Findings Of Fact Respondent Carter is the owner of real property located at 102 Hummingbird Lane, Crescent City, Putnam County, Florida, ("The Property") The Property has a shore length of 68.5 feet on Crescent Lake. Crescent Lake is a "water of the state" as defined in Section 403.031, F.S. The agency, now DEP, is the state agency charged with environmental concerns and permission to use submerged state lands. There are two types of authorization an applicant must receive in order to construct a dock on state owned submerged lands. The first is regulatory, which addresses issues concerning environmental impacts. The second is proprietary, which addresses issues concerning use of state owned submerged lands. Mr. and Mrs. Hageman, Petitioners herein, own property adjacent on the east of Mr. Carter's property. 1/ They have a 240 foot dock in place going out into Crescent Lake. Mr. Carter's westerly neighbor also has a shorter dock going into the lake. The Carters purchased the Property from an estate, with the announced intention to erect their own dock for water recreational purposes. Before closing the sale, they were warned off the property by Mr. Hageman who claimed his riparian rights would be violated if any dock were built on the Property. After inquiries to DEP and the Army Corps of Engineers, the Carters purchased The Property anyway. DEP has no jurisdiction to regulate docks under 1000 square feet. Mr. Carter received DEP Exemption 542504222 to construct a dock under 1000 square feet on The Property. Mr. Carter constructed a single family private use dock, including a boat shelter, extending from The Property into Crescent Lake. The dock was built approximately 35 feet from Hagemans' property line, straight out into the water, and 25 feet from the property line of his neighbor on the other side. This placed the Carter dock roughly perpendicular to the approximate center of Mr. Carter's shoreline. Petitioners conceded that Mr. Carter honored his westerly neighbor's property line, but asserted that he should have, and had not, honored his easterly property line, the line dividing his and Petitioners' property, waterward beyond the shoreline. In all, Petitioners Hageman have filed three formal petitions against the Carter dock. See Findings of Fact 16, 18, and 33, infra. All three petitions herein oppose the Carter dock as constructed upon a theory that it crosses Petitioner's riparian rights line and therefore violates the setback criteria found in Rule 18-21.004(3)(d) F.A.C.; that it blocks a channel exclusive to Petitioners' use and poses an impediment to navigation of all boats, particularly Petitioners' sailboat; that its boat shelter is enclosed contrary to rule; that it does not meet the ten-to-one rule; and that it blocks Petitioners' view and lowers their property value. The Hagemans initially filed a complaint with the DEP in regard to the dock. In response to the Hagemans' complaint, Steven Biemiller, an environmental specialist in the dredge and fill compliance/enforcement section of DEP's northeast district, and John Hendricks of the Army Corps of Engineers visited the Property on July 25, 1994. They found that the Carter dock as built exceeded 1,000 square feet in surface area. It was, however, consistent in length, width, and alignment with other docks in the area, including Petitioners' dock. Mr. Biemiller calculated Carter's dock to be 1,400 square feet. It therefore exceeded the state exemption criteria and required a state permit. Mr. Carter had constructed his dock without a valid permit from the state agency, and DEP responded by issuing him a warning letter. Carter and DEP thereafter entered into Consent Order O.C.G. 94-2443 to address the unpermitted dock construction. Testifying as an expert in the agency's enforcement and compliance procedures, Mr. Biemiller established that negotiated consent orders of this type are a standard agency procedure to resolve minor permitting violations. His testimony is accepted on that issue and to the effect that the purpose of all consent orders, including the one at issue here, is to return the non-complying structure to compliance with the applicable state rules and statutes. The consent order provides, in pertinent part, that Mr. Carter will (a) pay the agency $300.00, which amount includes a $200.00 civil penalty and $100.00 for agency costs and expenses; AND (b) reduce the size of his dock to under 1,000 square feet or obtain an after-the-fact permit whereby the agency would authorize the 1400 square foot dock to remain in place as already constructed. The Hagemans timely filed a petition challenging the consent order. The consent order herein addressed DEP's environmental concerns by jump-starting the permit process through which the agency could examine the environmental impacts posed by the dock project. In Mr. Biemiller's expert opinion, this consent order accomplished the agency's statutory and regulatory goals at that point because Mr. Carter paid his fine and applied for a dredge and fill permit. Agency permit 542558842 was issued to Mr. Carter on November 16, 1994. It approved the proposed project and authorized construction of a private use dock having a 4.75-foot wide plus 230-foot long access walkway, a 10.3-foot wide and 20.3-foot long covered boat shelter, plus an 8.5-foot long and 12.8-foot wide waterward "L" platform, within Crescent Lake, Putnam County. The Hagemans timely filed a petition challenging the permit. The Hagemans' concerns about the Carter dock and boat shelter blocking their view and diminishing their property value were raised by their petitions, but no evidence or argument was presented on the latter issue. "View" and market value concerns are not addressed by the jurisdiction or authority conferred upon DEP by either statute or rule, and may not be considered here. In determining whether or not to issue dredge and fill permits, the agency examines a project's impact on water quality, its biological impacts, whether the project is contrary to the public interest and how it impacts, if at all, on wetlands. The agency does not look at riparian rights. Those rights are addressed, if at all, by agency review of applications for consents of use and the rules applicable thereto. Thomas Wiley was the field inspector for the dredge and fill permit which is at issue. He visited Mr. Carter's property with another agency employee, Erica Robbins, to conduct a site assessment. Mr. Wiley prepared the Permit Application Appraisal. Mr. Wiley has a Bachelor of Science degree in environmental biology and twelve hours towards his Masters degree in the same discipline. He has been employed by the agency for four and a half years as a environmental specialist. During that time, he has reviewed approximately 300 dredge and fill applications. He was accepted as an expert in the agency's environmental resource permitting procedures and the impacts of dredging and filling projects on wetlands. Mr. Wiley recommended issuance of the permit in part based on his determination that the long term adverse impacts of the Carter dock on water quality are minimal and that the long term adverse impacts of the project on submerged resources also are minimal. His expert opinion on these issues is accepted, as is his unrefuted mixed fact and opinion testimony that the project site contains submerged beds of eelgrass (vallisnaria). These eelgrass beds end approximately 20 feet landward of the Carter boat shelter and dock. Carter's boat shelter and dock do not pose a significant impact to the eelgrass and will not adversely affect the conservation of fish and wildlife. The Carter boat shelter has one almost closed side, one side which descends to about one and a half feet above the water and two open ends. It is not substantially different from other local boat shelters. There are water hyacinths in the same area as the eelgrass and nearer to the shoreline. DEP has issued a permit to Mr. Hageman to clear such water hyacinths from a 25-foot swath in front of his property so as to keep clear the channel to his dock and boat shelter. The greater weight of the credible evidence is that Mr. Hageman has been zealous in his removal of water hyacinths and has exceeded the 25-foot limitation. Existence of this permit allowing Mr. Hageman to remove hyacinths and existence of this larger cleared swath of water/shoreline is not dependable evidence of the Hagemans' riparian rights claim and does not alter or affect DEP's determination that no aquatic plants will be seriously endangered by the Carter dock and boat shelter. The parties stipulated that the construction of Carter's dock has not, and will not, degrade the water quality of Crescent Lake and that the water quality standards set forth in Chapter 62-302 F.A.C., are not violated because of the construction of the dock. The parties stipulated that the Carter dock as constructed will not adversely affect the fishing or recreational value or marine productivity on Crescent Lake. The parties stipulated that the dock as constructed will not adversely affect any historical or archaeological resources under the provisions of Section 267.061 F.S. In determining whether a dock poses a navigational impediment, DEP looks for the presence of marked navigational channels and the proximity of the dock to other docks in the area. The credible competent evidence as a whole shows that the Carter dock is similar to the Hagemans' dock and is located about 100 feet west of the Hagemans' dock. The Carter structure also conforms with the prevailing alignment of all docks in the immediate area and its distance from neighboring structures is sufficient so that the Carter dock will not present a hindrance to navigation. The greater weight of the credible evidence is that the Hagemans have sailed in and out from their adjacent dock without any obvious problems occasioned by the Carter dock. There is plenty of room between the Carter and Hageman docks so that the Carter dock has not so far obstructed the Hagemans' ability to navigate their sailboat. Mr. Carter has provided reasonable assurances that his dock is not contrary to the public interest under Section 373.414 (1)(a) F.S. In determining the cumulative impacts a project may have, the agency looks at the total impact of past, present and future projects on water quality and function in wetland systems. Mr. Wiley determined it is reasonable to expect other lakefront property owners will construct docks into the lake, but based on his experience and expertise, he concluded that Mr. Carter's project's long-term impact still will continue to be minimal. The permit is appropriate and insures compliance with all applicable statutory and rule guidelines for dredge and fill permits. Mr. Carter also applied to the agency for a consent of use for submerged state lands. This was appropriate because Crescent Lake is a "water of the state". A consent of use is generally a letter of authorization for minor projects, such as single family docks, bulkheads and dredging that occur on state owned land and submerged land. The ten-to-one ratio found in Rule 18- 21.005(1)(a)2 F.A.C. allows an applicant to have ten square feet of preempted area for every linear foot of the shoreline that he owns. If an applicant meets the rule criteria, he is issued a consent of use. Generally, if an applicant exceeds the criteria, he would be issued a lease, as opposed to a consent of use. The agency issued a consent of use to Mr. Carter on December 5, 1994. The Hagemans filed a petition challenging the consent of use. DEP acts as staff for the Board of Trustees of the Internal Improvement Trust Fund. The authority to issue consents of use has been delegated to a planning manager. In the instant situation, that planning manager was Russell Price. Russell Price is employed by DEP as planning manager of the submerged land section and has served in that capacity for two years. Mr. Price holds a Bachelor of Science degree in biology, has a year of education towards his Master's degree in biology, and has reviewed approximately two to three hundred applications for consents of use. Mr. Price was accepted as an expert in state lands determination and regulation. In issuing the consent of use to Mr. Carter, Mr. Price relied on his education, training and experience in state lands regulation, and considered the application, the drawings, the agency's regulatory permit section's field report, comments from staff of the Army Corps of Engineers and a memorandum from the agency's Bureau of Surveying and Mapping. See Finding of Fact 40. Mr. Price opined, on behalf of the agency's interpretation of its own statute and rules, that the agency does not uniformly require a lease where the ten-to-one rule is minimally exceeded; that the agency will issue a consent of use if the applicant's structure is still relatively small and is configured in the minimum way possible to obtain access at reasonable water depths; that in its discretion, the agency does not apply the ten-to-one rule to require leases; 2/ and that consents of use are issued to single docks that are the minimum length necessary to reach reasonable access to navigable waters. Mr. Price issued the consent of use in this case after determining that Mr. Carter's dock as constructed was a single family dock configured in the minimum size and length necessary to achieve reasonable access to navigable waters and that the nearshore area located adjacent to Mr. Carter's upland property required that his dock exceed the ten-to-one ratio in order to access reasonable water depths for navigation. In so doing, Mr. Price relied on the DEP Permit Application Appraisal measurement of the water depth at the end of Carter's dock as 4.5 feet deep and analyzed the configuration and angle of the other docks in the area. This was in accord with the specific language of Rule 18-21.005(1)(a)1 F.A.C. 3/ Evidence adduced at formal hearing suggests that there has been some erosion, possibly due to the removal of the water hyacinths and that shows that it is environmentally desirable to avoid recreational contact with the eelgrass, especially by boats. These factors also support the reasonableness of Carter's dock configuration, even though it minimally exceeds the ten-to-one rule. Petitioners Hageman contended that their riparian rights may be determined by projecting a line straight waterward from the upland fence line between their lot and Mr. Carter's property. If that is the appropriate determination of their riparian rights, then the Carter dock does cross that projected line, but that projected line has not been placed by a surveyor or determined by a court of competent jurisdiction. At best, there has been a post erected by Mr. Hageman as the result of a prior lawsuit concerning easements. Respondent Carter's property is narrower than Petitioners' property and somewhat wedge-shaped. Petitioners assert that because the lake curves, Mr. Carter's riparian rights form a narrow pie slice-shaped area in the water. However, without a legal determination to that effect, there is only the foregoing unsupported assertion concerning either landowner's riparian rights. Although the agency's rules require a 25-foot setback of a dock (10- foot setback for marginal docks) from the applicant's riparian rights line, 4/ the agency does not measure the setback of a dock by that rule unless there has already been a determination of a riparian rights line by a court of law. DEP witnesses clearly enunciated and explicated agency policy that DEP does not affirmatively take it upon itself to determine riparian rights as between private land owners because the agency has no constitutional or statutory jurisdiction to do so. To Mr. Price's knowledge, the agency has never determined the riparian rights line of two private property owners. The agency relies on circuit courts to resolve those types of disputes. In response to the Hagemans' concerns about encroachment on their asserted riparian rights and in an abundance of caution, Mr. Price sent aerial photographs, the county plat map, and the drawings submitted with Mr. Carter's application to the DEP's Bureau of Surveying and Mapping. He requested that the Bureau make a guesstimation of the common riparian rights line based on a methodology it has developed for estimating riparian rights lines. The memorandum constitutes little more than legal research discussing various methodologies courts have used in the past for determining riparian rights. It reaches no definite conclusion with regard to the riparian rights between the Hagemans and Carter. Beyond explaining and supplementing the direct evidence of the agency policy to rely on courts to determine riparian rights, its contents and conclusions are unreliable hearsay which is outside the parameters of Section 120.58(1)(a) F.S., because no one connected with the preparation of that report testified at formal hearing. No reliable determination of the riparian rights line dividing the Petitioners' property and the property of Applicant/Respondent Carter was presented as evidence at formal hearing. DEP is not aware that any court determination specifically setting out the boundaries of the parties' riparian rights exists. DEP did not require Mr. Carter to institute a lawsuit to establish riparian boundaries before considering his application. This also appears to be common agency procedure. The agency addressed the absence of a clear showing of riparian rights and implemented its policy directed thereto in the standard language of the consent of use, which provided in pertinent part, as follows: 2. Grantee agrees that all title and interest to all lands lying below the historical mean high water line or ordinary high water line are vested in the Board, and shall make no claim of title or interest in said lands by reason of the occupancy or use thereof * * * 5. Grantee agrees to indeminity, defend and hold harmless the Board and the State of Florida from all claims, actions, lawsuits and demands arising out of this consent. * * * 12. In the event that any part of the structure(s) consented to herein is determined by a final adjudication issued by a court of competent jurisdiction to encroach on or interfere with adjacent riparian rights, Grantee agrees to either obtain written consent for the offending structure from the affected riparian owner or to remove the interference or encroachment within 60 days from the date of the adjudication. Failure to comply shall constitute a material breach of this consent and shall be grounds for its immediate termination.
Recommendation Upon the foregoing findings of fact and conclusions of law, it is RECOMMENDED That the Department of Environmental Protection enter a final order that dismisses the three petitions, ratifies the consent order, and issues the after- the-fact permit and consent of use with the safeguards already contained therein to protect the Petitioners' riparian rights in case the Petitioners hereafter obtain a circuit court determination of those riparian rights. DONE and RECOMMENDED this 7th day of July, 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 7th day of July, 1995
The Issue The ultimate issue in this proceeding is whether the Department should issue a permit to the Applicant. In its request for hearing, Petitioner asserted that the proposed dock extension would constitute a navigational hazard and would cause certain adverse environmental consequences. At the hearing, Petitioner withdrew its contentions as to adverse environmental consequences. The only issues raised during the course of the hearing relate to whether the proposed dock extension will result in navigational hazards to adjoining property owners.
Findings Of Fact The Applicant owns a lot which includes 52 feet of frontage along a cove which is located to the south of the Fort Pierce Inlet. Applicant presently has a dock which extends 85 feet out from his shoreline. The dock is 4 feet wide and has an 8-foot by 14-foot platform at the end, forming an "L" shape. The Applicant presently uses the dock for two of his own boats. Additionally, he rents four or five additional docking spaces. The Applicant is proposing to extend his dock an additional 72 feet out from his property. He proposes to remove the existing platform and place a 12-foot by 24-foot platform at the end of the extended dock, maintaining the "L" configuration. The Applicant has had problems mooring his own commercial fishing boat at his present dock due to shallow depths at low-water periods. He proposes to utilize the dock extension to moor one of his own boats in a deeper area and to moor a commercial fishing boat which is owned by his son. The platform at the end of the extended dock would be used for fishing by the Applicant and his family and guests. When completed, the Applicant's present dock and proposed addition would extend 157 feet northward from the Applicant's property. There is space for two boats to be moored on the east of the present dock. Applicant does not propose to allow the mooring of additional boats on the east side of the extension. Docking would be expressly prohibited on that portion of the proposed dock. The Petitioner, 1010 Seaway Drive, Inc., owns land immediately to the east of the Applicant's property. The Petitioner's property includes approximately 118 feet of water frontage. The Petitioner operates a commercial marina on its property. Petitioner has a dock which extends considerably farther to the north than the Applicant's present dock and also considerably farther than the Applicant's dock with the proposed extension. Petitioner contends that permitting the proposed extension would result in a navigational hazard for boats that are moored at Petitioner's dock. This contention is not supported by the evidence. There is more than 25 feet between the proposed extension of the Applicant's dock and any structure connected with Petitioner's dock. The closest structures are mooring poles, not the dock itself. The Applicant's dock as proposed for extension will continue to allow boats ample ingress and egress to Petitioner's dock. If the mooring and docking of boats were permitted on the east side of the Applicant's proposed extension, however, a significant navigational hazard would result. The property immediately adjacent to the Applicant's property to the west is owned by the Books. The Books' property includes 40 feet of water frontage. The Books presently moor their boat at a small dock which runs along their shoreline. The proposed extension of the Applicant's dock would require the Books to exercise more caution in docking their boat, but it would not significantly interfere with their ingress and egress. The 24-foot platform at the end of the proposed extension could cause some problems. The Applicant, however, has indicated his willingness to shorten the platform to 14 feet. Thus shortened, the proposed extension and platform will cause no significant interference with the Books' ingress and egress. Furthermore, the Books are left with adequate room to build a dock in the future.
Recommendation Based upon the foregoing Findings of Fact and Conclusions of Law, it is, hereby, RECOMMENDED: That the Department of Environmental Regulation issue a permit for the Applicant, Robert R. Phifer, to construct an addition to his existing dock in accordance with his application. The permit should contain all of the specific conditions included in the Department's letter of intent issued October 15, 1982. In addition, the platform at the end of the proposed extension should be reduced from 24 feet to 14 feet in length. RECOMMENDED this 29th day of April, 1983, in Tallahassee, Florida. G. STEVEN PFEIFFER Assistant Director Division of Administrative Hearings The Oakland Building 2009 Apalachee Parkway Tallahassee, Florida 32301 (904) 488-9675 Filed with the Clerk of the Division of Administrative Hearings this 29th day of April, 1983. COPIES FURNISHED: Ross A. McVoy, Esquire Madigan, Parker, Gatlin, Swedmark & Skelding Post Office Box 669 Tallahassee, Florida 32302 Alfred J. Malefatto, Esquire Department of Environmental Regulation 2600 Blair Stone Road Tallahassee, Florida 32301 Mr. Robert R. Phifer 1006 Seaway Drive Fort Pierce, Florida 33449 Ms. Victoria Tschinkel Secretary Department of Environmental Regulation 2600 Blair Stone Road Tallahassee, Florida 32301 Kevin X. Crowley, Esquire Department of Natural Resources 3900 Commonwealth Blvd., Suite 1300 Tallahassee, Florida 32303
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.
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
Findings Of Fact Petitioner is the owner of real property known as Lot 6, Block 10, Angler's Park, in Key Largo, Florida. He purchased that property in November of 1986. Petitioner's property is contiguous to sovereign submerged lands in Largo Sound, a sound of the Atlantic Ocean. The Board of Trustees of the Internal Improvement Trust Fund of the State of Florida holds title to submerged lands waterward of the mean high water line contiguous to Petitioner's property. The submerged lands contiguous to Petitioner's property lie within the boundaries of John Pennekamp Coral Reef State Park. The Board of Trustees dedicated the submerged lands contiguous to what is now Petitioner's property to the Florida Board of Parks and Historical Memorials, now the Division of Recreation and Parks of the Department of Natural Resources, on September 21, 1967. A dock existed on the submerged lands contiguous to Petitioner's property prior to 1967. The entire dock existed at least by 1938. The historic dock was probably one of the oldest docks in Largo Sound. Due to the passage of time and hurricanes, only the pilings and a concrete pad near shore still existed as of 1967. The dock was not rebuilt until 1988. Throughout the years, boats were moored at the dock. After the planking on the dock no longer existed, people still moored their boats to individual pilings. The dock was considered an excellent location for fishing, and people travelled by boat to the location, tying their boats to the pilings to fish. When Petitioner purchased his property, the only structures left on the contiguous submerged lands were thirteen concrete pilings and the concrete pad near shore. Only four of the pilings were sticking up out of the water. The remaining pilings were submerged. The original configuration of the historic dock was easily ascertained by the pilings and concrete pad. After Petitioner purchased his property, he began constructing a residence. He would travel from elsewhere in the Key Largo area by boat, would tie his boat to one of the pilings, and would wade ashore. Petitioner applied to Monroe County for a permit to rebuild portions of the dock. Although Monroe County accepted and retained his permit application fee, he was not issued a permit. Instead, he was told that he should contact the people at Pennekamp State Park. Petitioner then contacted Respondent's employees at Pennekamp State Park about reconstructing portions of the dock. In response to that inquiry Petitioner received a letter dated June 10, 1987, advising him that Respondent was not a permitting agency. That letter further recited two of Respondent's rules prohibiting the removal or destruction of natural features and marine life and construction activities in that state park. Having been frustrated by his attempts to obtain a permit to rebuild the dock from both Monroe County and from Respondent's employees at Pennekamp State Park, Petitioner made no further effort to obtain a permit or authorization from any other state, local, or federal government agency to reconstruct his dock. One day he backed a pickup truck to the edge of the water, hooked up, and raised the closest piling up in the air. Utilizing the existing pilings and adding additional ones, Petitioner rebuilt the dock "going a step at a time." In the course of his rebuilding the dock, Petitioner replaced the wooden decking and fasteners, replaced the wooden stringers and fasteners, added seven new concrete pilings, raised and repositioned several existing concrete pilings, and poured concrete footings for the new pilings. He completed rebuilding the dock in 1989. During the almost one year that he was rebuilding the dock, he worked in plain view of employees of local and state agencies. He was easily observed by the Coast Guard, the Marine Patrol, and the Park Service boats travelling to and through the Marvin D. Adams Waterway located approximately seventy-five feet from his property. No one told Petitioner to stop his construction activities. When it was completed, his dock was 12 feet wide and 84 feet long, 28 feet shorter than the historic dock. Petitioner's entire dock consists of 1018 square feet. Petitioner's dock is in the same location as the historic dock. Petitioner's dock is a private dock, used only by him when he moors his boat there occasionally. In re-building his dock, Petitioner extended it to a distance so that the water depth at the end of Petitioner's dock is four feet mean low water. Additionally, Petitioner left an open space of one to two inches between each plank on the deck so that sunlight could penetrate between the deck planking the entire distance of the dock. Pilings are an integral part of a dock. In 1988 Respondent began conducting a survey of private docks, commercial marinas, and fills, both authorized and unauthorized, within the boundaries of Pennekamp State Park as those boundaries were extended in 1967 to Key Largo. The survey was to be utilized in developing a policy regarding structures within the extended park boundaries. Petitioner's dock was included in that survey. The information which Respondent transmitted to the Governor and Cabinet regarding Petitioner's dock was that it was not authorized, that it was built in 1990, and that the water depth at the mooring area, considered by Respondent to be the terminal end of the dock, was two feet. Respondent did not advise the Governor and Cabinet that a dock had been in existence at Petitioner's property prior to 1967 and as far back as at least 1938, that the concrete pad and thirteen pilings from the historic dock still existed, or that Petitioner had rebuilt the dock in the same location, but shorter, than the historic dock. Further, Respondent did not advise the Governor and Cabinet that its water depth measurement of two feet was not taken at the waterward end of the dock, the way such a measurement is normally done. Respondent did advise the Governor and Cabinet that the access channel to the dock was four feet deep. On April 12, 1990, the Governor and Cabinet, sitting as the head of Respondent, approved a policy regarding development encroachments in Pennekamp State Park. The portion of that policy which relates to private docks provides as follows: Private docks must (1) be in existence prior to 1967 within state park waters to receive authorized structure status; (2) all docks within state park waters legally authorized by the Department of Natural Resources or the Board of Trustees during or after 1967 receive status as authorized structures; (3) that all other private docks in existence since 1967 within state park waters that are not legally authorized by Department of Natural Resources or the Board of Trustees have been evaluated on a case-by-case basis, taking into consideration any authorization issued by state and federal environmental agencies and, using the Florida Keys Marina and Dock Siting Policies and Criteria - 18-21.0041 Florida Administrative Code, as a guideline for reviewing environmental impact on marine communities, designate the structure as either authorized or require removal or modification; and (4) that no future authorizations will be issued for the construction of new private docks in state park waters. Respondent subsequently notified Petitioner that his dock fell into category (3), that it had been evaluated on an individual basis using the Florida Keys Marina and Dock Siting Policies and Criteria, that his dock had an impact on marine communities because it exceeded the size and dimension requirements and did not meet the water depth requirements, and that Petitioner's dock needed to be "modified." Respondent further advised Petitioner that the modifications required included reconstructing his dock to a T-shaped structure rather than Petitioner's rectangular-shaped structure. The new structure would be required to have a four-foot wide walkway with a terminal platform of no more than 160 square feet. Further, Respondent's proposed dock would also extend an additional 28 feet further into Largo Sound than Petitioner's dock. Respondent also required that Petitioner install permanent handrails along the dock in order to convert it to only a swimming/fishing pier, and the mooring of any water craft to the structure would be prohibited. Petitioner has not so modified his dock. There are algae, sea grasses, sponges, coral, and other vegetation and marine life beneath and adjacent to Petitioner's dock, constituting a marine community. Shading has an adverse impact on the growth of sea grasses and marine vegetation. Where shading exists under Petitioner's dock, the submerged land under the dock is nearly barren. However, Petitioner rebuilt the dock in a manner so as to reduce the effect of shading. The dock is 41 inches above water at high tide. The spacing between planks on the deck also allows sunlight to penetrate the water below Petitioner's dock. An underwater videotape of the area beneath and around Petitioner's dock reveals an extensive marine life habitat and nursery. The pilings which have been under water for such a long time have an extensive buildup of sponges and coral which, in turn, provide a habitat for an enormous number of fish. Spiny Florida lobsters live under Petitioner's dock, as do mangrove snapper, barracuda, porkfish, damselfish, reef fish, sea cucumbers, and urchins. In effect, Petitioner has created an artificial reef. Some of the barren areas beneath Petitioner's dock are a result of the halo effect, i.e., the crustaceans and fish living under the dock and in the sponges and soft corals on the pilings only graze so far from their homes in order to avoid predators. This halo effect can also be seen around the free-standing pilings outside of Petitioner's dock area. Even if the planking on Petitioner's dock were removed, the sea grasses would not grow back around the pilings since the grazing organisms would still be present. Although there may be less shading beneath Respondent's proposed dock than exists underneath Petitioner's dock, substantial damage to the marine community beneath Petitioner's dock would be caused by the removal of Petitioner's dock and the building of a new one. It is not clear that the long- term effect of Respondent's proposed dock would have less adverse impact than Petitioner's dock. It is likely, however, that the removal of the present dock, with or without the subsequent construction of Respondent's proposed dock, would have a substantial adverse effect on the healthy marine community now existing beneath and around Petitioner's dock.
Recommendation Based upon the foregoing Findings of Fact and Conclusions of Law, it is RECOMMENDED that a Final Order be entered giving Petitioner's dock authorized structure status. DONE and ENTERED this 10th day of February, 1992, 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 10th day of February, 1992. APPENDIX TO RECOMMENDED ORDER Petitioner's proposed findings of fact numbered 1-3 and 5-7 have been adopted either verbatim or in substance in this Recommended Order. Petitioner's proposed findings of fact numbered 4 and 9 have been rejected as unnecessary for determination of the issues involved herein. Petitioner's proposed findings of fact numbered 8 and 10-19 have been rejected as not constituting findings of fact but rather as constituting conclusions of law, argument of counsel, or recitation of the testimony. Respondent's proposed findings of fact numbered 2-7, 9-13, 16-18, 20, 21, 26-31, 33, 36, and 37 have adopted either verbatim or in substance in this Recommended Order. Respondent's proposed findings of fact numbered 1, 8, 14, 15, 25, 35, 40, and 41 have been rejected as being unnecessary for determination of the issues herein. Respondent's proposed findings of fact numbered 22-24 have been rejected as not constituting findings of fact but rather as constituting conclusions of law, argument of counsel, or recitation of the testimony. Respondent's proposed finding of fact numbered 19 has been rejected as being irrelevant to the issues herein. Respondent's proposed findings of fact numbered 32, 34, 38, 39, and 42-44 have been rejected as not being supported by the weight of the evidence in this case. COPIES FURNISHED: James H. Burgess, Jr., Esquire Syprett, Meshad, Resnick & Lieb, P.A. Post Office Box 1238 Sarasota, Florida 34230-1238 Suzanne B. Brantley, Esquire Department of Natural Resources Mail Station 35 3900 Commonwealth Boulevard Tallahassee, FL 32399-3000 Don E. Duden Acting Executive Director Department of Natural Resources Mail Station 10 3900 Commonwealth Boulevard Tallahassee, FL 32399-3000 Ken Plante, General Counsel Department of Natural Resources Mail Station 10 3900 Commonwealth Boulevard Tallahassee, FL 32399-3000
The Issue The issue in this case is whether Rule 18-20.004(5)(a)1, Florida Administrative Code, is an invalid exercise of delegated legislative authority.
Findings Of Fact 1. Rule 18-20.004(5)(a)1 provides: All docking facilities, whether for private residential single-family docks, private residential multi-slip docks, or commercial, industrial, or other revenue generating/income-related docks or public docks or piers, shall be subject to the following standards and criteria: no dock shall extend waterward of the mean or ordinary high water line more than 500 feet or 20 percent of the width of the waterbody at that particular location whichever is less; * * * Pursuant to stipulation, Petitioner has standing, a dock, and upland access to his property. The parties also stipulated that Petitioner's dock is limited by the 500-foot criterion, as the proposed dock extension would not exceed 20 percent of the width of the waterbody. Petitioner's upland property consists of a single family residence and is located adjacent to sovereign submerged lands located in the Gasparilla Island/Charlotte Harbor Aquatic Preserve. He has lawfully constructed a dock extending about 500 feet from the mean high water mark and into the waters of Charlotte Harbor. The consent of use granted Petitioner acknowledges the relative shallowness of the water adjacent to his property and correspondingly limits the draft of vessels to be moored to the dock. At mean low tide, the depth of the water at the end of Petitioner's dock is about two feet. Petitioner requested authorization to extend his dock waterward another 100 feet. On December 15, 1993, Respondents denied the request, in reliance upon the challenged rule and Section 258.42(3)(e)1, which allows the erection in an aquatic preserve of private residential docks for "reasonable ingress and egress of riparian owners." In a separate administrative proceeding, DOAH Case No. 94-2140, Petitioner is contesting the denial of his request to extend the dock. No single family docks in aquatic preserves extend over 500 feet into the water. In Charlotte Harbor, the average length of a single-family residential dock is 200 feet. Nearby Petitioner's dock is a 600-foot long public fishing pier, which was constructed before the subject 500-foot rule was promulgated. From mean high water waterward, the first habitat surrounding Petitioner's dock is an intertidal sand flat that extends about 100-150 waterward from shore. The next habitat is mostly unvegetated submerged bottom with patches of submerged aquatic vegetation that extends from the end of the intertidal sand flat to about 350-400 feet from shore. The vegetation of the latter habitat is mostly Cuban shoal grass, which occurs in no more than four patches of about 50 square feet, in an area measuring 25 feet in both directions from the dock. Last, extending from 350-400 feet waterward to the end of the dock, is a largely unvegetated area with sporadic pieces of attached algae. Unvegetated bottoms play no role in the propagation of fish or wildlife. The biological or scientific value of unvegetated bottoms is unaffected by a dock, although there is some evidence that toxic substances may leach from the construction materials and adversely impact nearby vegetation. However, the dredging caused by boat propellers scouring any form of submerged bottom suspends sediment that can be carried to areas of vegetated bottom, where the increase in turbidity may reduce the penetration of sunlight and thereby harm the aquatic vegetation. In the vicinity of Petitioner's dock, though, there is no evidence of significant prop dredging from recreational boating. The absence of submerged vegetation is more likely a feature of the high-energy shoreline where wave energy disrupts sediments and provides unsuitable habitat. In promulgating the predecessor to Rule 18- 20.004(5)(a)1, the Board of Trustees of the Internal Improvement Trust Fund attempted to balance interests that sometimes are competing, such as environmental, aesthetic, recreational, and private commercial. There was some concern that previously authorized docks in sovereign submerged lands had infringed upon the riparian access of adjacent upland owners. The 500-foot limitation was not in the original rule, which was promulgated in 1981, but was added by an amendment in 1985. The Board of Trustees of the Internal Improvement Trust Fund tried to set thresholds that would not result in the denial of more than a negligible number of dock applications, based on historic dock application data and predominant vessel lengths of under 27 feet. However, the record does not explain how the Board of Trustees of the Internal Improvement Trust Fund analyzed the above-described data so as to arrive at the 500-foot limitation now under challenge. Without providing more detail concerning the data and analysis, it is possible that a limitation of 100 feet or 900 feet would have satisfied the considerations stated in the preceding paragraph. Shallow water predominates in the aquatic preserves, and Board of Trustees of the Internal Improvement Trust Fund realized that a dock extending no more than 500 feet might not reach water depths that are readily navigable. The Board of Trustees of the Internal Improvement Trust Fund could not rationally adopt a rule to ensure minimum water depths for all docks, and chose the 500-foot limitation evidently to provide an easy-to-administer standard.
The Issue Whether the finger pier portion of Respondent Raab's dock creates a navigational hazard. The resolution of that issue will determine whether the dock qualifies for an exemption from an environmental resource permit under Rule 40E-4.051(3)(b), Florida Administrative Code, and Section 403.813, Florida Statutes.
Findings Of Fact DEP has the authority to regulate the construction of docks in jurisdictional wetlands and other waters of the State of Florida and on state submerged lands under Chapters 253, 373, and 403, Florida Statutes, and Chapters 62-330 (which adopts Chapter 40E-4) and 18-21, Florida Administrative Code. The Association is a residential community located in Sewall's Point, Martin County, Florida. All lots within the community abut navigable channels which provide ingress and egress to the ICW. These channels converge so that there is only one channel that connects to the ICW. Most of the residents of the community have large vessels that routinely navigate the channels within the community. At the time of the formal hearing, many of the vessels owned by residents of the community had drafts of four feet and at least two had drafts of five feet. In 1997, Mr. Raab purchased a residence in the Association that is located very close to where the channel meets the ICW. Because of that location, practically all residents of the Association have to pass in front of Mr. Raab's property when going into or returning from the ICW. The property at issue is located at 22 Simara Street, Sewalls Point, Martin County, Florida. The dock at issue in this proceeding is subject to DEP's regulatory authority. When Mr. Raab purchased this property in 1997, there was an existing marginal dock parallel to the bulk-head. Mr. Raab subsequently sought and received approval from DEP to demolish the existing marginal dock and replace it with a virtually identical structure. The existence and configuration of the marginal dock is not at issue in this proceeding. Mr. Raab thereafter sought to modify his approved marginal dock by adding a finger pier which extended into the channel 36 feet so he could dock his vessel perpendicular to the bulkhead. Mr. Raab's plan also called for the construction of two pilings 12 feet from the end of the finger pier. Mr. Raab had, as of the time of the formal hearing, re-constructed the marginal dock and had constructed the finger pier. 3/ The two additional pilings had not been constructed at the time of the formal hearing. After reviewing the modified project, DEP determined that the project was exempt from the need for an environmental resource permit under Rule 40E-4.051(3)(b), Florida Administrative Code, and Section 403.813, Florida Statutes. DEP also authorized Mr. Raab to use state-owned submerged lands if necessary. The Association thereafter timely challenged DEP's determination that the finger pier portion of the project (and the two additional pilings) did not require an environmental resource permit. There was a conflict in the evidence as to the functional width of the channel in front of Mr. Raab's property. 4/ Mr. Holly testified on behalf of the Association that the functional width of the channel was 83 feet. Mr. Lidberg, testifying on behalf of Mr. Raab, testified that the functional width was 101 feet. This conflict is resolved by finding that the functional width of the channel in front of the Raab property is 101 feet. 5/ The prevailing winds in the area in front of Mr. Raabb's dock blow into the dock. The depth of the water in the channels is influenced by tides. The principal reason Mr. Raab wants the finger pier is so that he can moor his boat with the bow to the prevailing winds in times of high winds. At the time of the formal hearing, Mr. Raab owned a vessel with an overall length of 44 feet. There was a conflict in the evidence as to whether Mr. Raab's finger pier and the two pilings that have been authorized, but not constructed, constitute a hazard to navigation. 6/ Based on the totality of the evidence, it is found that these structures do not create a navigational hazard. 7/
Recommendation Based on the foregoing Findings of Fact and Conclusions of Law, it is RECOMMENDED that DEP enter a final order dismissing the Association's challenge to the determination that Mr. Raab's project qualifies for an exemption from an environmental resource permit. DONE AND ENTERED this 1st day of March, 2000, in Tallahassee, Leon County, Florida. CLAUDE B. ARRINGTON 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 1st day of March, 2000.
The Issue The issue is whether the applicants-respondents Floyd and Alice Melton have provided reasonable assurances that their proposed dock meets the requirements of Chapter 403, Florida Statutes (1989) and Chapter 17, Florida Administrative Code, for issuance of a dredge and fill permit. Only four issues of disputed fact are raised by the pleadings in these cases: (1) whether the project will adversely affect navigation as that term is used in Section 403.918(2)(a)3., Florida Statutes; (2) whether the project will adversely affect recreational values in the vicinity of the project, in the context of the public interest test of Section 403.918(2)(a)4., Florida Statutes; (3) whether an increased number of boats at the proposed dock would cause "pollution" which would violate water quality criteria promulgated by the Department, and (4) whether the pilings will harm seagrasses in the vicinity of the dock.
Findings Of Fact An 85' dock perpendicular to the shoreline of the Meltons' property at Lot 4, Block 2, Buccaneer Point Estates, Key Largo, was in existence in 1988, some portion of which was apparently constructed without the benefit of a dredge and fill permit. On October 20, 1988, Floyd Melton applied to the Department (hereinafter "DER") for an after-the-fact permit for a 48' x 20' section, as an addition to a previously existing structure. After DER received the Meltons' permit application, an agency field inspector visited the site to determine whether the Meltons' proposed project could be constructed in conformance with Chapter 403, Florida Statutes, including the "public interest" tests at Section 403.918(2), and the "Keys Rule," Rule 17-312.420, Florida Administrative Code. The project site is located in Class III, Outstanding Florida Waters. The relevant factual determinations that DER personnel had to make at the Melton site, to ascertain compliance with the Keys Rule, were (a) the water depths, and (b) the presence or absence of seagrass communities in the proposed boat mooring area. The proposed 90' dock would have terminated over seagrass community in less than 5' of water depth. DER informed the Meltons, on February 9, 19890, that the permit would be denied unless they redesigned the dock to extend a distance of 275' out from the shore (289' total length), to where a water depth of 5' existed, limited the dock to a 4' width, and elevated the access walkway 6 feet above mean high water, to prohibit mooring along it and to increase light penetration underneath the dock. The Meltons amended their permit application to so comply. There are seagrasses under the entire length of the proposed dock. There are dense seagrass communities at the terminus of the proposed dock, surrounded by less dense seagrass communities. Under the boat currently moored near the terminus of the Meltons' uncompleted dock, there is a dense seagrass bed that is not adversely affected by the presence of the boat, which is moored in 5' of water. There is a "halo" of denuded bottom extending 4-6 inches around each piling, and occasional gouges that extend beyond the halo, which features are an ordinary and expected effect of driving pilings into the sea bed. Petitioners' expert's uncontroverted testimony is that 10 pilings placed in the dense seagrass bed at the end of the proposed dock would have no effect on the viability of that seagrass bed, while 100 pilings "would definitely damage" its viability. The survey introduced by the Meltons shows six pilings where the terminal platform is to be constructed, and three more offshore pilings for mooring purposes, for a total of nine. Other existing mooring pilings shown in the survey, landward of the proposed terminal platform, are to be removed in accordance with the permit. The water depth at the end of the Meltons' existing 85' dock is between 3.0' and 3.25', which is comparable to other existing docks in the area. Fast boats, such as water-skiing boats and one-person watercraft, operating in shallow water over a seagrass bed can damage seagrasses by "prop scarring" or by stirring up sediments. At another dock in the area, where the water depth is 3.75' at the dock's terminus, there is evidence of damage to seagrass beds by such prop-scarring. The water depth at the end of Petitioner Traurig's dock is only 1.67' to 2.0', necessitating very careful boat operation to prevent damage to seagrasses. The stipulated modification to the permit allowing three mooring pilings and requiring mooring waterward of the terminal platform clarifies DER's understanding that boats would only be moored on the waterward side of the terminal platform. No more than one or two boats can reasonably be moored at the facility. That is no more than could have been moored at the previous dock; in fact, it is equivalent to the two moored at Petitioner Traurig's dock. The environmental impact of the proposed Melton dock would be far less than that of the other docks along this shoreline, primarily because it causes boats to be operated and moored in deeper water. Neither the proposed project, nor the one or two boats that can be expected to moor at the terminal platform, will have any adverse effect on Florida Bay or the seagrass communities in the immediate vicinity. The entire area of Florida Bay except for the shoreline area where the Melton and other docks in the vicinity are located is open for navigation. It is between 0.4 and 0.5 miles from the end of the proposed dock to the nearest navigation channel. The proposed dock is not a hazard to navigation in that nearest channel, the Intracoastal Waterway. It is, however, an inconvenience and can present a hazard to unwary nighttime recreational users in the waters next to the shoreline where the Melton, Clarke, and Traurig docks are located. Petitioners' witnesses' testimony focused on how the Melton dock would force them to change their usual paths while recreating in the area, or traveling to and from nearby docks. Water-skiers and "knee-towers" have had to modify the route they used to take when water-skiing or knee-towing past the Melton property, now that much of the dock is in place. Some boat operators, Petitioners' witnesses included, continue to operate their boats so close to the Melton dock that near- collisions take place. A sailor chose to forego landing his catamaran at a dock near the Melton dock because its presence would have given him "a hard time getting out." Youngsters on "hydoslides" and "wet bikes," and in small boats, have passed landward of the outermost pilings of the uncompleted Melton dock, literally going under the structure, on several occasions. One neighbor witnessed three nighttime collisions with the uncompleted Melton dock by boaters, each of which ended when the boaters extricated themselves from the pilings. Traurig's tenant next door to the Meltons, when traveling to and from her dock, complained that "you can't go straight out anymore. You have to go out and then around. You have to be cautious..." Petitioner Traurig stated that the Melton dock would "almost cause her to jump out of her unpowered sailboat and tow it into her dock," as it would limit her ability to tack in the close confines created by the new dock. Petitioner Charles Clarke, whose property is separated from the Meltons by Petitioner Traurig's property, stated that the proposed dock is "an obstacle essentially to navigation and enjoyment of that waterway as I used it...," and that he is prevented from tacking into his dock by the presence of the Meltons' dock. Buccaneer Point is full of docks. The neighboring docks are generally approximately 100' long, while the Meltons' dock that DER proposes to permit will be 289' long, with mooring pilings and a boat extending this facility between 300' and 310' offshore. Boaters will be required to avoid this dock while recreating in the area, and while travelling to and from nearby docks. The proposed dock will discourage boaters and water- skiers from traveling through the very shallow waters off the ends of the other docks in the vicinity, potentially injuring themselves and the benthic communities. The Melton dock will not cross over the riparian lines of the Melton property. The project is clearly in the public interest by preventing ongoing adverse impacts of the existing dock, allowing the recolonization of habitat in those disturbed areas, and by extending the dock to prevent the destruction of the bay bottom. This is accomplished by elevating the dock to 6' and restricting its width to 4' in order to allow better sunlight penetration below the dock. This is also accomplished by prohibiting the mooring of vessels other than seaward of the terminus platform, thereby keeping vessels in deeper water to prevent additional destruction of the seagrass beds throughout the area. During the course of the final hearing, the Meltons and DER entered into several stipulations which will promote the absence of impact to the seagrass community. They have agreed that the following conditions will be made part of any permit issued by DER: The dock structure will be modified so that it is T-shaped rather than L-shaped. The terminal platform and access walkway will be of the dimensions contained in DER's "intent to issue." The access walkway can intersect the terminal platform at any point along the platform's 40' length. There will be 3 mooring pilings placed seaward of the terminal platform. The permit will restrict the mooring of vessels to the seaward side of the terminal platform. The Meltons will remove the 3 mooring pilings located to the right of the dock and 2 of the 4 pilings located to the left of the dock. The Meltons will not use a water-based barge in less than 2' of water in connection with the dock construction or driving or removing the pilings.
Recommendation Based upon the foregoing Findings of Fact and Conclusions of Law, it is RECOMMENDED that a Final Order be entered granting the Meltons' application for a dredge and fill permit, conditioned upon the stipulations and the mitigative recommendation set forth in this Recommended Order. DONE AND ORDERED in Tallahassee, Leon County, Florida, this 16 day of October, 1990. LINDA H. 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 16 day of October, 1990. APPENDIX TO RECOMMENDED ORDER DOAH CASE NOS. 89-6051 and 89-6135 Petitioners' proposed findings of fact numbered 2, 3, 6, 7, 22d, 22g, 22j, and 22r have been adopted either verbatim or in substance in this Recommended Order. Petitioners' proposed findings of fact numbered 1, 22f, 22h, 22i, and 22n- 22q have been rejected as not being supported by the weight of the evidence in this cause. Petitioners' proposed findings of fact numbered 4, 5, 19, 22a, 22c, 22e, 22i, 22k, and 22m have been rejected as being unnecessary for determination of the issues in this cause. Petitioners' proposed findings of fact numbered 8-18, 20, 21, 22b, 22s, and 22t have been rejected as not constituting findings of fact but rather as constituting recitation of the testimony, argument of counsel, or conclusions of law. The Department's proposed findings of fact numbered 1, 2, 6, 8-10, 12, 14, 15, 17, 19-23, and 26 have been adopted either verbatim or in substance in this Recommended Order. The Department's proposed finding of fact numbered 3 has been rejected as not being supported by the weight of the evidence in this cause. The Department's proposed findings of fact numbered 4, 5, and 25 have been rejected as not constituting findings of fact but rather as constituting recitation of the testimony, argument of counsel, or conclusions of law. The Department's proposed findings of fact numbered 7, 11, 13, 16, 18, and 24 have been rejected as being unnecessary for determination of the issues in this cause. Respondents Meltons' proposed findings of fact numbered 1-13 have been adopted either verbatim or in substance in this Recommended Order. COPIES FURNISHED: Michael F. Chenoweth, Esquire 31 Garden Cove Drive Key Largo, Florida 33037 James S. Mattson, Esquire Joseph J. Vetrick, Esquire MATTSON, TOBIN & VETRICK Post Office Box 586 Key West, Florida 33037 Cecile I. Ross, Esquire Assistant General Counsel Department of Environmental Regulation 2600 Blair Stone Road Tallahassee, Florida 32399-2400 Daniel H. Thompson, Esquire General Counsel Department of Environmental Regulation 2600 Blair Stone Road Tallahassee, Florida 32399-2400
