. Water in the Channel mixes due to direct tidal flow and the sheet flow of water due to shear wind stress. As water passes over the Channel, it sets up gyre, which is a mixing process. The open- water exposed Channel is subject to a high degree of mixing, even on normal waveless conditions, because of the wind transport of water and the tidal transport of water. The Channel is not a semi-enclosed basin. A semi- enclosed basin does not receive the direct forcing functions that an open-water channel receives. A semi-enclosed basin has no direct connection to open waters, but is connected to open waters by a narrower opening. Although a semi-enclosed basin exchanges water via every tidal cycle, the flushing process is one of slow mixing, in which a little bit of water is added to and withdrawn from the larger basin through the narrow opening during each tidal cycle. In such a case, a flushing analysis may be necessary to determine how much time and how many tidal cycles it may take to effect a complete exchange of the water in the semi-enclosed basin, and thus, for example, to dilute a pollutant to an acceptable level. A flushing analysis is not needed in this case because the Channel is an open-water, openly-exposed location subject to a high degree of mixing under normal day-to-day tidal processes. There is no greater basin connected by a restricting connection as with a semi-enclosed basin. Rather, the Channel has direct exposure to the tides, along with wind shear stress moving the water. The evidence in this case is substantial and persuasive, because the Channel is highly exposed to the open water and the tides, and a well-mixed and well-flushed aquatic system, that a flushing analysis is neither required nor necessary. Dock The dock made its first obvious appearance in 1981. It appears in a consistent shape and appearance through 2011. Aerial photographs taken in 2012, after the maintenance dredging of the Channel was conducted, show the dock had been removed. At the time of the hearing, the Applicants had installed new pilings and vent boards for the replacement dock, but the decking had not been installed. Work to complete the replacement of the dock was halted due to the pendency of the litigation challenging the structures. The proposed dock is less than 500 square feet. It is proposed for non-commercial, recreational activities. It is the sole dock proposed on the Property. The proposed dock will not impede the flow of water or create a navigational hazard. Boat Ramp Since the issuance of the 2008 approval, the boat ramp site was graded and stabilized in limerock material. The concrete ramp was not completed due to the pendency of the litigation challenging the structures. However, Applicants propose to pave the ramp with concrete. Based on Mr. Clark’s observations during his site visits, the boat ramp is landward of the mean high waterline depicted on the survey. The preponderance of the evidence demonstrates that the proposed boat ramp will provide access to the Channel, which provides a minimum navigational access of two feet below mean low water to the ramp. Applicants have agreed to install depth indicators at the ramp to identify the controlling depths of the navigational access. The work on the ramp involves no seagrass beds or coral communities. The ramp as proposed will require no more than 100 cubic yards of dredging. The total width of the ramp is to be 20 feet and the ramp surface will be no wider than 12 feet. Beach Area The area between the SW Jetty and the Mid-bulkhead is an accreted beach-type area that has been confined and protected by the Mid-bulkhead and the SW Jetty. The shoreline landward of the mean high water line, from the dry beach and to the upland, is somewhat steeper than adjacent unprotected shorelines, which is indicative of the grooming of the upper beach sediment and the stability of the shoreline between the Mid-bulkhead and the SW Jetty. As a result of the Hurricane Wilma storm surge, a substantial amount of sediment was swept across the Property and into the Atlantic waters. The beach area was inundated with sand and sediment from the overwash, which appears to have moved the shoreline well waterward of its previous position. Along the northern side of the SW Jetty, a substantial channelized gully was created. The configuration of the shoreline post-Wilma suggests that efforts were made by the then-owner of the Property to fill in the gully on the northern side of the SW Jetty, and to groom and restore the shoreline by redistributing sand and sediment on the Property. It is typical, and allowable under DEP emergency final orders, for affected property owners to redistribute overwashed deposits and place them back within the beach system. In that regard, the DEP encourages the redistribution of clean beach sand back onto the beach. The then-owners of the Property were not alone in taking steps to address the effects of Hurricane Wilma on their adjacent shorelines. The photographic evidence demonstrates that Petitioners engaged in similar restorative activities, which included bringing in material purchased from a contractor to fill in a gully created on their property by the overwash. Observation of representative soil samples from the beach area demonstrate that the soils are consistent with those in the upper beach areas found throughout the area. The only areas of inconsistent soils were found in the interior of the rock structure of the Mid-bulkhead, which contained a four to six-inch layer of soil with a different consistency and darker brown color, and small area of similar soil directly adjacent thereto and well above the mean high water line. The greater weight of the competent, substantial, and credible evidence demonstrates that there was no substantial amount of “fill” from off-site placed on or adjacent to the beach area. Rather, the nature, appearance, and composition of the soils suggests that the temporary increase in the size of the beach area after Hurricane Wilma was the result of grooming and redistribution of sand and sediment pushed onto the Property and into the nearshore waters by the Hurricane Wilma storm surge. In the years since Hurricane Wilma, the influence of normal tidal and weather-driven events has returned the beach area between the mid-bulkhead and the SW jetty to roughly the configuration that existed prior to the passage of Wilma, though it remains somewhat waterward of its pre-Wilma location.
Recommendation Based on the foregoing Findings of Fact and Conclusions of Law set forth herein it is RECOMMENDED that the Department of Environmental Protection enter a final order approving the February 20, 2013, proposed Permit, as conditioned by Applicants’ December 12, 2013, Proposed Changes to the Pending Agency Action. DONE AND ENTERED this 25th day of July, 2014, in Tallahassee, Leon County, Florida. S E. GARY EARLY Administrative Law Judge Division of Administrative Hearings The DeSoto Building 1230 Apalachee Parkway Tallahassee, Florida 32399-3060 (850) 488-9675 Fax Filing (850) 921-6847 www.doah.state.fl.us Filed with the Clerk of the Division of Administrative Hearings this 25th day of July, 2014.
The Issue The issue is whether Respondent, Daniel A. Reynolds, should take corrective action and pay investigative costs for allegedly controlling, eradicating, removing, or otherwise altering aquatic vegetation on eighty-seven feet of shoreline adjacent to his property on Lake June-in-Winter (Lake June) in Highlands County, Florida, without an aquatic plant management permit.
Findings Of Fact Based upon all of the evidence, the following findings of fact are determined: Respondent is the riparian owner of the property located at 260 Lake June Road, Lake Placid, Highlands County (County), Florida. He has owned the property since 2001 and resides there with his wife and two young children. The parcel is identified as Parcel ID Number C-25-36-29-A00-0171-0000. The southern boundary of his property, which extends around eighty-seven feet, abuts Lake June. Respondent has constructed a partially covered dock extending into the waters of Lake June, on which jet skis, a canoe, and other recreational equipment are stored. The Department is the administrative agency charged with protecting the State's water resources and administering and enforcing the provisions of Part I, Chapter 369, Florida Statutes, and the rules promulgated under Title 62 of the Florida Administrative Code. The parties have stipulated that Lake June is not wholly-owned by one person; that it was not artificially created to be used exclusively for agricultural purposes; that it is not an electrical power plant cooling pond, reservoir, or canal; and that it has a surface area greater than ten acres. As such, the parties agree that Lake June constitutes "waters" or "waters of the state" within the meaning of Florida Administrative Code Rule 62C-20.0015(23), and is not exempt from the Department's aquatic plant management permitting program under Florida Administrative Code Rule 62C-20.0035. Unless expressly exempted, a riparian owner who wishes to control, eradicate, remove, or otherwise alter any aquatic plants in waters of the state must obtain an aquatic plant management permit from the Department. See § 369.20(7), Fla. Stat.; Fla. Admin. Code R. 62C-20.002(1). An aquatic plant is defined as "any plant, including a floating plant, emersed, submersed, or ditchbank species, growing in, or closely associated with, an aquatic environment, and includes any part or seed of such plant." See Fla. Admin. Code R. 62C-20.0015(1). These plants are found not only in the water, but also along the shoreline when the water recedes below the high water mark. They provide important habitat for fish, insects, birds, frogs, and other animals. Torpedo Grass and Maidencane are two common species of aquatic plants or weeds. Applications for a permit are filed with one of the Department's regional offices. After a site inspection is made, a permit is issued as a matter of right without charge or the need for a hearing, and it is effective for a period of three years. A Department witness indicated that there are approximately 1,300 active permits at the present time, including an undisclosed number of permits for property owners on Lake June.3 It is undisputed that Respondent has never obtained a permit. A statutory exemption provides that "a riparian owner may physically or mechanically remove herbaceous aquatic plants . . . within an area delimited by up to 50 percent of the property owner's frontage or 50 feet, whichever is less, and by a sufficient length waterward from, and perpendicular to, the riparian owner's shoreline to create a corridor to allow access for a boat or swimmer to reach open water." § 369.20(8), Fla. Stat. The exemption was established so that riparian owners could create a vegetation-free access corridor to the waterbody adjacent to their upland property. The statute makes clear that "physical or mechanical removal does not include the use of any chemicals . . . ." Id. If chemicals are used, the exemption does not apply. Under the foregoing exemption, Respondent could remove up to 43.5 feet of aquatic vegetation in front of his property on Lake June, or one-half of his eighty-seven foot shoreline. By way of background, since purchasing his property in 2001, Respondent has had a long and acrimonious relationship with his two next door neighbors, Mr. Slevins (to the west) and Mr. Krips (to the east).4 Neither neighbor uses Lake June for recreational purposes. After purchasing the property, Respondent says that Mr. Slevin began to verbally harass and threaten his family, particularly his wife. When Respondent observed the two neighbors repeatedly trespassing on his property, including the placing of an irrigation system and a garden over the boundary lines, Respondent built a fence around his lot, which engendered a circuit court action by the neighbors over the correct boundary line of the adjoining properties. Respondent says the action was resolved in his favor. According to Respondent, Mr. Slevins and Mr. Krips have filed "probably 100 to 200 different complaints on everything from barking dogs, to weeding the yard to calling DEP." Respondent also indicated that Mr. Slevins is a personal friend of the Highlands County Lakes Manager, Mr. Ford. As his title implies, Mr. Ford has the responsibility of inspecting the lakes in the County. If he believes that aquatic vegetation has been unlawfully removed or altered, he notifies the Department's South Central Field Office (Field Office) in Bartow since the County has no enforcement authority. Mr. Reynolds says that a personal and social relationship exists between Mr. Slevins and Mr. Ford, and through that relationship, Mr. Slevins encouraged Mr. Ford to file at least two complaints with the Field Office alleging that Respondent removed aquatic vegetation in Lake June without a permit. In 2002, the Department received a complaint about "aquatic plant management activity" on Respondent's property. There is no indication in the record of who filed the complaint, although Respondent suspects it was generated by Mr. Slevins. In any event, after an inspection of the property was made by the then Regional Biologist, and improper removal of vegetation noted, Respondent was sent a "standard warning letter" that asked him "to let it regrow" naturally. According to the Department's Chief of the Bureau of Invasive Plant Management, Mr. William Caton, Respondent "did not" follow this advice. In 2004, another complaint was filed, this time by the Highlands County Lakes Manager. After an inspection was made, another letter was sent to Respondent asking him to "let it regrow," to implement a revegetation plan, and to contact the Department's Regional Biologist. After receiving the letter, Respondent's wife telephoned Mr. Caton, whose office is in Tallahassee, and advised him that the complaint was the result of "a neighbor feud." Among other things, Mr. Caton advised her that the Department would not "get in the middle" of a neighbor squabble. At hearing, he disputed Mrs. Reynolds' claim that he told her to disregard the warning letter. He added that Respondent did not "follow through with" the corrective actions. As a result of another complaint being filed by the Highlands County Lakes Manager in 2006, a field inspection was conducted on July 12, 2006, by a Department Regional Biologist, Erica C. Van Horn. When she arrived, she noticed that the property was fenced and locked with a "Beware of Dog" sign. Ms. Van Horn then went to the home of Mr. Slevins, who lives next door, and was granted permission to access his property to get to the shoreline. The first thing Ms. Van Horn noticed was that the "lake abutting 260 Lake June Road was completely devoid of vegetation." She further noted that "on either side of that property [there was] lush green Torpedo Grass." Ms. Van Horn found it "very unusual" for the vegetation to stop right at the riparian line. Although she observed that there was "a small percentage of Maidencane" on the site, approximately ninety to ninety-five percent of the frontage "was free of aquatic vegetation." Finally, she noted that the dead Torpedo Grass on the east and west sides of the property was in an "[arc] shape pattern," which is very typical when someone uses a herbicide sprayer. During the course of her inspection, Ms. Van Horn took four photographs to memorialize her observations. The pictures were taken from the east and west sides of Respondent's property while standing on the Slevins and Krips' properties and have been received in evidence as Department's Exhibits 1-4. They reflect a sandy white beach with virtually no vegetation on Respondent's shoreline or in the lake, brown or dead vegetation around the property lines on each side, and thick green vegetation beginning on both the Slevins and Krips' properties. The dead grass to the east had been chopped into small pieces. During her inspection, Ms. Van Horn did not take any samples or perform field testing to determine if herbicides had been actually used since such testing is not a part of the Department's inspection protocol. This is because herbicides have a "very short half life," and they would have broken down by the time the vegetation turns brown leaving no trace of the chemicals in the water. Ms. Van Horn left her business card at the gate when she departed and assumed that Respondent would contact her. On a later undisclosed date, Respondent telephoned Ms. Van Horn, who advised him that he was out of compliance with regulations and explained a number of ways in which he could "come into compliance with these rules," such as revegetation. She says he was not interested. After her inspection was completed, Ms. Van Horn filed a report and sent the photographs to Mr. Caton for his review. Mr. Caton has twenty-seven years of experience in this area and has reviewed thousands of sites during his tenure with the Department. Based on the coloration of the vegetation right next to the green healthy vegetation on the adjoining properties, Mr. Caton concluded that the vegetation on Respondent's property had "classic herbicide impact symptoms." He further concluded that the vegetation had been chemically sprayed up to the boundary lines on each side of Respondent's property before it was cut with a device such as a weedeater. Based on the history of the property involving two earlier complaints, Respondent's failure to take corrective action, and the results of the most recent inspection, Mr. Caton recommended that an enforcement action be initiated. On August 11, 2006, Ms. Van Horn sent Respondent a letter advising him that a violation of Department rules may have occurred based upon the findings of her inspection. The letter described the unlawful activities as being "removal of aquatic vegetation from the span of the total adjacent shore line and significant over spray on to aquatic vegetation of neighboring properties on either side of [his] property." Respondent was advised to contact Ms. Van Horn "to discuss this matter." On May 15, 2007, the Department filed its Notice alleging that Respondent had "chemically controlled" the aquatic vegetation on eighty-seven feet of his shoreline in violation of Section 369.20(7), Florida Statutes, and Florida Administrative Code Rule 62C-20.002(1). The Notice sought the imposition of an administrative penalty in the amount of $3,000.00, recovery of reasonable investigative costs and expenses, and prescribed certain corrective action. On April 28, 2008, the Department filed an Amended Notice alleging that, rather than chemically removing the vegetation, Respondent had controlled, eradicated, removed, or otherwise altered the aquatic vegetation on his shoreline. The Amended Notice deleted the provision requesting the imposition of an administrative penalty, expressly sought the recovery of investigative costs and expenses of not less than $179.00, and modified the corrective action. After her initial inspection, Ms. Van Horn rode by the property in a Department boat on several occasions while conducting other inspections on Lake June and observed that the property "was still mostly devoid of vegetation." At the direction of a supervisor, on June 15, 2007, she returned to Respondent's property for the purpose of assessing whether any changes had occurred since her inspection eleven months earlier. This inspection was performed lakeside from a Department boat without actually going on the property, although she spoke with Respondent's wife who was standing on the dock. Ms. Van Horn observed that the area was still "devoid of vegetation but there was some Torpedo Grass growing back on the [eastern] side." She estimated that "much more" than fifty percent of the shoreline was free of vegetation. Photographs depicting the area on that date have been received in evidence as Department's Exhibits 5-7. Both Respondent and his wife have denied that they use any chemicals on their property, especially since their children regularly swim in the lake in front of their home. Respondent attributes the loss of vegetation mainly to constant use of the back yard, dock area, and shoreline for water-related activities, such as swimming, using jet skis, fishing, and launching and paddling a canoe. In addition, the Reynolds frequently host parties for their children and their friends, who are constantly tramping down the vegetation on the shoreline and in the water. He further pointed out that beginning with the house just beyond Mr. Krip's home, the next five houses have "no vegetation" because there are some areas on the lake that "naturally do not have any vegetation across them." Finally, he noted that Lake Juno suffered the impacts of three hurricanes in 2004, which caused a devastating effect on its vegetation. Respondent presented the testimony of Brian Proctor, a former Department aquatic preserve manager, who now performs environmental restoration as a consultant. Mr. Proctor visited the site in June 2007 and observed "full and thick" Torpedo Grass "growing in the east and west of the property lines." Based on that inspection, Mr. Proctor said he was "comfortable stating that at the time [he] did the site visit in June of '07 there was nothing that appeared to be chemical treatment on Mr. Reynold's property." He agreed, however, that the "shoreline vegetation was poor," and he acknowledged that it was unusual that Lake Juno was lush with aquatic vegetation in front of the neighboring properties to the east and west but stopped at Respondent's riparian lines. When shown the June 2006 photographs taken by Ms. Van Horn, he acknowledged that it "appeared" the property had been chemically treated. He was able to make this determination even though a soil test had not been performed. Photographs introduced into evidence as Respondent's Exhibits 1-4 reflect that on June 27, 2007, there was thick green vegetation on both sides of his property, although one photograph (Respondent's Exhibit 1) shows only limited vegetation along the shoreline and in the lake in the middle part of the property. The photographs are corroborated by a DVD recorded by Respondent on the day that Ms. Van Horn returned for a follow-up inspection. While these photographs and DVD may impact the amount of corrective action now required to restore the property to its original state, they do not contradict the findings made by Ms. Van Horn during her inspection on July 12, 2006. Finally, photographs taken in 2003 to depict what appears to be chemical spraying of vegetation and the construction of a bulkhead without a permit by Mr. Slevins have no probative value in proving or disproving the allegations at issue here. The greater weight of evidence supports a finding that it is very unlikely that heavy usage of the shoreline and adjacent waters in the lake by Respondent's family and their guests alone would cause ninety-five percent of the shoreline and lake waters to be devoid of vegetation when the inspection was made in July 2006. Assuming arguendo that this is true, Respondent was still required to get a permit since the amount of vegetation altered or removed through these activities exceeded more than fifty percent of the vegetation on the shoreline. More than likely, the vegetation was removed by a combination of factors, including recreational usage, mechanical or physical means, and the application of chemical herbicides on each riparian boundary line, as alleged in the Amended Notice. The fact that the Department did not perform any testing of the water or soil for chemicals does not invalidate its findings. Finally, the acrimonious relationship that exists between Respondent and his neighbors has no bearing on the legitimacy of the charges. Therefore, the allegations in the Amended Notice have been sustained. The parties have stipulated that if the charges are sustained, Respondent is entitled to recover reasonable costs and expenses associated with this investigation in the amount of $179.00. As corrective action, the Amended Notice requires that Respondent obtain a permit to remove Torpedo Grass from his property and to replant "126 well-rooted, nursery grown Pontederia cordata ("pickerelweed") at the locations depicted on the map" attached to the Amended Notice. Because the evidence suggests that some of the area in which vegetation was removed in 2006 had regrown by July 2007, the proposed corrective action may be subject to modification, depending on the current state of the property.
The Issue The issue is whether to approve Steven A. Walker's application for a coastal construction control line (CCCL) permit authorizing him to conduct certain construction activities at 100 Park Avenue, Anna Maria, Florida.
Findings Of Fact Based upon all of the evidence, the following findings of fact are determined: History of the Proceeding Since 2005, Petitioner has owned property at 104 Park Avenue, Anna Maria, Sarasota County, Florida. The parcel fronts on the Gulf of Mexico and is adjacent to property owned by the Stephen A. Walker Land Trust (Land Trust) located at 100 Park Avenue. The Trustee of the Land Trust is Stephen A. Walker, who is the applicant in this proceeding. On March 5, 2009, Mr. Walker filed an application with the Department for a permit authorizing the construction of "a new single family residence with a pool, driveway and multiple structures" seaward of the CCCL on his parcel. See Joint Exhibit 11. The application was accompanied by a letter from the City Planner, B. Alan Garrett, indicating that the proposed activity "does not contravene the City of Anna Maria local setback and pervious coverage requirements of the zoning code provisions." See Joint Exhibit 3. On June 26, 2009, the Department, through its Bureau of Beaches and Coastal Systems, issued a Final Order granting the application subject to certain general and special conditions. See Joint Exhibit 47. A Notice to Proceed with the construction was issued the same date. See Joint Exhibit 46. Separate written notice of the Department's proposed action was also served on both Petitioner and his attorney. See Joint Exhibits 49 and 50. On July 22, 2009, Petitioner filed his Petition with the Department contesting the proposed agency action. See Joint Exhibit 51. As grounds, Petitioner contended generally that the environmental permitting requirements under Florida Administrative Code Rule 62B-33.0052 had not been met, and that the proposed activity violated both the City's Plan and the zoning code. Id. Evidence regarding the latter allegations was later excluded as being irrelevant. See Order dated March 12, 2010. At hearing, counsel for Petitioner represented that he was no longer alleging that the application did not qualify for a permit under the environmental permitting requirements of the rule. However, he continued to assert that the proposed construction will violate the City's Plan and zoning code. A suit in circuit court has been filed seeking an adjudication of those claims and apparently is still pending. See Friday v. City of Anna Maria, Case No. 2010-CA2369 (12th Cir., Manatee Cty Fla.). Permitting Criteria The general permitting requirements for issuance of a CCCL permit are found in Rule 62B-33.005. There is no dispute that these criteria have been satisfied. Rule 62B-33.008 contains the permit application requirements and procedures. Paragraph (3)(d) of the rule provides that an application for a CCCL permit shall contain the following information: Written evidence, provided by the local governmental entity having jurisdiction over the activity, that the proposed activity, as submitted to the Bureau, does not contravene local setback requirements or zoning codes. Joint Exhibit 3 is a letter dated February 2009 authored by B. Alan Garrett, City Planner, who states that he had reviewed the application and plans filed with him on February 2, 2009, and that the proposed construction "does not contravene the City of Anna Maria local setback and pervious coverage requirements of the zoning code provisions." This letter satisfies the requirement of the rule.
Recommendation Based on the foregoing Findings of Fact and Conclusions of Law, it is RECOMMENDED that the Department of Environmental Protection enter a final order granting the application of Stephen A. Walker, Trustee, for a coastal construction control line permit authorizing certain activities seaward of the CCCL at his property in Anna Maria, Florida. DONE AND ENTERED this 24th day of May, 2010, in Tallahassee, Leon County, Florida. S D. R. ALEXANDER Administrative Law Judge Division of Administrative Hearings The DeSoto Building 1230 Apalachee Parkway Tallahassee, Florida 32399-3060 (850) 488-9675 Fax Filing (850) 921-6847 www.doah.state.fl.us Filed with the Clerk of the Division of Administrative Hearings this 24th day of May, 2010.
The Issue The issues in these cases are whether the Respondent, Roy Palmer, is entitled to a Noticed General Environmental Resource Permit, under Florida Administrative Code Chapter 62-341, and a Consent of Use under Florida Administrative Code Chapter 18-21.
Findings Of Fact Procedural History On or about February 13, 1995, the Respondent, Roy Palmer (Palmer), applied for a wetland resource permit to construct a 395-foot boat dock for use at his single-family residence at property he owned on Sarasota Bay, an Outstanding Florida Water. As proposed, this dock was to originate from the northern part of Palmer's property and have a terminal platform with two boat moorings and two boat lifts. On September 1, 1995, the Department of Environmental Protection (the Department or DEP) gave notice of intent to issue a permit for a shorter (370-foot) dock originating from the southern part of the Palmer property. The Petitioners filed a petition for administrative hearing challenging the intended action. DEP referred the petition to the Division of Administrative Hearings (DOAH), where it was assigned DOAH Case No. 95-5311. On or about December 11, 1995, Palmer applied for a noticed general environmental resource permit (ERP) permit for his dock under new DEP rules went into effect on October 3, 1995. This proposal was for the 370-foot dock originating from the southern part of the Palmer property. On or about January 10, 1996, DEP acknowledged receipt of the noticed general ERP (No. 582819483) and informed Palmer that it appeared to meet the requirements of the new rule. DEP also gave notice of intent to grant Palmer's application for consent of use of sovereign submerged lands necessary to construct the dock. (The record is not clear when the application for consent of use was filed.) The Petitioners filed a petition for administrative hearing challenging agency action regarding both the noticed general ERP and the consent of use. DEP also referred this petition to DOAH, where it was assigned DOAH Case No. 96-0736. Palmer withdrew the original permit application and moved to dismiss DOAH Case No. 95-5311. In July, 1996, Palmer applied for a noticed general ERP to build a still shorter (232-foot) dock originating from the southern part of the Palmer property (Permit No. 292583). Apparently, no notice of the application was published or required to be published. It is not clear whether the Petitioners "filed a written request for notification of any pending applications affecting the particular area in which the proposed activity is to occur." Palmer's second noticed general ERP (No. 292583) was amended on or about August 19, 1996, to eliminate one boat mooring and one boat lift. DEP took no action on Palmer's second application for a noticed general ERP No. 292583. On September 23, 1996, Palmer filed a Motion to Dismiss the Petition for Administrative Proceeding in DOAH Case No. 96-0736 because he had withdrawn the previous application for a noticed general ERP for a 370-foot dock (No. 582819483) and was proceeding only on the second noticed general ERP (No. 292583) for the 232foot dock. Palmer's intent was to dismiss only the portion of his prior application regarding the noticed general permit, but not the consent of use. On October 28, 1996, the Petitioners filed a petition for administrative hearing challenging noticed general ERP No. 292583 for the 232-foot dock. This petition alleged that the Petitioners filed a written objection to noticed general ERP No. on September 16, 1996, which requested a written response, and that no response of any kind was received until the Petitioners inquired and were told that DEP did not intend to respond to either the noticed general ERP (No. 292583) or the Petitioners' objection. Proposed Dock at Issue The proposal at issue is for a 227-foot access pier and 20 foot by 5 foot terminal platform with only one boat mooring and one boat lift. The length, location, and design of Palmer's proposed dock was changed in an attempt to satisfy the Department of Environmental Protection (DEP or the Department) and Palmer's neighbors. Palmer's task in this regard was difficult in part because a longer dock with a terminus in deeper water could have less impact on seagrasses (the major environmental concern) but would have a greater impact on the neighbors' views of Sarasota Bay (the major infringement of riparian rights concern.) In the final version, Palmer tried to balance these conflicting concerns. As proposed, neither the terminal platform, boat lift, nor mooring location occurs over submerged grassbeds, coral communities or wetlands. Starting at the mean high water line, the first 75 feet of the access pier for the proposed dock will traverse essentially no sea grasses. In the next 75 feet to 150 feet of the access pier, there will be approximately 80% vegetative cover consisting primarily of the seagrass halodule wrightii. Between 150 feet and 200 feet, there will be approximately 20% vegetative cover consisting of the seagrasses halodule wrightii and thalassia testudinum. Between 200 feet and 232 feet, seagrasses consisted primarily of thalassia testudinum, except that the terminal platform is located in an area of essentially bare sand. Starting at 80 feet from the mean high water line, the access pier for the proposed dock will ramp up to 5 feet above mean high water for the next 20 linear feet and continue at that elevation for the next 112 feet to reduce shading of the seagrasses. Then it will descend stairs for the next 5 linear feet, until it is 3.5 feet above mean high water, and will continue at that elevation for 10 more feet to where it joins the 20 foot by 5 foot terminal platform. In this way, wherever it traverses seagrasses, the access walkway portion of the pier will be elevated 5 feet above mean high water. The access walkway will be only 4 feet wide and will have half-inch wide gaps between its deck boards to allow sunlight through and further reduce shading of the seagrasses. The access walkway also will have handrails that are maintained in such a manner as to prevent use of the access walkways for boat mooring or access. As proposed, the terminal platform and boat lift occurs in a location with minimum depth of 2.2 feet below the mean low water level. There is some water 1.7 feet deep in the vicinity of the terminal platform, but the structure can be used without traversing the shallow water. The structure is designed so that boat mooring and navigational access will be in water at least 2 feet deep. Including access pier and terminal platform, the total area of Palmer's proposed dock over sovereign, submerged land would be 1,008 square feet. There will be no wet bars or living quarters over wetlands or surface waters or on the pier, and there will be no structures enclosed by walls or doors. There will be no fish cleaning facilities, boat repair facilities or equipment, or fueling facilities on the proposed dock. No overboard discharges of trash, human, or animal waste, or fuel will occur from the dock. The only dredging or filling associated with construction of Palmer's proposed dock will be the minimum dredge and fill required for installation of the actual pilings for the pier, terminal platform, and boat lift. Altogether, less than 30 square feet of bay bottom will be disturbed during construction and displaced to accommodate the pilings. Palmer's noticed general ERP is subject to the general conditions set out in Florida Administrative Code Rule 62- 341.427. Among those conditions is the requirement that Palmer implement best management practices for erosion, turbidity, and other pollution control to prevent violation of state water quality standards. The pilings will be jetted, not driven, into place to minimize disturbance of the bay bottom and temporary increases in turbidity. Turbidity barriers will be installed and maintained in a functional condition at each piling until construction is completed and soils are stabilized and vegetation has been established. Used properly, turbidity barriers have proved effective in containing temporary turbidity from dock construction. Based on the expert testimony, it is found that the construction of Palmer's proposed dock will not significantly impact seagrasses. The Petitioners presented expert testimony on seagrasses, but their expert testified only generally based on studies showing that shading negatively impacts seagrasses. He had no prior knowledge of the Palmer dock design, seagrass coverage, or the depth of the water. When apprised of some information concerning Palmer's proposed dock, he admitted that the studies involved far more severe shading conditions than would be caused by the proposed dock. He could not testify that the Palmer dock design would harm seagrasses, with the exception of those actually removed by the installation of the pilings. Accidental boat propeller dredging in using a dock can be a secondary impact on seagrasses from dock construction. But while a dock could perhaps attract a few boats, the dock's presence also might cause boaters to steer clear of the dock or reduce speed in the vicinity of the dock, which could result in a net reduction in the risk of damage to seagrasses from accidental prop dredging. Petitioners Dr. Franklin Pfeiffenberger, James Castoro, and Winifred Castoro jointly own a dock to the south of the Palmer property. This dock, which was built in the 1930's, projects 190 feet into Sarasota Bay and traverses seagrasses. Unlike the proposed Palmer dock, the Pfeiffenberger dock is not elevated, and it terminates in seagrasses. The seagrasses under the Pfeiffenberger dock are the same types as those located in the Palmer dock alignment--a combination of halodule wrightii and thalassia testudinum. The dock has been rebuilt a number of times over the years. Upon physical inspection, apparently healthy and growing seagrasses were found underneath the Pfeiffenberger dock. The proposed dock will not harm wildlife, including manatees (the only endangered species in the area, animal or plant). Manatees use Sarasota Bay in general, but the east side of the bay, where the Palmer property is located, is not a high use area. It is shallow and would not be considered "select" habitat for manatees. The proposed dock would not have any detrimental effect on manatee travel patterns; they could easily swim around the dock. Manatees eat seagrasses and other aquatic vegetation, but the proposed dock will not have significant adverse impact on those resources. Finally, while a dock could perhaps attract a few boats, the dock's presence also might cause boaters to steer clear of the dock or reduce speed in the vicinity of the dock, which could result in a net reduction in the risk of injury to manatees in the area from boat collisions and prop scarring. Except for temporary turbidity during construction, no other water quality parameters will be violated as a result of the construction of Palmer's proposed dock. Palmer's proposed dock and its use will not significantly impede navigability in Sarasota Bay. The bay is approximately 18,000 feet wide at that point, and it is approximately 4,800 feet from Palmer's property to the Intracoastal Waterway. Since the water is shallow near shore in the vicinity of the Palmer property, relatively few boats frequent the area. Those that do are generally smaller boats. These boats easily could navigate so as to avoid the dock; very small boats, such as canoes and kayaks, might even be able to carefully pass under the elevated portion of the dock. Palmer's proposed dock also would not be a serious impediment to other recreational uses of Sarasota Bay in the area. The water is too shallow for swimming. Fishing could improve because the dock could attract baitfish. People could continue to wade-fish by walking around or even under the proposed dock. Palmer's proposed dock is aesthetically consistent with the area in which it is located. All the Petitioners have some sort of man-made structure projecting out into Sarasota Bay from their property. As already mentioned, Dr. Pfeiffenberger and the Castoros have a 190-foot dock projecting straight out into Sarasota Bay. Within the past five years, Dr. Pfeiffenberger has installed a bench to sit on at the end of the dock. To the north of the Palmer property, property owned by Mr. and Mrs. Cabaniss has a yacht basin formed by a sea wall that projects roughly perpendicular to the shoreline out into the bay. Immediately north of the Cabaniss property, there is a boat house on the Goldman property where it abuts the yacht basin. The Goldmans' boat house is approximately 20 feet in length and 10 feet in height from ground level. Immediately south of the Palmer property, Ms. Stenhouse has a small dock (which appears to be located over seagrasses.) As a result, the viewsheds of Palmer and the Petitioners already contain many docks and man- made structures. In addition, the Ringling Causeway and bridge can be seen from all of these properties. Palmer's proposed dock will appear in some views from the Petitioners' properties. Generally, the closer the neighbor, the more will be seen of Palmer's proposed dock. Some of the Petitioners will only be able to see the proposed dock if they go out to the westerly edge of their properties on the bay. While the proposed dock will appear in and alter these views, it will not eliminate any Petitioner's view of Sarasota Bay. Even the closest neighbors will have some unobstructed views around the proposed dock. It also will be possible to see over and under the proposed dock, similar to the way in which many of the Petitioners now enjoy their views. There are tall pine and palm trees on the Cabaniss property between their house and their view of the bay. Most of the other properties in the vicinity appear to have similar viewsheds. Ms. Stenhouse has a large stand of mangroves of the western edge of her property; they cover approximately 60 percent of the panorama from her house, but they are trimmed up so she can see through them. While some people would prefer not to have the Palmer dock there, other people might view the availability of single- family residential docks to be an asset to the properties in the neighborhood. Based on expert testimony, it cannot be found that property values in the area would go down as a result of Palmer's proposed dock. Palmer's proposed dock does little if anything to further the idealistic goals and objectives of the City of Sarasota Comprehensive Plan and the Sarasota Bay Management Plan to restore and expand seagrasses in Sarasota Bay in that the proposed dock will eliminate some seagrasses. However, only approximately 30 square feet of seagrasses will be lost. Otherwise, the proposed dock is consistent with other goals and objectives of the City of Sarasota Comprehensive Plan and the Sarasota Bay Management Plan in that the dock has been aligned and planned so as to minimize impacts on seagrasses while balancing the neighbors' desire to minimize the impact on their views of Sarasota Bay. Palmer's Riparian Rights Palmer and his wife received a Warranty Deed, dated August 27, 1993, from James Kirk, II, individually and as personal representative of the Estate of Marie Ferguson. The deed describes Lots 27 and 28 of the Indian Beach subdivision in Sarasota, Florida, with a western boundary "along the shores of Sarasota Bay." Palmer attached this deed to his applications. Since at least November 1992, the mean high water line of Sarasota Bay has been west of a seawall on the Palmer property. The evidence was clear that the seawall has been there since at least 1944 and that Palmer has not filled the area to the west of the seawall or built any structure that influences its existence. The evidence was not clear as to the creation and history of upland to the west of the seawall. From aerial photographs, it appears that at least some upland has existed to the west of the seawall at least from time to time for at least the last 30 years. For reasons no witness could explain, the Palmers also received a Warranty Deed from Kirk, dated September 3, 1993, purporting to convey title only up to the seawall on the Palmer property. Likewise for reasons no witness could explain, a land surveyor named Lawrence R. Weber prepared a boundary survey based on the description in the September 3, 1993, Warranty Deed. Also for reasons no witness could explain, the Palmers received a Quit Claim Deed from Kirk, dated October 20, 1993. This instrument quitclaimed to the Palmers "all of the Grantor's property to the mean high water line of Sarasota Bay, including riparian rights." Except for the mysterious September 3, 1993, Warranty Deed from Kirk, all deeds in the chain of title back to at least 1944 reflect an intention to convey riparian rights. A deed given by Helen and Frederick Delaute to Cecilia and Harold Wilkins, dated April 19, 1944, described the westerly boundary of the property as running northerly along the shores of Sarasota Bay and specifically referenced riparian rights. (This deed attached a survey showing the still-existing seawall.) The next deed in the chain of title was from the widowed Cecilia S. Wilkins to Edward and Laura Williams dated December 27, 1954. The metes and bounds description again referenced the westerly boundary as running along the shores of Sarasota Bay and specifically referenced foreshore accretions and riparian rights. The next deed in the chain of title was from Edward and Laura Williams to Aidan and Wilma E. Dewey dated June 30, 1958. This deed again defined the westerly boundaries of the property as the shores of Sarasota Bay and specifically referenced foreshore accretions and riparian rights. The next deed in the chain of title was from Aidan and Wilma Dewey to Edward and Marie Ferguson dated August 23, 1967. This deed again defined the westerly boundary of the property as the shores of Sarasota Bay and specifically referenced foreshore accretions and riparian rights.
Recommendation Based upon the foregoing Findings of Fact and Conclusions of Law, it is RECOMMENDED that the Department of Environmental Protection enter a final order issuing Noticed General Environmental Resource Permit (No. 292583) and Consent of Use (No. 582819483) to Roy Palmer. DONE AND ENTERED this 1st day of September, 1998, in Tallahassee, Leon County, Florida. J. LAWRENCE JOHNSTON Administrative Law Judge Division of Administrative Hearings The DeSoto Building 1230 Apalachee Parkway Tallahassee, Florida 32399-3060 (850) 488-9675 SUNCOM 278-9675 Fax Filing (850) 921-6847 Filed with the Clerk of the Division of Administrative Hearings this 1st day of September, 1998. COPIES FURNISHED: Richard Filson, Esquire Filson and Penge, P.A. 2727 South Tamiami Trail, Suite 2 Sarasota, Florida 34239 Thomas I. Mayton, Esquire T. Andrew Zodrow, Esquire Department of Environmental Protection 3900 Commonwealth Boulevard Mail Station 35 Tallahassee, Florida 32399-3000 David M. Levin, Esquire Icard, Merrill, Cullis, Timm, Furen & Ginsburg Post Office Box 4195 Sarasota, Florida 34237 Alexandra St. Paul, Esquire The Riverview Center 1111 3rd Avenue, West Suite 350 Bradenton, Florida 34205 Kathy Carter, Agency Clerk Department of Environmental Protection Office of General Counsel 3900 Commonwealth Boulevard Mail Station 35 Tallahassee, Florida 32399-3000 F. Perry Odom, General Counsel Department of Environmental Protection Office of General Counsel 3900 Commonwealth Boulevard Mail Station 35 Tallahassee, Florida 32399-3000
Findings Of Fact On or about July 9, 1987 an application for conditional use approval to allow off-premises sale of beer and wine (2APS) was filed on behalf of Petitioner for property located at 2030 Gulf to Bay Boulevard in Clearwater, Florida. The property is zoned general commercial (CG). A public hearing before the Planning and Zoning Board was held on August 4, 1987. At that hearing, the Petitioner's representative was not allowed to give rebuttal testimony, although the Board's by-laws do allow the applicant to rebut testimony in opposition to the application, and rebuttal is, in fact, usually allowed. The Petitioner's representative did not specifically request an opportunity to rebut the opponent's testimony, but assumed he would be given an opportunity to speak before the Board voted. The Planning and Zoning Board voted 3-2 to deny conditional use approval for this application. A timely appeal was taken by Petitioner on August 18, 1987. With this application, Petitioner seeks approval to sell beer and wine at a 7-11 convenience store. By subsequent application and approval of the Planning and Zoning Board on September 1, 1987 Petitioner has been granted a conditional use for 1APS, package sale of beer only. However, this 1APS application and approval is not at issue in this case. The parties stipulated that the property in question is within five hundred feet of a church and several residences.
Findings Of Fact Respondent, Woodland, is made up of property owners in Woodland Lakes subdivision, an area abutting on Woodland Bayou, situated off Pensacola Bay in Santa Rosa County, Florida. Petitioner, Margaret B. Miller, owns property directly across the channel which forms the entrance to Woodland Bayou and which is the proposed location for the bulkhead and riprap forming the subject matter of this dispute. Mrs. Miller and her late husband purchased their property, which is not located in Woodland Lakes subdivision, in 1957. Their lot is located on Pensacola Bay and at the time she and her husband purchased the property, they were looking for an area that had the special characteristics of this lot she now owns. It included big trees, a gentle slope to the Bay, and a view out over Pensacola Bay across a sandy peninsula which extended out into the bay a considerable distance and which they owned. At the time they made their purchase, Woodland Bayou opened into Pensacola Bay at the East End but the opening near Mrs. Miller's property was obstructed by a sandy beach. The extent of channel blocking and obstruction caused by this sandy beach was the subject of a lawsuit between the Millers, the Woodland Lake Property Owners Association, and the State of Florida 1n June, 1972. The substance of that suit was concerned with ownership of the land which extended out from the Miller property into Pensacola Bay over which certain of the parties desired to cut a channel from Woodland Bayou into Pensacola Bay. There was substantial conflict in the testimony at the time as to whether there was a natural channel existing across the Miller property prior to 1957-1958 or not, or, in the alternative, whether the Millers filled in an existing channel thereby blocking reasonable entrance to Woodland Bayou. The answer to that question is irrelevant to the issue in this hearing. However, a judgment of the Circuit Court entered on June 13, 1972, awarded to the Millers title to property which extended out across the currently existing channel dredged subsequent to that time by the Respondent, Woodland, to a point into Pensacola Bay. The decision of the court also awarded to the Trustees of the Internal Improvement Fund a section of property directly west of the northern tip of the Miller property consisting of a strip approximately 40 feet wide and a maximum of76 feet long lying approximately perpendicular to the currently-existing channel and through which it was envisioned the channel would be dredged from the entrance of Woodland Bayou out to Pensacola Bay. By so doing, the canal would have made a left turn coming out of the bayou into Pensacola Bay but the Miller's property, which was not then split by the canal, would be left intact. According to Mr. Hunsley, the dredging completed after the entry of the final judgment in the Quiet Title suit was not done consistent with the dictates of that judgment. Instead, the channel was cut straight out from the bayou across the Miller property, and so it remains to this day. He contends, however, that historically, the channel existed in this very spot and that the Millers as well as other property owners in the area at the time, closed the channel off by dredging and filling at their own expense some time in 1957 and 1958. Regardless of the history regarding the genesis of the channel, however, the fact remains that the channel now exists in a straight line from Woodland Bayou to Pensacola Bay across the Miller property and has so since 1972 when it was dredged subsequent to the lawsuit. The channel, being a tidal channel and subject to sand drift caused by wind and wave action, tends to become clogged with sand on a periodic basis. Because of the increased clogging currently experienced, sometime prior to September 9, 1983, the officers of Woodland circulated a petition to secure the permission of all the neighbors in the subdivision to construct a bulkhead on the Woodland side of the channel across from and up channel from the Miller property. This petition, which at the time did not include riprap, was approved by all property owners in the subdivision except for 2 and was then forwarded to the Gulf Breeze City Council to allow the Council to assess costs in the amount of approximately $600.00 per property owner against the property owners in the event DER approved the permit to construct the bulkhead. Mrs. Miller was not solicited to sign the Petition nor will she be assessed any of the costs of construction of the bulkhead if approved since she is not a property owner in the subdivision in question. The petition was circulated, according to Mr. Kettenring, who has lived in the area for several years, because of the increasing sedimentation. To his knowledge, the channel was last dredged in 1982 and 1983. Prior to that time, during the period 1979-1981, he recalls at least three fish kills in the bayou but none since the dredging was accomplished. The residents of Woodland and the surrounding owners are all on septic tanks. There is no city sewage service to this area and every year there is a change in the clarity of the water in Woodland Bayou in the summer. During warmer weather, as the temperature increases, the water becomes cloudy and full of algae. However, after dredging was accomplished and the channel was opened further both in width and in depth, the water quality improved considerably. Mr. Kettenring has seen patterns of sand drifting from the point into the channel. The area has changed considerably in that the point has scalloped out into the channel blocking it. As a result, the bayou, which is at the mainland source of the channel, is currently somewhat brackish. Access of boat owners to the bayou has become impaired. On September 9, 1983, the application submitted by Woodland was received by DER, and a determination was made that the proposed project lay in Class III waters of the State, the standards for which are outlined in Rule 17-3.121, Florida Administrative Code. Shortly thereafter on September 28, 1983, DER notified Woodland that the application was incomplete in that the application fee had not been submitted, aerial photographs of the area were required, and a consent for the use of State-owned land was necessary. In addition, it was determined that Woodland needed to provide detailed plans for compliance with State water quality standards as well as a hydrographic survey. All requirements were subsequently met except for the survey. The application originally called for an additional 300 foot bulkhead to the east of the area in question here and the hydrographic survey referred to that bulkhead. Subsequent to the filing of the application, however, that bulkhead portion of the project was deleted and when that was done, the need for the hydrographic survey was obviated. Since all other shortcomings in the application had been corrected, the project was then reviewed by Mr. Hambrick who recommended the installation of riprap in front of the remaining bulkhead and grass, and on December 20, 1984, DER published an intent to issue for the project. The project in question is a 150 feet long bulkhead fronted with 35 cubic yards of riprap at the toe. The bulkhead will be located at the entrance channel of Woodland bayou across from Petitioner's property. Mr. Hambrick, who initially reviewed the application for DER and who signed off on it in December, 1984, visited the site in question on at least 2 or 3 occasions in relation to the application and because Mrs. York, Miller's neighbor, also had an application for a bulkhead pending. He looked at the property and determined that the amended application did not call for riprap. However, because the new law requires riprap in front of seawalls, he recommended that the riprap be installed here where there is no grass. In other words, according to Mr. Hambrick, riprap will be placed flush against the bulkhead where no sea grasses exist but will curve out in front of the sea grasses where there is grass at the foot of the bulkhead which will proceed behind the grassed area. The purpose of using riprap is to dissipate wave energy. Riprap will diminish the effect of the wave and its adverse effect on Petitioner's property. Mr. Hambrick is of the opinion that installing the bulkhead and riprap would not cause or increase damage to Petitioner's property and based on the criteria he used in analyzing the project, he feels that it is in the public interest. The factors he used in his consideration of this project include: that an erosion problem exists in the area, that bulkheading and riprapping would reduce the need for dredging, that there is a history of fish kills in the area, that maintaining a channel would help flush out the bayou, and homeowners on the bayou would have access to Pensacola Bay and their interests constituted a part of the public interest. Since the revised application was completed in October, 1984, it therefore had to comply with the criteria outlined in the new water quality bill which are two-fold in general application. These are: that the project will have no adverse effects on water quality of Woodland Bayou but would likely improve it through the increased flushing of the bayou as a result of maintaininq the channel, and that a need for dredging would be reduced since the channel will not shoal in as much. According to Mr. Hambrick, at the present time there is a collapsing and sluffing off of soil along the channel, which has increased since his prior visit in November, 1984. In his analysis of the project, he considered the effects that the project would have on the public interest, water quality, wildlife and fish in the area, and the historical and archeological aspects of the area. In his opinion, riprap would provide a habitat for marine wildlife which is a plus factor and would help to maintain a shallow shore environment. It would help to maintain a stand of marsh grass that is presently in the area and which is being covered with sand coming from the eroding point. In his opinion, there would be no adverse effect on the archaeological aspects of the area nor is there any indication of any adverse effect on the public interest, including Mrs. Miller. He also considers there would be no adverse effect on marine productivity which, in his opinion, would very likely improve as a result of the project. In his opinion, overall the project will maintain and even enhance the public interest considerations in the area and there would be no damage to the marine bottom by the installation of the riprap. Since the bulkhead will be fronted by riprap, it is not considered a vertical seawall which would be prohibited by the statute as it is currently constituted. Mr. Hambrick is quite certain in his opinion that since Mrs. Miller's property is already bulkheaded and riprapped, there would be no further erosion of her property. Consequently, there would be no adverse ecological effect notwithstanding the fact that Mrs. Miller contends that keeping the channel open would be a continuing trespass to her property. She also contends that when she put in her bulkhead, now at water's edge, it was designed as a retaining wall and was located in sand some substantial distance from the water. When the channel was cut across her land, the beach from the channel to the "retaining wall" eroded and when it appeared the wall would be undercut as well, she put in the riprap. All of this would be perpetuated by the construction of Woodland's project which would keep the channel open and keep it naturally closing as she believes it would do if left alone. In short, Mr. Hambrick's analysis of the situation including his personal visits to the site lead him to conclude that the project will not: harm water quality in the area, increase the number of boats using the channel, influence the speed of boats that use the channel, or increase erosion of Petitioner's property. This opinion is supported by that of Dr. Echternacht, a hydrographic engineer who is also convinced that construction of the proposed bulkhead and riprap would not cause any erosion to Petitioner's property. In fact, the riprap in front of the bulkhead will act to absorb wave energy and since it cannot be placed in a vertical manner, it reduces that amount of reflected energy. The bulkhead and riprap as proposed here would reduce the amount of soil infusion into the channel and thereby the amount of dredging needed. The technical aspects of the proposal were also considered by Mr. Fancher, the dredge and fill supervisor for DER in the Northwest District. When he reviewed the application, including Mr. Hambrick's proposal for riprap, he concurred with it. In order to appropriately receive a permit, applicants must show that the application conforms to both water quality and public interest standards. After his review of the entire project, Mr. Fancher concluded that this project would not adversely affect water quality standards and would not adversely affect but in fact might promote public interest considerations. When the Florida Legislature passed its new water quality bill in October, 1983, it prohibited the construction of most vertical seawalls. In Mr. Fancher's opinion, what is proposed here is not a vertical seawall and there is no evidence submitted by Petitioner to refute this. In fact, there was no evidence presented by Petitioner, save her own testimony which does not serve to overcome the expert opinions to the contrary, that the proposed project fails to meet the tests set out under the laws of this State.
Recommendation Based on the foregoing Findings of Fact and Conclusions of Law, it is, therefore RECOMMENDED that the Respondent, Woodland Lake Property Owners, Inc.'s permit to construct a bulkhead be issued as modified. RECOMMENDED this 11th day of October, 1985, in Tallahassee, Florida. ARNOLD H. POLLOCK 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 Administrative Hearings this 11th day of October, 1985. COPIES FURNISHED: Kenneth G. Oertel, Esq. Oertel and Hoffman 2700 Blair Stone Road Suite C Tallahassee, Florida 32301 J. B. Murphy, Esq. 506 S. Palafox Street Pensacola, Florida 32501 Brad Thomas, Esq. Department of Environmental Regulation 2600 Blair Stone Road Tallahassee, Florida 32301 Victoria Tschinkel Secretary Department of Environmental Regulation Twin Towers Office Building 2600 Blair Stone Rd. Tallahassee, Florida 32301
Findings Of Fact Petitioner River Trails is the developer of a condominium community in Palm Beach County known as River Walk. River Walk is contiguous to and immediately adjacent to 2600 feet of South Florida Water Management District (hereinafter "SFWMD") property bordering Canal C-18 in Palm Beach County. The right- of-way adjacent to C-18 as well as the bottom of C-18 is owned by SFWMD. C-18 is not in an area designated as Outstanding Florida Waters. As required by Section 403.813(2), Florida Statutes, River Trails sought and obtained on January 12, 1984, a permit from the SFWMD to construct a dock and boat ramp in Canal C-18. The permit conveyed no property rights to River Trails. On October 12, 1984, River Trails asked DER to confirm that River Trails' proposed boat ramp qualified for an exemption pursuant to Section 403.813(2)(c), Florida Statutes. By letter dated December 20, 1984, DER informed River Trails that the proposed boat ramp did qualify for the exemption and, therefore did not require any permit from DER. On October 18, 1984, River Trails asked DER to confirm that River Trails' proposed dock of 1,000 square feet or less qualified for an exemption from DER's permitting authority pursuant to Section 403.813(2)(b), Florida Statutes. However, on November 30, 1984, DER informed River Trails that its proposed dock did not qualify for the exemption because there was already an existing dock on SFWMD property on Canal C-18. As authority for its position, DER cited the following sentence in DER Rule 17-4.04(9)(c), Florida Administrative Code: "A private dock is a single pier at a parcel of property." On the 2600 feet of SFWMD-owned right-of-way contiguous to River Trails, there are presently no docks. On SFWMD-owned right-of-way east of River Trails, between River Trails and the southwest fork of the Loxahatchee River, there are two docks approximately 300 feet apart located in front of single-family residences. DER contends all contiguous property owned by an individual, group or entity, including a water management district, constitutes a "parcel of property" and accordingly does not recognize River Trails' claim to an exemption because of the existence of these docks. Prior to River Trails' request that DER confirm River Trails' right to an exemption, DER had not interpreted water management district-owned right-of-ways to be a "parcel of property" within the meaning of Rule 17- 4.04(9)(c). In the past, the SFWMD has permitted numerous docks of less than 1,000 square feet on SFWMD-owned right- of-ways. Copies of these permits were routinely forwarded to DER. While these docks were and are on right-of-ways which DER now defines as a "parcel" within the meaning of Rule 17-4.04(9)(c), DER has not required permits for these docks. The DER employees who interpret the rule in question as part of their duties and whose depositions were introduced at hearing do not agree on the configuration which constitutes a single pier, on the degree of ownership or control required over a parcel of property by an applicant for an exemption, or on the definition of a parcel of property. DER has failed to adequately explain its deviation from past agency practice in interpreting SFWMD right-of- way as a parcel of property. But for DER's new interpretation of the term "parcel of property" found in Rule 17-4.04(9)(c), Florida Administrative Code, River Trails' proposed dock meets the statutory and rule requirements for an exemption from obtaining a permit from DER.
The Issue This proceeding concerns an Intent to Issue a dredge and fill permit given by the Department of Environmental Regulation ("DER") to Respondent, Edmund Burke ("Burke"), for construction of a retaining wall and wooden pile-supported bridge crossing a portion of the South Fork of the St. Lucie River in Martin County, Florida. The ultimate issues for determination are whether Petitioner has standing to challenge the proposed DER action, and if so, whether the proposed agency action complies with the requirements of Sections 403.91 through 403.938, Florida Statutes, and applicable rules.
Findings Of Fact Respondent, Edmund Burke, on January 15, 1988, filed with the Department of Environmental Regulation ("DER") application number 431441608 for a permit to construct a permanent, pile supported, wooden bridge approximately 80 feet long and 10 feet wide connecting the mainland with an island in the South Fork of the St. Lucie River in Martin County, Florida. The bridge was to span a 50 foot canal or creek ("channel") in the River. One of two retaining walls was to be located on the mainland peninsula. The other retaining wall was to be located on the island (the "initial project"). Between January 15, 1988, and April 28, 1989, the initial project was modified by Respondent, Burke, to satisfy DER concerns over potential impacts, including secondary impacts, relevant to the application. The width of the bridge was reduced from 10 feet to 6 feet. The retaining wall initially planned at the point where the bridge intersects the island was eliminated. The retaining wall on the mainland side of the bridge was relocated above mean high water. Sixty feet of the proposed bridge runs from mean high water to mean high water. An additional 10 feet on each end of the bridge is located above mean high water. The project remained a permanent, pile supported, wooden bridge (the "modified project"). The Intent to Issue, dated April 28, 1989, indicated that the modifications required by DER had been made, that the modifications satisfied DER concerns relevant to the initial project, and that DER intended to issue a permit for construction of the modified project. The elimination of the retaining wall obviated any necessity for backfill on the island. The reduction in the width of the bridge virtually eliminated the secondary impacts on the surrounding habitat, resulted in less shading of the water, and precluded vehicular traffic over the bridge. The final modification that was "necessary in order for [DER] to approve this application" was the reduction in the width of the bridge from 10 feet to 6 feet. Petitioner's Exhibit 17. DER's requirement for this final modification was communicated to Mr. Cangianelli in a telephone conversation on April 6, 1989 (Petitioner's Exhibit 18), and memorialized in a letter to Respondent, Burke, on April 14, 1989 (Petitioner's Exhibit 17). The final modification was made, and the Intent to Issue was written on April 28, 1989. Petitioner's Case. Property commonly known as Harbor Estates is adjacent to the site of the modified project. A constructed harbor and contiguous park are located within the boundaries of Harbor Estates. Both are used by residents of Harbor Estates and both are proximate to the site of the modified project. The harbor entrance and site of the modified project are located on opposite sides of a peninsula approximately 40 feet wide and approximately 125 feet long. Boats operated by residents of Harbor Estates that can navigate under the modified project need only travel the length of the peninsula, a distance of approximately 125 feet through the channel, in order to reach the harbor entrance. Boats operated by residents of Harbor Estates that cannot navigate under the proposed bridge must travel around the island, a distance of approximately 1800 feet in the main body of the St. Lucie River, in order to reach the harbor entrance. However, Petitioner presented no evidence that prior to the construction of the bridge the channel was navigable by boats not capable of passing under the bridge after the bridge was completed. Petitioner, Harbor Estates Associates, Inc., submitted no evidence to show facts necessary to sustain the pleadings in the Petition concerning the inadequacy of modifications required by DER. Of Petitioner's 26 exhibits, Exhibits 1-19, 24 and 25 were relevant to the initial project but were not material to claims in the Petition concerning the inadequacy of the modifications required by DER. Petitioner's Exhibit 20 was cumulative of DER's Exhibit 6B. Petitioner's Exhibits 22 and 26, respectively, concern a 1980 bridge permit and a Proposed Comprehensive Growth Management Plan for Martin County, Florida. Petitioner offered no expert testimony in support of the pleadings in the Petition including assertions that: the modified project will have a direct adverse impact upon water quality and the welfare or property of others; the channel is navigable by deep-draft motor vessels; the modified project will result in shoaling that will have to be corrected at the expense of Harbor Estates; the modified project will result in prohibited destruction of mangroves; or that the modified project will cause any of the other specific adverse effects described in the Petition. The testimony of fact witnesses called by Petitioner was not material to Petitioner's claims that modifications required by DER were inadequate. The testimony of Bob Nicholas was relevant to allegations of prior violations but was not dispositive of any issue concerning the adequacy of modifications required by DER. The testimony of William Burr was admitted as rebuttal testimony relevant to precedents in the general area of the modified project but failed to address the adequacy of modifications required by DER. Petitioner consistently demonstrated a lack of knowledge of the applicable law, the proper scope of the formal hearing, and the distinction between argument and evidence. Petitioner repeatedly attempted to establish violations of laws not relevant to the proceeding including local laws and other environmental laws. Petitioner attempted to establish issues by arguing with witnesses during direct and cross examination, and by repeatedly making unsworn ore tenus representations of fact. There was a complete absence of a justiciable issue of either law or fact in this proceeding because Petitioner failed to show facts necessary to sustain the pleadings. Petitioner presented no evidence refuting Respondent, Burke's, showing that the modifications required by DER were adequate to assure water quality and the public health, safety, or welfare, or the property of others. Evidence presented by Petitioner was not material to the issue of whether the modifications required by DER were adequate for the purposes of the law applicable to this proceeding. Therefore, Petitioner participated in this proceeding for a frivolous purpose, primarily to cause unnecessary delay, or to needlessly increase the cost of licensing or approval of the proposed activity. Respondents' Case. The island to be accessed by the modified project is approximately 2.5 acres in area and contains mostly wetland. The island is approximately 900 feet long. The portion of the island that is beyond DER permit jurisdiction is less than 200 feet long and less than 50 feet wide. The site of the modified project is located in Class III waters. Respondent, Burke, provided adequate assurances that portions of the modified project not extending over open water will be constructed upon property owned by him. The single retaining wall to be constructed at the southeastern terminus of the modified project will be constructed landward of DER jurisdiction. The modified project permits neither the installation of water or electrical conduits to the island nor any excavation, filling, or construction on the island. Respondent, Burke, must provide notification to DER before any such activity is begun. The bridge will accommodate no vehicular traffic larger or heavier than a golf cart. Golf cart access is necessary in order to accommodate a physical disability of Respondent, Burke. The modified project employs adequate methods to control turbidity, limit mangrove alteration on the island, and limit potential collisions with manatees. Vegetation, including mangroves, will not be removed. Incidental, selective trimming of vegetation will be allowed to create access to the island. The single retaining wall to be constructed on the mainland will be located landward of mangroves. Turbidity curtains will be used during construction to minimize short term water quality impacts. The modified project requires turbidity screens to be installed if there is any indication of sedimentation. No mechanical equipment will be located on the island during construction. No boats will be moored at the site of the modified project. The modified project will cause no significant downstream shoaling or silting. The site of the modified project is located approximately 15 feet from an existing fishing platform. No significant shoaling has been associated with that platform. The impacts associated with the modified project are similar to the impacts associated with single family docks in the area. No significant shoaling has been associated with such docks. The modified project is not a navigational hazard. The elevation is sufficient to accommodate small boats, canoes, and row boats. Reflective devices are required to alert night boat traffic of its presence. There is adequate clearance under the bridge to prevent obstruction. DER reviewed all applicable rules and criteria in considering the modified project. The modified project will have no adverse effect upon public health, safety or welfare, or the property of others. The modified project will not adversely impact the conservation of fish, wildlife, or their habitats. The modified project will not adversely affect navigation, the flow of water, or cause harmful erosion or shoaling. The modified project will not adversely impact fishing value or marine productivity in the area. The modified project will have no adverse impact upon recreational values in the vicinity. The modified project was reviewed in a manner that is customary for similar projects reviewed by DER. It is common practice for DER employees, as they did in this case, to rely upon opinions of other DER professionals in formulating an intent to issue. Other projects within DER jurisdiction in the general geographic area of the modified project and within the same region were considered in DER's review process. Other docks and marinas have been constructed and are proposed for construction within the South Fork of the St. Lucie River. Bridges including pedestrian bridges have been and are proposed to be constructed in Martin County. DER did not require a hydrographic study because the modified project was considered a minor project. DER review took into account the intended future use of the island property and DER's past experience with Respondent, Burke. As part of its review, DER reviewed a conceptual bridge to a single family residence on the island which would not require any fill or construction of retaining walls. In addition, DER considered previous violations on the island under Florida Administrative Code Rules 17-4.070, 17-4.160, and 17-4.530 in connection with an earlier permit that expired before the initial project was begun. Respondent, Burke, provided reasonable assurances that he is the owner of the site of the proposed project. Respondent, Burke, signed DER's property ownership affidavit and submitted a survey. DER's Intent to Issue does not authorize any construction in any area within the jurisdiction of DER other than the modified project. The Intent to Issue constitutes compliance with state water quality standards. DER has not received any requests for a jurisdictional determination in the general geographic area of the modified project. No enforcement action has been initiated by DER or at the request of a third party against Respondent, Burke, for alleged violations of DER rules.
Recommendation Based upon the foregoing Findings of Fact and Conclusions of Law, it is RECOMMENDED that the Department of Environmental Regulation enter a Final Order on the merits issuing the requested permit and awarding reasonable attorney's fees and costs in accordance with this Recommended Order. DONE AND ORDERED in Tallahassee, Leon County, Florida, this 4th day of April, 1990. DANIEL MANRY 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 4th day of April, 1990. APPENDIX Petitioner has submitted proposed findings of fact. It has been noted below which proposed findings of fact have been generally accepted and the paragraph number(s) in the Recommended Order where they have been accepted, if any. Those proposed findings of fact which have been rejected and the reason for their rejection have also been noted. Although most of Petitioner's proposed findings were cast in the form of "fact", they were in substance argument and rejected accordingly. The Petitioner's Proposed Findings of Fact Proposed Finding Paragraph Number in Recommended Order of Fact Number of Acceptance or Reason for Rejection 1 Included in part in Finding 1 Findings as to ownership are rejected as beyond the jurisdiction of the undersigned. Finding as to the late filed exhibit is rejected as irrelevant. 2-4, 10-12, Rejected as either irrelevant 16, or not supported by the record. 5 and 6, 37, 40 Rejected as unsupported by 42 the record. 7, 8, 15 Rejected as irrelevant 17, 21-29 and immaterial 9, 13, 14, 18-20 Rejected as immaterial 30-33, 35 and 36 37(a), 38, 39, 41, 48 20(A) Rejected as irrelevant and immaterial except the last sentence is included in Finding 13 34 Included in Finding 12 Rejected as not supported by the record, hypothetical and immaterial. Rejected as not established by clear and convincing evidence. Respondent, Burke, has submitted proposed findings of fact. It has been noted below which proposed findings of fact have been generally accepted and the paragraph number(s) in the Recommended Order where they have been accepted, if any. Those proposed findings of fact which have been rejected and the reason for their rejection have also been noted. Respondent. Burke's, Proposed Findings of Fact Proposed Finding Paragraph Number in Recommended Order of Fact Number of Acceptance or Reason for Rejection 15 and 16 Included in Finding 1 17, 26, 27 Included in Finding 2 18, 48 Included in Findings 15 and 16 19, 30, 31, 42 Included in Finding 13 20, 21, 44 Included in Findings 4 and 14 22, 23, 25, 32 Included in Finding 17 24 Included in Finding 16 25, 36-38 Included in Finding 17 Included in Finding 18 Included in Finding 3 Included in Finding 10 Included in Finding 19 35, 39, 43 Included in Finding 20 40, 41 Included in Finding 11 45-47 and 49 Included in Finding 16 51 and 52 Included in Findings 6-8 54 Included in Finding 5 and 8 50 and 53 Rejected as irrelevant and immaterial Respondent, DER, has submitted proposed findings of fact. It has been noted below which proposed findings of fact have been generally accepted and the paragraph number(s) in the Recommended Order where they have been accepted, if any. Those proposed findings of fact which have been rejected and the reason for their rejection have also been noted. The Petitioner's Proposed Findings of Fact Proposed Finding Paragraph Number in Recommended Order of Fact Number of Acceptance or Reason for Rejection 1 and 2 Included in Findings 1 and 2 3 Included in Finding 10 4 and 5 Included in Finding 16 6, 9 Included in Finding 2 7 and 8 Included in Findings 9 and 11 10 Included in Finding 13 11 Included in Finding 15 Included in Finding 17 and 14 Included in Finding 16 COPIES FURNISHED: Dale H. Twachtmann, Secretary Department of Environmental Regulation Twin Towers Office Building 2600 Blair Stone Road Tallahassee, FL 32399-2400 Daniel H. Thompson General Counsel Department of Environmental Regulation Twin Towers Office Building 2600 Blair Stone Road Tallahassee, FL 32399-2400 Patricia E. Comer Assistant General Counsel Department of Environmental Regulation Twin Towers Office Building 2600 Blair Stone Road Tallahassee, FL 32399-2400 Patricia V. Bartell Qualified Representative 615 S.W. St. Lucie Street Stuart, FL 34997 J. A. Jurgens Jones, Foster, Johnson & Stubbs, P.A. 505 South Flagler Drive West Palm Beach, FL 33402
Findings Of Fact The Subject Property. The property at issue in this proceeding consists of approximately 205 acres of land located in Clay County, Florida. The subject property is known as "Station Pond (Oak Forest Extension)." Station Pond was subdivided into 40 lots by an unrecorded subdivision plat. The lots range in size from approximately three to fifteen or twenty acres. Roads, which are unpaved, surrounding Station Pond, and drainage for Station Pond, are privately owned. The roads and drainage were completed prior to December of 1978. A boundary survey of Station Pond was prepared and contains a surveyor's certification of January 8, 1980. Pre-1985 Subdivision Regulations of Clay County. Prior to September of 1985 Clay County did not require platting of subdivisions such as Station Pond. In September of 1985, Clay County adopted Ordinance 85-68 creating three types of subdivisions and providing for the regulation thereof. An exception to these requirements, however, was included in Ordinance 85-68: subdivisions shown on a certified survey prior to September of 1985 with lots and roads laid out would continue to not be subject to regulation so long as the lots continue to comport with the survey. Government Action Relied Upon Before the Applicant's Sale of the Property. The Applicant was aware that it could develop Station Pond as an unrecorded subdivision in Clay County. The development of Station Pond comes within the exception to Ordinance 85-58. In a letter dated December 15, 1978 the Clay County Director of Planning and Zoning informed the Applicant that Oak Forest Clay County would "issue building permits in accordance with the uses permitted and lot/building requirements for an Agricultural zoned district, and in accordance with all other local ordinance provisions, state statutes, etc., as enclosed." This representation was based upon the conclusion of Clay County that Oak Forest was not subject to Clay County subdivision ordinances. Similar conclusions were reached by the Clay County Health Department in a letter dated September 8, 1978, and by the Clay County Public Works Director in a letter dated December 18, 1978. The Applicant's Detrimental Reliance. The Applicant's predecessor corporation provided dirt roads around part of Station Pond. The roads were constructed prior to December of 1978. The costs of the roads incurred by the Applicant was approximately $15,000.00. Rights That Will Be Destroyed. If the Applicant must comply with the Clay County comprehensive plan it will be required to pave the roads of the subdivision and provide an approximately 3 mile long paved access road. Procedural Requirements. The parties stipulated that the procedural requirements of Vested Rights Review Process of Clay County, adopted by Clay County Ordinance 92-18, as amended, have been met.
