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FRED ROTH vs. DEPARTMENT OF NATURAL RESOURCES, 88-002058 (1988)
Division of Administrative Hearings, Florida Number: 88-002058 Latest Update: Oct. 31, 1988

Findings Of Fact Sunset Company of Wilton, Incorporated, is the record title owner of a parcel of real property in Government Lot 1, Section 5, Township 66 South, Range 33 East, on Crawl Key No. 3 also known as Fat Deer Key, Monroe County, Florida. A portion of that parcel has been conveyed by Sunset Company to Whaler's Plaza, Incorporated, although that deed may not have been recorded. Petitioner Fred Roth owns and controls both corporations and exerts ownership and control over the entire parcel. The submerged lands in Tarpon Creek which are waterward of the line of mean high water contiguous to the parcel are sovereignty submerged lands. Roth received "major development" approval from Monroe County to develop the parcel by constructing a commercial/retail development known as "Whaler's Plaza.' The major development plan submitted to and approved by Monroe County includes a docking facility. In 1979 Roth filed an application with the Florida Department of Environmental Regulation for a private dock facility at Whaler's Plaza. The Department of Environmental Regulation approved that application and issued to Roth Permit/Certification No. 44-18542-5E. Roth never constructed that docking facility, and the permit expired on August 1, 1980. One of the agencies involved in reviewing that permit application was the Respondent. On June 26, 1979, Respondent notified Roth that upon review of the application in DER File No. 44-18542-5E, it had determined that the submerged lands were state-owned but that no lease agreement with Respondent would be required. After Permit No. 44-18542-5E expired on August 1, 1980, the Department of Environmental Regulation directed a letter to Petitioner advising him that the permit had expired and further advising him that if he wished to pursue the project he would have to obtain a new permit. in October 1983 Roth sought new authorization from the Department of Environmental Regulation and Respondent to construct a docking facility at Whaler's Plaza. His application was assigned DER File No. 440774875. On December 29, 1983, Respondent notified Roth that a lease would be required for the use of state-owned lands contiguous to Whaler's Plaza, relative to DER File No. 440774875. Respondent's rules changed in 1982 so that Roth's docking facility would be required to meet new criteria. The docking facility proposed by Roth in 1983 was similar to the docking facility proposed in 1979. The 1983 proposed modified docking facility was still represented to the Department of Environmental Regulation to be a private boat dock. The Department of Environmental Regulation issued an intent to deny the 1983 application under its then-existing rules, and Roth requested a formal hearing on that preliminary denial. Before a final hearing could be conducted, Roth again modified the proposed docking facility so that he qualified for a dredge and fill permit exemption from DER, so that no DER permit was needed for his project. A final order was entered by the Department of Environmental Regulation on August 27, 1985. While Roth's 1983 application was pending before the Department of Environmental Regulation, Roth was processing his application with Respondent for a submerged land lease for the docking facility. The documents he filed with Respondent, however, indicated that the docking facility was not intended to be a private dock but rather was a dock related to the commercial development at Whaler's Plaza. Roth represented to Respondent that the proposed docking facility would be for the convenience of patrons of the stores and restaurant at Whaler's Plaza and for his own personal use. Specifically, on June 3, 1985, Roth directed a letter to Respondent pursuant to Respondent's request for additional information. He described the Whaler's Plaza docking facility as follows: The wood dock will be used for arriving and departing customers of the restaurant and stores and my own personal use. The upland land use and activities of the property--will be developed into a shopping center. At the present time, the first phase is completed which is a one-story building containing four units, housing six retail stores, plus offices. The next phase will consist of three more buildings having five units each, 1,0000 [sic] sq. ft. each unit which will be for retail stores and offices, and the final phase will be a 200 seat restaurant, a miniature [sic] petting zoo and possibly a miniature golf course. ... 70 percent of the slips will be open to the general public for their convenience In patronizing the restaurant and stores; the remaining 30 percent of the slips will be for my own personal use. Roth never completed the lease application he filed with Respondent, and he failed to obtain approval for the use of the sovereignty submerged lands preempted by the docking facility proposed in DER File No. 440774875. Eventually, his pending application with Respondent was deactivated, and the file was closed. In late 1986, Roth initiated construction of his docking facility on sovereignty submerged lands, and he caused 30 pilings with cross-bracing to be placed into the submerged lands. On September 1, 1986, Grant Gelhardt, one of Respondent's enforcement officers, discovered the dock being constructed and verbally instructed Roth, through Mrs. Roth, to immediately cease construction activity. No further construction has taken place. Despite the verbal notification, a subsequent warning notice sent by certified mail, and Respondent's Notice of Violation and Order for Corrective Action, Roth has failed to remove the pilings and/or to take corrective measures regarding the partially completed docking facility. Roth has allowed vessels to be moored at the partially completed docking facility, has moored his own vessels at the partially completed docking facility, and has failed to prevent other persons from mooring at the partially completed docking facility. Roth's actions have resulted in damage to a benthic seagrass community on the adjacent sovereignty submerged lands over which Roth's partially completed docking facility is located, and over which vessels using the facility have been and would be moored. Those submerged lands constitute a benthic community of seagrass which supports various fauna and which would be adversely affected by completion and operation of the docking facility. The water depths in the area are shallow, with areas of less than -4 feet mean low water. The width of Tarpon Creek in the project area is approximately 100 feet. The length of the partially completed docking facility is approximately 150 feet. Although the dock extends parallel to the shore, the distance the dock extends into Tarpon Creek, as measured from the shoreline, is approximately 35 feet. Roth knowingly trespassed on sovereignty submerged lands by initiating construction of the docking facility, and he has willfully damaged those lands by drilling holes and placing pilings, and by allowing moored vessels to shade the seagrass. Although Roth ceased construction of the docking facility when told to stop, he has failed to attempt to resolve the violation, to remove the pilings, to seek an after-the-fact approval, or to cease all mooring of vessels on sovereignty submerged lands adjacent to the uplands, even subsequent to receiving the Notice of Violation and Order for Corrective Action. Respondent's June 26, 1979 letter to Roth authorized the activities described in DER Permit No. 44-18542-5E, for the period authorized by that permit. Roth knew that the DEP permit, and therefore Respondent's approval to engage in the activity authorized by that permit, had expired. Roth further knew that his new application filed in 1983, DER File No. 440774875, which was approved by DER after Roth further modified it in order to qualify for an exemption, did not exempt him from obtaining authorization from Respondent to use sovereignty submerged lands for the project and further knew that when he commenced construction of the docking facility in 1986 that he had not obtained approval from Respondent to use state-owned submerged lands. Roth offered no evidence to demonstrate any detrimental reliance upon the June 26, 1979, DNR letter, and the letter did not create a vested right for Roth to construct a different docking facility at a later time without authorization from Respondent. The uplands at the Whaler's Plaza commercial/retail development are owned by for-profit corporations which Roth controls and which derive income from the business and commercial activities at Whaler's Plaza. The docking facility intended primarily for the use of customers of Whaler's Plaza would therefore constitute a revenue generating/income related activity.

Recommendation Based upon the foregoing Findings of Fact and Conclusions of Law, it is, RECOMMENDED that a Final Order be entered requiring petitioner to: Remove the unauthorized structure within 20 days from the date on which the Final Order is entered and in accordance with Respondent's supervision of that removal; Immediately cease all mooring of vessels on sovereignty submerged lands adjacent to the uplands of the parcel known as Whaler's Plaza until authorized to use state-owned lands; and Pay a fine of $2500 within 15 days of receipt of a certified letter from the Executive Director of the Department of Natural Resources demanding payment to the internal improvement Trust Fund. DONE and RECOMMENDED this 31st day of October, 1988, at Tallahassee, Florida. LINDA M. RIGOT, Hearing Officer Division of Administrative Hearings The DeSoto Building 1230 Apalachee Parkway Tallahassee, Florida 32399-1550 (904) 488-9675 Filed with the Clerk of the Division of Administrative Hearings this 31st day of October, 1988. COPIES FURNISHED: David L. Manz, Esquire Post Office Box 177 Marathon Florida 33050 Ross S. Burnaman, Esquire Department of Natural Resources 3900 Commonwealth Boulevard Tallahassee, Florida 32303 Tom Gardner, Executive Director Department of Natural Resources 3900 Commonwealth Boulevard Tallahassee, Florida 32303

Florida Laws (3) 120.57253.002253.77 Florida Administrative Code (3) 18-14.00218-14.00318-14.005
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JAMES CASTORO AND WINIFRED CASTORO; JELKS H. CABANISS, JR.; ANNE CABANISS; STANLEY GOLDMAN AND GLORIA GOLDMAN; FRANKLIN H. PFEIFFENBERGER; AND KATY STENHOUSE vs ROY PALMER AND DEPARTMENT OF ENVIRONMENTAL PROTECTION, 96-000736 (1996)
Division of Administrative Hearings, Florida Filed:Sarasota, Florida Feb. 08, 1996 Number: 96-000736 Latest Update: Oct. 19, 1998

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

Florida Laws (7) 120.569120.57253.0326.012373.403373.414403.814 Florida Administrative Code (12) 18-21.00118-21.00318-21.00418-21.00518-21.00762-302.30062-341.20162-341.21562-341.42762-343.09062-4.24262-4.530
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PETER W. MANSFIELD vs. PATCO, INC. & DER, 79-000528 (1979)
Division of Administrative Hearings, Florida Number: 79-000528 Latest Update: Jun. 27, 1979

Findings Of Fact Patco proposes to build a dock offshore of a condominium it is now constructing on Anna Maria Key in Manatee County, Florida. At the proposed dock, condominium residents could moor 22 boats in Watson's Bayou, which opens onto Sarasota Pass (also known as Anna Maria Sound). A house owned by Mildred S. Mansfield, petitioner Peter's mother, sits on a waterfront lot on the north shore of Watson's Bayou. The main part of the proposed dock would parallel the edge of the bayou, running 248 feet in a north-south direction, 30 to 45 feet offshore. Some 47 marine pilings six inches in diameter would support the decking on the main part, which would be elevated four feet above mean sea level. At its mid- point, the main part of the dock would be joined to the land by a perpendicular- access walkway with the same open substructure and at the same height as the main part of the dock. Of the ten pilings planned as the foundation for the access walkway, six would be seaward of the mean high water line. Eleven catwalks or finger piers are planned to extend perpendicularly into the bayou from the main part of the dock, at intervals of 24 to 28 feet. Two six inch marine pilings would support each catwalk or finger pier at a height of slightly more than three feet above mean sea level. Between every pair of finger piers, two boat slips are planned; and slips are planned on either side of every finger pier. Between every pair of slips not separated by a finger pier, Patco proposes to place a mooring piling, equidistant from the two finger piers nearest it. These ten mooring pilings would stand seaward of the finger piers, but no more than 70 feet seaward of the mean high water line. Patco also plans to put in two pilings along each of two imaginary lines, running shoreward from either end of the main part of the dock, and perpendicular to the main part of the dock. The purpose of these pilings, which would be about eight feet apart, would be to discourage boat traffic between the main part of the dock and the shore. Two boulders would be placed in shallow water for the same purpose. A water system and electrical service are planned for the dock, but neither fuel nor lubricants are to be dispensed and no waste or sewage system is planned. Patco plans to operate the facility, including emptying containers it intends to provide for trash, until it sells the dock to an association of slip owners, who will take over its management. Patco will not allow people to live aboard boats moored at the dock and a condition of any sale to an association will be that the association not allow live-aboards. With occasional breaks, there is a fringe of black, white and red mangroves along the shore opposite the main part of the proposed dock. Louise Robertson testified without contradiction that mangroves bordering Patco's property have been trimmed and in some cases cut down. The access walkway is planned for one of the natural breaks in the mangrove fringe, however, a spot where there are no mangroves. Applicant's Exhibit No. 6. The waters of Watson's Bayou are Class III waters. Experience with a similar dock built by Patco near the proposed site some 15 months before the hearing indicates that the proposed dock would not violate DER's water quality standards. Shortly before the hearing, a biologist's superficial examination of waters in the vicinity of the dock that has been built revealed no water quality problems as a result of the dock. Increased boat traffic in the vicinity would result in additional oils and greases in the water but, after reasonable opportunity for mixture with the waters of Watson's Bayou, oils and greases would probably not exceed 15 milligrams per liter, or otherwise violate the criteria set forth in Rule 17-3.05(2)(r) Florida Administrative Code. Patco plans to engage a subcontractor to put the pilings in. The subcontractor would "jet" the pilings by using a pump mounted on a barge to force water down to the bottom through a hose. This process would result in sand being temporarily suspended in the water. Patco proposes to curtain off or "diaper" the area where pilings are to be jetted in, so as to contain the turbidity, and so as to keep silt out of an oyster bed nearby. The parties stipulated that the project would not violate turbidity standards, if such precautions are taken. The parties also stipulated that the proposed dock would not violate DER's dissolved oxygen or biochemical oxygen demand standards. The evidence established that DER has reasonable assurance that none of its water quality standards would be violated by the dock Patco proposes to build. At mean sea level, there is ample water at the site of the proposed slips to float any vessel capable of entering Watson's Bayou from the waters outside. The channel into Watson's Bayou from Sarasota Pass is only three feet deep at low tide. This shallow channel prevents boats drawing more than a few feet from entering the Bayou through the channel, but a 46 foot ketch once came in on a high tide. In the proposed slips, mean sea level depths would range from six or seven feet at the seaward end of the finger piers to three or four feet at the landward end of the slips. Mean low water depths are about seven/tenths of a foot lower. With a spring tide, the water may fall six inches below mean low water levels. There is virtually no danger that boats would run aground in the proposed slips. The bottom underneath the proposed dock is sandy and wholly devoid of grasses or other marine vegetation. Between the shore and the main part of the dock however, there is an oyster bed whose northern edge is approximately five or ten feet south of the site proposed for the access walkway. This oyster bed extends about 280 feet in a southerly direction, but does not extend as far west as the site proposed for the main part of the dock. Jetting in the proposed pilings would not result in the death of a single oyster. As long as boats stay on the seaward side of the main part of the proposed dock, the oysters would not be harmed by boat traffic. Other fauna at the site include some benthic polychaetes, tunicates and other arthropods. The jetting in of pilings would injure and displace any of these creatures who were in the immediate vicinity, but their mobility is comparable to that of fishes and they would soon reestablish themselves. Once in place, the pilings would afford a habitat for barnacles and related marine life. A public boat launching ramp is situated 150 to 200 feet from the southern end of the proposed dock. The ramp is far enough away from the proposed dock that construction of the dock would not interfere with launching boats. The water in this part of Watson's Bayou is deep enough that the proposed dock would not create a serious impediment to navigation. Under certain wind conditions, however, a sailboat beating into the main part of Watson's Bayou from the ramp might have to make an additional tack or two if the proposed dock is built. Conversely, with southerly winds, a boat under sail making for the ramp from the main part of Watson's Bayou might have to tack more often if Patco builds the dock it proposes. The dock Patco plans to build would not create a navigational hazard nor cause erosion of the shoreline. The parties stipulated that the dock would not substantially alter or impede the natural flow of navigable waters. The State of Florida owns the bottom into which Patco plans to jet pilings. Respondent DER contacted Florida's Department of Natural Resources about the proposed dock in October, 1978. By letter dated November 21, 1978, the Department of Natural Resources advised the DER that the project would "not require a lease . . . as this application is considered a private dock." DER's Exhibit No. 1. On the strength of biological and ecological surveys and repeated visits to the site by Linda Allen, an environmental specialist in DER's employ, the DER gave notice of its intent do issue the permit Patco seeks. The foregoing findings of fact should be read in conjunction with the statement required by Stuckey's of Eastman, Georgia v. Department of Transportation, 340 So.2d 119 (Fla. 1st DCA 1976), which is attached as an appendix to the recommended order.

Recommendation Upon consideration of the foregoing, it is RECOMMENDED: That DER grant Patco's application for permit on the following conditions: That no submerged or transitional vegetation be destroyed in constructing the dock. That the construction area be diapered so as to restrict siltation to the smallest practicable space and, in any event, so as to separate the work area from the oyster bed. That no dredging by any method be used to gain access to the dock. That the owner of the dock allow no docking except in slips seaward of the main part of the dock. That the owner of the dock maintain lines and floats between the ends of the main part of the dock and the landward pilings; and take other appropriate steps to discourage boat traffic between the main part of the dock and the shore. That the owner of the dock forbid living on board boats moored at the dock; forbid the discharge of sewage and garbage into the water; and furnish trash receptacles for the dock. DONE and ENTERED this 6th day of June, 1979, in Tallahassee, Florida. ROBERT T. BENTON, II Hearing Officer Division of Administrative Hearings Room 101, Collins Building Tallahassee, Florida 32301 (904) 488-9675 APPENDIX Paragraphs one through eleven, thirteen through seventeen and nineteen through twenty-two of respondent Patco's proposed findings of fact, have been adopted, in substance. Paragraph twelve of respondent Patco's proposed findings of fact has been adopted insofar as the plan for pilings and boulders. The evidence did not establish that this, without more, would suffice to protect marine life on the bottom between the shore and the main part of the dock. Paragraph eighteen of respondent Patco's proposed findings of fact reflects the evidence in that it was shown that the proposed dock would not degrade water quality below minimum standards for Class III waters; but degradation of water quality as a result of oils and greases can be expected, within lawful limits. COPIES FURNISHED: Dewey A. Dye, Jr., Esquire Patricia A. Petruff, Esquire Post Office Box 9480 Bradenton, Florida 33506 Alfred W. Clark, Esquire Twin Towers Office Building 2600 Blair Stone Road Tallahassee, Florida 32301 Mr. Peter W. Mansfield 1861 Meadow Court West Palm Beach, Florida 33406

Florida Laws (1) 120.57
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LEO JOSEPH BERGER vs. JEEMAN, INC., 88-001293 (1988)
Division of Administrative Hearings, Florida Number: 88-001293 Latest Update: May 27, 1988

The Issue Should the Respondent, STATE OF FLORIDA DEPARTMENT OF ENVIRONMENTAL REGULATION, grant the applicant, JEMAAM, INC., a dredge and fill permit pursuant to the Notice of Intent dated March 2, 1988, in File No. 361414445?

Findings Of Fact The Respondent, JEMAAM, INC., is the owner and the developer of real property contiguous to state waters in Lee County, Florida. The condominium project on the property is known as Island's End Condominiums. As part of Phase III of the condominium project, Respondent JEMAAM built a dock. This dock is the subject of this administrative hearing because the Respondent JEMAAM wants to reconfigure and relocate portions of the dock structure. Respondent JEMAAM filed an application for a dredge and fill permit with the Respondent DER in order to modify the exiting dock. The Respondent JEMAAM seeks to modify the dock by relocating a 3.92' x 61' section of the existing dock to a more waterward location. This area of the dock is the southerly extension, which fronts the Petitioners' condominium unit. The application process was begun on November 3, 1987, and completed on February 26, 1988. A Notice of Intent to Issue a dredge and fill permit for the proposed project was issued on March 2, 1988, by the Respondent DER. The dock is subject to the Respondent DER's permitting requirements because the construction activity is to take place in state waters and the dock structure exceeds 1,000 square feet in size. In addition, the Respondent JEMAAM has agreed not to undertake further dredge or fill work or any other construction in wetland areas under the Respondent DER's jurisdiction unless a valid permit had been obtained for such activities. The Petitioners, LEO J. BERGER and KATHLEEN D. BERGER, are the owners of Condominium Unit Number 102 in Phase III of Island's End Condominiums in Lee County, Florida, which is adjacent to Respondent JEMAAM's dock. The Petitioners filed an administrative complaint in which they disputed the appropriateness of the Intent to Issue dated March 2, 1988. In support of their position, the Petitioners identified a number of areas of controversy and alleged that the Respondent JEMAAM's application did not meet the "reasonable assurances" required for permit issuance. The Petitioners' allegations, which are properly before the Hearing Officer, are as follows: Shallow water in the area where the new dock configuration is to be located would result in propeller dredging of littoral shallows. The proposed waterward relocation of a portion of the dock would present a navigational hazard in the channel as well as in the shallows and around the dock. The proposed relocation would cause harmful shoaling in the area, which would affect boating safety as well as the habitat. The dock relocation and associated boat traffic will disrupt and harm bird and fish habitats. The dock may be within the Estero Bay Aquatic Preserve. Based upon the evidence adduced at hearing, I find as follows as to the allegations raised by the Petitioners in their administrative complaint: There are sufficient water depths, based upon the Bathymetric profile and a number of reviews by the Respondent DER in the proposed relocation area, to prevent harmful propeller dredging by boats using the dock. However, to assure that harmful turbidity and propeller dredging does not occur, the dock extension arm can be completely handrailed in the shallow, landward area. The addition of a shielded, steady burning light and navigational markers should minimize any impediment to navigation caused by the dock relocation. The main channel is not far from this area, and most boating traffic in the general area is confined to the main channel. The additional markers and lighting requirements combine with the current conditions to alert all reasonable and prudent boaters to the hazards and challenges of the area. The evidence is inconclusive as to the extent to which the dock structure has increased shoaling in the area. Much of the shoaling is attributed to the natural conditions of the area, a back-bay coastal zone. The shoaling which has occurred is thought to be beneficial by the experts who testified at hearing because the development of grasses has increased. This creates a positive habitat for Cuban shoalweed, brittle starfish, and several species of crab. Relocation of a portion of the dock will not substantially affect the shoaling activity in the area. The bird and fish habitats in the area do not appear to be adversely affected by the current dock. It is not anticipated that the relocation of a portion of the dock will change the ongoing development of the habitats. The bird roosting area on the sandbar includes a larger variety of species now than it did before the current dock was built, according to studies done by James W. Beever III. The installation of the additional channel markers was suggested by Beever, an expert witness in the case, as a means to enhance the viability of the sandbar as a habitat. The markers aid in steering boat traffic away from the area and prevent the beaching of boats on the sandbar. James W. Beever III is the current resource and research coordinator of the Estero Bay Aquatic Preserve. Based upon his testimony, the proposed dock relocation is not within the aquatic preserve. The areas of controversy raised by the Petitioners in their administrative complaint were sufficiently met by the reasonable assurances of the Respondent JEMAAM that the purported harms would not occur. The project is not contrary to the public interest under the criteria set forth in Section 403.918, Florida Statutes, as represented by the Respondent DER in the Notice of Intent to Issue and proved at hearing.

Florida Laws (1) 409.913
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BOARD OF COMMISSIONERS OF JUPITER INLET DISTRICT vs PAUL THIBADEAU AND DEPARTMENT OF ENVIRONMENTAL PROTECTION, 03-004099 (2003)
Division of Administrative Hearings, Florida Filed:West Palm Beach, Florida Nov. 05, 2003 Number: 03-004099 Latest Update: Sep. 09, 2005

The Issue The issues are whether Respondent Thidadeau is entitled to a Noticed General Permit, pursuant to Florida Administrative Code Rule 62-341.427, and a Letter of Consent, pursuant to Florida Administrative Code Rule, to construct a single family dock in the central embayment of the Loxahatchee River in Palm Beach County.

Findings Of Fact By Joint Application for Environmental Resource Permit/Authorization to Use Sovereign Submerged Lands/Federal Dredge and Fill Permit filed August 14, 2002, Respondent Paul Thibadeau (Applicant) requested a Noticed General Permit (NGP) and Letter of Consent for a single-family dock to be constructed at his home located at 129 River Road, Palm Beach, Florida (Application). The dock would extend from the southern shore of the Central Embayment of the Loxahatchee River, which is Class III waterbody that is also an Outstanding Florida Water and Aquatic Preserve. At the time of the filing of the Application, Applicant's contractors and Respondent Department of Environmental Protection tried various alignments to avoid impacts. Petitioner Board of Commissioners of Jupiter Inlet District (District) is an entity created by the Legislature to operate and maintain the Jupiter Inlet and maintain and preserve the Loxahatchee River. The District's jurisdiction covers the Central Embayment and Applicant's property. The District employs an engineer to inspect the Central Embayment for navigational hazards. Intervenors Andrea Cameron and Jeffrey Cameron and Douglas Bogue reside in shoreline property to the west of Applicant's property. The Camerons and Mr. Bogue live on the same cove that the west side of Applicant's property abuts. Mr. Bogue's parcel is the second parcel to the west of Applicant's parcel, and the Camerons' parcel is the third parcel to the west of Applicant's parcel. Intervenors swim, fish, birdwatch, boat, and otherwise use the area in which Applicant would construct the dock and platform. Applicant has owned his property for a little over seven years. Applicant's property consists of nearly 1.5 acres of land that forms a peninsula jutting into the Central Embayment from the southern shoreline near the Alternate A1A bridge, which marks the east end of the Central Embayment. Applicant owns 1000 linear feet of shoreline. The proposed dock and platform would be constructed on the northwest side of Applicant's property. Applicant currently owns a dock, measuring five feet into the water by 67 feet along the shoreline, in the canal on the east side of his property. The water depth at this dock is only four inches at the lowest tides and less than one foot at mean low water. Seagrasses--mostly shoalgrass and threatened Johnson's seagrass--grow in the vicinity of this dock, and it is a reasonable inference, given the nearby seagrass beds, prevailing shallow depths, shading effect of the present dock, and the relocation of prop and boating disturbances, that seagrass would recolonize the area of the existing dock, after it is removed. Applicant has agreed to amend either the NGP or Letter of Consent to condition the approval of the construction and use of the proposed dock upon the removal of the existing dock. The Application describes a dock that is 270 feet long and four feet wide. At the end of the dock is a 160 square-foot terminal platform. The diagram shows the dock running 110 feet due north from an upland point that is ascertainable only approximately by reference to a concrete sidewalk and mangrove fringe depicted on the drawing. The dock then turns to the northwest and runs 160 feet to the terminal platform, which measures 5.3 feet by 30 feet. Boat-lift pilings are waterward of the waterward edge of the platform. The diagram depicts approximations of water levels, at mean tide, along the dock. The shorter run of the dock ends in water two feet deep, at mean tide. The longer run crosses a long sandbar and terminates between the 3.5- and 4-foot contours. A cross-section in the Application shows mean high water at about 1.0 feet (presumably National Geodetic Vertical Datum, or NGVD) and mean low water at about -0.5 feet NGVD. The cross-section reveals that the waterward edge of the terminal platform is at almost -3.33 feet NGVD and the landward edge of the terminal platform is at about -3.2 feet NGVD. This means that, at mean low water, the water level would be a little more than 2.75 feet deep at the waterward edge of the terminal platform and about 2.75 feet deep at the landward edge of the terminal platform. The pilings, which are waterward of the waterward edge of the terminal platform, are at -3.5 feet NGVD. This means that, at mean low water, the water level would be about 3 feet deep at the most waterward pilings. However, the second slip, which mostly runs along the end of the dock, not the terminal platform, is in shallower water. According to a drawing that is part of the Application, the waterward end of this slip is at the same depth as the landward end of the terminal platform, so it would be in about 2.75 feet of water at mean low water, and the landward end of this slip is at -2.0 feet NGVD, so it would be in about 1.5 feet of water at mean low water. Disagreeing with this drawing, Applicant Exhibit 61 indicates that the shallowest water depth at the second boat slip is at least two feet at mean low water. Although the scale of District Exhibit 62 prevents a precise determination, District Exhibit 62 seems to agree with this value, as well as other landward values, contained in Applicant Exhibit 61. The superior detail of both of these exhibits, as compared to that of the drawing accompanying the application, compels a finding consistent with the deeper water levels reported on Applicant Exhibit 61 and District Exhibit 62. Thus, the water depth, at mean low water, is at least two feet at the second boat slip. DEP environmental scientists visited Applicant's site twice before issuing the permit and snorkeled the area proposed for the dock to find the location that would result in the minimum impacts. On the first visit, the DEP scientists did not record the tide, but, in the second visit, they snorkeled the area at mean low water. After DEP approved the permit, its scientists snorkeled the site a third time, also at mean low water. Applicant has worked closely with DEP at all stages of the permitting process. In fact, early discussions resulted in several different alignments and locations for the proposed dock. After DEP's environmental scientists determined for themselves the location of the seagrass beds in the affected area, Applicant settled on a location and alignment acceptable to the DEP scientists and revised the application (Revised Application). The Revised Application locates portions of the dock deck over some seagrass beds, but adds restrictions, beyond those normally imposed on docks built in Aquatic Preserves, to reduce or eliminate the impacts of the dock on these seagrass beds. The Revised Application narrows the dock deck by one foot to three feet, replaces solid decking with grated decking for the first 200 feet from the shoreline, adds handrails for the first 200 feet from the shoreline, and raises the elevation of the dock deck from five feet to seven feet above mean high water for the first 200 feet from the shoreline. The Revised Application also changes the width of the terminal platform from 5.3 feet to 6 feet and its length from 30 feet to 25 feet. The Revised Application clearly identifies two boat slips: one on the waterward side of the long side of the terminal platform and one perpendicular to the first slip, along the north side of the end of the dock deck. Lastly, the Revised Application reduces the dock deck from 270 feet to 250 feet to the shoreline. The proposed alignment of the dock passes between two relatively small seagrass beds immediately offshore of the northwest side of Applicant's property. The cove contains a large seagrass bed, mostly confined to water depths of less than 1.5 feet at mean low water. A little more than 50 feet of the dock passes over the eastern edge of this large seagrass bed, and the most waterward 40-50 feet of the dock passes over bottom that is uncolonized by seagrass. The seagrass that is traversed by the dock is mostly confined to the long sandbar that the dock would cross. Petitioner presented several alternatives to the present alignment. These are depicted in District Exhibit 79. Petitioner and its witness ultimately selected Alternative F, which would be a shorter dock running to the northeast off the northern tip of Applicant's property. Passing over little, if any, seagrass, this dock would terminate in a hole that is three feet deep at mean low water. However, Alternative F provides Applicant with little better access than he has at present. The northern route to the channel requires several turns and passes over much seagrass. The longer eastern route runs over 600 feet in a narrow, turning channel that contains only 1.5-2.0 feet of water at mean low water. This side of Applicant's property is more exposed to currents and winds than the west side abutting the cove, so accurate navigation of a vessel with the engine trimmed partly up would be more difficult. Channels, especially shallow ones, shift over time and shoal up, especially given this tendency within the Central Embayment. The Central Embayment is a shallow waterbody prone to shoaling due to sedimentation. The main channel through the Central Embayment generally runs along the north shoreline of the Central Embayment, although it runs in a more central location as it approaches the Alternate A1A bridge at the east end of the Central Embayment. Applicant's property, which is close to the A1A bridge, is relatively close to the main channel. A shallow area with interspersed seagrass beds separates Applicant's property from the main channel. Applicant operates a 24-foot boat with a 200- horsepower outboard motor. The boat requires 12 inches of water to float with the engine up and 24 inches of water for the skeg and prop to clear the bottom with the engine down and the boat operating at idle or low speed. To ingress or egress the existing dock, Applicant can operate his boat only within two hours of high tide. To reach the main channel, Applicant must navigate poorly marked, local channels. The longer local channel runs east from Applicant's property and requires several turns. The shorter local channel runs north of Applicant's property and enters the southern access channel at a point near to its junction with the main channel. The southern access channel is an important channel in the Central Embayment, whose shoreline has been densely developed. A long sandbar runs through the center of the Central Embayment. Rather than navigate to the west of the sandbar, most boat operators coming from the south shoreline take the southern access channel, which shortens the time it takes for them to leave the Central Embayment. A mangrove island at the east end of the long sandbar is located immediately north and west of the southern access channel, just west of its junction with the main channel. Directly across from the mangrove island, in a southeasterly direction, is the northwest side of Applicant's property, from which the dock would extend, running toward the southern access channel. Boating traffic in the southern access channel may reach over 100 trips during a 10-hour period on weekends. In the vicinity of the proposed terminal platform, two large, privately installed pilings exist nearly in the center of the southern access channel. The closer of these pilings would be about 95 feet from the proposed terminal platform. One of the pilings marks the junction of the southern access channel with the main channel. The closer piling is between the proposed platform and the mangrove island to the northwest. Boats operate to the south and east of these pilings, typically at planing speeds of at least 20 miles per hour. In the vicinity of the proposed terminal platform, the southern access channel is 120-150 feet wide, and the waterward edge of the platform is about 70 feet from the center of the channel. The bathymetry in the vicinity of the proposed platform reduces the navigational hazard posed by the proposed project. The -3 and -4 feet NGVD contours run parallel along the southern edge of the southern access channel in the vicinity of the proposed terminal. Both contours, on either side of the proposed terminal, take sharp turns landward 25-50 feet on either side of the proposed platform. The effect of this bathymetry is to create a sort of submerged cove for the proposed terminal platform, which is protected from passing boat traffic from the fact that these contours are generally 25-75 feet further waterward on either side of the platform. For instance, at mean tide, boaters approaching the area of the platform would presumably wish to stay in water deeper than three feet, so they would unlikely find the platform to be a navigational hazard. Additionally, an imaginary line extending from the takeoff point of the dock on Applicant's shoreline, along the dock, to a point on the opposite shoreline would run about 13,800 feet. This line would run just east and north of the mangrove island described above. The drawing of riparian lines at this location is much more difficult due to the irregular shoreline and the orientation of the southern access channel. Originally, Applicant proposed a riparian line that ran from the westernmost extent of his property, which is located at the end of the waterway running along the west side of the property. Dutifully running this line perpendicular to the orientation of the southern edge of the southern access channel, Applicant deprived a corner of his neighbor's property of any riparian rights at all. During the hearing, Applicant redrew proposed riparian lines. The appealingly named, "Equitable Allocation" line does more justice to the neighbor by not crossing his property. Instead, this line runs roughly along the middle of the canal- like waterway on the west side of Applicant's property and, at the mouth of this waterway, turning to the northwest to run perpendicular to the southern edge of the southern access channel. The problem with the "Equitable Allocation" line offered by Applicant emerges when it is considered in broader scale, sufficient to encompass not only Applicant and his neighbor to the immediate west, but also that neighbor's neighbor to the immediate west. The "Equitable Allocation" line does no equity to the riparian access of one of the two landowners to the west of Applicant. However, the task in this case is not to draw riparian lines, but to determine whether the proposed dock or platform is within 25 feet of another landowner's riparian line. Applicant Exhibit 62 draws the 25-foot offset line. If the riparian- rights line runs perpendicular to the orientation of the southern access channel (the so-called "Equitable Allocation"), the terminal platform and dock are offset by more than 25 feet from the line. If the riparian-rights line extends property lines without regard to the orientation of the channel, then the platform, but not the dock, would be within the 25-foot offset. As noted in the Conclusions of Law, case law teaches that the location of the channel and property boundaries receive consideration in establishing riparian rights. When based on the larger-scale map of Applicant Exhibit 63, any equitable application of these factors would not result in the establishment of a riparian rights line within 25 feet of the proposed terminal platform or dock. The proposed dock and platform would impact the aesthetic enjoyment of nearby landowners and others using the waters of the Central Embayment. Swimmers and sunbathers set up on the sandbar and throw balls and flying disks. The proposed dock would divide the sandbar into two sections of about 170 feet and 100 feet. The impact of the dock, with its pilings spaced at ten-foot intervals, is unclear on these recreational users, as it is on users of canoes and kayaks, which also occupy these waters. The record does not portray a high-energy, strong-current environment in this area, which is essentially at the mouth of a small cove, so it is difficult to infer that typical currents will create unsafe conditions for swimmers, kayakers, or canoeists around the pilings. Likewise, the record does not establish the net impact of the dock and platform on fish, birds, and other wildlife using the area. The platform covers submerged bottom that is uncolonized by seagrass, and, given its coarse sand and shell hash, as well as the water depths and water clarity, this bottom is unlikely ever to be colonized by seagrass. The portion of the dock that traverses seagrass will shade this vegetation, but the effect of shading is mitigated by the seven-foot elevation of the deck, translucency of the decking material, and near north-south orientation of the deck. The construction of the takeoff of the deck will not require significant alterations to the existing mangrove fringe. The issue of cumulative impacts is not that the average dock in the Central Embayment is 80 feet, and the proposed dock is over three times longer. Nor is it that only two docks on the southern shoreline of the Central Embayment would equal or exceed in length the length of the proposed dock, and one of these two docks serves a planned unit development. The length of the dock is subordinate to the depth of the water to be reached by the dock. The more relevant issue, as to cumulative impacts, is that the proposed dock would extend to water whose depth is -3.5 feet NGVD, and the majority of docks in the Central Embayment terminate in water at least one foot shallower. An estuary whose urbanized shoreline appears almost condominiumized in aerial photographs, the Central Embayment will undergo shoreline development to match whatever DEP permits in its most generous permitting decisions. However, a close examination of District Exhibit 62 reveals numerous examples of docks or platforms terminating in -3.5 or even -4.0 feet NGVD, so the potential of the Letter of Consent generating cumulative impacts, strictly in the termination depths of docks, is small. The most relevant concern, as to cumulative impacts, is the potential for the construction of docks where no docks presently exist and the number of such docks that would need to extend 250+ feet to reach water depths comparable to those reached by the proposed dock and platform. Perhaps landowners abutting such extensive stretches of flats have been discouraged from trying to obtain permits for such lengthy structures. Perhaps Applicant himself was emboldened to seek the present NGP and Letter of Consent due to the permitting of the other single- family dock of comparable length on the southern shoreline. The problem as to this aspect of cumulative impacts is that the record does not support findings as to the number of littoral parcels without docks and the number of such parcels that would require docks of 250+ feet to reach the depths involved in this case. These cumulative impacts, if any, are too speculative to assess. Thus, the analysis of cumulative impacts in this case is necessarily restricted to consideration of the impacts of some additional pressure to construct docks to one-foot deeper water than has historically limited docks and the accumulation of additional impacts to resources, such as seagrass, or recreational uses, such as boating and swimming, from an authorization to build the proposed dock and platform. The record does not support findings of significant adverse cumulative impacts from this proposed activity. Moreover, the elimination of 335 square feet of shallow-water dock and the possible recolonization of seagrass, including threatened Johnson's seagrass, mitigate any cumulative impacts and limit or even eliminate the precedential value of the permitting decisions in this case.

Recommendation It is RECOMMENDED that the Department of Environmental Protection: Grant the Noticed General Permit. Grant the Letter of Consent upon two conditions: a) the prohibition against any boat mooring to the slip for any period of time, if the boat requires more than two feet of water with its engine in normal operation position and the boat operating at idle or slow speed; and b) the removal of the existing dock prior to the construction of the new dock and platform. DONE AND ENTERED this 25t day of July, 2005, in Tallahassee, Leon County, Florida. S ROBERT E. MEALE Administrative Law Judge Division of Administrative Hearings The DeSoto Building 1230 Apalachee Parkway Tallahassee, Florida 32399-3060 (850) 488-9675 SUNCOM 278-9675 Fax Filing (850) 921-6847 www.doah.state.fl.us Filed with the Clerk of the Division of Administrative Hearings this 25th day of July, 2005. COPIES FURNISHED: Kathy C. Carter, Agency Clerk Department of Environmental Protection 3900 Commonwealth Boulevard Mail Station 35 Tallahassee, Florida 32399-3000 Greg Munson, General Counsel Department of Environmental Protection 3900 Commonwealth Boulevard Mail Station 35 Tallahassee, Florida 32399-3000 Kevin S. Hennessy Lewis, Longman & Walker, P.A. SunTrust Building 1001 3rd Avenue West, Suite 670 Bradenton, Florida 34205 Thomas F. Mullin Lewis, Longman & Walker, P.A. 1700 Palm Beach Lakes Boulevard Suite 1000 West Palm Beach, Florida 33401 Marcy I. Lahart Marcy I. Lahart, P.A. 711 Talladega Street West Palm Beach, Florida 33405 John S. Yudin Guy & Yudin, LLP 55 East Ocean Boulevard Stuart, Florida 34994 Toni Sturtevant Assistant General Counsel Christine A. Guard Senior Assistant General Counsel Department of Environmental Protection 3900 Commonwealth Boulevard Mail Station 35 Tallahassee, Florida 32399-3000

Florida Laws (7) 120.569120.57163.3161253.141253.77373.118373.406
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BAY OAKS CIRCLE ASSOCIATION, INC. vs DEPARTMENT OF ENVIRONMENTAL PROTECTION, 99-000851 (1999)
Division of Administrative Hearings, Florida Filed:Terra Verde, Florida Feb. 23, 1999 Number: 99-000851 Latest Update: Aug. 31, 1999

The Issue The issue in the case is whether the Petitioner should be granted an environmental resource permit and authorization to use sovereign submerged lands for construction of an extension to an existing multi-family residential docking facility.

Findings Of Fact The Petitioner, Bay Oaks Circle Association, Inc., represents the 20 property owners of the Bay Oaks Circle subdivision. Bay Oaks Circle borders on Lemon Bay. Lemon Bay is a Class II Outstanding Florida Water. Lemon Bay is also an aquatic preserve and a designated state "Special Water." The Lemon Bay aquatic preserve is recognized for its water quality and resources. To protect the resources, special standards are applicable to review of permits for aquatic activities. The Petitioner's existing dock was permitted in the 1970's. The dock has four slips and extends approximately 100 to 120 feet from the shoreline into water depths of approximately one to one and a half feet at low tide. The dock attaches to the shoreline from a 45.5-foot wide easement owned by the Petitioner. There is evidence of prop dredging in the existing mooring area. The existing mooring area has little natural value as a water resource. Initially, the proposed dock was to extend another 120 feet (for a total extension of 220-240 feet) into deeper water approximately three to three and a half feet at low tide and would accommodate a mooring area for eight slips. In the area of the proposed dock, most of Lemon Bay is about three and a half feet deep at low tide. The application was subsequently amended to provide an extension of 112 feet for a total length of 199.5 feet, with six boat slips. The final proposal provided for a 104 feet long by three feet wide access walkway. Two 16 feet long by two feet wide "finger" piers would extend from the walkway. The end of the walkway would terminate in a dock platform 8 feet by 20 feet wide. The total square footage of proposed structure over water is 536 square feet. The proposed mooring areas are defined by mooring pilings place into the bay bottom. The applicant seeks a sovereign submerged land lease to permit the preemption of 2,219 square feet of submerged bottom land. Because the proposed dock exceeds 500 square feet in an Outstanding Florida Water, a standard environmental resource permit must be obtained before the proposal can be constructed. Two of the proposed mooring slips are over seagrasses. Additionally, two shallow areas located nearby contain seagrasses. Seagrasses provide the basis of the food chain in the waters. Adverse impacts to seagrass beds negatively affect marine productivity, as well as the fishing and recreational values of the waters. The proposed dock expansion poses a threat to the seagrass beds at the mooring slips and in the shallow areas near the shoreline and to the east of the proposed dock. Although the proposed dock extension does not appear to directly impede a marked navigation channel, review of the bay bottom suggests that boats currently navigate in the proposed mooring area to avoid a shallower nearby shoal. It is likely that the proposed dock expansion would result in diversion of boat traffic into the seagrassed area of the shallower waters. Section 373.414(1), Florida Statutes, sets forth the review criteria used in consideration of a permit application when the proposed activity occurs in an Outstanding Florida Water. The Petitioner offered no evidence to establish that the permitting criteria set forth at Section 373.414(1), Florida Statutes, have been met. The proposed multi-family docking facility requires issuance of a sovereign submerged land lease before the facility can be constructed. Sovereign submerged land leases are reviewed according to the size of the proposed facility and the quality of the lands to be impacted by construction and operation. Submerged land is classified according to resource quality into "Resource Protection Areas (RPA)" to permit appropriate application review. An RPA I is an area of fragile, easily-damaged marine resources such as coral beds or seagrasses, that require the highest level of protection. An RPA II is an area or seagrasses or benthic animals which, while not as fragile as an RPA I, still require substantial protection. An RPA III is an area of sand that contains fewer marine resources than an RPA I or II. The seagrassed areas near the proposed docking facility are classified as an RPA I. The areas near the proposed docking facility contain less seagrass, but have substantial evidence of benthic anumals, and are classified as RPA II. According to the parties, the Petitioner must meet a "ten to one" rule to obtain a permit. In the alternative, the Petitioner may qualify for a lease if the proposed facility does not exceed the maximum square footage permitted for a single- family dock. The ten-to-one criteria provides that the total dock structure may not preempt more than ten times the linear footage of the property owner's shoreline, in which case a lease may be issued. In this case, the shoreline is 45.5 feet, resulting in a permissible preemption of 455 square feet. In this case the applicant proposes to preempt 2,219 square feet. According to the credited testimony of the Respondent’s witness, the single-family dock methodology does not qualify the proposed dock for permitting. Although a number of hypothetical dock proposals were discussed at the hearing, the hypothetical proposals are not included in the permit application. There is no evidence that the agency gave any formal consideration to hypothetical proposals prior to the hearing. At the hearing, the Petitioner proposed that the applicable rules be waived to allow the permit and lease to be issued. Specifically, the Petitioner proposed that the permitting criteria be waived as to dock design and minimum square footage. There is no credible evidence to support waiver of applicable statutes and rules in this case.

Recommendation Based on the foregoing Findings of Fact and Conclusions of Law, it is recommended that the Department of Environmental Protection enter a final order denying the application for the proposed dock extension filed by the Bay Oaks Circle Association, Inc. DONE AND ENTERED this 16th day of July, 1999, in Tallahassee, Leon County, Florida. WILLIAM F. QUATTLEBAUM Administrative Law Judge Division of Administrative Hearings The DeSoto Building 1230 Apalachee Parkway Tallahassee, Florida 32399-3060 (850) 488-9675 SUNCOM 278-9675 Fax Filing (850) 921-6847 www.doah.state.fl.us Filed with the Clerk of the Division of Administrative Hearings this 16th day of July, 1999. COPIES FURNISHED: Barry L. Dasher Bay Oaks Circle Association, Inc. 3075 Bay Oaks Circle Englewood, Florida 34223 Francine M. Ffolkes, Attorney Department of Environmental Protection Mail Station 35 3900 Commonwealth Boulevard Tallahassee, Florida 32399-3000 Richard G. Perkins 4005 Bay Oaks Circle Englewood, Florida 34223 Kathy Carter, Agency Clerk Office of the General Counsel Department of Environmental Protection Mail Station 35 3900 Commonwealth Boulevard Tallahassee, Florida 32399-3000 F. Perry Odom, General Counsel Department of Environmental Protection Mail Station 35 3900 Commonwealth Boulevard Tallahassee, Florida 32399-3000

Florida Laws (7) 120.57253.77267.061373.414373.421373.427403.031 Florida Administrative Code (1) 18-20.004
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SECRET OAKS OWNERS ASSOCIATION, INC. vs DEPARTMENT OF ENVIRONMENTAL REGULATION, 93-000863 (1993)
Division of Administrative Hearings, Florida Filed:St. Augustine, Florida Feb. 16, 1993 Number: 93-000863 Latest Update: Sep. 08, 1993

The Issue Whether or not Petitioner should be granted a dredge and fill permit for construction of a multi-family dock in either of the two configurations proposed in its application filed pursuant to Section 403.918 Florida Statutes.

Findings Of Fact Petitioner Secret Oaks Owners' Association, Inc. is a not-for-profit Florida corporation with its principal place of business in First Cove, St. Johns County, Florida. DER is the State agency charged with the responsibility of reviewing permits under Chapter 403, Florida Statutes and its applicable rules. Martin Parlato and his wife Linda Parlato are the owners of, and reside on, Lot 10, Secret Oaks Subdivision, First Cove, St. Johns County, Florida. They have standing as Intervenors herein under the following facts as found. Petitioner claims rights to dredge and fill pursuant to an easement lying along the southerly boundary of Lot 10 in Secret Oaks Subdivision, which is a platted subdivision in St. Johns County, Florida. The easement runs up to and borders the St. Johns River, a tidal and navigable river in St. Johns County, Florida. Petitioner filed an application for dredge and fill permit with DER on September 18, 1992. The dock was proposed to be five feet wide and 620 feet long including a 20 foot by 10 foot terminal platform and six associated mooring pilings. On November 3, 1992, the Petitioner filed an alternative proposal with DER. That submission proposed construction of an "L" shaped walkway into the St. Johns River to connect the easement with an existing private dock to the north, which dock is owned by the Intervenors. The walkway is proposed to be five feet wide and may extend approximately 80 feet into the river, and then turn north and run parallel to the shoreline a distance of 41 feet to connect with the existing dock. Additionally, the existing dock would be reclassified as multi-family and four mooring pilings would be placed on the south side of the terminal platform. It is undisputed that a DER permit is necessary to construct either dock requested by Petitioner. While Petitioner sought to create an issue regarding a dock that once was located emanating from the easement and connecting with the present dock emanating from Lot 10 in a configuration similar to the Petitioner's proposed auxiliary dock configuration, the previous dock was never permitted and would be subject to DER rules and potential removal orders if it still existed, unless some "grandfathering" legislation or rule protected the structure. No such "grandfather" protections have been affirmatively demonstrated. Instead, it was orally asserted, without any corroborating circuit court orders, that after Petitioner prevailed over Intervenors in circuit court on various real property, riparian rights, and property damage issues due to Intervenors' removal of the old dock, the circuit court had conditioned further relief upon Petitioner obtaining the necessary DER permit. In its Notice of Permit Denial dated January 22, 1993, DER stated several reasons why reasonable assurances had not been given by Petitioners that water quality would not be violated and that the project was not contrary to the public interest, and further stated, by way of explaining how the permit might still be granted, that, "Compliance with Florida Administrative Code Rule 17- 312.080(1) and (2) can be achieved for either proposal by complying with the following requirements: Determine the legal status of the easement to establish ownership and control; Design a structure to provide a sufficient number of slips to accommodate all members in sufficient depth of water so that the grassbeds will not be disturbed by boating activity, or specifically limit only the area of the dock in water greater than three feet to be utilized for mooring boats or boating activity and record this action in a long-term and enforceable agreement with the Department; Obtain documentation from adjacent landowners that demonstrates they fully recognize and consent to the extent of activity which may occur in the water by either proposal (i.e., single dock or access walkway). Subsequent to the denial of Petitioner's application, Petitioner and DER representatives met and discussed DER's recommendations for reasonable assurances outlined in the Notice of Permit Denial. DER representatives have also orally recommended alternatives for hiring a dock-master or creating assigned boat slips, but DER has received no formal submissions of information from the Petitioner. All of Petitioner's and DER's proposals have not been reduced to writing. No long-term enforceable agreement as proposed by DER in the Notice of Permit Denial has been drafted. The project site is located on the eastern shore of the St. Johns River, three-quarters of a mile north of Cunningham Creek and one mile south of Julington Creek, at First Cove, a small residential community in the extreme northwest of St. Johns County, where the St. Johns River is approximately 2.5 miles wide. Located at the proposed project site are submerged grass beds (eel grass) that extend from approximately 100 feet to 450 feet into the St. Johns River in depths of two to three feet of water. The water at the proposed project site is classified as Class III Waters suitable for recreational use and fishing, but the area is not listed as an Outstanding Florida Water. The grass beds at the proposed project site are important for the conservation of fish and wildlife and the productivity of the St. Johns River. They provide detritus for support of the aquatic based food chain and they provide a unique, varied, and essential feeding and nursery habitat for aquatic organisms. They are valuable for the propagation of fish. Endangered West Indian manatees seasonally graze on the eel grass in this locale during their annual migrations. Absent the replacement of the auxiliary dock, lot owners' primary access to the larger dock is by swimming or boating from the upland of the pedestrian easement to the larger dock. This can mean sporadic interaction with the eel grass. However, DER's experts are not so much concerned with the individual and occasional usages of Petitioner's lot owners but with the type of activity common to human beings in congregate situations encouraged by multi- family docks. The proposed construction of the auxiliary dock does not intrude on the eel grass as the dock does not extend 100 feet from the upland. The grassbeds end some 200 feet east of the west end of the dock. DER experts testified that the time-limited turbidity and scouring associated with construction of either proposed configuration would have very minimal impact, but the continual increased turbidity of the water over the eel grass to be anticipated from multi-family use of either dock may detrimentally affect juvenile aquatic life and the Manatees' feeding ground. The auxiliary dock as proposed provides no facilities for docking watercraft. The permit application provides for a maximum of four facilities for docking watercraft, presumably by tying up to four end buoys. Petitioner intends or anticipates that only four boats would ever dock at one time under either configuration because of planned arrangements for them to tie up and due to an Easement and Homeowners Agreement and Declaration recorded in the public records of the county. Among other restrictions, the Agreement and Declaration limits dock use and forbids jet ski use.1 The permit application seeks a multi alternative dock construction. Petitioner intends to control the use of the dock(s) only by a "good neighbor policy" or "bringing the neighborhood conscience to bear." Such proposals are more aspirational than practical. Petitioner also cites its Secret Oaks Owners' Agreement, which only Petitioner (not DER) could enforce and which Petitioner would have to return to circuit court to enforce. Petitioner has proposed to DER that it will limit all boating and water activity to the westward fifty feet of the larger dock, prohibit all boating and water activity on the auxiliary dock, and place warning signs on the docks indicating the limits of permissible activity, but Petitioner has not demonstrated that it will provide any mechanism that would insure strict compliance with the limited use restrictions placed on the homeowners in Secret Oaks by their homeowners' restrictive covenant. Testimony was elicited on behalf of Petitioner that Petitioner has posted and will post warning signs and will agree to monitoring by DER but that employing a dock master is not contemplated by Petitioner, that creating individual assigned docking areas is not contemplated by Petitioner, and that there has been no attempt by Petitioner to draft a long term agreement with DER, enforceable by DER beyond the permit term. The purpose of the dock is to provide access to the St. Johns River for the members of the Secret Oaks Owners' Association which includes owners of all sixteen lots, their families, and social invitees. Although there are currently only three or four houses on the sixteen lots, there is the potential for sixteen families and their guests to simultaneously use any multi-family dock. Although all sixteen lot owners do not currently own or operate boats, that situation is subject to change at any time, whenever a boat owner buys a home or lot or whenever a lot owner buys a boat. All lots are subject to alienation by conveyance at any time. It is noted that this community is still developing and therefore anecdotal observations of boating inactivity among homeowners before the old dock was torn down are of little weight. No practical mechanism has been devised to limit homeowners' use of the dock(s) if a multi-family permit is issued. Also, no practical mechanism has been devised to exclude any part of the boating community at large from docking there. Thomas Wiley, a DER biologist, accepted without objection as an expert in the environmental impacts of dredge and fill activities, and Jeremy Tyler, Environmental Administrator for DER's Northeast District, also accepted without objection as an expert in environmental impacts of dredge and fill activities, each visited the site prior to formal hearing. They concurred that the application to construct the 620 foot long dock presented the potential for a number of boats to be moored or rafted at the pier at any one time, particularly weekends and holidays, and that multiple moorings might greatly exceed the capacity intended by Petitioner. Wiley and Tyler further testified, without refutation, that over-docking of boats could hinder or block the use of the waters landward of the terminal structures by adjoining property owners. Congregations of power boats at marinas and facilities designated for multi- family use also pose a threat to the endangered West Indian manatees. With regard to alternative two of the application to reconstruct the unpermitted "L" shaped walkway, such a configuration would extend 80 feet of the "mean high water line", then run 41 feet parallel to the shoreline of Lot 10 before attaching to the existing pier and that the parallel portion of the walkway lies immediately adjacent to, and inshore of, the extensive submerged grass beds. According to Wiley and Tyler, it can reasonably be expected that boaters would utilize this walkway as a convenient boat loading/off facility rather than walking to and from the terminal end of the existing 620 foot long dock. Water depths vary from two to three feet offshore of the proposed structure, and the operation of boats, jet-skis, and other watercraft would result in prop scouring of the silt/sand bottom and damage to grass bed areas, degrading water quality and adversely impacting important habitat areas. The DER experts concluded that the applicant had not provided reasonable assurances that the proposed structures would not cause hindrances to ingress and egress or the recreational use of State waters by adjacent property owners, including Intervenors at Lot 10, that grass habitat areas will not be adversely impacted or inshore water quality will not be degraded by boating and related activity. The potential for intensive use of either of the proposed docks could result in a large number of boats and/or water activity at and around the docks. Submerged grass beds occur in waters generally less than three feet deep in areas near the docks. Any boating activity landward of 450 feet from the shore could seriously damage the extensive grass beds that occur there. Boating activity is likely to occur in the areas of the grassbeds if a number of boats are using the dock(s) at the same time or if a boater desires to minimize the length of dock to be walked, in order to reach the uplands. That damage is expected to be from prop dredging and resuspension of bottom sediments onto adjacent grasses. Upon the evidence as a whole, the project is neutral as to the public health, safety, welfare, and property of others, except to the extent it impacts the Intervenors as set out above. The anticipated increase in water-based activities around the proposed dock(s) will cause shifting, erosion and souring that can be harmful to the adjacent grass beds. The anticipated increase in water based activities around the proposed dock will adversely affect marine productivity because the clarity of the water in the area of the grass beds will be decreased. The project may be either temporary or permanent but should be presumed permanent. The project does not affect any significant historical or archeological resources. The current condition of the eel grass beds in the area is lush and valuable as a fish and wildlife habitat. In the course of formal hearing, DER witnesses testified that absent any disturbance of the grassbeds, DER would have no complaints about either proposed project configuration. After considering and balancing the above criteria, it is found that Petitioner has not provided reasonable assurance that the proposed project in either form would not violate state water quality standards and that it would not be contrary to the public interest.

Recommendation Upon the foregoing findings of fact and conclusions of law, it is recommended that the permit application be denied without prejudice to future applications. RECOMMENDED this 28th day of July, 1993, at Tallahassee, Florida. ELLA JANE P. DAVIS 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 28th day of July, 1993.

Florida Laws (1) 120.57
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JAMES E. WILLIAMS vs. CHARLES R. MOELLER, JULIA MOELLER, AND DEPARTMENT OF ENVIRONMENTAL REGULATION, 86-001095 (1986)
Division of Administrative Hearings, Florida Number: 86-001095 Latest Update: Aug. 06, 1986

Findings Of Fact On March 10, 1986, Respondents, Charles R. Moeller and Julia Moeller (Applicants) entered into a consent order with Respondent, Department of Environmental Regulation (Department) pursuant to which their request for an "after the fact" permit to construct an 5-slip docking facility in Florida Bay, Upper Matecumbe Key, Monroe County, Florida, was granted. Petitioners, James E. Williams and Charles W. Causey (Protestants) filed a timely request for formal administrative review of the Department's action. The Applicants are the owners of a 2.2 acre parcel of property situated on the northwestern side of central Upper Matecumbe Key, with approximately 280' frontage on Florida Bay. Since 1983, the Applicants have sought authorization to construct a multi-family dock facility for use in conjunction with their plans to develop the uplands as a condominium community. Protestants, James E. Williams and Charles W. Causey, are neighbors of the Applicants. Mr. Williams' property abuts the north boundary of Applicants' property, and extends northerly with 230' frontage on Florida Bay. Mr. Causey's property abuts the north boundary of Mr. Williams' land, and extends northerly with 230' frontage on Florida Bay. Protestants have used, and use, the waters adjacent to their residences, the project site, and Florida Bay for fishing, swimming, boating and other recreational pursuits. Protestants have standing to maintain this action. Background On February 28, 1983, Applicants filed their first request with the Department and the Army Corps of Engineers (Corps) for authorization to construct a docking facility to serve their proposed uplands development. That application sought authorization to construct a 10-slip docking facility, roughly "L" shaped, with a main pier extending into Florida Bay in a westerly direction and measuring 90' by 5', and the terminal section of the dock running southerly parallel to the shore line and measuring 100' by 5'. A row of 11 mooring piles spaced 10' apart, 20' landward of the terminal section of the dock, formed the 10 boat slips. As proposed, the facility was less than 1,000 square feet (sq. ft.), and exempt from the Department's permitting requirements. 1/ The Corps declined, however, to permit the facility as proposed. Noting that "a mixture of lush vegetation including mixed searasses and the hard corals" was located in the 2' to 3' MLW (mean low water) docking area, the Corps requested that the Applicants extend their pier further offshore to create dockage in waters of no less than -5' MLW depth. Consistent with the Corps' request, Applicants modified their proposal by extending their pier 170' offshore. In all other respects, their proposal remained unchanged. On August 12, 1983, Applicants received Corps' approval for their modified docking facility; however, their extension of the pier increased the docks' square footage to over 1,000 sq. ft., and subjected the project to the Department's permitting requirements. Accordingly, on October 7, 1983, Applicants filed a request with the Department for authorization to construct the dock facility approved by the Corps. On November 7, 1984, the Department issued its intent to deny the requested permit predicated on its conclusion that, inter alia, degradation of local water quality was expected, as well as destruction of marine habitat and productivity to such an extent as to be contrary to the public interest. Although advised of their right to request formal administrative review of the Department's proposed action. /2 Applicants took no action. On December 13, 1984, the Department entered a final order, which adopted the reasons set forth in its notice of intent to deny, and denied the Applicants' requested permit. The current application On January 24, 1985, Applicants filed their request with the Department for authorization to construct the docking facility which is the subject matter of these proceedings. The application sought permission to construct an 8-slip 3/ docking facility of the same configuration as previously applied for, but with a main pier measuring 170' by 4', and a terminal section of 79' by 4'. A row of 9 mooring piles spaced 10' apart, 20' landward of the terminal section of the dock, formed the 8 boat slips. Applicants still proposed the same wood construction, and wood dock piles, as well as using the terminal section of the dock as a batterboard type breakwater by attaching heavy boards to the waterward side of the dock. 4/ As proposed, the dock facility was less than 1,000 sq. ft. and exempt from the Department's permitting requirements. Accordingly, on January 30, 1985, the Department issued the Applicants a copy of their application marked "EXEMPT FROM DER D/F PERMITTING PER FAC RULE 17-4.04(9)(c)," and apprised the Applicants of the need to secure approval from the Department of Natural Resources (DNR) for use of state-owned submerged lands. Applicants promptly applied for DNR approval. On February 22, 1985, they received their first completeness summary, which was responded to on April 26, 1985, and on September 4, 1985, they received their second completeness summary, which was responded to on October 15, 1985. Finally, on December 5, 1985, Applicants received DNR approval conditioned upon Applicants execution and recording of a 10' conservation easement along the shoreward extent of Applicants' property to prevent the construction of any further dock facilities. Applicants duly executed and recorded the conservation easement. On December 24, 1985, Applicants received their Monroe County building permit, and commenced construction on January 22, 1986. On January 23, 1986, Protestants contacted the Department's local environmental specialist, David Bishof, to complain of the construction. Mr. Bishof promptly telephoned the applicant, Mrs. Moeller, and advised her that the subject waters had been designated Outstanding Florida Waters (OFW), and that docks in excess of 500 sq. ft. were no longer exempt. 5/ At this point in time, only 6-8 pair of pilings had been set. Notwithstanding Mr. Bishof's advice, Applicants continued to construct the dock facility until all pilings were in place and 500 sq. ft. of the main pier area was decked. On March 10, 1986, the Department and Applicants entered into the consent order which is the subject matter of these proceedings. That order granted the Applicants an "after the fact" permit to construct their 8-slip docking facility, and granted substantially affected persons the right to petition for formal administrative review. The project site The waters of Florida Bay which abut the Applicants' 280' shoreline are classified as Class III waters and have, since May, 1985, been designated as Outstanding Florida Waters (OFW). At Applicants' shoreline, erosion has cut an escarpment into the limestone such that the land's elevation drops abruptly from approximately 1' above MH to 2'-3' below MHW. Along much of the shoreline, erosion has undercut the limestone, forming small cliffs with an overhang of up to 5'. Very little vegetation exists on the exposed edge of the solution-faced limestone which forms the Applicants shoreline. What does exist consists of a few moderate to small red and black mangrove trees. On the face of the shoreline escarpment a rich biota is found, which includes star arene, bearded periwinkles, and star coral. A narrow band of turtlegrass, with some Cuban shoalweed, is found at the base of the escarpment. At 50' from shore along the path of the proposed pier, 6/ the depth is 4+- MHW and the bottom consists of gently sloping bedrock, with a thin layer of sediment. Sparse vegetation, consisting of patches of turtlegrass and Bataphora are found at this point, along with a healthy fauna community consisting of numerous sponges and moderate sized colonies of star coral. At a distance of 100' along the proposed dock route, the bottom is covered by a thin layer of sediment which allows for a fairly constant growth of turtlegrass. Depths at this point are approximately 6' MHW. The turtlegrass bed continues to the end of the proposed dock and generally covers the entire proposed docking area. Depths in the proposed docking area range between 6'-7' MHW. Lobster frequent the area, together with fish common to the Florida Keys. Areas of concern The only permit application appraisal conducted by the Department was done in connection with the Applicants' October 7, 1983 permit request, and at a time when the waters of Florida Bay did not carry the OFW designation. At that time, the Department's environmental specialist, David Bishof, found that: The proposed dock, along with the boats moored to it, when it is complete and in use, can be expected to shade approximately 2,000 ft 2 of seafloor. Much of the area that will be shaded, is covered by seagrass. A general decline in the quantity of seagrass in the shaded areas, can be expected to result from the project. With the loss of seagrass vegetation in the marina area, will also be the loss of the functions of habitat, sediment stabilization, primary production and pollution filtration. Activities that can normally be expected to be associated with the use of the proposed dock will result in the discharge of toxic metals, hydrocarbons, organic debris, detergents and miscellaneous trash. With a dock of the size being proposed, the above discharges are expected to be moderate in magnitude, but will probably not lower water quality below class III standards. These findings were not disputed in this proceeding. Although the dock area has been reduced from 100' to 79' in length, from 5' to 4' in width, and the number of boat slips from 10 to 8, the proposed dock, with the boats moored to it, can still be expected to shade approximately 1,900 sq. ft. of seafloor. 7/ This shading effect will result in the general decline in the quantity of seagrass in the dock area, and the consequent loss of habitat, sediment stabilization, primary production, and pollution filtration. Loss of seagrass in the dock area and surrounding area will be intensified by "prop dredging" and "scaring" due to seasonal tidal fluctuations of 1-3 feet. As sited, the proposed docks are located in waters of 6'- 7' NHW depth, as opposed to the 5' NLW depth recommended by the Department and the Corps. Other environmental consequences associated with the proposed facility include the discharge of hydrocarbons, toxic metals, detergents and organic debris into the surrounding waters. Mr. Bishof described these discharges as "moderate in magnitude" in his November, 1983 appraisal and concluded that they "will probably not lower water quality below class III standards." At hearing, with Florida Bay now designated OFW, Mr. Bishof again characterized the discharges as "moderate in magnitude" and opined that OFW standards would not be violated. While Florida Bay is a vast body of water, which offers the opportunity for pollutant dilution, the waters in the area of the proposed facility are relatively shallow and lacking in strong currents; conditions- conducive to pollutant buildup. There has been no appraisal of the proposed project since November, 1983, 8/ and no substantive evidence that the hydrography of the waters in the area is adequate to control pollutant buildup. Consequently, Mr. Bishof's opinion cannot be credited. Under the circumstances, Applicants have failed to provide reasonable assurances that the proposed facility will not violate state water quality standards. Public interest In considering whether a project is clearly in the public interest, Section 403.918(2)(a), Florida Statutes establishes seven criteria which must be considered and balanced. That subsection provides: In determining whether a project is not contrary to the public interest, or is clearly in the public interest, the department shall consider and balance the following criteria: Whether the project will adversely affect the public health, safety, or welfare or the property of others; Whether the project will adversely affect the conservation of fish and wildlife, including endangered or threatened species, or their habitats; Whether the project will adversely affect navigation or the flow of water or cause harmful erosion or shoaling; Whether the project will adversely affect the fishing or recreational values or marine productivity in the vicinity of the project; Whether the project will be of a temporary or permanent nature; Whether the project will adversely affect or will enhance significant historical and archaeological resources under the provisions of s. 267.061; and The current condition and relative value of functions being performed by areas affected by the proposed activity. The proposed project was not shown to promote any of the seven criteria. It would not, however, adversely affect the public health, safety or welfare or the property of others; adversely affect navigation or the flow of water or cause harmful erosion or shoaling; or adversely affect significant historical and archaeological resources. The relative condition of the vegetation and marine life in the area was shown to be good. Overall, the project was shown to be permanent and to have an adverse impact on the conservation of fish, habitat, marine productivity and recreational values. On balance, the proposed project is not clearly in the public interest, and no evidence was presented to mitigate its adverse impacts. Cumulative impact Section 403.919, Florida Statutes, mandates that the Department consider the cumulative impact of the proposed project in deciding whether to grant or deny a permit. Currently, there are no other projects existing, under construction, or for which permits or jurisdictional determinations have been sought, nor are there any projects under review, approved or vested, within one mile of the project site. Accordingly, cumulative impact is a neutral factor in the evaluation of the proposed project.

Florida Laws (7) 120.52120.57120.68267.061376.303403.1616.03
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BARRY ROBERTS AND GLORIA MEREDITH TRUST vs JULIA FONDRIEST AND STATE OF FLORIDA DEPARTMENT OF ENVIRONMENTAL PROTECTION, 20-002473 (2020)
Division of Administrative Hearings, Florida Filed:Tallahassee, Florida May 26, 2020 Number: 20-002473 Latest Update: May 05, 2025

The Issue The issue in these consolidated proceedings is whether the proposed single-family residential dock meets the requirements for a letter of consent for use of sovereignty submerged lands pursuant to chapters 253 and 258, Florida Statutes, and Florida Administrative Code Chapters 18-20 and 18-21, such that the Consolidated Regulatory Exemption and Letter of Consent for Department of Environmental Protection File No. 0319584-003EE, as amended on September 30, 2020, should be granted.

Findings Of Fact The Parties DEP is the state agency charged with regulating specified activities in state jurisdictional surface waters, pursuant to chapter 373, part IV, Florida Statutes. Additionally, DEP is charged with performing all staff duties and functions for the Board of Trustees of the Internal Improvement Trust Fund ("Trustees" or "Board") related to the administration of state-owned lands pursuant to chapter 253, including sovereignty submerged lands in aquatic preserves, pursuant to chapter 258. In this case, DEP is responsible for reviewing the application for the dock and issuing the Dock Approval that has been challenged in these proceedings. Fondriest owns the upland property riparian to the sovereignty submerged lands on which the Dock is proposed to be, at 1953 Long Beach Drive, Big Pine Key, Florida. She is the applicant for the Dock Approval that has been challenged in these proceedings. The Trust owns the upland property located at 1975 Long Beach Drive, Big Pine Key, Florida. This property is located immediately adjacent to, and west of, Fondriest's property. DeMaria and Appel own the upland property located at 1997 Long Beach Drive, Big Pine Key. This property is located two parcels west of Fondriest's property. Appel owns two other upland properties located on Long Beach Drive, neither of which is located immediately adjacent to Fondriest's property. Crilly is the holder of a marine turtle permit issued by the Florida Fish and Wildlife Conservation Commission ("FFWCC"), and she volunteers as a sea turtle monitor for the Long Beach Drive area of Big Pine Key. History of the Dock Approval and Notice of Agency Action As stated above, on December 10, 2019, DEP issued a regulatory general permit and letter of consent to Fondriest, approving the 2019 Approval, which was then proposed as an 800-square-foot structure for use as a pier for non-motorized vessels. There was no evidence presented that Petitioners received a clear point of entry to challenge DEP's proposed agency action issued on December 10, 2019, either through receipt of written notice by mail, or constructively through publication of notice of the proposed agency action in a newspaper or other publication medium. The Trust filed a Petition for Administrative Hearing on January 30, 2020; DeMaria filed a Verified Petition for Formal Administrative Hearing on January 31, 2020; and Crilly filed a Verified Petition for Formal Administrative Hearing on February 27, 2020. On September 11, 2020, Fondriest filed a revised application with DEP, reducing the size of the Dock to 500 square feet; requesting a verification of exemption from permitting, pursuant to rule 62-330.015(5)(b) and section 403.813(1)(b)2; and requesting authorization, pursuant to chapters 253 and 258, and chapters 18-20 and 18-21, to use sovereignty submerged lands. On September 30, 2020, DEP issued Florida Department of Environmental Protection’s Notice of Proposed Changes to Agency Action—i.e., the "Dock Approval"— 2 Because the Dock will have less than 500 square feet of over-water surface area, it is exempt, pursuant to section 403.813(1)(b). from permitting under chapters 373 or 403. Petitioners have stipulated that the Dock qualifies for the permitting exemption under section 403.813(1)(b). verifying the regulatory exemption and authorizing the use of the sovereignty submerged lands by a letter of consent.3 DEP's agency action proposing to approve the Dock supersedes all prior DEP agency action with respect to the Dock, and constitutes the proposed agency action at issue in these proceedings. Long Beach Drive and the Surrounding Area Fondriest's property is located on Long Beach Drive, Big Pine Key, in Monroe County. Long Beach Drive is located on a spit of land comprising the southern and westernmost part of Big Pine Key. The south side of Long Beach Drive, where Fondriest's, the Trust's, and DeMaria's and Appel's properties are located, borders the Straits of Florida.4 Thus, Fondriest's, the Trust's, and DeMaria's and Appel's properties are riparian to sovereignty submerged lands underlying the Straits of Florida. The land along Long Beach Drive is platted and has been developed for residential and commercial uses. The Long Beach Drive area of Big Pine Key is located within the Coupon Bight Aquatic Preserve ("CBAP"), an Outstanding Florida Water and aquatic preserve consisting of approximately 6,000 acres of bays, mangrove forests, seagrass beds, and offshore patch coral reefs. The Long Beach Drive area, including Fondriest's property, is characterized by a rocky shore, with some narrow sandy beaches. The shore accumulates a significant amount of weed wrack consisting of seaweed, seagrass, and other debris. A beach berm created by wave and tide action 3 The Dock Approval states that the Dock does not qualify for the federal State Programmatic General Permit for section 404 of the Clean Water Act and section 10 of the Rivers and Harbors Act. Separate federal approval for the Dock has been issued by the Army Corps of Engineers, and Monroe County has issued a Building–Floodplain–Development Permit for the Dock. 4 All references to the shore or shoreline along Long Beach Drive refer to the shore or shoreline abutting the Straits of Florida. exists along much of the shore. The berm is frequently overtopped by water during high tides and storms. The beach is disturbed due to frequent use by residents and sea turtle monitors. Among the activities that take place on the beach are kayak launching, beach walking, beach cleaning and restoration, vegetation planting, and sea turtle nest monitoring. Several docks already exist along the shore on Long Beach Drive. The longshore current along the shore at Long Beach Drive flows, and transports sand from, east to west. The existing mangroves, jetties, and points along the Long Beach Drive shoreline trap sand and cause accretion of updrift beaches and starvation of downdrift beaches. The competent, credible evidence establishes that the docks along the shoreline on Long Beach Drive do not significantly contribute to beach accretion, starvation, or erosion in the area. The Proposed Dock The Dock is a private residential single-family dock associated with Fondriest's single-family residence at 1953 Long Beach Drive. It will not be used for commercial purposes or residential habitation, and there are no boat houses, boat lifts, or other enclosures proposed or approved as part of the Dock. As approved, the Dock will occupy 498 square feet, consisting of a 142-foot-long by 3-foot-wide access dock and a 12-foot-long by 6-foot-wide (i.e., 72-square-foot) terminal platform, and extending a total length of 154 feet. The access dock will be constructed with pressure-treated lumber planks spaced half-an-inch apart, to allow light penetration. The supporting pilings are comprised of PVC-encased aluminum, spaced approximately 9 feet, 5 inches apart. The PVC casing will help protect the piles from corrosion, thus helping to protect water quality. The terminal platform, which also will be supported by PVC-encased aluminum pilings, will consist of fiberglass grating, which allows sunlight penetration in order to prevent shading of seagrasses and other benthic resources.5 The top of the terminal platform is designed to be a minimum height of five feet above the mean high water line ("MHWL"). Handrails will be constructed along each side of the dock for its entire length, to prevent vessel mooring in adjacent shallow areas, thus helping protect against damage to benthic resources. The Dock will be used solely for the water-dependent activities of launching vessels and swimming. Only non-motorized vessels, such as kayaks, canoes, and paddleboards, may be launched from the Dock, and then only when there is a minimum depth of 0.5 feet (six inches, or half-a-foot) of water at the terminal platform.6 Additionally, the terminal platform must include signs of at least one-square- foot each placed on each side of the platform, stating "no mooring of motorized vessels allowed." A ladder is proposed to be located on one side of the terminal platform to provide access to the water for swimming or kayak launching, and the Dock Approval imposes a requirement that the ladder cannot be located over seagrass or hard bottom benthic communities. Although some turbidity in the water column may be generated by launching kayaks or other non-motorized watercraft from the terminal platform, the turbidity would be temporary and would not exceed that currently generated by dragging or hauling a kayak or other vessel from the shore across the substrate, to access sufficient water depth for launching. To prevent potential trapping, under the Dock, of sea turtles and other animals, such as Key Deer, an enclosure consisting of barriers one inch apart must be constructed beneath the portion of the Dock's landward access ramp having less than three feet of clearance above grade. 5 This is a standard construction material frequently used for docks in Florida. As further discussed below, the benthic survey performed for the area comprising the footprint of the Dock showed that no seagrass beds or other significant benthic resources are present. 6 The 0.5-foot water depth is keyed to the mean low water datum. At mean high water, the water depth at the terminal platform is approximately 1.2 feet. The competent, credible evidence establishes that the rest of the Dock will be elevated approximately five feet above the MHWL, so will be of sufficient height to allow animals to pass under without being trapped or impeded, and will provide sufficient clearance for sea turtle monitors to pass under as they traverse the beach. The competent, credible evidence also shows that the Dock will not impede the flow of water. The design is such that there are no structures on, or beneath, the Dock that will act as dams to prevent, or otherwise affect, the flow of water under and around the Dock. The water depth at the end of the terminal dock is 0.5 feet at mean low water, and 1.2 feet at mean high water. The Dock does not extend out to a depth of four feet of water. The competent, credible evidence establishes that the Dock will not interfere with navigation. The water depth between the shore and the end of the Dock's terminal platform is too shallow to accommodate motorized watercraft, and the Dock will be of sufficient height to enable persons using non-motorized watercraft to pass under it. The Dock will be constructed to meet the 2017 Southern Building Code, so will be able to resist 180-mile-per-hour, three-second wind gusts. The credible, persuasive evidence establishes that in a storm, the decking and stringers on the Dock will be washed off the pilings and will not become windborne projectiles. The Dock pilings will be imbedded into the substrate to a minimum depth of five feet, using a vibration hammer, rather than drilling and punching the pilings into the substrate. Using a vibration hammer will generate less turbidity in the water column than using the drill-and-punch installation technique, and turbidity curtains must be erected and maintained around the construction footprint to control turbidity and protect water quality. Additionally, the pilings will be installed using a spud barge elevated above the substrate, which also will help reduce turbidity during construction. Any turbidity generated during construction will be temporary. Installing the dock pilings using a vibration hammer also will generate less noise than the drill-and-punch technique. The Jacksonville Office of the National Marine Fisheries Service has issued a biological opinion stating that the vibration hammer installation technique "may affect/is not likely to affect" certain species listed as endangered, threatened, or of special concern. Additionally, because the Dock will be constructed in an open waterbody, the noise generated by piling installation is anticipated to be insignificant. Construction of the Dock may only be conducted outside of sea turtle nesting season, which runs from April 15 to October 31. Dock construction activities also must meet the requirements and standards established by the United States Fish and Wildlife Service to protect manatees, sea turtle species, the Smalltooth Sawfish, and the Eastern Indigo Snake. The 2011 Standard Manatee Construction Conditions for In-Water Work require vessels to navigate at slow speeds; manatee awareness signs to be posted; and construction to stop if a manatee is spotted within 50 feet of the construction site. In any event, manatees are unlikely to be present in the vicinity of the Dock, due to the very shallow water. The sea turtle and Smalltooth Sawfish construction conditions require vessels to operate at idle speeds in the vicinity of the project; turbidity curtains to be erected and maintained; and construction to be stopped if individuals of these species are observed within 50 feet of the construction site. The Eastern Indigo Snake, an upland species, is unlikely to be present at the Dock construction site. To prevent harm to individuals of this species, the letter of consent requires that educational materials be distributed to the construction crew and educational signs be placed at the construction site. No permanent exterior lighting is authorized for the Dock. This will prevent the Dock from attracting sea turtles and other marine species that are drawn to light. No turning basins, access channels, or wave break devices are proposed to be constructed for or used by the Dock. Fondriest's property has approximately 100 linear feet of riparian shoreline. There are no other docks existing on the shoreline along Long Beach Drive for at least 65 linear feet in either direction. The Dock will be constructed perpendicular to the shoreline, and will be located in Fondriest's riparian area, set back more than 40 feet from each riparian line demarcating her riparian area. Thus, the Dock will be located well outside the 25-foot setback from each riparian line. Biological and Other Resources in the Vicinity of the Dock Much of the shoreline along Long Beach Drive below the MHWL, including that along Fondriest's property, consists of bare, hard rock. The water is extremely shallow, and the bare rock is exposed at low tide. Site assessments conducted in 2020 at the location and in the vicinity of the Dock, show that limestone caprock, loose rubble, and some deeper depressions in the rock exist in the footprint of the Dock. The substrate consists of hard, highly uneven rock, with pools of tannin-stained water. Water pooled in the rock depressions is heated at low tide and, due to rotting vegetation, is nutrient-rich. The dissolved oxygen levels are very low, rendering the pools incapable of supporting substantial marine life other than cyanobacteria and filamentous algae, both of which indicate poor water quality. Some algae species are attached to the limestone caprock in the footprint and immediate vicinity of the Dock. However, recent biological resource assessments show that no seagrass beds, corals, or other hard bottom communities exist in the footprint of the Dock. Thus, the competent, credible evidence shows that there are no aquatic resources of any significant value in the footprint, or immediate vicinity, of the Dock. A small seagrass bed is located near the terminal platform. The letter of consent requires avoidance of this seagrass bed during construction and use of the Dock. Additionally, as discussed above, turbidity curtains must be installed to prevent turbidity and siltation of this seagrass bed during construction. The evidence establishes that the area waterward of the MHWL along Long Beach Drive generally supports a rich aquatic community. Fish and aquatic invertebrates inhabit the water in the vicinity, and numerous bird species use the area waterward of the MHWL, including that bordering Fondriest's property, as feeding and foraging habitat. However, no non-speculative evidence was presented to show that the construction, presence, and use of the Dock will result in adverse effects to this aquatic community, or to any plant or animal species in this aquatic community. Additionally, the competent, credible evidence shows that none of these resources exist in the footprint, or immediate vicinity, of the Dock, and conditions have been imposed in the letter of consent to ensure that the construction and use of the Dock will not adversely affect these resources. To the extent that the vibration hammer installation of the pilings will result in noise that may cause fish, birds, and other animals to leave the area, that effect will be temporary and will cease when piling installation is completed. Although some benthic or attached species, such as seahorses, may be unable to leave the area, so may be subjected to noise stress, no persuasive, non-speculative evidence was presented showing that these species inhabit the area in the vicinity of the Dock. Thus, any alleged harm to these species is speculative. Because the Dock may only be used for nonmotorized vessels such as kayaks and canoes, use of the Dock will not generate noise or otherwise adversely affect the aquatic habitat waterward of the MHWL along Long Beach Drive. The Key Deer is listed as an endangered species. Key Deer traverse and forage along the shore at Long Beach Drive. No credible evidence was presented showing that the Dock would adversely affect the ability of Key Deer to traverse and forage on the beach on, or adjacent to, Fondriest's property. As discussed above, the Dock will be elevated waterward of the MHWL to approximately five feet above grade. The evidence showed that this height is sufficient to allow Key Deer to pass underneath without being impeded or trapped. No credible evidence was presented showing that the three-foot wide access ramp would interfere with Key Deer foraging or traversing along the beach. The competent, credible evidence establishes that the Loggerhead Sea Turtle and Green Sea Turtle, both of which are listed as endangered species, use the beach above the MHWL along Long Beach Drive, including the beach on Fondriest's property above the MHWL, for nesting. The FFWCC has determined, through its Florida Sea Turtle Nesting Beach Monitoring Program, that the shore along Long Beach Drive has a relatively low nesting density—i.e., within the lower 25% of nesting density values—for both of these sea turtle species. The evidence establishes that the Hawksbill Sea Turtle, Kemp's Ridley Sea Turtle, and Leatherback Sea Turtle do not use the beach along the Long Beach Drive shoreline for nesting. No competent, credible evidence was presented showing that significant sea turtle food sources are present in the footprint, or immediate vicinity, of the Dock. The competent, credible evidence does not show that the Dock will adversely affect the habitat value of the beach on Fondriest's property for sea turtle nesting, or that it will otherwise adversely affect nesting sea turtles and hatchlings. As previously discussed, an enclosure will be constructed under the access ramp to prevent nesting sea turtles and hatchlings from becoming trapped under the Dock. The competent, credible evidence establishes that the Dock will not adversely affect other protected species, including the Lower Keys Marsh Rabbit, the Keys Rice Rat, or the Mole Skink—none of which inhabit or use the marine/beach habitat present along the shore at Long Beach Drive. To this point, no evidence was presented showing that these species are, or ever have been, present on the beach at Long Beach Drive. Thus, no evidence was presented showing that the Dock adversely affect these species. The Dock will be Located in a Resource Protection Area 3 Areas within aquatic preserves are classified as Resource Protection Area ("RPA") 1, 2, or 3, for purposes of imposing restrictions and conditions on the use of sovereignty submerged lands, to protect discrete areas having high quality and transitioning habitat. The RPA 1 classification applies to areas within an aquatic preserve that have resources of the highest quality and condition. Areas classified as RPA 1 are characterized by the presence of corals, marine grassbeds, mangrove swamps, salt marshes, oyster bars, threatened or endangered species habitat, colonial water bird nesting sites, and archaeological and historical sites. The RPA 3 classification applies to areas within an aquatic preserve that are characterized by the absence of any significant natural resource attributes. The RPA 2 classification applies to areas within an aquatic preserve that are in transition, either having declining RPA 1 resources, or new pioneering resources within an RPA 3. Recent biological resource assessments conducted at the location of, and in the immediate vicinity of, the Dock show that no mangrove swamps, salt marshes, oyster bars, archaeological or historical resources, or colonial water bird nesting sites are present. As discussed above, although sea turtles nest on the beach along Long Beach Drive, this area does not constitute significant sea turtle nesting habitat, and there is no significant food source for adult or juvenile sea turtles in the vicinity of the Dock. Thus, the evidence shows that the Dock will not be located in an RPA 1. The biological resource assessments also showed that no transitioning resources are present at the location, or in the vicinity, of the Dock. The competent, credible evidence showed that current natural resource conditions at the site are the same as those that historically existed before Hurricane Irma struck the Long Beach Drive area in 2013. Thus, the evidence shows that the Dock will not be located in an RPA 2. Because there are no significant natural resource attributes or transitioning resources in the footprint and the immediate vicinity of the Dock, it is determined that the Dock will be located in an RPA 3.7 7 Some portions of the CBAP do contain seagrass beds, offshore coral patch reefs, and mangrove swamp communities, and provide habitat for protected species, including the Key Deer and colonial water birds, and, thus, merit an RPA 1 classification. By contrast, none of these habitats and conditions are present at the location, or in the vicinity, of the Dock. The definitions of RPA 1, 2, and 3 in rules 18-20.003(54), (55), and (56), respectively, refer to "areas within aquatic preserves" which contain specified resources types and quality. Fla. Admin. Code R. 18-20.004(54) through (56)(emphasis added). Additionally, rule 18-20.004(1)(a) provides that in determining whether to approve or deny a request to conduct an activity in an aquatic preserve, the Trustees will evaluate each request on a "case-by-case basis." See Fla. Admin. Code R. 18-20.004(1)(a)(emphasis added). These rules make clear that determining whether an activity will be located in an RPA 1, 2, or 3 necessarily entails a site-specific resource assessment to determine the type and quality of habitat, and the conditions present, at that specific site. As discussed above, the site-specific biological assessments conducted show that the Dock will be located in an RPA 3, and Petitioners did not present any site- specific evidence to rebut that classification. Cumulative Impacts Analysis In determining whether an activity proposed in an aquatic preserve may be approved, an analysis must be performed to determine the projected cumulative impacts of the activity. This analysis focuses on determining the impact of the proposed activity, combined with that of similar existing activities and similar activities currently under consideration for approval. See Fla. Admin. Code R. 18- 20.006. A cumulative impacts analysis performed by Fondriest's expert witness, Sandra Walters, showed that the Dock, in conjunction with similar existing docks and all other applications for docks that could be proposed for approval, will not result in adverse cumulative impacts to the aquatic resources in the CBAP. Walters's cumulative impacts analysis took into account both the acreage and linear footage of parcels within the CBAP for which a dock similar to the one at issue in this proceeding could be approved for construction. In performing a cumulative impacts analysis using linear feet of shoreline, Walters calculated a total of 19,357 feet, or 22.6 miles, of shoreline in the CBAP. Of this linear footage, approximately 7,500 linear feet of shoreline along Long Beach Drive and approximately 1,200 linear feet of shoreline along the ocean side of the Cook's Island portion of the CBAP are developable, for purposes of having the potential to be developed for a minimum-sized single-family residential dock similar to that proposed in this case. Walters's estimate is conservative, in that it included, as developable linear shoreline footage, parcels that likely could not be developed due to rate of growth, conservation easement, or other land use or environmental restrictions. Walters's linear footage analysis showed that approximately 5.7% of the entire CBAP shoreline possibly could be developed for construction of a perpendicular dock. Assuming that each of these docks is four feet wide—which is a valid assumption, using the four-foot maximum access dock width permitted under the aquatic preserves rules—a total of .23% of the shoreline would be impacted if a perpendicular dock was developed on each eligible parcel. Walters opined, credibly and persuasively, that this impact to the resources in the CBAP would be de minimis. In performing a cumulative impacts analysis on an acreage basis, Walters calculated that if a minimum-size single-family residential dock were developed on each of the 68 total developable lots within the CBAP, a total area of approximately 34,000 square feet, or approximately .013% of the acreage in the CBAP, would experience impacts similar to those created by the Dock. Walter credibly and persuasively opined that this impact to the resources in the CBAP would be de minimis. Walters used a conservative approach—i.e., projecting a realistic "worst case" scenario—in performing the cumulative impacts analysis. Specifically, she considered all parcels for which a minimum-size single-family residential dock reasonably could be proposed for approval in the future, rather than limiting her consideration of cumulative impacts to only those currently proposed for approval by the listed agencies. Additionally, she included impacts of similar dock projects for parcels that likely would not qualify for dock approval due to development restrictions. Thus, the cumulative impacts that Walters projected in her analysis are likely greater than the actual cumulative impacts of similar dock projects that reasonably can be anticipated to be developed in the area in the future. Petitioners presented the testimony of Michael Czerwinski regarding the cumulative impacts analysis required under the aquatic preserves rule for approval of an activity in an aquatic preserve. Czerwinski's analysis projected the potential cumulative impacts if every parcel along Long Beach Drive were developed with a minimum-size single-family residential dock, including the parcels on which development restrictions have been imposed such that they would not be eligible to be developed for a single-family residential dock. Based on this assumption, Czerwinski opined that such "buildout" along Long Beach Drive would result in a "cascading" or "nibbling" effect on the resources in the CBAP, and that there would be adverse impacts on sea turtle nesting habitat. Additionally, based on the unsupported assumption of maximum "buildout" of a single-family residential dock on every parcel along Long Beach Drive, Czerwinski projected that the resources within the entire CBAP would be adversely affected as a result of the cumulative impacts from approval of the Dock. Czerwinski's cumulative impacts analysis did not take into account the numerous parcels in the CBAP, including several on Long Beach Drive, that are unable to be developed for single-family residential docks due to conservation easements and local land development restrictions. As such, his analysis considered impacts which could not reasonably be expected to result in the Long Beach Drive area from approval of the Dock. Additionally, based on the unreasonable assumption of maximum dock buildout on every parcel on Long Beach Drive, Czerwinski projected adverse impacts to the entire CBAP as a result of the Dock. This analysis again failed to take into account that numerous parcels within the boundaries of the CBAP that are not located in the Long Beach Drive area also are under development restrictions that will prevent the construction of docks on those parcels. Czerwinski's analysis did not comply with the provisions of rule 18-20.005(1) and (3), which expressly limit the consideration of impacts to only those likely to affect the preserve and which reasonably could be expected to result from the proposed activity. For these reasons, Czerwinski's testimony regarding cumulative impacts as a result of the Dock was not credible or persuasive. As discussed above, Monroe County has issued a permit authorizing the construction of the Dock. This evidences that the Dock is permissible under the Monroe County local comprehensive plan. Additionally, as discussed in detail below, the Dock is an allowable use that is consistent with the CBAP Management Plan ("Management Plan"). As previously discussed, the competent, credible evidence establishes that there are no significant biological resources in the footprint, or in the immediate vicinity, of the Dock. Thus, the Dock will not cause the loss of beneficial biologic functions that would adversely impact the quality or utility of the CBAP. As previously discussed, the competent, credible evidence establishes that the Dock will not cause the loss of the beneficial hydrologic functions, either in the immediate vicinity of the Dock, or in the CBAP. As discussed above, the Dock will be a minimum-size single-family residential dock that will not adversely affect the quantity or flow of water. Accordingly, it is determined that the Dock will not have adverse cumulative impacts on the CBAP. Consistency with the CBAP Management Plan The Management Plan expressly identifies single-family private residential docks as an allowable use within CBAP, and specifies the standards that such docks must meet. Specifically, a dock may not extent waterward of the MHWL more than 500 feet or 20% of the width of the waterbody; must be designed to ensure maximum light penetration; the terminal platform may not be more than 160 square feet in area; and the access dock may not be wider than four feet. As discussed above, the Dock will comply with these standards. The Management Plan also delineates "management areas" within the CBAP, and describes resources and allowable uses within the different management areas. The Management Plan states that final determinations of allowable uses within a particular management plan are made by agency staff on a case-by-case basis. The sovereignty submerged lands along Long Beach Drive, out to a distance of 500 feet from shore, are designated as "Management Area SF/1." The sovereignty submerged lands bordering Fondriest's property are included within the Management Area SF/1. The resources included in Management Area SF/1 generally include grass beds, fringing mangroves, coral banks, coral heads, and hardbottom communities. However, as discussed above, the site-specific biological resource assessment surveys conducted on the sovereignty submerged lands bordering Fondriest's property showed that none of these resources are present at, or in the vicinity of, the Dock site. Furthermore, private single-family residential docks are expressly identified as an allowable use in the Management Area SF/1. Long Beach Drive is not a pristine, undeveloped shoreline. There are residences and some commercial uses along Long Beach Drive, with accessory uses such as seawalls, revetments, and private docks. The Dock is consistent with these existing uses and with the aesthetics of the shoreline on Long Beach Drive. Based on the foregoing, it is determined that the Dock is consistent with the CBAP Management Plan.8 Petitioners' Interests and Timeliness of Crilly's Petition The Trust's Interests The Trust owns a parcel of real property located at 1975 Long Beach Drive, immediately adjacent to, and west of, Fondriest's property. Barry Roberts and Gloria Meredith are the trustees of the Trust. 8 Rule 18-20.004(7) states, in pertinent part: "[t]he aquatic preserve management plans shall be used by [DEP] to preserve and restore the distinctive characteristics identified by the inventories for each aquatic preserve. The management plans for each aquatic preserve are available for guidance purposes only." Fla. Admin. Code R. 18-20.004(7)(emphasis added). Thus, to the extent a rule provision in chapter 18-20 conflicts with an aquatic preserve management plan, the rule controls. See Decarion v. Martinez, 537 So.2d 1083, 1084 (Fla. 1st DCA 1989)(an agency must follow its own rules). Neither Roberts nor Meredith, in their individual capacity, is a petitioner in these proceedings. Meredith testified that she and Roberts purchased the property at 1975 Long Beach Drive because of its location and the natural resources in the area, including the tide pool habitat in the rock depressions along the shore, and the animals that forage along, and inhabit, the shore. Meredith testified that she and Roberts both have a keen personal interest in, and use and enjoy, the natural resources along the shore at Long Beach Drive. They engage in bird watching; nature photography; kayaking; and observing nature, including Key Deer, birds, nesting sea turtles, and fish and invertebrates inhabiting tide pools in the rock depressions along the shore. After Meredith and Roberts purchased the property, they placed it in the Trust in order to preserve it, and its value as a residential property, for their children and grandchildren to enjoy in the future. Meredith and Roberts, as trustees of the Trust, have significant concerns about the aesthetic impact the Dock will have on the Trust property, particularly its impact on the view of the beach and the sunrise over the water. Meredith expressed her personal concern regarding the Dock's impacts on the biological resources at, and in the vicinity of, the Dock, and she also expressed concern that the Dock would interfere with her ability to safely walk along the shoreline. She testified that she was concerned that approval of the Dock would constitute a precedent, resulting in the construction of more docks and piers which would adversely affect the natural resources and the beauty of the beach. Meredith conceded that the Dock will be located within Fondriest's riparian area, will be set back more than 25 feet from the common riparian line, and will not cross the common riparian line into the Trust's riparian area. DeMaria's and Appel's Interests DeMaria is an original Petitioner in Case No. 20-2474, which is part of these consolidated proceedings, and Appel has moved to intervene and become a party to that case. DeMaria and Appel own the Deer Run eco-lodge bed and breakfast ("Deer Run") located at 1997 Long Beach Drive, immediately west of the property owned by the Trust. The Deer Run property is not located immediately adjacent to Fondriest's property. Appel owns two other parcels on Long Beach Drive, neither of which is located immediately adjacent to Fondriest's property. DeMaria testified that she and Appel purchased the Deer Run property because they were attracted to the unspoiled natural environment along Long Beach Drive. Deer Run attracts guests from around the world, who are drawn to the natural environment. These guests engage in nature photography and in-water recreational activities, such as kayaking, paddle boarding, and windsurfing; and they use and enjoy the natural resources and aesthetics of the area. DeMaria and Appel both testified that the presence of a long dock in close proximity to Deer Run would interfere with the view of the water and sunrise from Deer Run, and would significantly detract from the natural beauty and aesthetics of the environment at, and in the immediate vicinity of, Deer Run. Both testified that the presence of the Dock would render Deer Run a less attractive destination for guests. DeMaria testified that the presence of the Dock would interfere with her personal view of the water and the sunrise over the water; her ability to walk along shoreline below the MHWL; and her personal use and enjoyment of the natural beauty and aesthetics of the area. DeMaria also volunteers as a sea turtle nest monitor under the authority of Crilly's marine turtle permit. She expressed concerns similar to those expressed by Crilly—specifically, that the existence of the Dock would interfere with her ability to safely traverse the shoreline below the MHWL on Long Beach Drive to perform her sea turtle monitoring activities. Appel echoed DeMaria's concerns regarding the alleged injury to Deer Run's ecotourism business as a result of the Dock. He also testified that the presence of the Dock on Fondriest's property would injure his personal use and enjoyment of the natural beauty and aesthetics of the Long Beach Drive area. Appel also serves as a volunteer sea turtle monitor, and, in connection with that activity, traverses the shoreline along Long Beach Drive. He testified that the presence of the Dock would interfere with his ability to safely traverse the shoreline below the MHWL to conduct sea turtle monitoring activities. Appel also testified regarding the potential for the Dock to be damaged in storms, resulting in flying and floating debris that may damage his properties and the natural resources in the area. Crilly's Interests and Timeliness of Petition Crilly is the holder of a marine turtle permit issued by FFWCC, authorizing her to monitor sea turtle nesting along the beach at Long Beach Drive. Other volunteer sea turtle nest monitors work with Crilly under the authority of her permit. Crilly and her team of sea turtle monitors walk the beach daily during sea turtle nesting season. Crilly's responsibilities under the marine turtle permit include monitoring sea turtle nesting and false crawls; collecting data on the number of hatchlings that emerge from each sea turtle nest; and collecting data on sea turtle nesting mortality. The data are provided to the FFWCC for use in sea turtle research. Crilly testified that the Dock will impede her ability and that of her team to safely traverse along the shore below the MHWL to perform the sea turtle monitoring duties authorized under her permit. Specifically, Crilly testified that because the property above the MHWL is private, she must walk along the shoreline below the MHWL. The rock is slippery with numerous depressions, and traversing under the Dock would be treacherous. She testified that "I personally would not crawl under a dock and, therefore, I would not ask any of my volunteers on my team to crawl under a dock." According to Crilly, if she and her sea turtle nest monitoring team are unable to traverse the shoreline where the Dock will be located, they will be required to retrace their steps to the roadway on Long Beach Drive, walk down the road to a public access point, walk down to the beach, and walk back to the Dock, significantly increasing the time and effort to conduct their sea turtle monitoring activities. Crilly testified that she "learned of" DEP's approval of the Dock on December 30, 2019. No evidence was presented regarding whether, or how, Crilly received notice of the 2019 Approval sufficient to provide a clear point of entry for purposes of commencing the time for her to challenge that proposed agency action. Crilly filed her Petition challenging the 2019 Approval on February 27, 2020. When DEP issued the Dock Approval on September 30, 2020, superseding the 2019 Approval, Crilly already had filed her Petition at DEP, and the Petition had been referred to DOAH. IX. Findings of Ultimate Fact Regarding Compliance with Applicable Rules The term "dock" is defined in chapters 18-20 and 18-21. Chapter 18-20, applicable to aquatic preserves, defines a dock as "a fixed or floating structure, including moorings, used for the purpose of berthing buoyant vessels either temporarily or indefinitely." Fla. Admin. Code R. 18-20.003(19). Chapter 18-21, which generally governs approvals to use sovereignty submerged lands, defines a dock as "a fixed or floating structure, including access walkways, terminal platforms, catwalks, mooring pilings, lifts, davits and other associated water-dependent structures, used for mooring and accessing vessels." Fla. Admin. Code R. 18-21.003(22). The Dock meets the definition of "dock" in both rules.9 As discussed above, the Dock Approval limits mooring to non-motorized vessels, and Fondriest, a riparian owner, will use the Dock to access the water for the water-dependent activities of kayaking, paddle-boarding, and other water-dependent activities such as swimming, snorkeling, and fishing, consistent with rule 18-20.004(1)(e)5. 9 The Dock is not a "pier," which is defined as "a structure in, or, or over sovereignty lands which is used by the public primarily for fishing or swimming." Fla. Admin. Code R. 18-20.003(41)(emphasis added). As discussed above, the Dock is a private single-family residential dock that will be constructed on sovereignty submerged lands waterward of Fondriest's property. It will not be open to, or used by, the public for fishing or swimming. As previously discussed, the Dock meets the 500-square-foot threshold for purposes of exemption from regulatory permitting, pursuant to section 403.813(1)(b). The evidence also establishes that the Dock is a "minimum-size" dock, as defined in rule 18-21.002(39). Specifically, the Dock's area has been reduced to the smallest size possible that will provide Fondriest reasonable access to the water for kayak launching. The Dock's reduced size also will minimize impacts to resources at, and in the vicinity of, the Dock. Thus, the Dock has been designed to minimize any adverse impacts to fish and wildlife and threatened and endangered species habitat, as required by rules 18-21.004(2)(b) and (i), and 18-21.004(7)(d). Compliance with Aquatic Preserve Management Policies, Standards, and Criteria Rule 18-20.004 establishes the policies, standards, and requirements for approval of uses of sovereignty submerged lands in aquatic preserves. As discussed above, the Dock extends a total of 154 feet waterward from the MHWL. This is substantially less than the allowable 500-foot maximum extent from the MHWL, and also is substantially less than 20% of the width of the Straits of Florida, which spans from the Florida Keys to Cuba. Thus, the Dock is consistent with rule 18-20.004(5)(a)1. The competent, credible evidence establishes that the Dock will not be located in an area of significant biological, scientific, historic, or aesthetic value. However, even if such resources were present, the Dock would not cause adverse impacts due to its specific design features and the use of best management practices during construction. As discussed above, the Dock will minimize shading by reduction of the width of the access dock from four feet to three feet; by elevation of both the access dock and the terminal platform five feet above mean high water; and by the use of light-penetrable grating for the terminal platform. The Dock is designed to ensure that vessel use will not cause harm to site- specific resources, as required by rule 18-20.004(5)(a)3. The types of vessels that may use the Dock are limited to non-motorized vessels, and the letter of consent is conditioned to allow vessel launching only when there is a minimum depth of 0.5 feet of water at the terminal platform. As previously discussed, the evidence establishes that the Dock will be located in an RPA 3. Nonetheless, the Dock will comply with design standards applicable to docks in an RPA 1 or RPA 2. Specifically, the Dock will be constructed of wooden planking less than eight inches wide, spaced half an inch apart after shrinkage; will be elevated five feet above the MHWL; and will have a terminal platform consisting of light-penetrable grating to minimize shading. As previously discussed, the terminal platform will have a total area of 72 square feet—well below the 160-square foot maximum size allowed in aquatic preserves under rule 18-20.004(5)(b)6. The Dock extends out from the shoreline to a depth of approximately -0.5 ft at mean low water. Thus, Dock meets the requirement that it may not extend out from the shoreline further than to a maximum water depth of -4 feet at mean low water. Fla. Admin. Code R. 18-20.004(5)(b)3. Consistency with Coupon Bight Aquatic Preserve Management Plan Rule 18-20.004(7), which addresses management plans for aquatic preserves, states, in pertinent part: "[t]he aquatic preserve management plans shall be used by the Department to preserve and restore the distinctive characteristics identified by the inventories for each aquatic preserve." Rule 18-20.004(3)(a) states, in pertinent part: "all proposed activities in aquatic preserves having management plans adopted by the Board must demonstrate that such activities are consistent with the management plan." For the reasons discussed in detail above, it is determined that the Dock is consistent with the Management Plan, and, thus, complies with rule 18-20.004(3)(a). Public Interest Demonstration Chapters 18-20 and 18-21 both require an analysis to determine whether an activity proposed to be conducted on sovereignty submerged lands meets an applicable public interest test. Rule 18-20.004(1)(b), the aquatic preserve rule's public interest test, states, in pertinent part: "[t]here shall be no further sale, lease or transfer of sovereignty lands except when such sale, lease or transfer is in the public interest (see subsection 18- 20.004(2), F.A.C., Public Interest Assessment Criteria)." However, with respect to private residential single-family docks, rule 18-20.004(4)(c) states, in pertinent part: "[f]or the purpose of this rule, a private, residential single-family docking facility which meets all the requirements of subsection 18-20.004(5), F.A.C., shall be deemed to meet the public interest requirements of paragraph 18-20.004(1)(b), F.A.C." Fla. Admin. Code R. 18-20.004(1)(b)(emphasis added). As discussed herein, the Dock meets all applicable requirements in rule 18- 20.004(5). Accordingly, the Dock meets the aquatic preserves public interest test in chapter 18-20. The Dock also meets the public interest test codified in chapter 18-21. Rule 18-21.003(53) defines "public interest" as "demonstrable environmental, social and economic benefits which would accrue to the public at large as a result of the proposed action, and which would clearly exceed all demonstrable environmental, social, and economic costs of the proposed action." Rule 18-21.004(1) states: "[f]or approval, all activities on sovereignty lands must be not contrary to the public interest, except for sales which must be in the public interest." Fla. Admin. Code R. 18-21.004(1)(emphasis added). In this case, the Dock provides recreational water access to the riparian owner, and, as discussed extensively, will not have any adverse impacts on sovereignty lands, aquatic resources, or listed species. Thus, it is determined that the Dock is not contrary to the public interest, as defined in chapter 18-21. Petitioners assert that the Dock is inconsistent with article X, section 11 of the Florida Constitution, which states: Sovereignty lands. – The title to lands under navigable waters, within the boundaries of the states, which have not been alienated, including beaches below mean high water lines, is held by the state, by virtue of its sovereignty, in trust for all the people. Sale of such lands may be authorized by law, but only when in the public interest. Private use of portions of such lands may be authorized by law, but only when not contrary to the public interest. Fla. Const., art. X, §11 (emphasis added). Chapters 253 and 258, and the implementing rules codified in chapters 18-20 and 18-21, authorize the use of sovereignty submerged lands for private residential single-family docks when not contrary to the public interest. As discussed above, the Dock is not contrary to the public interest under chapters 18-20 and 18-21. Thus, the use of sovereignty submerged lands for the Dock is consistent with article X, section 11 of the Florida Constitution. Petitioners raised, as a public interest concern, their ability to walk below the MHWL along the shoreline on Long Beach Drive. The evidence shows that the Dock will, within its narrow footprint, present a minor hindrance to Petitioners' ability to walk unimpeded along the shoreline below the MHWL. However, the competent, persuasive evidence established that Petitioners will be able to duck under the Dock, or walk around the end of the terminal platform, where the water is relatively shallow. Importantly, Petitioners did not cite any statutory or rule provisions affording completely unencumbered access, by the general public, to all sovereignty submerged lands.10 Cumulative Impacts Rule 18-20.006 requires that an activity proposed in an aquatic preserve be evaluated for its cumulative impact on the aquatic preserve’s natural system. As extensively discussed above, Fondriest's expert, Walters, conducted a comprehensive cumulative impacts analysis that addressed all pertinent considerations in rule 18-20.006, and she concluded that the Dock will not have any 10 A key purpose of chapters 18-20 and 18-21 is to establish standards for approval of private uses of sovereignty submerged lands which may, to a certain extent, hinder the general public's access to those sovereignty lands. See Fla. Admin. Code R. 18-21.004 ("[t]he following management policies, standards, and criteria shall be used in determining whether to approve, approve with conditions or modifications, or deny all requests for activities on sovereignty submerged lands"); and Fla. Admin. Code R. 18-20.004 ([t]he following management policies, standards, and criteria are supplemental to chapter 18-21 . . . and shall be uses in determining whether to approve, approve with conditions or modifications, or deny all requests for activities on sovereignty submerged lands in aquatic preserves.") adverse cumulative impacts on the CBAP as a whole, or on any significant biologic, hydrologic, or other resources within the CBAP. As discussed above, Walters's analysis was comprehensive; her testimony was credible and persuasive; and her conclusion that the Dock will not result in adverse cumulative impacts to the CBAP, or to any resources within the CBAP, was rule- based, and considered all pertinent factual information. Based on the foregoing, it is determined that the Dock will not cause adverse cumulative impacts to the CBAP, or to any resources within the CBAP, as required by rule 18-20.006. Minimization of Adverse Impacts to Sovereignty Submerged Lands and Resources Rule 18-21.004(2)(b) states, in pertinent part, that activities that would result in significant adverse impacts to sovereignty lands and associated resources may not be approved. As discussed above, the evidence establishes that there are no significant natural resources present at the location, or in the vicinity, of the Dock. Thus, the Dock will not have adverse impacts on such resources or on sovereignty submerged lands. Nonetheless, numerous protective measures have been imposed as conditions to the letter of consent, to minimize the potential for adverse water quality impacts and to protect aquatic resources. Based on the foregoing, it is determined that the Dock will meet the resource impact minimization requirements in rules 18-20.004(5)(a)1. and 18-21.004(2). Measures to Avoid and Minimize Adverse Impacts to Listed Species and Habitat 18-21.004(7)(e) requires that "construction, use, or operation of the structure or activity shall not adversely affect any species which is endangered, threatened[,] or of special concern, as listed in rules 68A-27.003, 68A-27.004[,] and 68A-27.005." DEP consulted with FFWCC on the Dock application, to determine its potential impacts to species listed as endangered, threatened, or of special concern. As discussed above, FFWCC provided recommendations to minimize the Dock's potential impacts to several listed species, and those recommendations have been imposed as conditions to the letter of consent. As discussed above, the Dock will implement numerous measures to ensure that construction and use will not adversely affect manatees, sea turtle species, the Smalltooth Sawfish, and the Eastern Indigo Snake. As discussed above, Key Deer forage on and traverse the shore along Long Beach Drive. The competent, credible evidence establishes that the Dock will not impose any substantial barrier to the Key Deer's use of the shore on Fondriest's property, and will not otherwise adversely affect the Key Deer. Also, as discussed above, the competent, credible evidence establishes that due to the lack of suitable habitat, other protected species, such as the Lower Keys Marsh Rabbit, Keys Rice Rat, and Florida Keys Mole Skink are unlikely to inhabit, or otherwise be present at or near, the Dock site. Thus, it is determined that the Dock will not have any adverse impacts on these species. Based on the foregoing, it is determined that the Dock will not have adverse impacts to listed species and their habitat. Riparian Rights Chapters 18-20 and 18-21 require that the riparian rights of owners of upland riparian property adjacent to an activity seeking approval to use sovereignty submerged lands be protected. Rule 18-20.004(4) states, in pertinent part: "[n]one of the provisions of this rule shall be implemented in a manner that would unreasonably infringe upon the traditional, common law and statutory riparian rights of upland property owners adjacent to sovereignty lands." Rule 18-21.004(3) states, in pertinent part: None of the provisions of this rule shall be implemented in a manner that would unreasonably infringe upon the traditional, common law riparian rights, as defined in section 253.141, F.S., of upland riparian property owners adjacent to sovereignty lands. Satisfactory evidence of sufficient upland interest is required for activities on sovereignty submerged lands riparian to the uplands. All structures and other activities must be designed and conducted in a manner that will not unreasonably restrict or infringe upon the riparian rights of adjacent upland riparian owners. [A]ll structures, including mooring pilings, breakwaters, jetties and groins, and activities must be set back a minimum of 25 feet inside the applicant's riparian line. Exceptions to the setbacks are private residential single- family docks associated with a parcel that has a shoreline frontage of less than 65 feet, where portions of such structures are located between riparian less than 65 feet apart. Pursuant to rule 18-21.003(63), "satisfactory upland interest" means owning the riparian uplands or having some other possessory or use interest, as specified in the rule. Section 253.141(1) defines riparian rights as follows: Riparian rights are those incident to land bordering upon navigable waters. They are rights of ingress, egress, boating, bathing, and fishing and such others as may be or have been defined by law. Such rights are not of a proprietary nature. They are rights inuring to the owner of the riparian land but are not owned by him or her. They are appurtenant to and are inseparable from the riparian land. The land to which the owner holds title must extend to the ordinary high watermark of the navigable water in order that riparian rights may attach. Conveyance of title to or lease of the riparian land entitles the grantee to the riparian rights running therewith whether or not mentioned in the deed or lease of the upland. Fondriest owns the upland property riparian to the sovereignty submerged lands on which the Dock is proposed to be located, and Petitioners stipulated that she has a satisfactory upland interest for purposes of rule 18-21.004(3). The Trust owns upland property bordering the Straits of Florida; thus, riparian rights inure to the Trust property, pursuant to section 253.141. As previously discussed, the evidence establishes that the Dock will be set back over 40 feet from the common riparian line between Fondriest's property and the Trust's property. To this point, Meredith acknowledged that the Dock would be set back more than 25 feet from the common riparian line, and will not intrude into the Trust's riparian area. No evidence was presented showing that the Dock would unreasonably interfere with the Trust's traditional riparian rights of navigation, boating, swimming, or fishing within its riparian area. Meredith testified that the Dock would obstruct the view of the waterbody, the shore, and the sunrise over the water, from the Trust property. She appeared to assert these interests on behalf of the Trust and herself. However, as more fully discussed below, under Florida law, the riparian right to an "unobstructed" view does not entail a view completely free of any infringement or restriction by structures or activities appurtenant to neighboring riparian properties. Rather, the right to an "unobstructed" view means that a riparian owner is entitled to a direct, unobstructed view of the channel of the waterbody and a direct means of ingress and egress to the channel. No evidence was presented that the Dock—which will be constructed perpendicular to the shoreline within Fondriest's riparian area—would obstruct the Trust's or Meredith's view of the channel of the Straits of Florida. Additionally, as previously discussed, the Trust presented no evidence to show that the presence of the Dock in Fondriest's riparian area would interfere with the Trust's direct ingress and egress to and from the channel of the Straits of Florida. Accordingly, it is determined that the Dock will not unreasonably infringe on the Trust's riparian rights. Similarly, it is determined that the Dock will not unreasonably infringe on the riparian rights incident to the Deer Run property, or to Appel's properties on Long Beach Drive. To this point, Demaria and Appel did not present any evidence showing that the Dock will obstruct their view of the channel of the Straits of Florida, either from the Deer Run property, or from Appel's properties. DeMaria and Appel also failed to present evidence showing that the Dock would interfere with direct ingress and egress to and from the channel of the Straits of Florida, either from the Deer Run property or from Appel's properties. Accordingly, it is determined that, consistent with section 253.141 and rule 18-21.004(3), the Dock will not unreasonably infringe on the riparian rights of the Trust or of DeMaria and Appel. General Requirements for Authorization to Use Sovereignty Submerged Lands As discussed above, the Dock will be constructed and used in a manner that will avoid and minimize adverse impacts to sovereignty submerged lands and resources, consistent with rule 18-21.004(7)(d). The competent, credible evidence also demonstrates that the construction and use of the Dock will not adversely affect listed species, consistent with rule 18-21.004(7)(e). As discussed above, the Dock will not unreasonably interfere with the riparian rights of the Petitioners, consistent with rule 18-21.004(7)(f). Additionally, the Dock will not constitute a navigational hazard, consistent with rule 18-21.004(7)(g). Due to the shallow water in the footprint and in the vicinity of the Dock, navigation in the area is typically by kayak or canoe. The competent, credible evidence shows that the Dock will not impede navigation of these types of vessels. Because the sandy beach areas on Long Beach Drive are in private ownership, the Dock will not interfere with the public easement for traditional uses of sandy beaches, as provided in section 161.141, Florida Statutes; thus, the Dock is consistent with rule 18-21.004(7)(h). Also, as discussed above, the Dock will be constructed, operated, and maintained solely for the water-dependent uses of launching non-motorized vessels and swimming, consistent with rule 18-21.004(7)(j).

Recommendation Based on the foregoing Findings of Fact and Conclusions of Law, it is RECOMMENDED that the Department of Environmental Protection issue a Final Order granting Respondent Julia Fondriest's application for a Letter of Consent to Use Sovereignty Submerged Lands and verifying that the Dock is exempt from the requirement to obtain a regulatory permit, pursuant to section 403.813(1)(b). DONE AND ENTERED this 18th day of February, 2021, in Tallahassee, Leon County, Florida. S CATHY M. SELLERS 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 18th day of February, 2021. COPIES FURNISHED: Julia Fondriest Doug Scheele Lifetime Dock & Lumber, Inc. 24536 Overseas Highway Summerland Key, Florida 33042 Luna E. Phillips, Esquire Gunster, Yoakley & Stewart, P.A. Suite 1400 450 East Las Olas Boulevard Fort Lauderdale, Florida 33301 Deborah K. Madden, Esquire Gunster, Yoakley & Stewart, P.A. Suite 1400 450 East Las Olas Boulevard Fort Lauderdale, Florida 33301 Paul Joseph Polito, Esquire Department of Environmental Protection Mail Stop 35 3900 Commonwealth Boulevard Tallahassee, Florida 32399 Ralf Gunars Brookes, Esquire Ralf Brookes Attorney Suite 107 1217 East Cape Coral Parkway Cape Coral, Florida 33904 Noah Valenstein, Secretary Department of Environmental Protection Douglas Building 3900 Commonwealth Boulevard Tallahassee, Florida 32399-3000

Florida Laws (14) 120.52120.536120.54120.569120.57120.68161.141163.3161253.03253.141258.36258.42258.43403.813 Florida Administrative Code (15) 18-20.00118-20.00318-20.00418-20.00618-21.00218-21.00318-21.00418-21.00518-21.005128-106.10428-106.20528-106.21762-302.30062-4.24268A-27.003 DOAH Case (9) 04-224017-097217-532819-186520-000420-007120-247320-247420-2535
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OLD PELICAN BAY III ASSOCIATION, INC. vs TERRY CARLSON AND DEPARTMENT OF ENVIRONMENTAL PROTECTION, 08-000510 (2008)
Division of Administrative Hearings, Florida Filed:Fort Myers, Florida Jan. 28, 2008 Number: 08-000510 Latest Update: Aug. 11, 2008

The Issue The issue is whether Terry Carlson's application to construct and install a single-family dock in Lee County, Florida, is exempt from the need for an Environmental Resource Permit.

Findings Of Fact Based on the evidence presented by the parties, the following findings of fact are made: On April 27, 2007, Mr. Carlson filed with the Department an application to modify a single-family dock in a man-altered waterbody in Section 13, Township 46 South, Range 23 East, Lee County (County), Florida. In geographic terms, the property is located at 18570 Deep Passage Lane, which is at the base of a peninsula which extends for around one-half mile south of Siesta Drive, a roadway that appears to be in an unincorporated area of the County between the Cities of Fort Myers and Fort Myers Beach. See Carlson Exhibits 10A and 10B. Although Respondents have not stipulated to the facts necessary to establish Petitioner's standing, that issue is not identified in the parties' Joint Prehearing Stipulation as being in dispute. Because no member of the Association testified at final hearing, the number of members in the Association, the number who operate boats and their size, and the nature and purpose of the organization are not of record.5 It can be inferred from the record at the final hearing, however, that at least one member of the Association, Mr. Kowalski, who lives at 12228 Siesta Drive, operates a boat on the affected waterway. Carlson Exhibits 10A and 10B are maps of the general area and reflect that Siesta Drive begins at an intersection with San Carlos Boulevard (also known as County Road 865) to the east and terminates a few hundred yards to the west. (County Road 865 is a major roadway which connects Fort Myers and Fort Myers Beach.) On the south side of Siesta Drive are three man- made, finger-shaped canals, which extend to the south and provide access for boaters to the Gulf of Mexico. According to one expert, the finger canals are between one-fourth and three- quarters of a mile in length. The canals run in a straight line south for perhaps two-thirds of their length, then bend slightly to the southwest at "elbows" located a few hundred feet north of their outlets. Basins are located at the northern end of each canal. The third canal is the western most of the three canals and is at issue here. Carlson Exhibit 9 (an aerial photograph) reflects that a number of single-family residences, virtually all of whom have docks, are located on both sides of two peninsulas which lie between the three canals. Mr. Carlson owns property on the southern end of the peninsula between the second and third finger canals. It can be inferred from the record that Mr. Kowalski resides in or close to the basin in the third canal. Boaters wishing to depart the third canal must travel south to the end of the canal, make a ninety-degree turn to the east, pass through a channel which lies directly south of Mr. Carlson's proposed dock, head slightly northeast for a short distance, and then make another ninety-degree turn to the south in order to gain access to a channel (directly south of the second finger canal) leading into Pelican Bay and eventually the Gulf of Mexico, approximately one mile away. Boaters entering the third finger canal would travel in a reverse direction. At the point where the dock will be constructed, the channel appears to be around two-hundred fifty feet wide (from the applicant's shoreline to a cluster of mangrove trees to the south), but much of the channel, as well as the three canals themselves, have a soft bottom consisting of sand and silt, which limits the speed and accessibility of vessels. The original application requested authorization to construct a floating dock anchored by concrete pilings at the southern end of the finger canal in front of Mr. Carlson's property. (The proposed dock replaces an older wooden dock which has now been removed.) That application represented that the dock is private and less than 1,000 square feet; it is not located in Outstanding Florida Waters; it will be used for recreational, noncommercial activities associated with the mooring or storage of boats and boat paraphernalia; it is the sole dock constructed pursuant to the requested exemption as measured along the shoreline for a minimum distance of sixty- five feet; no dredging or filling will occur except that which is necessary to install the pilings necessary to secure the dock in place; and based upon the depth of the water shown in accompanying documents and the dock's location, the dock will not substantially impede the flow of water or create a navigational hazard. These representations, if true, qualify the dock for an exemption from permitting by the Department. See § 403.813(2)(b), Fla. Stat.6; Fla. Admin. Code R. 40E- 4.051(3)(b)1.-4. Based upon the information supplied in Mr. Carlson's application, Mark R. Miller, Submerged Lands and Environmental Resource Program Manager in the Department's South District Office (Fort Myers), issued a letter on May 8, 2007, advising Mr. Carlson that his application qualified for an exemption from Department permitting requirements and that the letter was his "authorization to use state owned submerged land (if applicable) for the construction of [his] project." After receiving the Department's first letter, Mr. Carlson elected not to publish notice of the Department's decision or provide notice by certified mail to any third parties.7 Therefore, third parties were not barred from challenging the Department's decision until after they received actual notice. The parties no longer dispute that after the Association received actual notice of the construction activities, it filed a request for a hearing within twenty-one days, or on December 26, 2007. Therefore, the request for a hearing is deemed to be timely. Section 403.813(2)(b)3., Florida Statutes, and Florida Administrative Code Rule 40E-4.051(3)(b)3. are identical in wording and provide that in order to qualify for an exemption, a dock "[s]hall not substantially impede the flow of water or create a navigation hazard." In its Petition, the Association contended that this requirement had not been satisfied. It also contended that the documents used in support of the initial application may not be valid. In the parties' Joint Prehearing Stipulation, the Association clarified this objection by contending that the exemption may have expired because site conditions have materially changed from those initially reviewed by the Department. This allegation is presumably based on the fact that during the course of this proceeding, Respondent submitted two revisions to its original construction plans. Sometime after the first letter was issued, new information came to light and on May 16, 2008, Mr. Miller issued a Revised Letter which stated that the Department had "determined that the proposed project as described in the above referenced application . . . does not involve the use of sovereignty submerged lands[,]" and that "no further authorization will be required from the Submerged lands and Environmental Resources Program." See Department Exhibit 2, which is a disclaimer for the relevant waters issued by the Board of Trustees of the Internal Improvement Trust Fund. The effect of the disclaimer was to render Florida Administrative Code Rule Chapter 18-21 inapplicable to this proceeding. By the time the Revised Letter had been issued, the original application had been revised twice, the last occurring sometime prior to the issuance of the Revised Letter. Among other things, the size of the dock has been increased to 997 square feet, and the dock will be placed nineteen feet landward and westward (or twenty-five feet east of Mr. Carlson's western property boundary) of the initial dock design for the purpose of improving navigation and creating less of an inconvenience to other boaters. The dock will now be located twenty-five feet from the seawall and is approximately seventy feet long and eight feet, five inches wide. A gangplank and floating platforms provide a walkway from the seawall to the proposed dock. On the western edge of the dock, running perpendicular to the seawall, will be pilings that will accommodate a boat lift for one of Mr. Carlson's boats. (The record reflects that Mr. Carlson intends to moor a forty-eight-foot Viking with a width of approximately sixteen feet, six inches, on the outside of the dock, parallel to the seawall, while a second boat will be stored in the boat lift.) A floating platform is located seaward of the main dock to allow access to the boat on the boat lift. After reviewing these changes, Mr. Miller reaffirmed his earlier determination and concluded that all criteria had still been met. In conjunction with the initial application, a Specific Purpose Survey of the channel dimensions was prepared by a professional surveyor, Mr. Timothy Mann, which reflects the bottom elevations of the channel in front of Mr. Carlson's property. The bottom elevations were calculated by taking manual and electronic readings using the national geodetic vertical datum (NGVD) of 1929. This method is accepted in the surveying and mapping industry to calculate bottom elevations. The survey was signed and sealed by Mr. Mann. The updated applications relied upon the same survey. In calculating the water depth, Mr. Mann subtracted the mean low tide in the Pelican Bay area from the bottom elevation survey. Mean low tide is an elevation of the average low tide over a nineteen year period. Mr. Mann obtained these average low tide records from the State. Mean low tide for the Pelican Bay area was determined to be approximately -0.5 NGVD. Therefore, if Mr. Mann's survey showed a depth of -7.77 feet, the water depth would be -7.27 feet. The survey reflects that there is at least a sixty-foot wide area beyond the proposed dock with depths at mean low water of between four and five feet. See Carlson Exhibits 7A and 7B. The mean low water survey adds further justification for the Department's determination because it is not required by the Department, and applicants do not normally submit one. It should be noted that although the Department has no rule for how deep a channel needs to be, a three-foot depth is typically used. To satisfy the navigation concern raised by Petitioner, Mr. Carlson engaged the services of two long-time licensed boat captains, both of whom were accepted as experts. Besides reviewing the dock design, on May 13, 2008, Captain Joe Verdino navigated the entire length of the third finger canal using a thirty-foot boat with a five-foot beam and twenty-four inch draft. The boat was equipped with a GPS sonar calibrated at the hull of the craft to verify the depth of the water shown in the Specific Purpose Survey. Based upon his measurements, Captain Verdino determined that there is at least another sixty feet beyond the proposed dock for other vessels to safely travel through the channel and that vessels with a draft of four to five feet would be able to safely navigate the area. Therefore, he concluded that a fifty-five-foot boat with a sixteen to eighteen-foot beam could safely navigate on the channel. Even though the measurements were taken when the canal was closer to high tide than low tide, the witness stated that this consideration would not alter his conclusions. He further opined that wind is not a major factor in this area because the channel is "well-guarded" by Fort Myers Beach, which essentially serves as a large barrier island to the southwest. He discounted the possibility of navigational concerns during nighttime hours since boats have lights for night travel. Significantly, he noted that the tightest navigable area in the third canal is at an elbow located several hundred feet north of Mr. Carlson's property, where a dock extends into the canal at the bend. Therefore, if vessels could navigate through a narrower passageway further north on the canal, then vessels would have no difficulty navigating safely in front of Mr. Carlson's proposed dock. After reviewing the plans for the proposed dock, Captain Michael Bailey also navigated the third canal and concluded that the canal can be safely traversed by a fifty-two- foot boat. This is the largest boat presently moored on the third canal. After Mr. Carlson's dock is constructed, he opined that there is at least "fifty plus" feet and probably sixty feet of width for other boats to navigate the channel, even if a forty-eight-foot boat is moored at Mr. Carlson's dock. In reaching these conclusions, Captain Bailey used a PVC pipe and staked out depths in the channel beyond the proposed dock to verify the figures reflected in the Specific Purpose Survey. PVC pipes provide the most accurate measurement of the actual distance from the water's surface to the bottom of the channel. Like Captain Verdino, he noted that the narrowest point on the canal was at the elbow several hundred feet north of the proposed dock where boats must navigate between a private dock on one side and mangrove trees on the other. Captain Bailey discounted the possibility of navigational hazards during nighttime hours since a prudent mariner always travels slowly and would not enter a finger canal at nighttime unless he had lights on the boat. Mr. Mark Miller also deemed the navigation issue to be satisfied. He did so after reviewing the Specific Purpose Survey, the aerial photograph, the location of the dock, the results of a site inspection, and other dock applications for that area that had been filed with his office. Based upon all of this information, Mr. Miller concluded that there is an approximate sixty-foot distance to the south, southeast, and southwest beyond Mr. Carlson's dock before the waters turn shallow (less than four to five feet deep), and that the dock would not pose a navigational hazard. In response to Petitioner's contention that the third set of drawings was not signed and sealed by a professional surveyor, Mr. Miller clarified that drawings for dock applications do not have to be signed and sealed. (The third set of drawings was based on the first set submitted to the Department, and which was signed and sealed by a professional surveyor.) He also responded to an objection that the Department's review did not take into account the size of the boat that Mr. Carlson intended to dock at his facility. As to this concern, Mr. Miller pointed out that the Department's inquiry is restricted to the installation of the dock only, and not the size of the boat that the owner may intend to use. Finally, even though the County requires that a building permit be secured before the dock can be constructed, and has its own standards, that issue is not a statutory or rule concern in the Department's exemption process.8 Petitioner further alleged that site conditions have materially changed since the original application was filed and that the exemption determination should automatically expire. (This allegation parrots boilerplate language used in the Rights of Affected Parties portion of the Department's two letters.) As to this contention, the evidence shows that the applicant revised its dock plans twice after its initial submission. The Association does not contend that it was unaware of these changes or that it did not have sufficient time to respond to them prior to final hearing. The third (and final) revision is attached to Respondents' Joint Exhibit 2 (the Revised Letter) and indicates that the dock will be 997 square feet, which is larger than that originally proposed, but is still "1000 square feet or less of surface area," which is within the size limitation allowed by the rule and statute. It will also be further west and closer to Mr. Carlson's seawall. These revisions do not constitute a substantial change in site conditions, as contemplated by the Department in its exemption process. In order to have materially changed site conditions, Mr. Miller explained that there must be an event such as a hurricane that substantially alters the nature of the channel. Therefore, there is no basis to find that a material change in site conditions has occurred and that the original determination of exemption, as revised, should automatically expire. Petitioner presented the testimony of Captain Marcus Carson, a licensed boat captain, who moved to the Fort Myers area in 2000. He noted that the three canals (known as "the three finger area") have always been a "little hazardous" and because of this he cautioned that only residents familiar with the waters should use them. On May 12, 2008, he accompanied Mr. Kowalski on a "brief trip" in Mr. Kowalski's boat up and down the third canal. Using a dock pole to measure depths, he found the deepest areas of the channel below Mr. Carlson's home to be between 4.6 and 5.0 feet. However, he conceded that a dock pole is not as accurate as a PVC pipe, which Captain Bailey used to take the same type of measurements. Based upon the first set of plans, which he used in formulating his opinions, Captain Carson criticized the dock as being "out of place," "overbearing," and not aesthetically pleasing. He also opined that once the dock is constructed, the channel would be too small for two fifty-foot boats to pass through the channel at the same time. However, these conclusions are based upon the assumption that the original dock plans and pilings would be used. The witness agreed that if the original plans have been modified, as they have, and the dock moved further west and closer to the seawall, he would have to reevaluate his opinions.

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 determining that Mr. Carlson's project is exempt from its permitting requirements. DONE AND ENTERED this 27th day of June, 2008, in Tallahassee, Leon County, Florida. S DONALD R. ALEXANDER Administrative Law Judge Division of Administrative Hearings The DeSoto Building 1230 Apalachee Parkway Tallahassee, Florida 32399-3060 (850) 488-9675 SUNCOM 278-9675 Fax Filing (850) 921-6847 www.doah.state.fl.us Filed with the Clerk of the Division of Administrative Hearings this 27th day of June, 2008.

Florida Laws (3) 120.569120.57403.813 Florida Administrative Code (1) 40E-4.051
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