The Issue The issues are whether Keith Rockman's construction of a dock and other structures on Choctawhatchee Bay in Fort Walton Beach, Florida, is exempt from Wetland Resource Permit requirements, and whether authorization to use sovereign submerged lands for the project should be given.
Findings Of Fact Based on the evidence presented by the parties, the following findings of fact are made: On December 19, 2005, Mr. Rockman, who lives at 325 Brooks Street, Southeast, Fort Walton Beach, Florida, filed an application with the Department's Northwest District Office in Pensacola requesting authorization to construct a platform seven feet wide by eight feet long; an access pier three feet long; another access pier four feet wide by forty-five feet long; four mooring pilings outside the slip; and ten mooring pilings inside the proposed slip, totaling 371 square feet. The application indicated that the proposed construction activities would take place in the Choctawhatchee Bay, a Class III water of the State, on which Mr. Rockman's property fronts. (This waterbody is more commonly known as the Santa Rosa Sound or the Intracoastal Waterway.) The property already had an existing 25-foot dock when Mr. Rockman purchased the property sometime in 2005; however, because Mr. Rockman wishes to dock a larger boat than the prior owner, he has requested authorization to build the structures in issue here. Based upon the information supplied by the applicant, Diana Athnos, an Environmental Manager with the Northwest District Office, advised Mr. Rockman by letter dated January 31, 2006, that the Department had "determined that [his] project is exempted from [the Department's] Wetland Resource Permit requirements by Rule 62-312.050(1)(d), Florida Administrative Code." The letter also stated that the "letter is your authorization to use sovereign submerged land (if applicable) for the construction of your project, as required by Chapter 253.77, Florida Statutes and Chapter 18-21, F.A.C." After Department approval was obtained, Mr. Rockman completed construction of the project. Mr. Rockman elected not to publish notice of the Department's decision or provide notice by certified mail to specific individuals. Therefore, third parties were not barred from challenging the Department's decision until after they received actual notice. Petitioner, who lives next door to Mr. Rockman, learned about the Department's decision in a telephone call with the Northwest District Office on March 8, 2006. The papers filed in this case indicate that Petitioner and other neighbors had actually observed construction activities on Mr. Rockman's property in November 2005 and had filed complaints with the Department regarding these unauthorized activities. These complaints evidently led to the filing of an application by Mr. Rockman. On March 17, 2006, Petitioner, who resides at 328 Brooks Street, Southeast, Fort Walton Beach, and has 50 feet of frontage on the water with a dock extending into those waters, filed a letter with the Department, which was treated as a Petition challenging the Department's earlier decision. This Petition was later dismissed by the Department on the ground it raised claims concerning Petitioner's riparian rights, a matter beyond the Department's jurisdiction. Petitioner then filed an Amended Petition on July 11, 2006, in which he again contended that his riparian rights would be severely restricted by the proposed activities, and that the dock would create a navigational hazard. Although Florida Administrative Code Rule 62-312.050(1)(d)3. requires that a project not "create a navigational hazard" in order to be exempt from permitting requirements, Petitioner opted to base his claims on two provisions in Florida Administrative Code Rule 18-21.004(7), which contains the general conditions for authorizations to use sovereign submerged lands. The riparian rights issue was again excluded from consideration at a status conference held on January 5, 2007. The parties advise that this issue is now being pursued in a separate action in circuit court. Through the introduction into evidence of its complete permit file as Department Composite Exhibit 1, the Department established that the proposed activities are exempt from permitting requirements under Florida Administrative Code Rule 62-312.050(1)(d). More specifically, the activity will take place in waters which are not located in Outstanding Florida Waters; the structures are less than 1,000 square feet of surface area over the landward extent of waters of the State; they will be used for recreational purposes; they will be constructed on pilings; they will not substantially impede the flow of water or create a navigational hazard; and the structure is the sole dock constructed pursuant to the exemption as measured along the shoreline for a minimum distance of 65 feet. The dock and associated structures and pilings will be constructed over sovereign submerged lands owned by the State of Florida. Under Florida Administrative Code Rule 18-21.005(1), which specifies the forms of authorization for consent to use sovereign submerged lands, "no application or written authorization is required for an activity that is exempt from the requirements of obtaining a permit," so long as certain conditions are met, including those found in Florida Administrative Code Rules 18-21.004(7). See Fla. Admin. Code R. 18-21.005(1)(b). The only relevant condition raised in the Amended Petition is whether or not the "[s]tructures or activities shall . . . create a navigational hazard." Fla. Admin. Code R. 18-21.004(7)(g). In construing this rule, and the similar requirement in Florida Administrative Code Rule 62- 312.050(1)(d)3., the Department considers whether the structures will create a navigational hazard for boaters on the Intracoastal Waterway, as well as the owners of property who reside on either side of Mr. Rockman. In his Amended Petition, Mr. Woolshlager contended that the proposed structures or activities will create a navigational hazard when he accesses the dock in front of his property. As clarified at hearing, Petitioner does not dispute that he (or any "good boat driver") has adequate ingress and egress for his smaller boat, even with the larger dock on Mr. Rockman's property. Indeed, the record shows that he has been observed leaving his dock and accessing the Intracoastal Waterway. However, Petitioner indicated that if he should die, his wife intends to sell the property. If the new purchaser desires to dock a larger boat, he fears that there will not be sufficient room to do so, and the value of his property will be diminished. Through testimony from a licensed boat captain, it was established that Mr. Rockman's dock does not create a navigational hazard for boaters in the Intracoastal Waterway whose boat channel lies at least 600 feet or so from the shoreline, or for property owners on either side of the applicant's property. Although Petitioner cannot dock a larger boat than he now has (a 21-foot boat), this is because he needs to dredge out the area where his existing dock is built and reconfigure its shape. (Mr. Woolshlager agreed that his dock actually encroaches a few feet onto Mr. Rockman's property; however, Mr. Woolshlager advises that the prior owner (who sold the property to Mr. Rockman) agreed to this encroachment when he purchased the property.) Therefore, all criteria have been satisfied.
Recommendation Based on the foregoing Findings of Fact and Conclusions of Law, it is RECOMMENDED that the Department of Environmental Protection enter a final order granting Mr. Rockman's application for an exemption from permitting requirements and authorization to use state-owned submerged lands. DONE AND ENTERED this 7th day of May, 2007, in Tallahassee, Leon County, Florida. S DONALD R. ALEXANDER Administrative Law Judge Division of Administrative Hearings The DeSoto Building 1230 Apalachee Parkway Tallahassee, Florida 32399-3060 (850) 488-9675 SUNCOM 278-9675 Fax Filing (850) 921-6847 www.doah.state.fl.us Filed with the Clerk of the Division of Administrative Hearings this 7th day of May, 2007. COPIES FURNISHED: Lea Crandall, Agency Clerk Department of Environmental Protection 3900 Commonwealth Boulevard Mail Station 35 Tallahassee, Florida 32399-3000 John N. C. Ledbetter, Esquire 4641 Gulfstarr Drive Suite 102 Destin, Florida 32541-5324 Nona R. Schaffner, Esquire Amanda G. Bush, Esquire Department of Environmental Protection 3900 Commonwealth Boulevard Mail Station 35 Tallahassee, Florida 32399-3000 Michael William Mead, Esquire John S. Mead, Esquire Michael Wm Mead, P.A. Post Office Drawer 1329 Fort Walton Beach, Florida 32549-1329 Gregory M. Munson, General Counsel Department of Environmental Protection 3900 Commonwealth Boulevard Mail Station 35 Tallahassee, Florida 32399-3000 Michael W. Sole, Secretary Department of Environmental Protection 3900 Commonwealth Boulevard Tallahassee, Florida 32399-3000
The Issue Whether Southern Hy Power Corporation (Hy Power) has provided reasonable assurance, based on plans, test results, or other information, that its proposed hydroelectric facility will comply with the Management and Storage of Surface Water (MSSW) statutes and rules of Southwest Florida Water Management District (SWFWMD) and the Wetland Resource Management permit (WRM)/water quality certification statutes and rules of the Florida Department of Environmental Protection (DEP).
Findings Of Fact By Joint Prehearing Stipulation the parties agreed to the following description of the parties and the project: PARTIES: The Department of Environmental Protection (the Department) is a government agency in the State of Florida existing by virtue of Section 20.255, Florida Statutes, and operating pursuant to Chapters 253, 373, 376, and 403, Florida Statutes, and Title 62, Florida Administrative Code. Under an interagency agreement with SWFWMD, the Department also implements Title 40D, Florida Administrative Code. The Department is located in Tallahassee, Florida, and it has a district office in Tampa, Florida, which district includes Levy County. Southern Hy Power Corporation is a Florida Corporation whose principal offices are located at 7008 Southwest 30th Way in Gainesville, Florida. Betty Berger is an interested party with a mailing address of Post Office Box 83, Inglis, Florida. The Campbells are an interested party with a mailing address of 245 Palm Street, Inglis, Florida. Hy Power applied on August 31, 1993, to the Department for a WRM permit/water quality certification to construct a hydroelectric facility on the Inglis By-Pass Channel. The project is located in Section 12, Township 17 South, Range 16 East, within the town of Inglis in Levy County. The facility consists of a powerhouse located on the south side of the channel measuring about 28 feet wide by 115 feet long, drawing water from the Inglis By-Pass Channel, passing it through a single-pit type turbine and discharging downstream of the Inglis By-Pass Spillway Dam. Hy Power applied on August 4, 1998, to the Department for a MSSW permit for the same proposed hydroelectric facility on the Inglis By-Pass Channel. DESCRIPTION OF PROPOSED PROJECT The project involves the construction of an intake structure, powerhouse, and tailrace on a 0.61-acre area located on the south side of the existing Inglis By-Pass Spillway. The facility will take advantage of the existing hydrostatic head that exists on either side of the Spillway Dam, to generate electricity. The powerhouse will be constructed below grade and will contain a single megawatt turbine and generating unit. The intake structure will divert flows from the upstream side of the Spillway Dam through the powerhouse and back into the By-Pass Channel. A small one-story control building and low profile substation will be constructed above grade within the boundaries of the project area. The hydroelectric project is considered to be a "Run of the River" type of facility because it can only use that water which flows down the existing channel. The geometry of the channel restricts flow to a certain amount, therefore the project cannot create or use flows above those that the By-Pass Channel can provide. The overall authority for control of water levels in Lake Rousseau and flow to the lower Withlacoochee River will remain with the DEP. Lake Rousseau was created in 1909 when the Inglis Dam was constructed across the Withlachoochee River for the purposes of hydroelectric generation. The dam impounds over 11 miles of the Withlachoochee River and forms a lake approximately 3,000 to 4,000 acres in size. Prior to construction of the Barge Canal, water released from the Inglis Dam would flow down the lower portion of the Withlachoochee River about 10 miles before entering into the Gulf of Mexico. In the mid to late 1960's the Army Corps of Engineers (ACOE) built a portion of the Cross Florida Barge Canal between the Gulf of Mexico and Lake Rousseau. The canal severed the Withlachoochee River downstream of the Inglis Dam causing its flow to be diverted into the Barge Canal and then into the Gulf. In order to maintain the flow of freshwater from Lake Rousseau to the lower segment of the River, the 8,900-foot long Inglis By- Pass Channel and Spillway were constructed. The resulting downstream flow ensures navigation in the lower portion of the River and sustains its freshwater and estuarine environment. The water level in Lake Rousseau is generally maintained at an elevation of 27.5 feet above mean sea level (msl) by a combination of the Inglis Dam, the Inglis Lock, which is located in the Barge Canal, and the By-Pass Channel Spillway. These water control features are known collectively as the Inglis Project Works. The water levels in the lower Withlachoochee River immediately to the west of the By-Pass spillway are close to sea level. The resulting head provides the potential energy needed to drive the proposed generator turbine. Under normal conditions the majority of water released from Lake Rousseau flows over the Spillway Dam into the lower segment of the River. According to the DEP Office of Greenways and Trails (OGT), the maximum capacity of the existing By-Pass Channel Spillway is 1,540 cubic feet per second. The hydroelectric project will divert whatever flow is allowed around the existing spillway through the turbine and back into the channel. When the Cross Florida Barge Canal project was cancelled in the 1990's, the ACOE transferred ownership of the property to the State of Florida Board of Trustees, who in turn has leased the property to the DEP for use as the Cross Florida Greenbelt State Recreation and Conservation Area. Management of this property, the control of river flow and lake levels, and operation of the Inglis Project Works are exercised by the DEP's OGT. The OGT utilizes a document entitled "Water Control Plan for Inglis Project Works," dated September 1994, as a guide to operating the structures. The Water Control Plan is incorporated as part of the MSSW intent to issue. On or about April 25, 1995, the Governor and Cabinet, sitting as the Board of Trustees of the Internal Improvement Trust Fund ("Trustees"), approved a request from Hy Power to sublease 0.61 acres of Greenway property at the project site for the purpose of providing electric power. The request was challenged by Berger and the Campbells, and resulted in an administrative hearing held on November 3, 1995. As a result of the hearing, Administrative Law Judge Larry Sartin entered a Recommended Order on July 12, 1996, that the Board enter an order approving execution by the DEP of the proposed sublease and dismissing the petition of Berger and the Campbells. The Recommended Order was approved by the Trustees in its entirety in a Final Order dated April 12, 1996 ("Final Order"). Berger v. Southern Hy Power Corporation et al., Case No. 95-3589. A copy of the Final Order is listed as an exhibit to this Stipulation, and the Findings of Fact and Conclusions of Law contained therein are adopted herein. As previously ruled by the undersigned, the previous Final Order is res judicata as to Petitioners in this case, who are collaterally estopped from challenging any of the findings of fact or conclusions of law contained in the previous Final Order. Petitioners reserve the right to litigate issues of fact and law not addressed in the Findings of Fact or Conclusions of Law contained in that Final Order with regard to the permittability of this project under the WRM and MSSW permitting proposals, and to raise objections as to relevance to this proceedings of any of the Findings of Fact or Conclusions of Law in the Final Order. On February 21, 1995, Hy Power filed application with the Federal Energy Regulatory Commission (FERC) for a conduit exemption from the licensing requirements of Part I of the Federal Powers Act (FPA) for the proposed project. Petitioners and various other persons filed protests with FERC in opposition to the project. On April 21, 1997, FERC issued an Order Granting Conduit Exemption, a copy of which is listed as an exhibit to this Stipulation. Petitioners in this case are collaterally estopped from challenging any of the findings or conclusions contained in that Order Granting Conduit Exemption. Petitioners reserve the right to litigate issues of fact and law not addressed in the Findings of Fact or Conclusions of Law contained in that Order Granting Conduit Exemption with regard to the permittability of this project under the WRM and MSSW permitting proposals, and to raise objections as to relevance to this proceedings of any of the findings or conclusions in the Order Granting Conduit Exemption. FACTS ADDUCED AT HEARING OUTLINE OF PROJECT The proposed project calls for the construction of a water retention structure along the existing By-Pass spillway, the excavation of a large hole in which the powerhouse and turbine would be constructed "in-the-dry" south of the existing dam, and a millrace below the proposed project to return the water back into the existing water course. Conflicting testimony was received regarding the facts surrounding the construction of the project. These included: whether the proposed project will touch the existing wing walls of the existing dam; whether the water retention structure is a coffer dam; whether the proposed water retention structure will safely retain the water; whether the powerhouse and turbine have sufficient negative buoyancy to stay in the ground; whether the proposed excavation will weaken the existing dam; and whether the de-watering of the excavation site will adversely impact ground and surface water. PROJECT DESIGN AND ENGINEERING Engineering for the project was directed by witness Richard A. Volkin, a professional engineer and president and CEO of Engineering Company, Inc., based in Canton, Massachusetts. Mr. Volkin has extensive national and international experience in the design, management, and operation of hydroelectric facilities. Other engineers in Mr. Volkin’s firm worked on the project under Mr. Volkin’s direct supervision, including John May, who became registered as a professional engineer in Florida in order to sign and seal the engineering drawings for the project, which he initially did around 1994. Mr. May became ill and retired in 1998. Because of the length of time the application process has taken and the fact that Mr. May retired, there was a time while the application was pending, when Hy Power's design team was without a registered Florida engineer. When this was brought to the attention of Hy Power, Hy Power substituted Steven Crockett for Mr. May as the Florida-registered professional engineer of record for the project. DEP routinely accepts an applicant’s changing its engineer of record during the course of permit application or construction. Mr. Crockett is a civil and structural engineer who has considerable experience in preparing dam structural designs. Mr. Crockett independently reviewed and evaluated the engineering drawings for the project. Mr. Crockett resealed the drawings by using his drawn seal and signing the plans because his embossed seal was not readily available and time was of the essence. Mr. Crockett has advised DEP that he is now engineer of record for the project, using the appropriate DEP forms. Mr. Volkin’s firm performed all of the studies required by the various agencies, including a geotechnical study of the area, a 50-year analysis of water flow in and out of the Lake Rousseau regime, and water quality evaluations of water in the By-Pass Channel. The ACOE performed deep hole borings of the soils (approximately 36-40 feet below sea level) in the area of the project site to determine soil stabilization conditions at the site when they were constructing the Inglis Project Works. The soil conditions found can reasonably be expected to be similar today. Mr. Volkin’s company also took its own eight-foot deep surface core samples. The purpose of those samples was to verify the ACOE data. The new core samples verified the original core samples. Mr. Volkin also reviewed the ACOE’s engineering drawings developed from construction of the Spillway Dam. These show that the dam is founded on limestone bedding that has been stabilized with concrete. The hydroelectric facility will be constructed adjacent to and south of the dam structure and adjacent to and north of the barge canal. The same type of limestone bedrock is found in the area of the proposed construction. The facility design includes an intake channel on the upstream channel and a tailrace downstream. Those are the only structures that will be constructed next to the By-Pass Channel. The construction of the facility itself will be "in the dry." Hy Power will use coffer dams to seal off the construction site from the By-Pass Channel, so that there will not be water leakage from the Channel into the construction site. Water from the By-Pass Channel will enter the power plant when the coffer dams are lifted and the water is allowed to flow into the facility. The Petitioners presented the testimony of Bill Edwards, an individual with considerable experience in the construction of bridges, cofferdams, and similar concrete structures in aquatic and semi-aquatic conditions. Mr. Edwards is a former hard-hat diver who worked all over the world and worked in Florida for many years prior to his retirement. Based upon his experience and expertise in construction related to projects of this type, his testimony is credible and worthy of consideration. Mr. Edwards pointed out that if the proposed water retention structure did not touch the wing wall of the existing dam, it could not keep the water out and would not have the strength that it needed to retain the water. Hy Power’s witnesses explained that the retention structure would be set close enough to the existing wing wall that waterproofing materials could be placed between the two structures to keep the water out. Further, that the existing plans did not show interior bracing which would be included for structural strength and integrity. In sum, the retention structure will be in contact with existing dam’s wing wall, but will be free standing and not dependent upon the strength of the wing wall for its strength. Mr. Edwards pointed out that a cofferdam by definition has walls on all sides of the structure. The structure proposed by Hy Power did not have walls all the way around the proposed excavation. In rebuttal, Hy Power presented evidence that its plans were conceptual, design drawing and not construction plans. Hy Power represented that in actuality it would put as many walls as were necessary to keep the water out of the hole it intended to excavate. Trash racks will be constructed at the intake structures to protect aquatic life and make sure that trash and vegetation do not enter the intake structure or go down river. The trash rack bars will be two inches on center, which the U.S. Fish and Wildlife Service has determined as the appropriate size for the protection of fish. The turbine blades are "double regulated," and operate generally between 60 and 90 revolutions per minute. The design enables the turbine to operate at a constant speed to generate a consistent flow of electricity, notwithstanding the fact that the flow of the water may vary. The blade speed is not very fast, and the 2.5-meter blades provide a two to three-foot opening. This design acts to prevent fish mortality. There are four ways to shut off the flow of water through the proposed structure: close the pitch of the blades, close the wicket gates, allow the counter balance to the wicket gates to kick in and automatically close the gates, and close off the main gates. This is a fail safe system ("four level redundancy") designed to work upon any failure. Once water goes through the generator, its velocity is reduced to no greater than its intake rate which is a maximum of three feet per second. This prevents the water being discharged from the tailrace from causing erosion. If the head of water in the dam produces a flow exceeding three feet per second, it can be diverted over the other dams which will be functional. The power plant will be encased in concrete, except for a small access way that enables a person to go down a set of stairs to the plant. It will be a sealed, waterproof structure, as required by FERC and the ACOE. This will prevent penetration of groundwater, or flood waters in the event a massive flood overtops the plant. The only water entering the powerhouse will be through the turbine tunnel for power generation purposes. Mr. Edwards pointed out that the powerhouse was a closed structure and as such would have positive buoyancy, that is, it would float. Mr. Edwards pointed out that the proposed site is between the barge canal and By-Pass spillway and there is a great deal of groundwater and potentiometric pressure in the existing water table. In sum, there is a unlimited supply of groundwater at the site, and powerhouse could float out of the ground just like an empty swimming pool. Hy Power presented rebuttal evidence that the weight of the building, the turbine, and the water flowing through the turbine would be close to negative buoyancy, and they would add additional weight to the structure as necessary to keep it in place. The project is designed to generate three megawatts of electric power which is enough electricity to serve between 300 and 3000 homes, depending on usage. The project is designed to be unmanned. This is common for facilities such as this. The plant can be operated by remote control, unlike the existing controls at the By-Pass Dam, which are operated manually. DEP can access, monitor, and control remotely the generator's operation to include shutting the facility down at any time. There will be remote sensors to monitor water elevations. Flood protection will improve because of the ability of DEP to manage water flow from a remote location. If there is any major disruption, the plant will shut itself down. The project is classified as "green power." In other words, it generates natural energy without any disruption to the environment. The project will have minimal to no impact on the environment. There will be no significant changes in water quality compared to existing conditions as a result of either construction or operation of the facility. WRM Permit Criteria Hy Power has provided reasonable assurances that the proposed project will not cause a violation of state water quality standards of Section 403.918(a), Florida Statutes (1991). The parties stipulated that turbidity and dissolved oxygen were the two surface water quality issues of concern in this proceeding. The receiving water body is the Inglis By-Pass Channel. The Inglis By-Pass Channel is a Class III surface water. The project is not located in a OFW. While the lower Withlacoochee River is an OFW, the OFW designation runs up the natural river itself, and does not include the Spillway Dam, tailrace, or the remainder of the By-Pass Channel. There would be no degradation of water quality at the point of contact with the Withlacoochee River OFW. The DEP and FERC looked specifically at potential for turbidity and dissolved oxygen in determining whether the project would violate state water quality standards. The standards for turbidity and dissolved oxygen will not be violated. Because the By-Pass Dam is an under flow structure, a minimum of oxygenation currently occurs as water flows through the existing dam. The proposed project runs the water underground through the generator; however, Hy Power will measure the dissolved oxygen below the dam in the Lower Withlacoochee River. In the event there is any lowering of dissolved oxygen, Hy Power can install a "sparge ring" to reoxygenate the water going through the turbine so that dissolved oxygen remains at current levels. No turbidity will be added to the receiving water as a result of the project, because water velocity is low and the structure is encased in concrete and rip-rap. The only other potential for turbidity would occur when the coffer dams are removed after construction is complete. The coffer dams can be removed with the generator closed to permit any turbidity to settle. The amount of siltation that might occur when the generator is opened would be insignificant. Where a project is not in a OFW, an applicant must provide reasonable assurance that the project will not be contrary to public interest. See Section 403.918(2), Florida Statutes (1991). Hy Power has provided such assurances. The project will not directly affect public health, safety or welfare, or the property of others. See Section 403.918 (2)(a)1., Florida Statutes. There are concerns relating to the structural integrity of the proposed facility and adjacent structures which are discussed extensively below. The project will have no adverse impact upon the conservation of fish and wildlife, including threatened and endangered species and their habitat. See Section 403.918 (2)(a)2., Florida Statutes. While manatees are not likely to be found at the project site, the installation of the trash racks will eliminate any potential adverse impact on manatees. In fact, the racks will be an improvement over the current unprotected Spillway Dam. DEP procedures require a specific manatee control plan be implemented to deal with site specific concerns. The project will not adversely affect navigation or the flow of the water or cause harmful erosion or shoaling. See Section 403.918(2)(a)3., Florida Statutes. The project will not adversely affect fishing or recreation values or marine productivity in the vicinity of the project. See Section 403.918(2)(a)4., Florida Statutes. The permanent project and its construction will cause no significant environmental impacts. See Section 403.918(2)(a)5., Florida Statutes. There will be no adverse impacts to significant historical and archeological resources. Section 403.918(2)(a)6., Florida Statutes. With regard to the impact on current conditions and relative value of functions being performed by the areas affected by the proposed activity, there will be no negative impacts. See Section 403.918(2)(a)7., Florida Statutes. Improvement will result from better control of water flow at the project site, installation of trash racks and implementation of green power. THE FORESEEABLE ADVERSE SECONDARY OR CUMULATIVE IMPACTS Potential adverse secondary impacts related to power transmission are addressed through the fact that there is an existing power line corridor that can be used to transmit the electricity. Any need to change the corridor could be addressed by subsequent DEP permitting. Cumulative impacts are not at issue. Mr. Gammon, with Florida Power, acknowledged that the current electric company, presumably Florida Power, would be required by FERC to transport the electricity generated by Hy Power over its existing corridor and poles. No final decision has been made regarding how to access the site with equipment during construction. Several feasible construction options exist, and there are several ways of accessing the site with heavy equipment vehicles and without impacting wetlands. Any final decision would be subject to DEP approval. Since the project meets the public interest criteria of Section 403.918(2)(a), Florida Statutes, and wetland impacts are minimal, the project is permittable without the need for mitigation. See Section 403.918(2)(b), Florida Statutes. The ACOE has issued a permit for the facility. The permit varies slightly from the DEP intent to issue in the use of reinforced concrete rather than rip-rap on the bottom half of the intake channel. This is to comply with ACOE preference, but the variation has only an environmental benefit. Counsel for Petitioners sought to elicit testimony from Linda Sloan, Executive Director of the Withlacoochee Regional Planning Council, with regard to compliance of the proposed project with the Town of Inglis Comprehensive Plan and Land Development Code. Such compliance is not relevant to this proceeding. At any rate, Ms. Sloan conceded that any prohibition that might apply in the Land Development Code to construction of the proposed facility could potentially be alleviated by exemption or variance provisions in the Code. MSSW PERMIT CRITERIA The project will provide adequate flood protection and drainage in the conventional sense. See Rule 40D-4.301(1)(a), Florida Administrative Code. Because the amount of impervious area is minimal, runoff from the project will not in any way contribute to increased flooding or adversely impact drainage patterns. The total amount of impervious area of the facility is less than that of a single-family residence. SWFWMD rules do not even require MSSW permits for single-family residences because the impact is not significant. The only purpose for requiring a MSSW permit for the project is to review the project’s potential downstream impacts to the watershed, not stormwater runoff from the facility itself. The project will not cause adverse water quality or water quantity impacts on adjacent lands in violation of Chapter 373, Florida Statutes, or cause a discharge that violates state water quality standards. See Rule 40 D-4.301(1)(b), Florida Administrative Code. As indicated by the WRM water quality findings above, the project will not generally violate state surface water quality standards. See Rule 40 D-4.301(1)( c), Florida Administrative Code. The project will not generally cause adverse impact on surface or groundwater levels or flows. See Rule 40 D- 4.301(1)(d), Florida Administrative Code. Since the project is a run-of-the-river, it will not diminish the capability of a lake or other impoundment to fluctuate through the full range established for it under Chapter 40D-8, Florida Administrative Code. The project will not cause adverse environmental impacts, or adverse impacts to wetlands, fish, and wildlife or other natural resources. The project can be effectively operated and maintained. See Rule 40D-4.301(1)(g), Florida Administrative Code. The project is a slow speed, low maintenance facility. The design concept is well established and has been successfully used for many years. Possible adverse affects to public safety are discussed below. The project is consistent with the requirements of other public agencies. See Rule 40D-4.301(1)(i), Florida Administrative Code. Potential harm to water resources within the SWFWMD are discussed below. See Rule 40D-4.301(1)(j), Florida Administrative Code. The proposed project generally will not interfere with the legal rights of others. See Rule 40D-4.301(1)(k), Florida Administrative Code. The proposed project is not against public policy. See Rule 40D-4.301(1)(l), Florida Administrative Code. The project complies with the requirements contained in the Basis of Review. See Rule 40D-4.301(2), Florida Administrative Code. There is a dispute as to whether the project was within or at the edge of the 100-year flood plain. This dispute is related to how one interprets the rule as it relates to the millrace and the location of the facility which is under ground. In the conventional sense, the project is not in the flood plain. Further, the project is designed in such a way, that it is waterproof if it were topped with water. While in the past SWFWMD may have had concerns that the project might cause downstream flooding, SWFWMD currently has no such concerns, given the run-of-the-river status of the proposed project. The operation of the project will not cause downstream flooding. The DEP included in its intent to issue, conditions contained in the sublease between Hy Power and the DEP in order to ensure that the facility would remain run-of-the-river, would comply with the water control plan, and would otherwise comply with the terms of the sublease. The DEP has final control over water flow and can revoke the permit or otherwise take enforcement action against Hy Power if Hy Power fails to comply with the water control plan. GROUNDWATER IMPACTS Operation of the project will not cause groundwater contamination or otherwise have adverse groundwater impacts. Some concerns about groundwater during excavation of the construction site were raised. The conflicting evidence received regarding them is discussed below. An area of concern was the de-watering plan for the project. Everyone agrees there will be some water seepage into the construction site that will have to be pumped out. The parties disagree regarding the amount of water that will have to be removed. Their estimates of amount of water to be removed vary because their estimates of size and over-all depth of the site vary. Petitioners presented credible evidence that a potential exists for the construction site to have a large quantity of water because of its location between two sources of surface water (the By-Pass Channel and Barge Canal), because of the makeup of the subsurface, and because of the depth of the construction. Hy Power credibly represents that if excessive groundwater is found, it can address the adverse impacts through its de-watering plan that would have to be filed with FERC and DEP. The technology exists to address the de-watering of the project. Such plans are routinely considered by DEP after a construction permit is issued and before de-watering occurs. There is very little evidence of sinkhole activity in the project area, and the construction activities are not expected to cause any sinkhole activity. NOISE POLLUTION Mr. Bitter expressed concerns that FERC would require the facility to install a very loud siren that would result in sudden noise adverse to the well-being of neighbors. Mr. Bitter is unfamiliar with FERC siren requirements at run-of the-river hydroelectric facilities. In contrast, Mr. Volkin, who has substantial experience in this area, testified that the only alarm device that would be required would be for the protection of the workers during construction. The purpose of the alarm is to warn persons below a dam spillway of a change in the volume of water being let out of the impoundment. In the case of a run-of-the-river facility, the volume is near constant, changing only gradually. Therefore, even if a warning siren had to be installed its use would be limited to significant changes in flow or testing. This would not constitute a nuisance. Further, the facility is located in the vicinity of the Crystal River Nuclear Power Plant which has its own warning sirens. It would be prudent to make any warning devices required for this structure significantly different from those at the nuclear plant and to limit their use. DAM SAFETY AND FERC REVIEW In reviewing whether Hy Power’s applications complied with the relevant permitting criteria, the DEP took into consideration the review of the facility already performed by FERC. FERC will also be responsible for reviewing the project as it is being constructed. Mr. Edwards also raised concerns about the structural stability of the By-Pass Dam itself. This has been a subject of concern by those responsible for the dam, and a survey of the structure was conducted in 1993, referred to as the Greiner Report. The Greiner Report identified specific maintenance problems that have been and are being addressed by the DEP. However, DEP’s maintenance plan does not address specifically the possibility that the weight of the dam over time has caused some shifting in the dam. Hy Power has only a few core borings and only one at the location of the generator. Hy Power is using the ACOE’s original borings, as confirmed by several new ones, to develop its preliminary plans. The DEP considered FERC and the ACOE as responsible agencies for determining the structural integrity of the dam. DEP has taken FERC’s review of this facility into consideration as part of DEP’s own permitting review. It is normal for DEP to rely on outside sources and agencies for assistance in determining compliance with DEP permitting criteria such as public health and safety, and it is reasonable for DEP to do so in this instance. Most states do not have the full capability to evaluate dam safety, and so they rely on FERC and ACOE. On April 21, 1997, the project received a conduit exemption from FERC. The application process is illustrated in Hy Power Exhibit 11. Hy Power submitted to DEP detailed information about the dam, the associated structures and the proposed project which had been reviewed by FERC and the ACOE, the two agencies in the United States who are responsible for dam structure design, control, and administration. Included in the package was the Greiner Report and Hy Power’s review of it. FERC evaluated the project, the Inglis By-Pass Dam structure, and the proximity of the project to the Dam in relation to structural impact, upstream and downstream impacts, water quality, and environmental issues. Mr. Edwards raised concerns regarding the ability of the limestone bedrock to sustain additional construction in the area of proposed construction. This is a material issue in the controversy which impacts several aspects of the proposed construction. Mr. Edwards pointed out that the barge canal channel was constructed with the use of explosives that caused a fracturing of limestone bedrock. He pointed out that the steel panels, which Hy Power proposes to drive into the bedrock to construct the water retention structure necessary to excavate the hole into which the turbine and powerhouse would be placed, will further fracture this bedrock. This creates two potential dangers. It could permit water to move under and around the bottoms of the panels, potentially scouring the loosened material from the base of the panels and making them unstable and subject to failure. It could weaken the entire southern wing of the existing spillway dam. Mr. Edwards opined that this could result in catastrophic failure of the dam or the coffer dam. Such a failure would cause major destruction and loss of life to those persons living and working in and along the lower Withlacoochee River. Hy Power presented rebuttal evidence that it could and would, if necessary, inject concrete into the limestone to stabilize it and avoid the concerns raised by Mr. Edwards. FERC specifically evaluated concerns raised by project opponents over the poor physical condition of the By-Pass Channel Spillway structures, relying particularly on the 1993 Greiner Report. FERC noted that the DEP had entered into a contract to correct any deficiencies listed in the Greiner Report, which "did not conclude that the deficiencies at the By-Pass Spillway threaten downstream life and property." The FERC review concluded that the dam was safe. To ensure safety, FERC is requiring that Hy Power do a complete stability analysis of the dam prior to any construction. Articles 301 and 302 of the FERC exemption ensure that all final drawings and specifications be submitted to FERC prior to construction, along with a supporting design report consistent with FERC’s Engineering Guidelines; that FERC can require changes to assure a safe and adequate project; and that Hy Power must also submit approved coffer dam construction drawings and specifications at least 30 days prior to starting construction. FERC has its own engineering staff who will go to the site and do their own analysis, along with the ACOE, of the dam and structures, prior to any construction commencing. This is a detailed design review evaluation so that the latest information on the dam will be made known immediately prior to construction, and will prevent any catastrophic event from happening. Under FERC procedures, FERC requires the applicant to obtain the DEP permits prior to requiring applicant to submit more detailed construction designs for FERC's consideration. These more detailed designs in turn will be subject to further review by DEP and FERC. It is assumed that Hy Power will comply with the post- permitting procedures and requirements, and will present complete, detailed construction drawings for FREC and DEP approval. Hy Power’s failure to complete the process would result in denial of a construction permit.
Recommendation Based upon the foregoing Findings of Fact and Conclusions of Law set forth herein, it is RECOMMENDED: That the DEP enter a Final Order that issues the two permits challenged in this proceedings, WRM Permit No. 38-237096-3.001 and MSSW Permit No. 38-0129249-002, subject to the conditions contained in the Intents to Issue in the respective WRM and MSSW Permits and as described in the Recommended Order. DONE AND ENTERED this 2nd day of March, 2000, in Tallahassee, Leon County, Florida. STEPHEN F. DEAN 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 2nd day of March, 2000. COPIES FURNISHED: Daniel H. Thompson, Esquire Berger Davis & Singerman 215 South Monroe Street, Suite 705 Tallahassee, Florida 32301 Andrew Zodrow, Esquire Department of Environmental Protection 3900 Commonwealth Boulevard Mail Station 35 Tallahassee, Florida 32399-3000 John S. Clardy, III, Esquire Crider Law Firm Plantation Point 521 West Fort Island Trail, Suite A Crystal River, Florida 34429 Teri Donaldson, General Counsel Department of Environmental Protection 3900 Commonwealth Boulevard Mail Station 35 Tallahassee, Florida 32399-3000 Kathy Carter, Agency Clerk Department of Environmental Protection 3900 Commonwealth Boulevard Mail Station 35 Tallahassee, Florida 32399-3000 Bernard M. Campbell Bessie H. Campbell 245 Palm Street Post Office Box 159 Inglis, Florida 34449 Sarah E. Berger Post Office Box 83 Inglis, Florida 34449
The Issue Whether petitioners have timely availed themselves of a clear point of entry into administrative proceedings on Mr. and Mrs. Rankin's application for a permit to build a dock and, if so, whether the permit application should be granted?
Findings Of Fact On April 12, 1982, Frederick W. Rankin applied for a dredge and fill permit to construct a dock six feet wide and 300 feet long in the waters of Bayou Chico in Escambia County, Florida. Paralleling the dock on either side of the outboard end, two rows of mooring pilings 19.5 feet distance from the dock were proposed in the application. On April 20, 1983, Mark N. Snowdon, an employee of the Department of Environmental Regulation (DER) inspected the site, and, in an official DER permit application appraisal dated April 23, 1982, reported: Two large support vessels (crew boats) are moored at a small pier immediately east of the site. A commercial marina facility i[s] located directly across the bayou (north) from the project site. Bayou Chico is approximately 0.25 mile wide at this point. DER Exhibit No. 4. Between the crew boats' dock (Gulfwater Marine) and the site proposed for the Rankins' dock is the mouth of a small embayment (the bayouette). The Holzbauers own a house and lot, separated from the Rankins' lot by a parcel less than 75 feet wide, that fronts on the bayouette. PERMIT ISSUES DER issued a permit on June 9, 1982, and work began on the Rankins' dock on June 12, 1982. On the same day, Mr. Holzbauer inquired of the men putting in pilings whether DER had issued a permit for the work, then telephoned DER and asked DER's Mr. Fancher the same question. Mr. Fancher told Mr. Holzbauer that a permit had been issued, which was the first Mr. Holzbauer was told of issuance of the permit. As far as the evidence revealed, no notice of intent to issue preceded issuance of the permit. On June 26, 1982, the Holzbauers received a letter from W. Richard Fancher on behalf of DER, dated June 24, 1982, in which he stated: It is my understanding that, until recently, you had no knowledge of this private dock project. If this is correct, you may consider this formal notice of the activity. Should you object to this permit, including any and all of the conditions contained therein, you may file an appropriate petition for administrative hearing. This petition must be filed within 14 days of the receipt of this letter. Further, the petition must conform to the requirements of Part III, Chapter 17-1 and Section 28-5.201, Florida Administrative Code (copies enclosed). The petition must be filed with the Office of General Counsel, Department of Environmental Regulation, Twin Towers Office Building, 2600 Blair Stone Road, Tallahassee, Florida 32301. If no petition is filed within the prescribed time, you will be deemed to have waived your right to request an administrative hearing on this matter. DER Exhibit No. 1. A copy of Mr. Fancher's letter to the Holzbauers was also sent to Mr. Rankin. On July 8, 1982, a letter from the Holzbauers to Ms. Tschinkel reached DER's Office of the Secretary, protesting issuance of the permit and alleging that the dock did not conform to permit conditions. 1/ This letter was referred to the Division of Administrative Hearings, whose Director entered an order, sua sponte, on July 28, 1982, that "[t]his matter is dismissed without prejudice." No. 82-1947. An amended petition dated August 4, 1982, reached DER's Office of the Secretary on August 9, 1982, and the Division of Administrative Hearings on August 20, 1982. No. 82-2314. NO PERMIT RELIANCE The dock has been continued to completion, at a cost of $11,000.00. As built, the dock veers out from shore at a more easterly angle than the permit purported to allow. Whereas the permit contemplated construction at an angle several degrees west of north, the dock has in fact been built at an angle about 15 degrees east of north. One result is that the end is some 90 feet east of the point contemplated by the permit. Although a DER employee testified that this deviation was "within reason," it is clearly a significant departure from what the permit putatively allowed. The Rankins only own 86 feet of bayou frontage. The mouth of the bayouette is no more than 110 feet across. The mooring pilings, moreover, have been set in two rows parallel to the dock not 19.5 feet on either side, but 40 feet from the west side of the dock and 30 feet from the east side. If any of the landowners on the bayouette (with one exception) tried to build a pier perpendicular to their shore line extending even half the length of the Rankins' dock, it would intersect the Rankins' dock. NAVIGATION While the dock does not seal off the bayouette, it makes access considerably more difficult, especially for Mr. Holzbauer who sails in and out in his 14 foot boat. The dock juts out from the point at the western edge of the entrance into the bayouette at such an angle that it comes within 70 feet of the eastern edge of the entrance into the bayouette. Petitioner's Exhibit No. The crew boats moored to the east of the Rankins' dock have overall lengths ranging from 65 to 85 feet and there were three of them moored at Gulfwater Marine last summer. When the crew boats are docked, the distance between the westernmost one and the most inboard mooring piling next to the Rankins' dock is 81.5 to 103 feet. Where traffic from Bayou Chico to Pensacola Bay passes under a bridge, the channel is only 80 feet wide and the crew boats sometimes hit the bridge. The greatest problem the Rankins' dock has caused the crew boats is making docking more difficult. It is not always easy to turn an 85 foot boat around in the wind. The root of the problem, according to Mr. Kingry, who owns the crew boats, is that a patch of slightly deeper water in this generally shoaled area has been cut or blocked by the Rankins' dock. Sooner or later, Mr. Kingry predicted, a crew boat will "wipe out" the Rankins' mooring pilings.
Recommendation Upon consideration of the foregoing, it is RECOMMENDED: That the Department of Environmental Regulation deny the application for a dredge and fill permit for a dock located and aligned as this dock is. DONE and ENTERED this 27th day of April, 1983, in Tallahassee, Florida. ROBERT T. BENTON, II Hearing Officer Division of Administrative Hearings The Oakland Building 2009 Apalachee Parkway Tallahassee, Florida 32301 (904) 488-9675 Filed with the Clerk of the Division of Administrative Hearings this 27th day of April, 1983.
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 The issue is whether ADR of Pensacola should be issued a wetland resource permit and sovereign submerged lands authorization allowing the construction of a 30-slip docking facility on Big Lagoon, Escambia County, Florida.
Findings Of Fact Based upon all of the evidence, the following findings of fact are determined: Background In this environmental permitting dispute, Petitioner, Michael L. Guttmann, who lives less than one mile from the project site, has challenged the proposed issuance by Respondent, Department of Environmental Protection (Department), of a Wetland Resource Permit (permit) and Sovereign Submerged Lands Authorization (authorization) which would allow Respondent, ADR of Pensacola (applicant), to construct a 30-slip docking facility on Big Lagoon, Escambia County, Florida. The facility will be part of a condominium project to be constructed on the upland portion of the property. As grounds for contesting the permit, Petitioner contended that the Department failed to consider "the long term health of Big Lagoon," navigational hazards created by the project, or public safety; failed to impose an adequate "monitoring program"; did not provide for a "contingency plan for hurricane activity"; failed to consider that the activity will degrade a nearby Outstanding Florida Water [OFW]; and failed to take into account "existing unused marina slips close by." The petition further alleged that the foregoing concerns constituted violations of Section 373.414, Florida Statutes (2000), and Rules 62-4.242, 62-302.300, 62-302.700, and 62- 312.080, Florida Administrative Code. The cited statute identifies "additional criteria" for issuing a permit while the first three rules pertain to OFWs. The last rule contains general standards for the issuance or denial of a permit. Petitioner raised no issues concerning the issuance of the authorization in his initial pleading. Until April 2000, the upland property was owned by the applicant. It was then sold to Harbour Pointe of Pensacola, Inc., which has subsequently entered into an agreement with the applicant allowing the applicant to construct the dock, operate the permit, and purchase a condominium unit. If the application is approved, applicant intends to construct a 442 feet x 4 feet access pier with seventeen 30 feet x 1.5 feet finger piers, thirteen 40 feet x 1.5 feet finger piers, and a 74 feet x 1.5 feet terminal platform, to form a 30-slip docking facility at 10901 Gulf Beach Highway on Big Lagoon, a Class III water in Escambia County, Florida. Approval to use the submerged lands is found in the authorization. The dock will be located in a "fairly pristine area" in Big Lagoon a few miles southwest of Pensacola, Florida. That body of water is six miles in length and is separated from the Gulf of Mexico by a slender coastal barrier island known as Perdido Key, which lies approximately one statute mile south of the project. Continuing west along the shoreline next to the project site are a string of single-family homes with small dock facilities, most of which are less than 1,000 square feet in size and thus exempt from Department permitting requirements. To the east of the undeveloped property are more undeveloped lots and a private yacht club with extensive docking facilities. The facility being challenged here will not be a public marina; rather, it will serve the residents of a proposed upland condominium (consisting of two buildings) to be constructed at the same location. The project is more commonly referred to as the Harbour Pointe Marina. It is fair to infer that Petitioner and adjoining property owners object not only to the dock, but also to the condominium project. The application and project When the application was originally filed with the Department in July 1995, it contained plans for a longer dock and more slips. Due to a reduction in the length of the pier and number of slips to conform to Department rules, other technical changes, and various requests by the Department for additional information, the draft permit was not issued by the Department until May 2000. The Department considers this a "major project" with "major [hydrographic and water quality] issues connected with it." In reviewing the application, the Department considered whether reasonable assurance had been given by the applicant that water quality standards would not be violated, and whether the additional criteria in Section 373.414(1)(a)1.-7., Florida Statutes (2000), had been satisfied. The Department concluded that water quality standards would not be degraded, and that the project, as designed and permitted, was not contrary to the public interest. In making the public interest determination, the Department typically assigns a plus, minus, or neutral score to each of the seven statutory factors. In this case, a neutral score was given to historical and archaeological resources [paragraph 373.414(1)(a)6.] since there were none, while the permanent nature of the project [paragraph 373.414(1)(a)5.] caused it to be rated "a little bit on the minus side"; all other factors were given a plus. Department witness Athnos then concluded that on balance the project "was a plus because it will not adversely affect any of these things." The access pier (dock) runs perpendicular from the shoreline and stretches out some 442 feet to where the water reaches a depth of seventeen feet, which is the deepest point in Big Lagoon. The unusual length of the dock is required so that the boat slips will begin past the seagrass colony (which lies closer to the shore), to prevent boat propeller blades from cutting the top of the seagrass, and to reduce the amount of sedimentation stirred up by the boat propellers. Aerial photographs confirm that when completed, the dock will probably be the largest in Big Lagoon, and much larger than the neighboring docks to the west. The use of boat slips will be limited to condominium owners. Only 19 slips will be constructed initially, since the applicant has secured approval at this time for only the first phase of the condominium project. When approval for the second phase is secured, the applicant intends to add an additional 11 slips. Water quality In his initial pleading, Petitioner made a general allegation that the Department failed to consider "the long term health of Big Lagoon"; there were no specific allegations regarding water quality standards. In his Proposed Recommended Order, however, he argues that the [a]pplicant failed to provide reasonable assurances that water quality standards would not be violated." Assuming arguendo that the issue has been properly raised, Petitioner has still failed to substantiate his allegation. That portion of Big Lagoon where the project will be located is a Class III water of the State. Studies on metals, greases, oils, and the like submitted by the applicant reflected that the "water quality [in that area] did not exceed the standards in Rule 62-302." To provide further reasonable assurance regarding water quality standards, the applicant has voluntarily agreed to use concrete piling and aluminum docks. Unlike wooden piling and docks, these types of materials do not leach toxic substances such as arsenic, copper, and acromiom into the water. In addition, special permit conditions require that sewage pumpout equipment be located at the site so that boats will not discharge raw sewage into the waters. Liveaboards are prohibited, and fueling will not be available at the facility. Finally, the cleaning of fish is not allowed, and boat owners cannot scrape their boat bottoms while docked at the facility. All of these conditions are designed to ensure that water quality standards will not be violated. Enforcement mechanisms for the above conditions are found in either the permit itself or Chapter 403, Florida Statutes. Also, one of the conditions in the draft permit expressly states that the applicant is not relieved of liability for harm or injury to humans, plants, or property caused by the construction of the dock. However, if a permit is issued, Condition 9 of the permit should be modified to require that trained personnel be available twenty-four hours per day, rather than just during standard business hours, to assist boaters with, and ensure that they use, the sewage pumpout equipment. Any permit issued should also require that boats be placed on lifts while using the docking facilities. This will prevent any leaching of paint from the boat bottoms into the waters. Otherwise, the paint would cause a degradation of the water. The more persuasive evidence supports a finding that, with the additional conditions, reasonable assurance has been given that the state water quality standards applicable to Class III waters will not be violated. Outstanding Florida Waters In his complaint, Petitioner has contended that "the proposed activity will degrade an [OFW] as a result of its close proximity to the Gulf Islands National Seashore," and that the"[D]epartment has made no analysis of this project['s] impact on the [OFW] which is adjacent to the proposed activity." The record discloses that the southern portion of Big Lagoon has been designated as an OFW. This area includes the waters around Gulf Islands National Seashore and Big Lagoon State Park; they begin approximately 650 to 700 feet south of the end of the dock. As noted earlier, the project is located within Class III waters. Because the Department found that no violation of state water quality standards in those waters would occur, it likewise concluded, properly in this case, that the project would have no impact on any OFW, even though such waters begin some 650 or 700 feet away. Under these circumstances, there would be no reason to assess the water quality in the OFWs or the projected impacts on those waters, as Petitioner suggests. In the absence of any credible evidence to the contrary, it is found that the project will not adversely impact an OFW. Hydrographic characteristics If a dock has more than ten boat slips, the Department routinely conducts a hydrographic (flushing) study to determine whether the structure will adversely affect the flow of the water in the area or cause erosion or shoaling on adjacent properties. In the summer of 1999, a Department engineer conducted a hydrographic study using a dye tracer and concluded that flushing characteristics were excellent and that there would be no adverse effects caused by the project. This conclusion has not been credibly contradicted. Therefore, it is found that the dock will not adversely affect the flow of water or cause harmful erosion or shoaling. Navigational issues In his initial pleading, Petitioner raised a contention that the project will create "navigational hazards" because the dock "extends nearly into a navigation channel which routinely carries commercial towboats transporting hazardous material, the spill of which would adversely affect Big Lagoon." He also alleges that the rupture of a vessel could impact public safety. Channel markers placed by the U.S. Army Corps of Engineers in the Intracoastal Waterway (of which Big Lagoon is a part) define a navigational channel for boats approximately 400- 500 feet south of the end of the proposed dock. That channel is used by both recreational and commercial traffic, including barges and other large watercraft which regularly haul oil, chemicals, and other products through the Intracoastal Waterway to and from Pensacola, Panama City, and St. Marks, Florida. The water in the marked channel is only thirteen feet deep. Because the U.S. Army Corps of Engineers has jurisdiction over the maintenance of the marked channel, the Department defers to that entity's judgment in determining whether a proposed structure will impede navigation in the marked channel. The proposed dock ends near the deepest part of the natural channel where the water reaches a depth of seventeen feet. Because of the deeper water to the north, which allows the boat captain to "get better steerage," the commercial boat traffic sometimes tends to follow the natural channel, rather than the marked channel formed by the navigational aids. When they do so, however, they are straying from the so-called "legal" channel. Petitioner's expert, a retired tugboat captain, opined that in a storm or squall, a commercial boat using the natural rather than the marked navigational channel might be blown extremely close to the dock or even strike it, thus causing a hazardous situation. He acknowledged, however, that he was not predicting more accidents because of the construction of the dock; he also admitted that the dock would not cause ships to "sudden[ly] have problems navigating that Big Lagoon." The location of the proposed dock was shown to the U.S. Army Corps of Engineers and the Florida Marine Patrol, and there were no adverse comments regarding this issue by either agency. In the absence of any negative comments by those agencies, and the acknowledgement by Petitioner's own witness that the dock will not cause accidents or create navigational problems for other boaters, the more persuasive evidence supports a finding that the project will not adversely affect navigation or public safety in Big Lagoon. Seagrass and monitoring Petitioner has alleged that Big Lagoon "is the healthiest body of water in Escambia County with a white sand bottom and abundant seagrass," and that the proposed project will adversely affect its "long term health." He also alleges that the Department has failed to provide a "remedy or punishment should the results [of the Department's monitoring plan] indicate that the seagrass has been harmed"; that the Department's monitoring plan is not "of sufficient duration to reasonably report the long-term effect of concentrated mooring and traffic" or "sufficiently specific to insure usable data"; and that the data relied upon by the Department [such as photographs] were not "sufficient" to determine the existing health of the seagrass. The evidence reflects that a "nice, healthy seagrass community" is found in the area where the dock will be constructed. It stretches out several hundred feet from the shoreline to where the water reaches a depth of around six feet. The Department considers seagrass to be a "most important resource" which should be protected. This is because seagrass is essential for "binding" the shoreline and stabilizing the sediments, and it serves as a nursery area for juvenile fish and shellfish. Indeed, due to these beneficial effects, far more species of shellfish are found in areas where seagrass thrives than in areas where no seagrass exists. To protect the seagrass, the dock has been extended out 442 feet from the shoreline so that the first boat slip begins at a depth of seven feet, or just past where the seagrass ends. This will prevent the scarring of the grass by boat propellers and reduce turbidity that is typically caused by propeller dredging and boat wakes. Thus, at least theoretically, no boat activity by condominium owners is contemplated in waters of less than seven feet. Because seagrass requires as much light as possible to survive, educational signs will be posted in the area to warn boaters that seagrass is found closer to the shoreline, and that mooring in that area is prohibited. There is, however, no enforcement mechanism to ensure that condominium owners or nonresidents comply with these warnings. Under the draft permit, the Department is allowed to access the premises at reasonable times for sampling or monitoring purposes. A special section of the draft permit includes a number of requirements pertaining to the monitoring of turbidity levels during dock construction while another section requires the applicant to take photographs of the existing seagrass beds at numerous locations before, during, and after construction of the dock. Condition 14 requires that the permittee maintain "records of monitoring information" for at least three years. The evidence supports a finding that if a permit is issued, a mapping of the seagrass should be made prior to construction of the dock and during the height of the growing season (September and October). When the photographing of the area is performed, the applicant should use a sampling protocol that is based on a scientifically determined method. Also, both affected and unaffected areas should be monitored to compare the effect of the additional boat traffic on the seagrass after the dock is constructed. All of these conditions should be incorporated into any issued permit. According to Dr. Heck, a marine biologist who specializes in the study of seagrass and testified as an expert on behalf of Petitioner, seagrass beds in Big Lagoon have been "shallowing up" or thinning out in recent years due to decreasing water clarity. In other words, as the water becomes cloudier from more and more boat activity, the sunlight cannot penetrate and the seagrass will not thrive. The seagrasses most susceptible to disappearing are those that are found at the deepest depth. Doctor Heck attributed the decline in seagrass to increased human activity in the area. This activity is related not only to the existing homeowners in the area, but also to the non-resident boaters (both recreational and commercial) who use the waters in that area. A Department study conducted in 1995 confirmed that the only seagrass area in North Florida "significantly affected" by propeller scarring was an area in Big Lagoon known as Scallop Cove, near Spanish Point. This study is consistent with those studies performed by Dr. Heck in the late 1990's, and one as recently as last year, that support a finding that seagrass in Big Lagoon is on the decline due to both propeller scarring and increased turbidity caused by wakes from larger recreational boats. For this reason, Dr. Heck concluded that the addition of thirty boats at the project site, some of which would be as large as 30 feet or so, would have a "negative effect" on the seagrass colony. This in turn will cause a negative effect on the marine productivity in the area, as well as the conservation of fish and their habitat. Doctor Heck's testimony on this issue is found to be the most persuasive. Other concerns Petitioner further contends that the Department failed to provide a "meaningful contingency plan for hurricane activity." This matter, however, is beyond the permitting jurisdiction of the Department. Petitioner has also contended that the Department failed to take into account "existing unused marina slips close by" which could be used by the condominium owners. Like the prior issue, this matter is not a consideration in the permitting scheme. Another issue raised by Petitioner, albeit untimely, was that the construction of this dock could lead to further development in Big Lagoon. There was, however, no evidentiary support for this contention. Indeed, there is no evidence that future permit applications with impacts similar to this application can reasonably be expected in the area. At hearing, Petitioner raised for the first time a contention that the applicant no longer owns the upland property and thus a permit/authorization cannot be issued to that entity. Aside from this issue being untimely, the fact that a permit holder does not own the upland property is not unusual. If this occurs, permits and authorizations (leases) are routinely transferred to the new owner once the Department receives the necessary title information. It is not a ground to defeat the application. Petitioner also raised for the first time at hearing a contention that the site plan approval for the condominium has expired under a provision of the Escambia County Land Development Code and therefore the permit should be denied. Again, the issue is untimely; more importantly, it should be addressed in another forum since the Department has no jurisdiction over this issue. Likewise, a legitimate concern by an adjoining property owner, witness Hobgood, and an area realtor, that Hobgood's single-family property would probably decline in value if the project is built is nonetheless beyond the Department's jurisdiction. Finally, a contention that the Department improperly calculated the maximum number of boat slips for an 88-unit condominium project has been rejected. The record contains a lengthy explanation by witness Athnos which shows that the Department's calculation under Rule 18-21.004(4)1., Florida Administrative Code, was correct. Those calculations are also detailed in Respondents' Exhibit 14.
Recommendation Based on the foregoing findings of fact and conclusions of law, it is RECOMMENDED that the Department of Environmental Protection enter a final order denying the application of ADR of Pensacola for a wetland resource permit and sovereign submerged lands authorization. DONE AND ENTERED this 28th day of February, 2001, in Tallahassee, Leon County, Florida. DONALD R. ALEXANDER Administrative Law Judge Division of Administrative Hearings The DeSoto Building 1230 Apalachee Parkway Tallahassee, Florida 32399-1550 (850) 488-9675, SUNCOM 278-9675 Fax Filing (850) 921-6847 www.doah.state.fl.us Filed with the Clerk of the Division of Administrative Hearings this 28th day of February, 2001. COPIES FURNISHED: Kathy C. Carter, Agency Clerk Department of Environmental Protection 3900 Commonwealth Boulevard Mail Station 35 Tallahassee, Florida 32399-3000 Michael L. Guttmann, Esquire 314 South Baylen Street, Suite 201 Pensacola, Florida 32501-5949 Charles T. Collette, Esquire Department of Environmental Protection 3900 Commonwealth Boulevard Mail Station 35 Tallahassee, Florida 32399-3000 David A. Sapp, Esquire 1017 North 12th Avenue Pensacola, Florida 32501-3306 Teri L. Donaldson, General Counsel Department of Environmental Protection 3900 Commonwealth Boulevard Mail Station 35 Tallahassee, Florida 32399-3000
Findings Of Fact Based on the stipulations and admissions of the parties, on the exhibits received in evidence, and on the testimony of the witnesses at hearing, I make the following findings of fact. Facts admitted by all parties The water quality standards contained in Rule 17-3.111, Florida Administrative Code will not be violated by this project. There are no aquatic macrophytes located in the area of the proposed project. The proposed project is located within 500 feet of the incorporated municipality of Horseshoe Beach, Florida. The proposed project is located within Class II waters of the State not approved for shellfish harvesting. The project will not adversely affect the conservation of fish and wildlife, including endangered or threatened species, or their habitats. The proposed project will be of a permanent nature. The project will not adversely affect or will not enhance significant historical or acheological resources under the provisions of Section 267.061, Florida Statutes. The rest of the findings The Applicant, Dixie County, applied for a dredge and fill permit to construct a dock which would expand the existing public dock at Horseshoe Beach. In accordance with the revised plans dated October 23, 1986, the proposed facility would consist of a pier 6 feet wide and 120 feet long designed to accommodate six boat slips, each 30 feet wide and 40 feet long. The boundaries of the boat slips will be demarcated by pilings set 10 feet apart. Four of the boat slips would be primarily for the use of commercial fishing boats and commercial shrimping boats. The other two boat slips (the two slips closest to the land) would be reserved for the exclusive use of recreational and other small vessels. By adding a catwalk 3 or 4 feet wide down the middle of the two slips reserved for recreational vessels, the usefulness of those slips to recreational vessels would be greatly enhanced and the narrowness of the resulting slips would preclude their use by large vessels. Adding the two catwalks would be a minor addition to the proposed project which would greatly enhance the usefulness of the project and at the same time avoid the possibility that large vessels in the two slips closest to the land would impede ingress and egress at the nearby boat lift, boat fueling facility, and boat ramp. Adding a reasonable number of permanent trash or garbage containers would also enhance the usefulness of the proposed project and minimize the possibility of improper disposal of trash and garbage which is generated by the normal use of a dock by fishermen and boaters. The proposed project site is located in the Gulf of Mexico at Horseshoe Beach, Florida, and would extend into the waters of the Gulf, which is a tidally influenced water body adjacent to Dixie County, Florida. The water along the shoreline of the area is shallow for a considerable distance waterward, except where basins and channels have been dredged. The Horseshoe Beach area is relatively unpolluted. The existing public dock at Horseshoe Beach is used primarily by recreational vessels, but there is also extensive commercial fishing and Shrimping boat activity in the area. The project is located at the mouth of a canal with direct access to the Gulf. Several commercial fishhouses operate from the canal bank, which generates extensive commercial boat traffic past the proposed project site. Large numbers of commercial shrimp boats presently dock along the canal that ends near the proposed project site. The proposed project requires no dredging. The only filling required by the proposed project is the placement of pilings into the bottom of the Gulf of Mexico. Even though the plans do not specify whether concrete or wooden pilings will be used, this lack of specificity in the plans is irrelevant. Regardless of what types of pilings are used on this project, the filling activity will not violate the water quality criteria contained in Rule 17- 3.051(1), Florida Administrative Code. The placement of the pilings will not adversely affect the public health, safety, and welfare. Further, the proposed project will not adversely affect any property interests of the Petitioners within the scope of Chapter 403, Florida Statutes. The Gulf bottom in the area of the proposed project has already been disturbed. The presently existing suspension of particulate material in the water column, a natural occurrence in the area of the project, results in low visibility which means that seagrass beds and other marine vegetation, which provide shelter and detrital deposits for fish and other marine resources, will not grow. Coast Guard regulations prohibit commercial fishing vessels from depositing materials into the water within three miles of the coast line. Commercial fishing vessels must prominently display a sticker reciting that regulation and it is the practice of commercial fishing vessels operating in the vicinity of Horseshoe Beach to comply with this Coast Guard no discharge requirement by cleaning nets and scrubbing decks outside the three mile limit. It is not the practice of Commercial fishing vessels to deliberately discharge diesel fuel, fish parts or other material into the water while docked. Further, the limited number of commercial fishing vessels which could dock at the proposed facility at the same time cannot reasonably be expected to create discharges in amounts creating a nuisance, posing any danger to the public health safety or welfare, or violating the water quality criteria contained in Rule 17-3.051(1), Florida Statutes. Although small amounts of diesel fuel can become mixed with bilge water and be discharged by automatic bilge pumps while commercial fishing vessels are docked, there is no evidence that this would be in amounts Sufficient to create a nuisance or violate water quality criteria. To the contrary, notwithstanding a large amount of commercial boat traffic past the proposed site and notwithstanding the fact that large numbers of shrimp boats dock up the canal from the proposed site, the water in the area of the proposed site has remained relatively unpolluted. The proposed project will not affect the normal wind and wave action in the area of the proposed project. Such wind and wave action presently results in free exchange between the waters of the open Gulf and the waters near the shore. This free exchange of waters means that any pollutant discharges in the area of the proposed project will be diluted and rapidly dispersed into the Gulf of Mexico. There will be no measurable difference in the wind and wave action, or in the water exchange, after the proposed project is built. No harmful shoaling or erosion is expected to result from construction of the proposed project. Any docking structure extending out into the Gulf of Mexico will obviously have some effect on navigation in the area of the dock, but there is no evidence that the proposed dock will present a hazard to navigation or any significant interference with customary navigation patterns. The distance between the nearest channel marker and the waterward end of the proposed project is more than 200 feet. The angle of the proposed dock and its Spatial relation to the main Horseshoe Beach turning basin cause no impediment to navigation. The placement of Coast Guard Safety lights on the dock would minimize any potential for impeding navigation or posing a danger to the public health or safety during hours of darkness.
Recommendation Based on all of the foregoing, I recommend that the Department of Environmental Regulation issue a Final Order in this case granting the permit applied for by Dixie County. It is also recommended that the permit be made subject to the following additional conditions: That one or more Coast Guard safety lights be placed on the proposed expansion to the dock; That catwalks be added down the middle of the two most landward of the proposed boat slips; and That a reasonable number of trash or garbage receptacles be permanently located on the proposed expansion to the dock to minimize the possibility of trash and garbage being thrown overboard. DONE AND ENTERED this 30th day of October, 1987, at Tallahassee, Florida. MICHAEL M. PARRISH, Hearing Officer Division of Administrative Hearings The Oakland Building 2009 Apalachee Parkway Tallahassee, Florida 32399-1550 (904) 488-9675 Filed with the Clerk of the Division of Administrative Hearings this 30th day of October, 1987. APPENDIX TO RECOMMENDED ORDER, CASE NO. 86-1448 The following are my specific rulings on all of the proposed findings of fact submitted by all of the parties. The paragraph numbers referred to below are references to the paragraph numbers in the parties' respective proposed recommended orders. Ruling on findings proposed by the Petitioners: Paragraph 1: Accepted. Paragraph 2: Accepted. Paragraph 3: Accepted. Paragraph 4: First sentence is rejected as appearing to be more in the nature of an introduction to a discussion of legal issues than a proposed finding of fact. Second and third sentences are rejected as repetitious Paragraph 5: Entire paragraph rejected as unnecessary speculative generalizations in light of the other evidence in this case. Paragraph 6: Entire paragraph rejected as unnecessary speculative generalizations in light of the other evidence in this case. Paragraph 7: Rejected as contrary to the greater weight of the evidence. Paragraph 8: Entire paragraph is rejected as appearing to be more in the nature of an introduction to a discussion of legal issues than proposed findings of fact. Paragraph 9: Entire paragraph rejected as contrary to the greater weight of the evidence; construction of the dock may be expected to bring about some changes in the nature of the boat traffic in the immediate area, but nothing of the nature or magnitude suggested by these proposed findings. Paragraph 10: Rejected as contrary to the greater weight of the evidence. Paragraph 11: First sentence is rejected as contrary to the greater weight of the evidence. Second sentence is accepted in part and rejected in part. Rejected portion is irrelevant. Third sentence is rejected as irrelevant. Fourth Sentence is accepted. Fifth sentence is rejected as contrary to the greater weight of the evidence and as repetitious Sixth sentence is rejected as contrary to the greater weight of the evidence. Paragraph 12: Entire paragraph rejected as contrary to the greater weight of the evidence. Rulings on findings Proposed by the Respondent: Paragraph 1: Accepted. Paragraph 2: Accepted in substance. Paragraph 3: First two sentences accepted in substance. Last sentence rejected as irrelevant. Paragraph 4: Accepted. Paragraph 5: Accepted. Paragraph 6: Accepted. Paragraph 7: Rejected as unnecessary recitation of opposing party's contentions and not proposed finding of fact. Paragraph 8: Accepted in substance. Paragraph 9: Accepted in substance. Paragraph 10: Accepted. Paragraph 11: Accepted in substance. Paragraph 12: Accepted. Paragraph 13: First sentence accepted in substance. Second sentence accepted in part and rejected in part; rejected portion concerns riparian rights, which are irrelevant to whether this permit should be issued. Paragraph 14: Entire paragraph rejected as irrelevant. Paragraph 15: Accepted in substance. Paragraph 16: Accepted. Paragraph 17: Accepted in substance. COPIES FURNISHED: Frederick M. Bryant, Esquire Moore, Williams & Bryant, P.A. Post Office Box 1169 Tallahassee, Florida 32302 J. Doyle Thomas, Esquire County Attorney Post Office Box 339 Cross City, Florida 32628 Ann Cowles-Fewox, Legal Intern Twin Towers Office Building 2600 Blair Stone Road Tallahassee, Florida 32399-2400 Karen Brodeen, Esquire 2600 Blair Stone Road Tallahassee, Florida 32301 Dale Twachtmann, Secretary Twin Towers Office Building 2600 Blair Stone Road Tallahassee, Florida 32399-2400
Findings Of Fact Sea Isles Condominium Association (Petitioner) is the riparian owner of lands at 25714 Hickory Boulevard, Bonita Springs, Florida 33923. The Petitioner's lands lie along the Broadway Channel connecting the Gulf of Mexico to Estero Bay. There are 84 upland units in the condominium. Some condominium residents without docking slips have requested that the Petitioner apply for expansion of the existing facility. The waters adjacent to Petitioner's upland property are located within the Estero Bay Aquatic Preserve (pursuant to Section 258.39(28), Florida Statutes) and are designated as Outstanding Florida Waters (OFW) by the Department of Environmental Regulation (DER). At some point in approximately 1982, the condominium developer sought approval for the construction of docking facilities. By letter of January 25, 1982, Richard P. Ludington, then Director of the Division of State Lands of the Department of Natural Resources (DNR), indicated that there was no objection to the proposed dock project. The parties to this case have jointly stipulated that the Ludington opinion was based on the fact that the proposed project was a private non-income producing facility (a lease therefore not being required) and was not in conflict with any existing rules. The DER issued permit number 36-42521-5E, dated February 9, 1982, and the U.S. Army Corps of Engineers issued general permit number SAJ-33, both approving and authorizing the construction of the docking facility. Although the water body had been designated as an aquatic preserve, there were no adopted administrative rules regulating such projects at the time of the initial dock construction. The approved sixteen slip docking facility was constructed along the margin of the shoreline in 1983 by the developer of the condominium. Due to extremely shallow water depths, only two of the slips were accessible. At some point thereafter, the Petitioner began efforts to remedy the unusable slip situation. Initially, the Petitioner desired to dredge the area, but was unable to secure approval to dredge from regulatory agencies. The Petitioner then began to consider additional solutions. The solution upon which the Petitioner decided was removal of the existing slips and construction of an extended boardwalk and dock located in navigable water. On March 28, 1985, the DNR notified the Petitioner that the project would require approval in the form of a submerged land lease from the Governor and Cabinet, sitting as the Board of Trustees of the Internal Improvement Trust Fund ("Board"). On August 20, 1985, the DER issued permit number 361011295, authorizing the removal of the existing structure and the construction of a 22 slip docking facility as proposed by the Petitioner. On behalf of the Board, the DNR reviews applications for leases of sovereignty submerged lands. In reviewing such requests, the DNR calculates the maximum amount of sovereignty submerged lands which may be preempted by a proposed facility. According to administrative rule, the area of sovereignty submerged land preempted by a private residential multi-slip docking facility may not exceed the total square footage equal to ten times the riparian waterfront footage of the affected waterbody. DNR's calculation of the affected shoreline indicated that the Petitioner's riparian waterfront measured 433 feet. Application of the 10:1 ratio would indicate that the area of sovereignty submerged land preempted by the proposed multi-slip docking facility could not exceed 4330 square feet. As early as 1986, a surveyor employed by the Petitioner believed the DNR shoreline calculation to be erroneous and determined the Petitioner's riparian shoreline to be 601 feet. After discussing the discrepancy between measurements, the DNR representative informed a representative of the Petitioner that Sea Isles could obtain a mean high waterline survey to determine the actual shoreline footage if it disagreed with the DNR calculation. Although there is testimony that a survey provided to the DNR established the mean high waterline, the greater weight of the evidence establishes that the survey was not identified as a mean high waterline survey, but as a safe upland line survey. No credible mean high waterline survey was provided to the DNR by the Petitioner at that time. Abutting the Petitioner's property to the south is a man-made channel which results in an unnatural extension of the shoreline. Such extensions are not included in computing the allowable square footage of sovereign submerged lands because the man-made shoreline does not abut sovereign submerged lands. It is unclear whether the calculations of shoreline were affected by this consideration. Despite the discrepancy, the Petitioner reduced the size of the requested docking facility to include a boardwalk and dock of ten slips totalling approximately 4300 square feet and extending 208 feet into the waterbody (approximately 35 percent of the waterbody's width). The length of the extension violates administrative rule provisions governing extension into a waterbody which are addressed elsewhere herein. On July 23, 1986, Lee County passed a resolution of approval for the proposed docking facility land lease and granted a variance to Lee County Ordinance 85-25. The resolution of approval contained additional requirements, included a provision restricting the approval to not more than ten slips. The Petitioner asserts that the determination of shoreline was incorrect and was the result of "mutual mistake". The evidence fails to establish that the Petitioner's acceptance of the DNR's shoreline determination was based upon "mutual mistake." The evidence establishes that the Petitioner's representatives were aware of the discrepancy. The fact that the Petitioner agreed to deed a 575 foot conservation easement to the Board (to offset the potential adverse impact on manatee habitat as discussed elsewhere herein) would suggest that the parties were aware that the 433 foot measurement was inaccurate. For whatever reason, the Petitioner agreed to the DNR shoreline and dock calculation which formed the basis for the lease approved by the Board. Prior to approval of the lease, the Board reviewed a written "public interest" assessment which indicates that the length of the boardwalk to the proposed docking facility exceeded standards set by administrative rules. Pursuant to rule, exceptions to length restrictions may be made only where the applicant demonstrates that such exception is necessary to insure reasonable riparian ingress and egress. The Petitioner apparently demonstrated that, given the location of the existing sand flat, such exception was necessary to provide ingress and egress. According to the written analysis, the proposed project adversely impacted the manatee habitat located in the aquatic preserve. The analysis states that 575 foot conservation easement to the Board would offset the potential adverse impact on manatee habitat. The Petitioner committed to the conservation easement in order to meet the public interest test required of all docking facilities within an aquatic preserve. Special lease condition paragraph 5 requires the Petitioner to record a conservation easement for approximately 575 linear feet of shoreline in perpetuity to run with the land. The provision requires that documentation of the recording of the easement be provided to the Board within thirty days of the Board action and prior to execution of the lease. The lease conditions clearly indicate that the Petitioner will not seek authority to expand the docking facility. Special lease condition paragraph 5 prohibits any additional docking facilities or any other such development along the lessee's shoreline. Review of proposed special lease condition paragraph 6 (as compared to the staff recommendation and a subsequent affidavit executed by the Petitioner's representative on June 6, 1987) indicates that the paragraph appears to contain a typographical error in deleting the word "not" from the condition. The greater weight of the evidence establishes that the Petitioner agreed not to request authorization to dredge the docking area or channel or to request additional expansion of the facility. On April 21, 1987, the Board, apparently acting against the staff recommendation, voted to grant to the Petitioner a submerged land lease for the construction of a ten slip facility. Representatives of the Petitioner appeared before the Board during consideration and approval of the lease. On June 6, 1987, a representative of the Petitioner executed an affidavit on behalf of the Petitioner which sets forth the language of special condition paragraph six as originally proposed. In the affidavit, the Petitioner's representative agrees not to apply for authorization to dredge the dock or access channel, or to request expansion of the facility. A deed of conservation easement dated October 21, 1985, and signed by a representative of the Petitioner, was attached to the materials submitted to the Board for the April 21, 1987 meeting. Contrary to the lease requirement, the attached deed of conservation easement was never recorded. In 1986 or 1987, a conservation easement was recorded by the Petitioner in favor of the Board, but the easement contained no legal description of the subject property. However, the recorded easement does prohibit additional docking facilities and waives the Petitioner's rights of ingress or egress related to any such additional facilities. In early 1991, the Petitioner requested approval to expand the existing dock from 10 to 14 slip. The expanded structure would preempt 5620 square feet of sovereign submerged land. On May 15, 1991, the DER granted approval of the four slip expansion. On November 27, 1991, the DNR, by letter signed by Michael E. Ashley, Chief of the Bureau of Submerged Lands and Preserves, denied the requested four slip expansion. The letter was prepared at the direction and with the approval of the Director of the Division of State Lands. Mr. Ashley cites two reasons for the denial. First, the request violated the terms of the existing lease which provides that there will be no expansion requested. Second, the Petitioner had failed to record the 575 foot conservation easement which was required by the terms of the original lease. The request for extension was not presented to the Governor and Cabinet for consideration, but was reviewed by the "agenda review committee" of the DNR. The committee includes the Deputy Director, two Deputy Assistant Executive Directors, the General Counsel, and the Cabinet Coordinator for the DNR. The committee reviews matters which are identified as potentially requiring Board action to resolve. Where issues exist related to existing sovereignty submerged land leases, the DNR attempts to resolve the matter without referral to the Board. The authority to conduct business in this manner has not been reduced to writing, but is based on verbal direction from the Board and from Cabinet assistants. Subsequent to the letter of denial issued by Mr. Ashley, the Petitioner on or about December 30, 1991, filed a conservation easement granting to the Board, a perpetual interest in a parcel of land lying ten feet landward of the Safe Upland Line as described in the deed recorded in the records of Lee County, Florida, (OR 2268, Page 0401) with the Clerk of Court for Lee County. The parcel of land identified in the deed runs along the shoreline for a distance of 601 feet. The easement provides for modification by the signed agreement of the parties. Because the Petitioner seeks to expand an existing lease, it is required to demonstrate an additional public benefit would result from approval of the request. The Petitioner has proposed to plant an area of mangroves in the shallow "sand bar" area located behind the existing slips. There is no additional public benefit related to the request. The evidence fails to establish that granting the request to expand the docking facility is in the public interest.
Recommendation Based on the foregoing, it is hereby RECOMMENDED that the Board of Trustees of the Internal Improvement Trust Fund enter a Final Order denying the request of Sea Isles Condominium Association to modify the existing sovereignty submerged land lease to provide for four additional boat slips to their existing ten slip docking facility. DONE and RECOMMENDED this 15th day of April, 1993 in Tallahassee, Florida. WILLIAM F. QUATTLEBAUM 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 15th day of April, 1993. APPENDIX TO RECOMMENDED ORDER, CASE NO. 92-1077 The following constitute rulings on proposed findings of facts submitted by the parties. Petitioner The Petitioner's proposed findings of fact are accepted as modified and incorporated in the Recommended Order except as follows: 17. Rejected, not supported by the greater weight of credible and persuasive evidence. 19. Rejected as to comments by Miller, irrelevant. 20-21. Rejected, irrelevant. Rejected as to 6,010 square feet of permissible preemption. Based upon shoreline calculation which is not supported by the greater weight of credible and persuasive evidence. Rejected, irrelevant. The manatee information was required under the conditions of the existing lease, and do not constitute a benefit to be considered in addressing the request to modify the lease. Respondent The Respondent's proposed findings of fact are accepted as modified and incorporated in the Recommended Order except as follows: 16. Rejected, unnecessary. COPIES FURNISHED: The Board of Trustees of the Internal Improvement Trust Fund c/o Kenneth Plante, General Counsel Department of Natural Resources 3900 Commonwealth Boulevard Mail Station #10 Tallahassee, FL 32399-3000 Robert Routa, Esquire Post Office Drawer 6506 Tallahassee, Florida 32314-6506 L. Kathryn Funchess, Esquire Assistant General Counsel Department of Natural Resources 3900 Commonwealth Boulevard Mail Station #35 Tallahassee, Florida 32399-3000
Findings Of Fact Sunset Company of Wilton, Incorporated, is the record title owner of a parcel of real property in Government Lot 1, Section 5, Township 66 South, Range 33 East, on Crawl Key No. 3 also known as Fat Deer Key, Monroe County, Florida. A portion of that parcel has been conveyed by Sunset Company to Whaler's Plaza, Incorporated, although that deed may not have been recorded. Petitioner Fred Roth owns and controls both corporations and exerts ownership and control over the entire parcel. The submerged lands in Tarpon Creek which are waterward of the line of mean high water contiguous to the parcel are sovereignty submerged lands. Roth received "major development" approval from Monroe County to develop the parcel by constructing a commercial/retail development known as "Whaler's Plaza.' The major development plan submitted to and approved by Monroe County includes a docking facility. In 1979 Roth filed an application with the Florida Department of Environmental Regulation for a private dock facility at Whaler's Plaza. The Department of Environmental Regulation approved that application and issued to Roth Permit/Certification No. 44-18542-5E. Roth never constructed that docking facility, and the permit expired on August 1, 1980. One of the agencies involved in reviewing that permit application was the Respondent. On June 26, 1979, Respondent notified Roth that upon review of the application in DER File No. 44-18542-5E, it had determined that the submerged lands were state-owned but that no lease agreement with Respondent would be required. After Permit No. 44-18542-5E expired on August 1, 1980, the Department of Environmental Regulation directed a letter to Petitioner advising him that the permit had expired and further advising him that if he wished to pursue the project he would have to obtain a new permit. in October 1983 Roth sought new authorization from the Department of Environmental Regulation and Respondent to construct a docking facility at Whaler's Plaza. His application was assigned DER File No. 440774875. On December 29, 1983, Respondent notified Roth that a lease would be required for the use of state-owned lands contiguous to Whaler's Plaza, relative to DER File No. 440774875. Respondent's rules changed in 1982 so that Roth's docking facility would be required to meet new criteria. The docking facility proposed by Roth in 1983 was similar to the docking facility proposed in 1979. The 1983 proposed modified docking facility was still represented to the Department of Environmental Regulation to be a private boat dock. The Department of Environmental Regulation issued an intent to deny the 1983 application under its then-existing rules, and Roth requested a formal hearing on that preliminary denial. Before a final hearing could be conducted, Roth again modified the proposed docking facility so that he qualified for a dredge and fill permit exemption from DER, so that no DER permit was needed for his project. A final order was entered by the Department of Environmental Regulation on August 27, 1985. While Roth's 1983 application was pending before the Department of Environmental Regulation, Roth was processing his application with Respondent for a submerged land lease for the docking facility. The documents he filed with Respondent, however, indicated that the docking facility was not intended to be a private dock but rather was a dock related to the commercial development at Whaler's Plaza. Roth represented to Respondent that the proposed docking facility would be for the convenience of patrons of the stores and restaurant at Whaler's Plaza and for his own personal use. Specifically, on June 3, 1985, Roth directed a letter to Respondent pursuant to Respondent's request for additional information. He described the Whaler's Plaza docking facility as follows: The wood dock will be used for arriving and departing customers of the restaurant and stores and my own personal use. The upland land use and activities of the property--will be developed into a shopping center. At the present time, the first phase is completed which is a one-story building containing four units, housing six retail stores, plus offices. The next phase will consist of three more buildings having five units each, 1,0000 [sic] sq. ft. each unit which will be for retail stores and offices, and the final phase will be a 200 seat restaurant, a miniature [sic] petting zoo and possibly a miniature golf course. ... 70 percent of the slips will be open to the general public for their convenience In patronizing the restaurant and stores; the remaining 30 percent of the slips will be for my own personal use. Roth never completed the lease application he filed with Respondent, and he failed to obtain approval for the use of the sovereignty submerged lands preempted by the docking facility proposed in DER File No. 440774875. Eventually, his pending application with Respondent was deactivated, and the file was closed. In late 1986, Roth initiated construction of his docking facility on sovereignty submerged lands, and he caused 30 pilings with cross-bracing to be placed into the submerged lands. On September 1, 1986, Grant Gelhardt, one of Respondent's enforcement officers, discovered the dock being constructed and verbally instructed Roth, through Mrs. Roth, to immediately cease construction activity. No further construction has taken place. Despite the verbal notification, a subsequent warning notice sent by certified mail, and Respondent's Notice of Violation and Order for Corrective Action, Roth has failed to remove the pilings and/or to take corrective measures regarding the partially completed docking facility. Roth has allowed vessels to be moored at the partially completed docking facility, has moored his own vessels at the partially completed docking facility, and has failed to prevent other persons from mooring at the partially completed docking facility. Roth's actions have resulted in damage to a benthic seagrass community on the adjacent sovereignty submerged lands over which Roth's partially completed docking facility is located, and over which vessels using the facility have been and would be moored. Those submerged lands constitute a benthic community of seagrass which supports various fauna and which would be adversely affected by completion and operation of the docking facility. The water depths in the area are shallow, with areas of less than -4 feet mean low water. The width of Tarpon Creek in the project area is approximately 100 feet. The length of the partially completed docking facility is approximately 150 feet. Although the dock extends parallel to the shore, the distance the dock extends into Tarpon Creek, as measured from the shoreline, is approximately 35 feet. Roth knowingly trespassed on sovereignty submerged lands by initiating construction of the docking facility, and he has willfully damaged those lands by drilling holes and placing pilings, and by allowing moored vessels to shade the seagrass. Although Roth ceased construction of the docking facility when told to stop, he has failed to attempt to resolve the violation, to remove the pilings, to seek an after-the-fact approval, or to cease all mooring of vessels on sovereignty submerged lands adjacent to the uplands, even subsequent to receiving the Notice of Violation and Order for Corrective Action. Respondent's June 26, 1979 letter to Roth authorized the activities described in DER Permit No. 44-18542-5E, for the period authorized by that permit. Roth knew that the DEP permit, and therefore Respondent's approval to engage in the activity authorized by that permit, had expired. Roth further knew that his new application filed in 1983, DER File No. 440774875, which was approved by DER after Roth further modified it in order to qualify for an exemption, did not exempt him from obtaining authorization from Respondent to use sovereignty submerged lands for the project and further knew that when he commenced construction of the docking facility in 1986 that he had not obtained approval from Respondent to use state-owned submerged lands. Roth offered no evidence to demonstrate any detrimental reliance upon the June 26, 1979, DNR letter, and the letter did not create a vested right for Roth to construct a different docking facility at a later time without authorization from Respondent. The uplands at the Whaler's Plaza commercial/retail development are owned by for-profit corporations which Roth controls and which derive income from the business and commercial activities at Whaler's Plaza. The docking facility intended primarily for the use of customers of Whaler's Plaza would therefore constitute a revenue generating/income related activity.
Recommendation Based upon the foregoing Findings of Fact and Conclusions of Law, it is, RECOMMENDED that a Final Order be entered requiring petitioner to: Remove the unauthorized structure within 20 days from the date on which the Final Order is entered and in accordance with Respondent's supervision of that removal; Immediately cease all mooring of vessels on sovereignty submerged lands adjacent to the uplands of the parcel known as Whaler's Plaza until authorized to use state-owned lands; and Pay a fine of $2500 within 15 days of receipt of a certified letter from the Executive Director of the Department of Natural Resources demanding payment to the internal improvement Trust Fund. DONE and RECOMMENDED this 31st day of October, 1988, at Tallahassee, Florida. LINDA M. RIGOT, Hearing Officer Division of Administrative Hearings The DeSoto Building 1230 Apalachee Parkway Tallahassee, Florida 32399-1550 (904) 488-9675 Filed with the Clerk of the Division of Administrative Hearings this 31st day of October, 1988. COPIES FURNISHED: David L. Manz, Esquire Post Office Box 177 Marathon Florida 33050 Ross S. Burnaman, Esquire Department of Natural Resources 3900 Commonwealth Boulevard Tallahassee, Florida 32303 Tom Gardner, Executive Director Department of Natural Resources 3900 Commonwealth Boulevard Tallahassee, Florida 32303
Findings Of Fact Upon consideration of my observation of the witnesses and their demeanor while testifying, documentary evidence received including the parties pre- hearing stipulation, the following relevant facts are found: Respondent DOT filed a dredge and fill permit based on its application filed with Respondent DER and proposed to upgrade a 4.9 mile segment of State Road 80 from a 2-lane roadway to a rural 4-lane divided roadway which included construction of new north and south bound bridges over a canal (designated as L- 8) and constructing a triple box culvert to replace the existing bridge over Callery Judge Canal, located from 20 mile bend to 5.5 miles west of State Road 7, Palm Beach County, Florida. (Joint Composite Exhibit 1). Respondent DER published the required notice of its intent to issue the applied for permit by DOT in the April 14, 1986 edition of the Palm Beach Post Times, a newspaper of general circulation. Petitioner is the fee simple owner of the property located to the west of Callery Judge Canal. Petitioner's property includes a drainage easement which has been given to the Seminole Water Management District and includes submerged portions of the canal. Callery Judge Canal is a water control structure. Callery Judge Canal is connected to another canal designated as C-51, which is also a water control structure. The length of Callery Judge from the C-51 Canal extends approximately 400 feet. There are water control structures at the end of Callery Judge Canal and approximately 4 miles both east and west of the C-51 Canal. As such, there is limited navigability of the C-51 Canal by Petitioner. The C-51 Canal is used by Petitioner and unidentified public members for recreational navigation purposes. There is no commerce navigation on either the C-51 or Callery Judge Canal. Petitioner currently has navigational access to C-51 through Callery Judge. Petitioner owns two boats which he has from time to time used on the Callery Judge Canal to get to the C-51 Canal. Both C-51 and Callery Judge Canal are Class 3 water bodies. Respondent DER has dredge and fill jurisdiction over both canals as they connect to state waters. Respondent DOT, in addition to publishing notice in the Palm Beach Post Times, sent written notice to adjacent property owners advising them of DOT's application and only Petitioner protested based on his claim of impaired navigation from Callery Judge to C-51. Additionally, Petitioner objected on the basis that the project would adversely affect his riparian rights of access to C-51 and that the effect of issuing of the requested permits would amount to the taking of private property without first making payment of full compensation to him. The existing bridge which expands Callery Judge Canal does not meet state safety practices inasmuch as there is only the approximately 2 feet between the edge of the travel lane to the face of the railing. This space provides only a 2 foot recovery lane for disabled vehicles. With the triple box culverts as applied for by DOT, an adequate recovery lane of approximately 10 feet will be provided which meets state safety requirements for recovery lanes. (Testimony of Midgett). The triple box culverts will allow for DOT to complete its planned widening of the bridge on both ends and thereby eliminate adverse safety concerns relating to traffic "bottle necking." Fish, alligators, and other wildlife will be able to continue passing from Callery Judge to C-51 after installation of the triple box culverts as proposed by DOT and therefore there will be no adverse impacts on fish and wildlife conservation. The proposed culverts will allow drainage to continue and water flow will not be constricted. Following construction of the triple box culverts, Petitioner may continue to enjoy other riparian rights that he presently enjoys. Thus, Petitioner may continue to swim and bathe in Callery Judge Canal. Petitioner may also continue to navigate Callery Judge for fishing and other recreational purposes. There are no marinas, boat lifts, boat ramps or other facilities on C- 51 or Callery Judge Canals which would provide navigation access to the canals by the general public. The one boat facility in either canal is a boat ramp in C-51 maintained by the South Florida Water Management District. The Palm Beach County Health Department, a local approved DER program, (pursuant to Section 403.916, Florida Statutes), reviewed the subject application and determined that DOT's application, with modifications incorporated in Respondent DER's intent to issue, provided the reasonable assurances and was in the public interest pursuant to Section 403.918(2), Florida Statutes. Petitioner's riparian rights to navigate Callery Judge Canal and access to C-51 would be impaired by the Respondent DOT's installation of the triple box culverts as applied for. However, when these adverse impacts are balanced against the other factors as required pursuant to Section 403.918(2), Florida Statutes, Petitioner's adverse impacts are considered to be negligible. Respondent DOT has provided Respondent DER reasonable assurances that water quality standards will not be violated based on the proposed project. Respondent DOT has provided Respondent DER reasonable assurances that by use of turbidity screens during construction of the culverts, turbidity values 50 feet down stream from the project site will not exceed 29 N.T.D.'s above background.
Recommendation Based on the foregoing Findings of Fact and Conclusions of Law, it is RECOMMENDED: That Respondent, Department of Environmental Regulation, grant Respondent, Department of Transportation, a dredge and fill permit as set forth with the conditions accompanied in its Notice of Intent to Issue, based on the determination herein that the proposed activities are not contrary to the public interest. RECOMMENDED this 18th day of December, 1986, in Tallahassee, Florida. JAMES E. BRADWELL Hearing Officer Division of Administrative Hearings The Oakland Building 2009 Apalachee Parkway Tallahassee, Florida 32399-1550 (904) 488-9675 Filed with the Clerk of the Division of Administrative Hearings this 18th day of December, 1986. APPENDIX TO RECOMMENDED ORDER, CASE NO. 86-1846 Rulings on Respondent, Department of Environmental Regulation's proposed Recommended Order. Paragraph 12, adopted as modified, paragraphs 12, 17 and 18, Recommended Order. Paragraph 13, adopted as modified, paragraphs 15 and 16, Recommended Order. Paragraph 18, rejected as unnecessary for resolution of the issues. Paragraph 19, adopted as modified, paragraph 15, Recommended Order. Paragraph 21, first sentence adopted and remainder rejected as being speculative or conclusionary. Paragraph 24 the parties Stipulation and other statements respecting the parties positions were not incorporated in the Recommended Order as being unnecessary or was not the subject of testimony based on the stipulation. Rulings on Respondent, Department of Transportation's proposed Recommended Order. Paragraph 1 adopted as modified, paragraph 8, Recommended Order. Statutory and Code provisions are not recited in the Recommended as findings of fact. However, official notice was taken of the pertinent rules, regulations and statutory provisions. Paragraph 4 substantially adopted, paragraphs 3, 4 and 5, Recommended Order. Paragraph 12 rejected as being unnecessary to determine the issues posed herein and based on the ultimate determination that the project was in the public interest, paragraph 15, Recommended Order. Rulings on Petitioner's proposed Recommended Order. Paragraph 5, first sentence attributable to Respondent, Department of Transportation, rejected as no evidence was introduced to substantiate that Respondent DOT was unaware that Petitioner was owner and holder of a riparian property right of access. Paragraph 4, last sentence rejected as evidence adduced indicates that Petitioner's rights to gain access between his riparian lands and the C-51 canal was considered, paragraph 16, Recommended Order. Paragraph 5, last sentence rejected as there was a determination that the proposed project was in the public interest and that any impairment of Petitioner's access was counter balanced against public considerations as required in Section 403.918(2), Florida Statutes. Paragraph 16, Recommended Order. Paragraph 6, rejected as being contrary to other credited evidence which indicates that the proper balancing test was in fact made. See paragraphs 10-18, Recommended Order which deals with the consideration of the public interest criteria set forth in Section 403.918(2), Florida Statutes. COPIES FURNISHED: Mark S. Ulmer, Esquire 200 SE Sixth Street, Suite 404 Ft. Lauderdale, Florida 33301 Mel Wilson, Esquire Department of Transportation Mail Station 58 605 Suwannee Street Tallahassee, Florida 32301 Karen A. Brodeen, Esquire Department of Environmental Regulation 2600 Blair Stone Road Twin Towers Office Building Tallahassee, Florida 32301 Victoria Tschinkel, Secretary Twin Towers Office Building 2600 Blair Stone Road Tallahassee, Florida 32301
Findings Of Fact Permitting History This development was originally known as North Largo Yacht Club and was owned and developed originally by the Largo Brand Corporation. That developer and this development received Development of Regional Impact approval from the county commission of Monroe County in accordance with Chapter 380, Florida Statutes in 1974. In 1975 that developer received various permits and water quality certifications authorizing construction of the "Atlantic Marina" (the existing marina) from both the Florida Board of Trustees of the Internal Improvement Trust Fund and the United States Army Corps of Engineers. The marina was ultimately constructed and no further governmental approvals are required for the present Respondents to make full use of the existing marina which has an authorized boat capacity of 363 boat slips, which are situated around long piers extending from the shore of the marina basin out into the marina basin. Sometime after construction of the marina, the mortgagee, through foreclosure, obtained title to the property from Largo Brand Corporation which has since dissolved, ultimately conveying it to City National Bank as trustee under a Florida land trust. City National Bank filed the present application in its original form but in February, 1984, conveyed the property to Port Bougainville, Inc. and Port Bougainville Enterprises, Inc., the present Applicant/Respondent who succeeded City National Bank as the real parties in interest prosecuting the present permit application, as modified. The permit application as it presently exists is the result of various modifications suggested by the Department of Environmental Regulation and agreed to by the present Applicant/Respondents, which had the effect of causing the Department to change its position from one of denial of the permit to one of approval, by issuance of a Notice of Intent to grant the permit in June of 1984. The Applicant/Respondent's original decision to apply for the new permit was based upon aesthetic considerations and a desire to redesign and change the theme of the development and the marina itself. It is thus proposed that the boat-mooring facilities be moved to the periphery of the basin and the piers or docks extending out into the basin be removed. This would create an open body of water in the basin, more in keeping with the "Mediterranean Village Harbor" theme of the entire development. The original application filed in early 1984, called for realignment of the docks rather than removal, and the creation of various baylets or inlets along the access canal and contained no proposal for shoaling the existing boat basin. The Department used this original proposal as a basis for its Intent to Deny the Permit Application since it considered those modifications unacceptable in terms of the likelihood that it might degrade water quality or at least not improve the ambient water quality then existing in the marina basin and entrance canal. The Respondents acceded to the demands of the Department, employed additional consultants and redesigned the project, including the creation of a sophisticated hydrographic model by which, and through which, the Respondents ultimately proposed (with the Department's agreement) to revise the application as follows: Shoal the entire basin and canal system to no more than -6 Ft. mean low water; widen and sculpt the access canal on the west side and install solid flow baffles on the east side so as to create a sinusoidal or curving configuration in the canal to improve mixing of the water in the canal and basin system; remove the existing docks and construct new docks around the periphery of the basin so as to provide a decreased number of boat slips and capacity for a total of 311 boats; install one bubble screen surrounding the fueling facilities to contain oil and fuel spills and another at the entrance of the access canal where it opens into the Garden Cove Channel so as to prevent organic materials from outside the canal and basin system from being carried into it with tidal currents and wind; installation of "batter boards" along the length of the waterward or easterly and southeasterly side of the access canal so as to protect the mangroves along that side of the canal from the effects of wake energy caused by boats. After further "free-form" review, investigation and negotiation, the Department required, and the Respondents agreed to make the following additional modifications to the marina development plan: Shoal the north end of the basin to -4 ft. mean low water; slightly reconfigure the access canal and install an additional wave baffle on the eastern periphery of the canal in order to improve circulation in the western portion of the boat basin; relocate the proposed fueling facilities more toward the rearward center of the basin in order to further isolate them from the outstanding Florida waters lying at the outward, "seaward" end of the project; provide funds necessary to more adequately mark the Garden Cove Channel in accordance with the requirements specified by the Department of Natural Resources so as to further ensure that boat traffic and possible propeller damage could be prevented to the marine grassbeds and other marine life on either side of the Garden Cove Channel; install tidal level gauges at the mouth of the Garden Cove Channel which would show boaters wishing to use the channel and access canal the current, minimum depths prevalent in the channel and canal; grant to the Department a "conservation easement" binding upon the Respondent which would provide the following: That no hydraulic connection be made from any of the upland lakes on the Respondent's property to the marina, to the canal, to the channel or any other state waters; an agreement not to employ boat lifts that would require a dredge and fill permit from the Department; an agreement not to apply for additional permits so as to increase the number of boat slips in the marina beyond the 311 presently proposed; to develop a reef management plan in conjunction with the Florida Audubon Society to include educational programs for the public as well as underwriting the installation of mooring buoys and adequate channel markers in the John Pennekamp Reef Park, the Outstanding Florida Waters (OFW) involved in this proceeding. During the time of construction of the proposed marina modifications, the entire marina will be closed and isolated from the waters of Garden Cove by the installation of a dam at the entrance to the marina access canal where it opens into Garden Cove. The dam will remain in place until turbidity resulting from the dredging, filling and construction has settled and the waters in the marina have achieved the turbidity standards required by the Department and its rules contained in Chapter 17 3, Florida Administrative Code. All the proposed modification work will be performed landward of the surveyed mean high water line. Additionally, a storm drainage system will be installed which will prevent any stormwater runoff from being deposited into the marina harbor. The stormwater runoff will be routed away from the harbor through the use of a reverse gradient around the periphery of the harbor and runoff from the adjacent real estate development will be thus routed away from the harbor into grass swales to be collected into holding areas for filtration. Ambient Water Quality in the Marina and Garden Cove Respondents tendered Dr. Earl Rich, a professor of Biology at the University of Miami as an expert in ecology and he was accepted without objection. Since 1974 he has conducted extensive studies with attendant sampling, observation and water quality monitoring in the Port Bougainville Marina. Beginning in 1983 he also performed certain chemical analyses on the water samples from the marina. Photographs taken underwater in the marina basin were adduced and placed in evidence, as were the results of the observations and tests. It was thus established that there is a dense growth of macroalgae in the marina at a depth of about six feet, although at the nine-foot level there is much less such growth. Concomitantly, the deeper holes in the marina basin exhibit a low dissolved oxygen reading and are largely responsible for the frequently occurring, low dissolved oxygen reading in the marina system that is lower than acceptable standards embodied in Chapter 17-3, Florida Administrative Code. Garden Cove itself is a shallow embayment open toward the Atlantic Ocean in a generally easterly direction, characterized by a rocky or coarse sediment bottom substrate. It is characteristic of this area that organic materials such as seaweeds and the like, are transported by currents and winds into Garden Cove from other marine areas. The underwater vegetation in Garden Cove is lush. There are extensive shallow-water marine grass beds. These vegetated areas support a large population of marine animals and fish. Dissolved oxygen is, of course, essential to the metabolism of these organisms. The two primary means for oxygen to enter the water are as a result of photosynthetic activity of marine plants and through oxygen entering the surface waters through waves and wind action, with that surface water being distributed and mixed so as to disburse the action throughout the water column. The term biochemical oxygen demand or BOD, refers to the rate at which organisms use oxygen in the water. If there are many active photosynthetic organisms, as in Garden Cove, the production of oxygen during the day, as for instance by the seagrasses in the cove, exceeds the BOD of the plant and animal community in the water body, in which case the plants contribute excess oxygen to the air. During hours of darkness, plant and animal communities in the water body will continue to consume oxygen although there will be no photosynthesis to contribute oxygen. Therefore, in an underwater community rich in plant and animal life, such as Garden Cove, the dissolved oxygen level is typically higher during the daylight hours and BOD readings will be decreased during the night, reaching a low level during the early morning hours. Frequently, dissolved oxygen readings in Garden Cove are below state standards for waters of the State under natural conditions. These low DO readings occur commonly in Garden Cove during conditions of calm wind. Indeed, Dr. Rich has measured dissolved oxygen in Garden Cove below the four-part per million state standard even before the present marina and canal were ever constructed. Since the opening of the marina there have been times when the DO readings in Garden Cove have been lower than those inside the marina itself. Hydrodynamics of the Modified Marina The proposal by the permit applicant calls for widening the access channel into the marina to approximately 130 feet by excavating upland on the western bank of the canal. The access canal will then be reconfigured during the excavation into a winding or curving fashion. That adjustment, along with the solid flow baffles to be installed on the eastern bank of the canal, will set up a winding or sinusoidal flow of tidal currents. The sinusoidal flow will induce secondary helical currents that will move water repeatedly from the top to the bottom of the canal and then back, thereby significantly improving the mixing action. The improved mixing of the waters in the canal and marina will serve two purposes: It will disperse any pollutants so as to reduce pollutant concentrations. It will disperse the oxygen introduced into the surface waters by wave and wind throughout the water column. Dr. Bent Christensen is Chairman of the University of Florida Hydraulics Lab. Using knowledge gained in hydrographic modeling as a result of work he performed in carrying out a "Sea Grant study" under the auspices of the University of Florida, Dr. Christensen designed a computer model of the proposed Port Bougainville marina and access canal by which, in turn, he designed the winding access canal which will emulate nature in producing a turnover of water induced by current velocities and canal configuration, rather than by temperature differences in water. The computer model takes into account tidal flows and wind-induced velocities which are important to mixing of water within the system. Using this model, Dr. Christensen was able to redesign the marina canal so as to improve water quality within that system as well as improving the quality of water leaving the system into Garden Cove. Drs. Lee and Van de Kreeke are ocean engineers who testified as expert witnesses on behalf of Petitioners. They sought to dispute Dr. Christensen's conclusion that the redesign would improve DO levels within the marina based upon their independent determination that a different design would increase flushing times for the system. Flushing, however, is a simplistic way of analyzing water quality. Flushing analysis assumes that the only means to improve water quality is to replace water within the system with water from outside the system. The Christensen model and the resulting proposed design of the marina and canal, on the other hand, improves water quality through internal mixing action. The proposed design actually reduces flushing time, but more importantly, maximizes dispersion of water within the system and along with it, dissolved oxygen. The design introduces dissolved oxygen throughout the water column in the system through internal mixing because of the sinusoidal configuration of the canal and the helical currents the canal configuration sets up. The concentration of pollutants measured by the State Water Quality Standards are, in turn, reduced through the same hydrodynamics. Dr. Van de Kreeke admitted that a key ingredient in his model was the assumption he had regarding BOD in the system, but he had no idea what the BOD extant in the Port Bougainville system might be. He also admitted that his calculations did not take into consideration the factor of wind mixing of the waters in the system and acknowledged that wind can and does play an important role in flushing and mixing the waters in marinas. Finally, Dr. Van de Kreeke admitted that he could not fully analyze Dr. Christensen's assumptions in arriving at his model and design because he did not have the information Dr. Christensen relied upon. Thus, Dr. Christensen's model and design is accepted as more credible than that of Drs. Van de Kreeke and Lee. That model and design establishes that the quality of water exiting the marina into the Outstanding Florida Waters in Garden Cove will be improved by the modifications proposed to be constructed in the marina. Impact on Benthic Communities The northerly end of the marina basin will be sloped from -6 feet to - 4 feet. This widening and shallowing of the marina basin and access channel will have the affect of promoting the growth, regrowth and welfare of the benthic communities in the waters in the marina and access canal by providing greater light penetration to the bottom of the marina. The widening will have the effect of causing a greater portion of the marina bottom to be lighted during the day since at the present time, the bank and surrounding trees shade the marina basin for substantial portions of the day. The increased light penetration will result in more photosynthetic activity by the plant life in the marina and canal such that increased amounts of oxygen will be produced enhancing the dissolved oxygen levels of the marina waters. In that connection, the Respondents' expert, Dr. Rich, has examined a number of marinas and observed very healthy benthic communities in marina harbors more densely populated with boats than will be the proposed marina. Another significant improvement in the ecological status of the present marina will be the placing of a bubble screen device across the mouth of the entrance canal. This will have the effect of preventing floating organic materials such as sargassum, from entering the marina. Marinas typically experience problems related to dissolved oxygen levels in their waters because of an accumulation of floating organic material which tends to settle to the bottom creating excessive biochemical oxygen demand in their decomposition process, thus resulting in decreased dissolved oxygen levels. Thus, the bubble screen will aide in decreasing BOD. Likewise, a bubble screen device is proposed to be placed around the fueling facilities in the rearward portion of the marina basin so as to prevent the spread of pollutants such as spilled oils, greases and fuels, which may occur during routine fueling operations from time to time. Inasmuch as the modifications have been shown to cause some improvement in the dissolved oxygen level in the waters of the marina basin and access canal, it has been demonstrated that the modifications will not interfere with the conservation of marine wildlife and other natural resources. The bodies of water consisting of the marina, the access canal and Garden Cove, at the present time support a diverse marine community that can be expected to continue to flourish. Neither will the proposed activity destroy any oyster or clam beds, as none have been shown to exist in these waters. Dr. Rich has monitored waterways and offshore waters at a nearby, comparable marina, The Ocean Reef Club, for approximately ten years. He has discerned no noticeable impact on the benthic communities within that marina from a very heavy boat traffic during that period of time. The boats using The Ocean Reef Club Marina are typically larger than will use the Port Bougainville facility and boats of over 100 feet in length commonly use The Ocean Reef Club. In terms of impact on offshore benthic communities, he has observed no visible impact by the heavy amount of boat traffic using The Ocean Reef Marina from the standpoint of comparison of the experience with that marina, in terms of biological impacts, with the marina configuration proposed by the Applicant/Respondents. In short, the proposed marina configuration as contrasted to the existing permitted marina, represents an improvement because of the increased surface area providing increased oxygen exchange through wave and wind action, the shoaling which will also be beneficial to dissolved oxygen levels because of its enhancement of photosynthetic processes, and because of the proposed marina management steps designed to prevent floating organic material from entering the marina. Thus, the modified design was shown to provide a meaningful improvement in general ecological conditions within the marina and hence, in the offshore waters of Garden Cove with which the marina waters exchange and mix. Water Quality Dr. Eugene Corcoran is Professor Emeritus of the Rosensteel School of Marine and Atmospheric Sciences. He is a marine chemist and performed a chemical analyses of the samples taken for the water quality report presented by Respondents and in evidence as Respondent's Exhibit 17. Dr. Corcoran also performed the analyses for the ongoing water sampling program conducted by Dr. Renate Skinner, an expert witness for Petitioners. The Petitioners accepted Dr. Corcoran as an expert witness without objection. The proposed marina modifications involved in this permitting application were thus shown to cause no violations of the state standards for dissolved oxygen. The Rio Palenque Water Quality Study in evidence indeed documented a number of instances where dissolved oxygen fell below the state minimum standards of four parts per million in the present marina. Once the modifications are completed there still may be instances when dissolved oxygen falls below that standard, but this can be attributed to natural phenomenon and the same relatively low levels of dissolved oxygen below state standards have been observed in the offshore waters of Garden Cove itself, which is an Outstanding Florida Water. Significantly, however, it was established that concentrations of dissolved oxygen will likely increase as a result of these modifications, the inducement of the helical flow and consequent vertical mixing, the widening of the entrance canal and the shoaling of the bottoms in the marina basin and canal, as well as the measures to be taken to reduce the deposition of organic materials in the marina basin and canal. The only water quality criteria placed in contention by the Petitioners and Intervenors were dissolved oxygen and copper. Although a number of Petitioners' witnesses were qualified to address the impacts of water quality on different marine organisms, only Dr. Curry was qualified as an expert in water quality. Dr. Curry's chief concern was with dissolved oxygen, which is based on the Rio Palenque Study showing present low values for dissolved oxygen in the marina as it now exists. Dr. Curry did not establish that the proposed modifications to the marina would themselves cause dissolved oxygen violations and although he testified in great detail concerning his attempt to compute the amount of copper that might be given off by the bottom paint of boats in the modified marina, he was unable to render an opinion that the modifications would increase copper levels in the waters in the marina. He acknowledged that his calculations were based on the assumption that all the boats in the marina would be using copper anti-fouling paints and his calculations took into account an assumption that all boats in the marina would have been painted within the last six months as a base datum for his calculations. Additionally, he did not take into account dispersion ratio associated with the hydrodynamic forces present in the modified marina. Dr. Curry admitted that he had never studied copper levels in a marina environment and was unable to explain the chemical effects on water quality of copper anti-fouling paints on boats. In all his sampling, he only found one instance of a violation of the Chapter 17-3 copper standard and that occurred within only a few millimeters of the hull of a newly-painted boat. Other fallacies involved in Dr. Curry's analysis, concern the interaction of seawater with copper bottom paint. Since seawater has a high level of carbonates, copper is immediately complexed with organic compounds such as amino acids. These organic complexes are soluble in seawater and indeed, serve as important nutrients to phytoplankton and other beneficial marine organisms. Thus, that portion of the total complex copper precipitated from the water as well as that portion taken up as nutrients would not be included in any concentrations of copper measured in the water column. Additionally, Dr. Curry's computations did not take into account the dispersion of copper concentrations due to mixing or flushing, which has a direct beneficial effect on reducing concentration of copper and other pollutants in the water column. Thus, Dr. Curry's computations are deemed immaterial, inasmuch as he effectively admits that the modifications to the marina would not be detrimental to water quality. The proposed modifications will not lower ambient water quality or significantly degrade the waters in the adjacent John Pennekamp Park, Outstanding Florida Waters. Since it has been established that the marina modifications will likely improve water quality within the marina, logically, the water quality in the park to some degree might be slightly improved, since those waters exchange with the waters in the marina. There will be no increase in concentrations of any pollutants emanating from the Port Bougainville Marina as a result of the proposed modifications. Improved Marking of Garden Cove Channel The Applicant/Respondents are required to provide improved navigational markers in the Garden Cove Channel, pursuant to an amended development order. Additionally, they have agreed to provide additional channel markers delineating the channel from the entrance of the existing marina to the Garden Cove Channel proper. With regard to the Garden Cove Channel, the Respondents proposed to move certain existing channel markers to more clearly identify that channel, which would make certain portions narrower and thereby eliminate boat passage over some shallow areas populated with marine grasses which presently lie within the marked channel. The Respondents also propose to add two more sets of channel markers at the seaward end of Garden Cove Channel, so that boats exiting the channel heading for the open sea will avoid certain shallow marine grass areas. The reason for this is to avoid possible damage to valuable marine grass beds and habitat which might be caused by prop wash of boats crossing over them, as well as actual contact and scouring by propellers or potential grounding of boats navigating these areas. Witness Balfe for the Respondents has personally sounded the entire length of the access canal and Garden Cove Channel. His soundings are admitted in evidence as Respondent's Exhibit 19 and are unrefuted. It was established therefore, that the bottom configuration of that access channel is basically flat or level with only minor irregularities of less than a foot. There are no rock outcroppings or other obstructions which would reduce the controlling depth below -4 feet. Approximately 12 times per year however, during "spring tides", the ambient water depths in Garden Cove could be expected to go below -4 feet mean low water. During these times the tide will be approximately 6 to 8 inches below that normal depth. Perhaps 25 times per year the tide is 5 or 6 inches below that mean low depth. The tide gauge which will be installed will alleviate possible propeller scouring or grounding damage to grass beds and marine habitat, especially during those abnormally low tides, by providing boat operators a current, up-to-date reading on the depths in the channel. Contributions to Park Management Plan and Marina Management Plan The Applicant/Respondents have agreed to a permit condition requiring a financial commitment to assist in the management of the John Pennekamp Park so as to minimize the adverse impacts of human use of the park. This commitment includes the provision of $75,000 to finance a study and preparation of a management plan for the John Pennekamp Coral Reef State Park and Key Largo National Marine Sanctuary, which would include study of the feasibility of inaugurating an entry permit system for the park, a testing and certification program for commercial dive boat operators, possible zoning of the park to allow recovery of the park coral reefs and other resources from the impacts of human visitors, locating central mooring buoys so that visitors' boats could be moored in one restricted area to avoid damage to the delicate coral reefs, and more adequately marking the boundaries of the park. Additionally, the Respondents propose to provide $50,000 for the acquisition of anchor buoys to be placed in selected areas of the park and to provide funds to finance a survey to more adequately identify the boundaries of the park. In order to more adequately protect water quality in the marina itself, the Respondents will inaugurate a marina management program which will include the installation of a sewage pump-out station and a pump-out station for motor oils and lubricants for boats. In addition to the two bubble curtains mentioned above, the Respondents will install containment booms and absorption mats and will permanently maintain a boat equipped with absorption mats and suction equipment for fuel or oil spill removal. The marina will prohibit persons living aboard boats, to prevent attendant sewage effluent problems, and will prohibit maintenance of boats, including painting and oil changes, while boats are in the water. This program will be monitored by an environmental protection officer employed by the condominium association under the auspices of the Respondents. Many of these marina management provisions are already requirements of the Port Bougainville 1982 development order referenced above. Management of Inland Lakes Although the use and management of the inland lakes on the Respondents' property is not directly involved in this permit application proceeding, the Respondents' overall development plan encompassed by the development order anticipates that at a future time a boat lift will be installed on upland so as to allow boats to be transferred from the inland lakes into the marina for access to marine waters. The lakes themselves, however, will not be open to the marina or to outside waters. The inland lakes are anticipated to provide dockage for approximately 200 boats, with restrictions against boats exceeding 20 feet in length and boats powered by combustion engines. The Respondents expect that the inland lakes will be primarily used by small boats such as canoes or sailboats. Dry storage for boats will be maintained on an upland site, for which a DER permit is not required. Neither is a permit for a boat transfer facility required since it would not involve dredging, filling or construction over water. The use of a boat lift, although it itself is not an issue before the Hearing Officer in this proceeding, would involve the potential of 200 or more boats using the marina in addition to those for which the marina is designed. This could occasion substantially greater risk for oil, grease and fuel spills and other potential damage to the water quality within the marina and damage to the marine habitat, grass beds and so forth within the marina, the access canal and the adjacent areas in Garden Cove. Accordingly, the conservation easement which the Respondents have agreed to provide the department as a condition to the grant of this permit should be amended to add a further condition on a grant of this permit so as to preclude placement of boats from the inland lakes into this marina or its access canal. Such a restriction would comport with the proposed uses of the inland lakes established by Mr. Scharenberg, the Respondent's principal. Boating Impacts Boat traffic in the Garden Cove Channel area is significant, with heaviest traffic occurring on the weekends when approximately two to three hundred boats navigate that channel. The boats presently using Garden Cove Channel come from a number of nearby marinas, small fishing docks and dry storage areas, as well as from a marked navigational channel called North Creek that provides access to the Garden Cove area and the Atlantic Ocean from Largo Sound. A small canal cuts through Key Largo into Largo Sound and provides access for boats in the Black Water Sound and other areas on the west side of Key Largo to the Garden Cove area and the Atlantic. The Port Bougainville Marina is expected to attract a mix of boats typical for such a marina, with the majority consisting of boats ranging from 27 to 35 feet in length. Approximately 20 percent of the boats will likely be in the 40-foot range. Larger boats may also use the marina, particularly those with a shallow draft, and "shoal draft" sailboats of 35 to 40 feet can safely navigate in and out of the marina. The marina, as it would be modified, would permit use of boats with a draft of up to three and one-half feet, although deeper draft boats could use the marina by timing arrivals and departures for the high tide, which is a common mode of operation by boat operators in the Florida Keys and other marine areas. The Port Bougainville Marina will contribute approximately 30 to 50 boats to the Garden Cove boat traffic on an average weekend out of the possible 311 boats in the harbor as it is proposed to be constructed. There will be a lesser number of boat arrivals and departures during the weekdays. The primary users of boats in and out of the marina will be people who own condominiums in the attendant real estate development. Temporary visitors, not owning boats moored in the marina, would typically use the dive charter boats and other rental boats in the surrounding areas, such as at the Ocean Reef facility. The existing marina which is already permitted and can be fully used at the present time from a legal standpoint, could accommodate the same reduced number and sizes of boats as the proposed modified marina by simply removing some of the present docks and finger piers. The Respondents propose to maintain approximately 20 slips for boats which are not owned by condominium unit owners, and they anticipate operating six to seven deep-sea charter boats as well as five smaller skiff-type charter boats, and perhaps as many as two dive charter boats with additional demands for charters to be serviced by charter boats in the surrounding areas. Boating adverse impacts on the marine benthic communities inside and outside of the marina will be minimized by the construction configuration of the marina and boat slips, the shoaling and widening of the marina basin and canal, and the channel marking and tidal gauging provisions proposed by the Applicant/Respondents. These safety arrangements would be further enhanced by the above-mentioned restriction on the placing of boats into the waters of the marina and canal from the inland lakes. The configuration of the proposed modified marina and the shoaling will have a beneficial effect in rendering use by extremely large boats, which might cause propeller, wake or grounding damage to the marine benthic communities unlikely because of the inaccessibility caused by the intentional shoaling. Coral Reef Impacts Dr. Peter Glynn is a qualified expert in marine ecology and was accepted as an expert witness in that area with particular emphasis, through his long specialization, in the ecology of corals and coral reefs. He has researched the effects of sediments, herbicides, pesticides, oxygen levels, temperature, salinity, tidal effects and oil pollution on corals. He testified as a rebuttal witness addressing concerns raised by Petitioners' and Intervenor's witnesses with regard to boat traffic, attendant turbidity and possible synergistic effects on coral reefs caused by oils, greases, low oxygen levels and turbidity. Dr. Glynn has studied corals in many areas of the world including the Caribbean and the Florida Keys. The coral reefs in Florida are similar to those in the Caribbean area and belong to the same "biogeographic province." He has dived in and examined the Garden Cove area and found four species of small reef building corals in Garden Cove. These were found in the vicinity of a shipwreck near the channel entrance to Garden Cove and the remainder of the corals observed in Garden Cove were in the bottom of the boat channel running through Garden Cove. There were no corals observed on the grass flats and in shallower areas of Garden Cove. The corals occurring in the boat channel are in isolated colonies of less than a foot in diameter. The Petitioners and Intervenors attempted to raise the possibility of synergistic adverse effects on corals posed by combinations of oils, oxygen levels, temperatures and sedimentation or similar impacts. It was not shown how or at what concentration turbidity might combine with various oxygen levels, temperatures or degrees of light penetration to produce such effects, however. The only type of synergistic effects on corals Drs. Glynn and Corcoran have observed is that between oils and pesticides. Although this effect has been demonstrated in another study area far removed from the Florida Keys, no such pesticide and oil synergistic impact has been observed in the Florida Keys area, chiefly because it is not an agricultural area characterized by significant use of pesticides. Likewise it was not established that suspended sediments in the Garden Cove area could have an adverse effect on corals by reducing light penetration. In tropical areas such as the Keys, light penetration is often saturating or in greater quantities than are really needed for healthy coral growth and indeed, many corals in these areas have pigments that naturally shield them from excess light because these coral species actually can suffer from too much light penetration. Additionally, Dr. Glynn has observed good coral reef health and growth in areas that are highly turbid. It was not established that an increase of sedimentation deposit on corals will necessarily have an adverse impact, particularly because most corals can accept a substantial amount of fine-grain sediment deposition without adverse effect. The manner in which the proposed marina modifications will be accomplished will minimize sedimentation at any rate since the canal will be dammed off from Garden Cove until all work is completed and all sedimentation within the marina and marina access canal has subsided to levels compatible with the state standards for turbidity. In any event, there is no evidence that boat traffic in Garden Cove at the present time influences the distribution and health of live coral, particularly since the main coral abundance in Garden Cove occurs in the heavily-used boat channel at the present time. Likewise, Dr. Glynn established that sediments from any increase in boat traffic in Garden Cove will not likely drift out on the offshore reef tract and be deposited on the reefs to their detriment in any event, since the fine sediments occurring in Hawk Channel and in Garden Cove, are largely precluded from deposition on the offshore reefs because the waters over the reef tract offshore have very different physical characteristics. That is, there is distinct interface between the inshore and oceanic waters caused by the strong wave assault and current action near the reefs, which precludes the fine sediments from the inshore areas remaining in the area of the reefs. Finally, any increase in the number of people visiting the Pennekamp Park attributable to use of the modified marina will not inevitably lead to degradation of the reefs. By way of comparison, studies of Kaneoi Bay in Hawaii where a major pollutant source from human sewage caused degradation of the coral reefs, showed that when sewage effluent was subsequently directed away from the reefs, the reefs rejuvenated and repopulated and are now used extensively for recreational activities without observable biological degradation. These studies are consistent with studies Dr. Glynn referenced with regard to Biscayne Bay National Park, which have shown no significant degradation occasioned by human visitation of the reefs in that park. Those studies have not shown a significant difference between the health of the "controlled reefs" and the reefs which are allowed to be used for recreational purposes. It was thus not established that there will be any degradation of the corals in the near-shore areas of Garden Cove nor in the offshore reef areas occasioned by any increased boat traffic resulting from the modification of the marina. Indeed, it was not demonstrated that the mere modification of the marina, which will actually accommodate fewer boats than are presently permitted, will cause any increase in present boat traffic at all. Dr. Glynn, in the course of his teaching and studies in the field of marine ecology has become familiar with the causes and effects of Ciguatera toxin in marine environments. He recently participated in the study of possible Ciguatera toxin at the grounding site of the freighter Wildwood on Molasses Reef, some miles distant from the marina site. All cases reported of such harmful concentrations of this toxin have originated from open water, outer coral reef environments, and not from near shore areas such as those involved in this case, where seagrasses and mangroves are the dominant marine communities. Ciguatera toxin organisms require clear open ocean water with strong currents and well-developed coral reefs which are found offshore in the Keys and not in the near-shore mangrove-type environments. The cause of Ciguatera is a concentration of toxin in the food chain. Although the bacteria that cause Ciguatera Toxin in fish, and resulting harmful effects in humans, occur everywhere in marine waters, the bacteria are not a hazard because generally, conditions are not appropriate for the bacteria to multiply. The two main species of dinoflagellates, that have been associated with causing Ciguatera poisoning do not occur in an environment such as the Port Bougainville Marina. They are typically concentrated in larger fish such as snapper, grouper and barracudas which cause problems when they are eaten by people. These species are not generally found in the inshore mangrove and grassbed areas such as are involved in the case at bar. Thus, the concerns expressed by Petitioner's witnesses concerning the possibility of Ciguatera poisoning occurring because of possible damage to corals and coral death caused by the dredge and fill operations, and boat operation associated with the marina and Garden Cove are, in reality, only unsubstantiated speculation.
Recommendation Having considered the foregoing Findings of Fact, Conclusions of Law, the evidence of record, the candor and demeanor of the witnesses and the pleadings and arguments of the parties, it is, RECOMMENDED: That the State of Florida, Department of Environmental Regulation, issue the requested permit subject to the conditions incorporated in the agreement or "conservation easement" executed between the Department and the Respondents with the further condition added to that conservation easement such that the deposition of boats from the inland lakes system into the marina and its access canal be prohibited. DONE and ENTERED this 9th day of April, 1985 in Tallahassee, Florida. P. MICHAEL RUFF Hearing Officer Division of Administrative Hearings The Oakland Building 2009 Apalachee Parkway Tallahassee, Florida 32301 (904) 488-9675 Filed with the Clerk of the Division of Administrative Hearings this 9th day of April, 1985. COPIES FURNISHED: Elizabeth J. Rickenbacker, Esquire 10500 Southwest 108th Avenue Miami, Florida 33176 Michael F. Chenoweth, Esquire 522 Southwest Third Avenue Miami, Florida 33130 Douglas H. MacLaughlin, Esquire Department of Environmental Regulation 2600 Blair Stone Road Tallahassee, Florida 32301 Michael Egan, Esquire, Robert Apgar, Esquire Post Office Box 1386 Tallahassee, Florida 32302 Victoria Tschinkel, Secretary Department of Environmental Regulation 2600 Blair Stone Road Tallahassee, Florida 32301 ================================================================= AGENCY FINAL ORDER ================================================================= BEFORE THE STATE OF FLORIDA DEPARTMENT OF ENVIRONMENTAL REGULATION SIERRA CLUB: UPPER KEYS CITIZENS ASSOCIATION, INC., a non-profit Florida corporation; PAMELA BERYL PIERCE, and FRIENDS OF THE EVERGLADES, INC., a non-profit Florida corporation, Petitioners, and DOAH CASE NOS. 84-2364 84-2365 FRIENDS OF THE EVERGLADES, INC., 84-2385 a non-profit Florida corporation; 84-2827 THE FLORIDA DIVISION OF IZAAK (Not consolidated) WALTON LEAGUE OF AMERICA, INC., a non-profit Florida corporation; UPPER KEYS CITIZENS ASSOCIATION, INC., a non-profit Florida corporation, Intervenor-Petitioners, vs. STATE OF FLORIDA DEPARTMENT OF ENVIRONMENTAL REGULATION, and PORT BOUGAINVILLE ASSOCIATES, LTD. a Florida limited partnership, and PORT BOUGAINVILLE ENTERPRISE, INC. a Florida corporation, Respondents. /
