Findings Of Fact Counsel for the respective parties stipulated to the following facts: Quayside Associates, Ltd., is a Florida limited partnership whose address is 10670 N.E. Quay Plaza, North Miami, Florida 33134. Respondent is the Department of Environmental Regulation, an agency of the State of Florida as defined in Section 120.52(1), Florida Statutes. This Petition relates to the Department's File No. DF13-28371-6E. Petitioner was the applicant for the subject permit and will, as applicant, be directly affected by a denial thereof. On February 28, 1980, Petitioner applied to the Department for approval of its Phase II Docking Facility which included an elevated walkway with wave break panels, nineteen (19) new wet slips and twenty-five (25) davits. (Exhibit "1") On March 6, 1980, a completeness review form was sent to the applicant's representative by the Department. (Exhibit "2") On March 6, 1980, the applicant's representative responded to the comments of the Department and completeness summary by letter from J. Frederic Blitstein to the Department's Subdistrict Office. (Exhibit "3") As shown by the Department letter of May 29, 1980, response to the completeness summary were received by the Department from the applicant on March 7 and 11, 1980, with final Department of Natural Resources clearance, as requested by the completeness summary, received by the Department of March 14, 1980 (see Exhibit 4). The response of the Depart- ment of Natural Resources is attached hereto as Exhibit "5". On March 20, 1980, the representative of the Department made an on-site visit to the site as shown by the Departmental Summary Permit Processing Worksheet attached as Exhibit "6". On April 9, 1980, the Department received the comments and recommendations of the Dade County Department of Environmental Resources Management which indicated that it had "no objection to the issuance of the Permit" subject to certain stipulations and conditions. (Exhibit "7") On June 25, 1980, the Department held its scheduled Biscayne Bay Aquatic Preserve Hearing in Miami, Dade County, Florida. On July 2, 1980, the Department issued a completion notice to the applicant indicating completion of the application on June 25, 1980. (Exhibit "8") On September 9, 1980, the Department issued its Letter of Intent to Deny which gives rise to the subject proceeding. (Exhibit "9") This Petition ensued and was filed with the Department on September 24, 1980. The State of Florida, Division of Administrative Hearings has jurisdiction over this matter and has jurisdiction to make an Interlocutory Ruling regarding same. This Stipulation may be utilized for interlocutory purposes or for all subsequent purposes.
Findings Of Fact The County applied on August 24, 1979, for a permit to construct a swimming beach on the southwest shore of Sylvan Lake in the northwest part of Seminole County, Florida. On December 4, 1979, the Department gave notice of its intent to grant the permit. As proposed, the beach would be 150 feet in length along the shoreline and be approximately 65 feet deep, 40 feet on the land side of the waterline and 25 feet on the lake side of the shore waterline. Three dock structures are also proposed. The first is a boat dock to be 6 feet wide, which will extend into the lake for 25 feet with a 15 foot "L" at its end. In addition, a 6 foot wide, 20 foot long fishing pier is proposed with a 6 by 20 foot "T" on its end. Finally, the County proposes constructing a 6 foot wide 15 foot long aquatic study platform that would terminate in a 6 by 30 foot "T". The County plans to remove vegetation from an area of 150 feet long by 25 feet. As agreed at the hearing, this removal would be by hand only.. No machinery would be used. The site of the project is owned by the County. As part of its application, the County agrees to leave undisturbed 2,630 feet of the remaining shoreline it owns. At the present time approximately 20 percent of the lake's total shoreline is occupied by developed residential property. Many of the homeowners have removed the vegetation from their shorelines. The County's agreement not to alter 90 percent of its shoreline would therefore be beneficial to preserving the natural state of the lake. Sylvan Lake is an oligotropic spring-fed lake of 160 acres. Its well vegetated shoreline alternates between large grassy marshes and well-defined uplands. The lake bottom in the project site is firm sand with little potential for causing a turbidity problem. The lake has excellent water quality. It is a valuable habitat for fish and aquatic dependent birds and mammals. The vegetation along the shoreline of the project site consist of sawgrass, pickerelweed, and some arrowhead on the land side with spatterdock and mats of floating maidencane on the water side. In a freshwater closed system such as this lake the rooted emergent plants are vital to maintaining the quality of the water. The plants stabilize nutrients, expert oxygen and keep the water cool. The removal of this vegetation from a 150 foot strip will have an adverse but insignificant impact on the biological resources and the water quality of the lake. The construction of the fishing pier, boat dock, and observation platform will have no lasting environmental impact and the limited turbidity which may be generated during their construction can be well contained by the use of turbidity curtains. The swimming beach is a part of the County's plan for a diverse recreational park to provide the public with facilities for nature trails, baseball, picnicking, etc. The water classification of Sylvan Lake is Class III. CONCLUSIONS OF LAW The Division of Administrative Hearings has jurisdiction over the parties and the subject matter of this case. Section 120.57(1), Florida Statutes (1979). In this proceeding the Respondent, County, has the burden of proving that it has given reasonable assurances that the short term and long term effects of the proposed project will not result in violations of the water quality standards of Chapter 17-3, Florida Administrative Code. Section 17- 4.28(3), Florida Administrative Code; Dowdy v. Department of Environmental Regulation, Case No. 79-219, Recommended Order (DOAH July 19, 1979). That burden has been carried. The water quality standards of a Class III body such as Sylvan Lake are set out in Section 17-3.09, Florida Administrative Code. There is a preponderance of competent and substantial evidence that those standards in either the long term or in the short term will not be violated by the proposed project. The requisite reasonable assurances have therefore been given by the applicant. Hand removal of aquatic vegetation from a 150 foot strip of shoreline on a 186 acre lake, will have at most, a de minimus impact on the marine life, water quality or neighboring biota of Sylvan Lake. The applicant has met the criteria for the issuance of a permit, pursuant to Section 17-4.07, Florida Administrative Code.
Recommendation Based on the foregoing Findings of Fact and Conclusions of Law, it is RECOMMENDED: That a final order be entered by the State of Florida, Department of Environmental Regulation determining that the requested dredge and fill permit be issued subject to the usual conditions and subject to the applicant's stipulation that any vegetation removal will be performed by hand and subject to any conditions contained in the Notice of Intent To Issue Permit. DONE AND ORDERED in Tallahassee, Leon County, Florida, this 30th day of April, 1980. MICHAEL PEARCE DODSON Hearing Officer Division of Administrative Hearings Oakland Building 2009 Apalachee Parkway Tallahassee, Florida 32301 (904) 488-9675 COPIES FURNISHED: Mr. & Mrs. Gilbert Lee Swartz Route 1, Box 228 DD South Sylvan Lake Drive Sanford, FL 32771 Nikki Clayton Seminole County Courthouse Room 302, 301 N. Park Avenue Sanford, FL 32771 Segundo J. Fernandez, Esq. and Stanley J. Niego, Esq. Department of Environmental Regulation Twin Towers Office Building 2600 Blair Stone Road Tallahassee, FL 32301 Mr. Raymond Lipton Route 1, Box 60-A Longwood, FL 32750
The Issue The issues are whether Respondent Lennar Homes, Inc., is entitled to an environmental resource permit to construct a 516- acre residential development in Miami-Dade County known as Lakes by the Bay South Commons Project and, if so, under what conditions.
Findings Of Fact On May 18, 2001, Respondent Lennar Homes, Inc. (Lennar Homes), filed an application with Respondent South Florida Water Management District (District) for an environmental resource permit (ERP) for a 516-acre residential development in Miami- Dade County known as Lakes By The Bay (Project). On June 12, 2002, Lennar Homes filed a revised ERP application for the Project. The application, as revised, is for an ERP conceptually approving the construction of a surface water management system to serve the Project and authorizing the construction to clear the site, excavate the wet retention areas, and expand an existing lake. Providing 3300 single- family residences, the Project is the last phase of a master planned residential development, which presently contains over 1500 residences north and west of the Project. The Project is bordered by Southwest 97th Avenue to the west, Southwest 87th Avenue to the east, Southwest 216th Street to the north, and Southwest 232nd Street to the south. Immediately south of the Project are a regional wastewater treatment plant and county solid waste landfill. These facilities occupy opposing banks of the C-1 Canal, which runs a short distance from the southwest corner of the Project. The Project site is drained, cleared, and infested with Brazilian pepper and melaleuca. The Project will impact 135 acres of wetlands, but these wetlands are severely degraded due to the construction of roads, berms, and canals. No evidence suggests that the site is presently used by any listed species. At present, drainage across the site is from west to east, where stormwater is intercepted by the L-31E levy and canal running along the west side of Southwest 87th Avenue. At its nearest point (the southeast corner), the Project is about one mile from the southern part of Biscayne Bay. Biscayne Bay is an Outstanding Florida Water. Much of its central and southern parts, including the area closest to the Project site, are within Biscayne National Park. In contrast to the northern part of Biscayne Bay, the central and southern parts contain significant mangrove-lined coastal wetlands. The bay bottom in southern Biscayne Bay hosts dense seagrass beds, and coral reefs within Biscayne National Park support a diverse community of marine life. The L-31E levy and canal redirect stormwater from the Project site south to the C-1 Canal, which runs, in this area, in a northwest-to-southeast direction before emptying into Biscayne Bay. The C-1 Canal drains an extensive area to the north and northwest of the Project. The landfill and water treatment plant are a short distance downstream of the Proposed Project. The parties have stipulated that the Project meets the following ERP criteria (with minor rephrasing from the stipulation): The Project will not adversely affect significant historical and archaeological resources. The Project is not located within an Outstanding Florida Water and will not result in the direct discharge of surface water into an Outstanding Florida Water. Lennar has proposed mitigation to offset the adverse impacts of the Project, and the mitigation is in the same drainage basin as the adverse impacts. Therefore, the Project will not generate unlawful cumulative impacts, in violation of Section 373.414(8)(a)-(b), Florida Statutes. The Project will not cause adverse water quality impacts to receiving waters and adjacent lands, in violation of Rule 40E-4.301(a), Florida Administrative Code. The Project will not cause adverse flooding to onsite or offsite property, in violation of Rule 40E-4.301(b), Florida Administrative Code. The Project will not cause adverse impacts to existing surface water storage and conveyance capabilities, in violation of Rule 40E-4.301(c), Florida Administrative Code. The Project will not adversely impact the maintenance of surface or ground water levels or surface water flows established pursuant to Section 373.042, Florida Statutes, in violation of Rule 40E-4.301(g), Florida Administrative Code. The Project will not cause adverse impacts to a work of the District established pursuant to Section 373.086, Florida Statutes, in violation of Rule 40E-4.301(h), Florida Administrative Code. The Project will be conducted by an entity with sufficient financial, legal, and administrative capability to ensure that the activity will be undertaken in accordance with the terms and conditions of the permit, as required by Rule 40E-4.301(j), Florida Administrative Code. No special basin or geographic area criteria established in Chapter 40E-41, Florida Administrative Code, are applicable to the Project. The Project will not adversely affect navigation or the flow of water or cause harmful erosion or shoaling, as prohibited by Section 373.414(1)(a)3, Florida Statutes. The Project will be permanent, as addressed by Section 373.414(1)(a)5, Florida Statutes. The District issued its Staff Report on March 13, 2002. The Staff Report approves the proposed mitigation plan, which would enhance or create and preserve 135 acres of onsite wetlands by creating an upland buffer, emergent marsh and transitional herbaceous shrub areas, and tree island areas. Much of the proposed mitigation area will occupy the southern half of the perimeter of the Project site. As proposed in the mitigation plan, Lennar Homes will grant the District a conservation easement over the mitigation area and will be required to meet certain mitigation performance conditions. Shortly prior to the commencement of the final hearing in this case, the District decided to change the proposed permit regarding mitigation. The purpose of the change was to require Lennar Homes to allow the mitigation area to be used as a flowway between the C-1 Canal, upstream of the nutrient loads deposited by the landfill and water treatment plant, and an area to the east of the Project site. The receiving area consists of vestigial tidal creeks leading to presently remaining tidal creeks that empty into small embayments within Biscayne Bay. The general purpose of the change was to remediate the loss of freshwater flows into these tidal creeks, the embayments, and Biscayne Bay that resulted from the construction of drainage canals and levies, such as C-1 and L31-E. Accordingly, the District issued an Addendum to Staff Report on August 9, 2002. The Addendum adds an easement to the original mitigation plan by adding Special Condition #24, which states: No later than 30 days after permit issuance and prior to commencement of construction resulting in wetland impacts, the permittee shall submit two certified copies of the recorded flowage easement for the mitigation area and associated buffers and a GIS disk of the recorded easement area The recorded easement shall be in substantial compliance with Exhibit 41. Any proposed modifications to the approved form must receive prior written consent from the District. The easement must be free of encumbrances or interests in the easement which the District determines are contrary to the intent of the easement. . . . Exhibit 41 (actually Exhibit 41A) is entitled, "Perpetual Flowage, Inundation, Construction, and Access Easement." Representing a grant from Lennar Homes to the District, the easement (Flowage Easement) is for any and all purposes deemed by [the District] to be necessary, convenient, or incident to, or in connection with, the unrestricted right to regularly, or at any time, and for any length of time[,] overflow, flood, inundate, flow water on, across, and through, store water on, and submerge the [encumbered property], together with the unrestricted right at any time to enter upon and access the [encumbered property], with any and all vehicles and equipment, including but not limited to the right to move, transport, store, operate, and stage equipment, materials and supplies, in order to construct, operate, and maintain any and all structures, improvements, equipment, pumps, ditches and berms upon the [encumbered property] deemed by [the District] to be necessary, convenient, incident to or in connection with the implementation of the BBCW Project on the [encumbered property], or in connection with any project in the interest of flood control, water management, conservation, environmental restoration, water storage, or reclamation, and allied purposes, that may be conducted now or in the future by the [District], or to carry out the purposes and intent of the statutory authority of the [District], presently existing or that may be enacted in the future, together with all right, title, and interest in and to the [BBCW] Project Structures. * * * This Easement shall at no time be construed to alleviate or release [Lennar Home's] responsibilities and require [sic] under ERP Permit No. to construct and maintain an on-site mitigation area as described and authorized in the ERP Permit. Other provisions of the Flowage Easement impose all risk of loss in connection with the flowway upon Lennar Homes, which indemnifies the District from all losses, costs, damages, and liability in connection with the flowway. On September 5, 2002, after the hearing, but a few days before the taking of the post-hearing testimony, the District issued a Revised Addendum to Staff Report. The Revised Addendum restates Special Condition #24 with a few relatively minor changes and adds Special Conditions ##25 and 26. Special Condition #25 attempts to harmonize the Flowage Easement with the original mitigation plan contemplated by the Staff Report. Special Condition #25 provides that when the District exercises its rights under the Flowage Easement, other special conditions shall be deleted, so as, for example, to relieve Lennar Homes of its obligations to maintain the mitigation area (except for a 25-foot buffer) and post a mitigation-performance bond. Special Condition #26 changes the language in the conservation easement, which was contemplated by the original Staff Report and mitigation plan, to harmonize this easement with the Flowage Easement. Lennar Homes has submitted a version of the Revised Addendum to Staff Report that would satisfy its concerns. The Lennar Homes version would require the District, within 30 days after issuing the ERP to Lennar Homes, to obtain permits from the U.S. Army Corps of Engineers and the local environmental regulatory agency, although not the Florida Department of Environmental Protection, which, under state law, would have to issue an ERP to the District before it could construct the flowway. The Lennar Homes version would also give the District only 90 days after issuing the ERP to Lennar Homes within which to exercise its right to construct the flowway and would sequence events so that Lennar Homes would not spend the estimated $2 million on wetland enhancement and creation and then lose the investment due to the inundation of the mitigation site with water, as authorized by the Flowage Easement. The Comprehensive Everglades Restoration Plan plays a crucial role in this case. But for this plan, the District would not have attached the additional conditions contained in the Addendum to Staff Report and Revised Addendum to Staff Report--without which conditions, the District now contends that Lennar Homes is not entitled to the ERP. Congress initially authorized the Central and Southern Florida (C&SF) Project in 1948. Objectives of the C&SF Project included flood control, water supply for municipal, industrial, and agricultural uses, prevention of saltwater intrusion, and protection of fish and wildlife. The C&SF Project attained these objectives, in part, through a primary system of 1000 miles each of levees and canals, 150 water-control structures, and 16 major pump stations. Unintended consequences of the C&SF Project have included the irreversible loss of vast areas of wetlands, including half of the original Everglades; the alteration in the water storage, timing, and flow capacities of natural drainage systems; and the degradation of water quality and habitat due to over-drainage or extreme fluctuations in the timing and delivery of freshwater into the coastal wetlands and estuaries. In 1992, Congress authorized the C&SF Project Comprehensive Review Study (Restudy). The objective of the Restudy was to reexamine the C&SF Project to determine the feasibility of modifying the project to restore the South Florida ecosystem and provide for the other water-related needs of the region. Completed in April 1999, the Central and Southern Florida Project Comprehensive Review Study Final Integrated Feasibility Report and Programmatic Environmental Impact Statement (Restudy Report) notes that, among the unintended consequences of the C&SF Project, was "unsuitable freshwater flows to Florida and Biscayne bays and Lake Worth Lagoon [that] adversely impact salinity and physically alter fish and wildlife habitat." The Restudy Report states that, absent comprehensive, new restoration projects, the "overall health of the [South Florida] ecosystem will have substantially deteriorated" by 2050. The Restudy Report recommends a comprehensive plan for the restoration, protection, and preservation of the water resources of Central and South Florida. This plan is known as the Comprehensive Everglades Restoration Plan (CERP). Acknowledging the complex dynamics of the restoration goals identified in CERP, the Restudy Report establishes Project Implementation Reports to tie together CERP and the detailed design necessary for the construction of individual restoration projects and adaptive assessments to monitor the performance of individual components, incorporate new data, and refine future components. The Restudy Report is, among other things, a programmatic environmental impact statement. The Restudy Report states: "Due to the conceptual nature of [CERP] and the associated uncertainties, many subsequent site-specific environmental documents will be required for the individual separable project elements." In May 2002, the District and U.S. Army Corps of Engineers completed a draft of the Project Management Plan for the Biscayne Bay Coastal Wetlands (BBCW PMP). Noting that a "major goal of [CERP] is to improve freshwater deliveries to Biscayne Bay," the BBCW PMP identifies the BBCW project as the means by which to restore some of the coastal wetlands and tributaries in south Dade County. The BBCW PMP states that the primary purpose of the BBCW project, which is one of sixty projects contained in CERP, is to "redistribute freshwater runoff from the watershed into Biscayne Bay, away from the canal discharges that exist today and provide a more natural and historic overland flow through existing and or improved coastal wetlands." The Cutler Wetlands subcomponent of the BBCW project encompasses the Project site. One of the objectives of the Cutler Wetlands subcomponent is to divert water from the C-1 Canal upstream of the landfill and water treatment plant to the east of the L-31E levy and canal. In connection with the Cutler Wetlands subcomponent and the possible role of the flowway identified in this case, the District retained Dr. John Meeder, a Biscayne Bay ecologist associated with the Southeast Environmental Resource Center at Florida International University, to perform an abbreviated study and issue a report concerning the conditions required for the restoration of the coastal wetlands in the vicinity of the coastal wetlands to the north of the C-1 canal and east of the Project site (Meeder Report). The Meeder Report studies two feasible freshwater delivery options and prefers a bypass flowway along Southwest 224th Street, across roughly the middle of the Project site and north of most of the proposed mitigation area, to the L-31E levy and canal. The distribution system resulting from the preferred route would use the natural grade of the land to divert the water to the coastal wetlands and tidal creeks to the east and south that are targeted for rehydration. The alternative flowway route would run along Southwest 232nd Street, in the approximate area of the Flowage Easement, but would require pumping to distribute the water north along the L-31E levy and canal for release to the targeted coastal wetlands and tidal creeks. Obviously, the District has chosen the less-preferred route to minimize the impact on the Project. The Meeder Report considers the amount of freshwater required for two rehydration options. In the first option, water diverted from the C-1 Canal and passing through the flowway would rehydrate only the tidal creeks, which then empty into the embayments that lead to Biscayne Bay. In the second option, water diverted from the C-1 Canal and passing through the flowway would rehydrate the tidal creeks and the surrounding coastal wetlands. To maintain an appropriate salinity range and rehydrate only the tidal creeks, the flowway would need to deliver 70 acre/feet per day in the dry season and 95 acre/feet per day in the wet season. To maintain an appropriate salinity range and rehydrate the tidal creeks and surrounding coastal wetlands, the flowway would need to deliver 209 acre/feet per day in the dry season and 1139 acre/feet per day in the wet season. Several factors militate against an attempt to rehydrate the coastal wetlands surrounding the targeted tidal creeks. Potential errors in data and analysis increase in magnitude with the larger freshwater diversions needed to rehydrate the tidal creeks and surrounding coastal wetlands, and Dr. Meeder admitted that the largest value was very approximate. Potentially serious impacts upon salinity and associated vegetative communities increase in likelihood with the larger freshwater diversions needed to rehydrate the tidal creeks and surrounding coastal wetlands. Also, the diversion of larger volumes of water from the C-1 Canal may have adverse impacts on downstream conditions. At the point of the C-1 Canal where it first enters the landfill and wastewater treatment plant (just downstream from the flowway), the average flow of the C-1 Canal is 350 acre/feet per day, but the median flow is only 160 acre/feet per day. (The average flow rate is skewed by occasional, very high daily flows of 4000 acre/feet during large storm events.) The larger volumes diverted to rehydrate the tidal creeks and surrounding coastal wetlands would, at times, withdraw a relatively large portion of the water from the C-1 Canal. For these reasons, the District justifiably elected to seek a flowway that would rehydrate only the tidal creeks, including the vestigial tidal creeks, but not the surrounding coastal wetlands. Petitioners and Lennar Homes have raised numerous other issues about the flowway that the District seeks to obtain. The District requires a 200-acre flowway to rehydrate adequately the vestigial tidal creeks, the presently remaining tidal creeks, the small embayment, and then the subject area of Biscayne Bay, but the mitigation area potentially available on the Project site is limited to about 135 acres, and some uncertainty exists as to whether the District can obtain control of the remaining land necessary to assemble a 200-acre flowway. Even the 200-acre flowway is probably insufficient to accommodate significant water treatment, so water quality issues remain outstanding, notwithstanding the better water quality upstream of the landfill and water treatment plant. Other issues arise from the requirement that the District obtain an ERP from the Florida Department of Environmental Protection, as well as one or more federal agencies, before it could construct the flowway. To the extent that this requirement delays and possibly precludes the construction of the flowway, this requirement militates against the inclusion of the Flowage Easement and new special conditions in the ERP. To the extent that this requirement insures that the flowway will not cause flooding or adverse water quality in the tidal creeks, embayment, and ultimately Biscayne Bay, this requirement militates in favor of the inclusion of the Flowage Easement and new special conditions in the ERP; the absence of detailed specifications for the design and construction of the flowway precludes any assurance that the flowway would not flood or otherwise damage the upland portion of the Project site, so subsequent permit-review is essential to the present inclusion of the Flowage Easement and new special conditions in the ERP. It is impossible to credit the District's evidence that various transition-zone wetland species would survive inundation under unknown flow rates, of variable depths, and of unknown and possibly indefinite duration. Lennar Homes legitimately is concerned that its substantial investment in mitigation, pursuant to the original mitigation plan, would be wasted if the District constructs the flowway. As presently drafted, the Flowage Easement and new special conditions contemplate that Lennar Homes would construct the original mitigation, at a substantial cost, and the District would later construct and inundate the flowway through largely the same area. Marketing of parcels in close proximity to the flowway might be complicated by the uncertainty concerning what will occupy the area beyond a resident's backyard--a benign passive mitigation area or a flowway that may range from a intermittently wet slough or glade to a placid lake to a raging swollen river--and by the probability that the District would not construct the flowway until 2009. The District justifies the Flowage Easement and new special conditions on two grounds. First, the District contends that the ERP without the Flowage Easement and new special conditions is harmful to the District's water resources. Second, the District contends that the ERP without the Flowage Easement and new special conditions is inconsistent with the overall objectives of the District. The first argument misses the mark. A project that is otherwise permittable, except for the fact that it interferes with the establishment of a restoration project, does not harm the water resources of the District; such a Project interferes with the improvement of the water resources of the District. In this case, the parties have stipulated that the Project will not cause adverse impacts due to the original mitigation plan. If adverse impacts means anything, it means harm to the water resources of the District. The second argument requires the identification of the District's objectives. The Florida Legislature has declared at Section 373.1502(2)(a), Florida Statutes, that CERP implementation is "in the public interest and is necessary for restoring, preserving and protecting the South Florida ecosystem . . .." In May 2000, the Florida Legislature enacted the Everglades Restoration Investment Act, which commits Florida to contribute over $2 billion for the implementation of CERP-- Florida's share for the first ten years of implementation. The Florida Legislature has made the implementation of CERP an overall objective of the District. Several factors are important in determining whether the ERP without the Flowage Easement and new special conditions would be inconsistent with the overall objective of the District to implement CERP. These factors require consideration of the purpose of the proposed restoration project; the extent of completion of the project's design, permitting, and construction; if the project has not yet been designed or permitted, the likelihood of construction; when the project would be constructed; the impact of the ERP without the Flowage Easement and new special conditions upon the proposed restoration project; and the existence of feasible alternatives to accomplish the same objectives as those achieved by the proposed restoration project. These factors generally favor the issuance of the ERP, but only with the Flowage Easement and new special conditions. The flowway project would rehydrate a portion of the estuarine waters of southern Biscayne Bay that are sufficiently healthy to respond vigorously to the new freshwater infusions, so the project is important. The C-1 Canal appears to be the only readily available source of sufficient volumes of freshwater to achieve the rehydration of the tidal creeks, and the proposed path through the Lennar Homes mitigation area appears to be the only readily available means by which to divert the freshwater to the targeted tidal creeks. If the flowway project is limited to the tidal creeks and does not extend to the surrounding coastal wetlands, the likely environmental impacts appear to be positive on the receiving areas and the downstream portion of the C-1 Canal. For these reasons, even though the project is at an early conceptual stage and construction would not start for six years, it seems likely to be constructed. The apparent difficulty in securing the necessary additional 65 acres may yet be overcome through property acquisition, and, if not, the District may be able to increase the capacity of the flowway without jeopardizing the adjacent uplands. For the reasons stated in the Conclusions of Law below, other factors in determining whether the ERP without the Flowage Easement and new special conditions would be inconsistent with the overall objective of the District to implement CERP require consideration of the impact upon Lennar Homes in accommodating the Flowage Easement and new special conditions. With two exceptions, the Flowage Easement and new special conditions do not impose an inordinate burden upon Lennar Homes. The flowway would occupy the portion of the Project site that would have been subject to the conservation easement that was part of the original mitigation plan. Lennar Homes' responsibility for maintenance is considerably lessened if the District constructs the flowway, whose special maintenance needs can only be met by the District or its contractors. Although Lennar Homes may experience some sales resistance due to the uncertainty of the use of the mitigation area, the assurances gained from the subsequent permitting process, during which the District will seek an ERP from the Florida Department of Environmental Protection for the construction of the flowway, should allay reasonable concerns about flooding and other damage to the adjacent uplands. In three respects, though, the District has abused its discretion in preparing the Flowage Easement and new special conditions. First, the District abused its discretion in requiring Lennar Homes to perform mitigation work in the mitigation area, pursuant to the original mitigation plan, to the extent that the products of such work will likely be destroyed or substantially harmed by the construction and operation of the flowway. The value of mitigation rests largely in the functions that it can support through longterm viability. The construction and operation of the surface water management system, the posting of a sufficient bond to guarantee future performance under either mitigation scenario, the execution and delivery into escrow of deeds and other legal instruments sufficient to meet the requirements of the Flowage Easement and new special conditions (subject to the two matters discussed in this and the two following paragraphs), and the construction of the portion of the original mitigation that would not be impacted by the flowway sufficiently respond to the need for mitigation, until the District finally determines the need for it to exercise its rights under the Flowage Easement. Second, the District abused its discretion by omitting any timeframe for the District to exercise its rights under the Flowage Easement and new special conditions. The timeframe proposed by Lennar Homes for the District to make this final determination of whether to proceed with the flowway is unreasonable and ignores the substantial period of time required to design, fund, and permit the flowway. But a timeframe may be especially important if Lennar Homes encounters more marketing resistance than might be reasonably anticipated. Therefore, the new conditions should provide that if construction of the flowway is not substantially completed by 2011, then the Flowage Easement shall be released and returned to Lennar Homes, upon its commencement, without delay, of the construction of any of the original mitigation that it did not already complete. Third, the District also abused its discretion in the Flowage Easement and new special conditions in the allocation of liability for the flowway, including apparently its construction, maintenance, and operation. The District would impose this liability upon Lennar Homes, which would have to indemnify the District for construction damage or any malfunctions in the operation of the flowway, such as damage to adjacent uplands by flooding, erosion, or contamination. The District has imposed this restoration project on Lennar Homes and has done so, not to avoid harm to the District's water resources, but to achieve the overall objective of the District to implement CERP. The District and its contractors, not Lennar Homes, will construct, maintain, and operate the flowway. The District, not Lennar Homes, has the expertise in the design, construction, and operation of water-control facilities of this type. This record does not disclose a single legitimate reason to impose upon Lennar Homes the liability for any aspect of the flowway that does not result from the acts or omissions of Lennar Homes or its assignees as owners of the adjacent uplands. Although, as stated in its proposed recommended order, the District does not object to the standing of Petitioners, Respondents did not stipulate to the standing of any Petitioners. Petitioners The Everglades Trust, Inc., and The Everglades Foundation, Inc., offered no witnesses concerning their standing, and no exhibits address the standing of these parties. The record thus fails to demonstrate that Petitioners The Everglades Trust, Inc., and The Everglades Foundation, Inc., are substantially affected by the proposed agency action. Petitioner National Parks Conservation Association, Inc., (National Parks) is a not-for-profit corporation registered in Florida as a foreign corporation. The corporate purpose of National Parks is to protect and enhance America's national parks, including Biscayne National Park, for present and future generations. National Parks seeks the protection and enhancement of the Biscayne National Park through the successful implementation of CERP. National Parks has 350,000 members, including 19,900 in Florida. Members of National Parks use Biscayne National Park for recreational boating, fishing, snorkeling, fish watching, scuba diving, and camping (on the barrier islands). Members of National Parks are actively monitoring the implementation of CERP. Petitioner Florida Audubon Society, Inc. (Florida Audubon), is a Florida not-for-profit corporation that was originally incorporated in Florida in 1900. The corporate purpose of Florida Audubon is to protect, conserve, and restore Florida's heritage through the preservation of the state's natural resources. Florida Audubon has adopted as its highest priority the design and implementation of CERP. Florida Audubon has 32,000 members in Florida, including over 2100 members in Dade County. Numerous of these members engage in bird watching, recreation, and scientific research in Biscayne National Park. Florida Audubon organizes membership trips to Biscayne Bay, conducts its annual Bird-athon and Christmas Bird Count in the vicinity of Biscayne Bay, and conducts various environment educational programs in and concerning Biscayne Bay. The issuance of the ERP without the Flowage Easement and new special conditions would substantially impact the ability of the District to restore this part of Biscayne Bay. Without such restoration, the functions of Biscayne Bay will slowly decline until eventually the overall health of the entire South Florida ecosystem will be substantially deteriorated. Thus, National Parks and Florida Audubon would be substantially affected by the issuance of the ERP without the Flowage Easement and new special conditions.
Recommendation It is RECOMMENDED that the District issue the environmental resource permit with the Flowage Easement and new special conditions, as modified in accordance with the matters presented in paragraphs 39-41. DONE AND ENTERED this 10th day of January, 2003, in Tallahassee, Leon County, Florida. ROBERT E. MEALE Administrative Law Judge Division of Administrative Hearings The DeSoto Building 1230 Apalachee Parkway Tallahassee, Florida 32399-3060 (850) 488-9675 SUNCOM 278-9675 Fax Filing (850) 921-6847 www.doah.state.fl.us Filed with the Clerk of the Division of Administrative Hearings this 10th day of January, 2003. COPIES FURNISHED: Henry Dean, Executive Director South Florida Water Management District Post Office Box 24680 West Palm Beach, Florida 33416-4680 Richard Grosso Louise Caro, Certified Legal Intern Environmental & Land Use Law Center, Inc. Shepard Broad Law Center 3305 College Avenue Fort Lauderdale, Florida 33314 Marcy I. LaHart Marcy I. LaHart, P.A. 711 Talladaga Street West Palm Beach, Florida 33405 Erin L. Deady Environmental Counsel 444 Brickell Avenue, Suite 850 Miami, Florida 33131 E. Thom Rumberger Rumberger, Kirk & Caldwell, P.A. 403 East Park Avenue Tallahassee, Florida 32301 Luna Ergas Phillips Douglas H. MacLaughlin Office of Counsel South Florida Water Management District 3301 Gun Club Road West Palm Beach, Florida 33406 Frank E. Matthews Gary V. Perko Hopping Green & Sams, P.A. Post Office Box 6526 Tallahassee, Florida 32314
The Issue Whether a permit (DER File #411890893) should be issued to James R. Langford in accordance with the Notice of Intent filed herein.
Findings Of Fact In addition to the Department and the National Park Service, a copy of the Initial Order was mailed to: James R. Langford, 6008 Shore Acres Drive, N.W., Bradenton, Florida; and James R. Langford, c/o Benson Engineering, Inc., 311 67th Street West, Bradenton, Florida 34209. Benson Engineering, Inc., was agent for James R. Langford in presenting Langford's application to the Department. All Orders and Notices of Hearings including the Initial Order, mailed to James R. Langford at 6008 Shore Acres Drive, N.W., Bradenton, Florida by the Division of Administrative Hearings were returned by the U.S. Postal Service indicating that the forwarding order had expired. All attempts by the undersigned, including contacting Benson Engineering, Inc., to contact Langford by telephone were unsucessful. Benson Engineering, Inc. received Notice of the Hearing. Mr. Benson appeard at the hearing, and advised the undersigned that he was the agent for Langford in presenting Langford's application to the Department. However, there was nothing in the record where Langford had requested that Benson be allowed to act as his Qualified Representative and Benson did not present anything at the hearing. Therefore, Benson was not allowed to act as Langford's Qualified Representative. Langford did not appear at the hearing, and made no contact with the undersigned, or counsel for the Department or counsel for the National Park Service. Counsel for both the Respondent and the National Park Service attempted to locate Langford on different occasions but were unsuccessful. Counsel for the Department even contacted the real estate office that was handling the sale of the property subject to the permit application but was also unsuccessful in this attempt. There was no evidence presented in support of Langford's application for a permit to build the dock in question.
Recommendation Accordingly, upon the foregoing Findings of Fact and Conclusion of Law, it is, RECOMMENDED: That the Department enter a Final Order denying Respondent James R. Langford's application for permit, DER File Number 411890893. DONE and ENTERED this 24 day of August, 1992, in Tallahassee, Leon County, Florida. WILLIAM R. CAVE 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 24 day of August, 1992. COPIES FURNISHED: Francine M. Ffolkes, Esquire Department of Environmental Regulation 2600 Blair Stone Road Tallahassee, Florida 32399-2400 Patricia Cortelyou-Hamilton, Esquire U.S. Department of the Interior National Park Service SE Regional Office 75 Spring Street SW Atlanta, Georgia 3030 James R. Langford 6008 Shore Acres Dr NW Bradenton, Florida 34209 James R. Langford c/o Benson Engneering Co. 311 67th Street W Bradenton, Florida 34209 Carol Browner, Secretary State of Florida Department of Environmental Regulation 2600 Blair Stone Road Tallahassee, Florida 32399-2400 Daniel H. Thompson General Counsel State of Florida Department of Environmental Regulation 2600 Blair Stone Road Tallahassee, Florida 32399-2400
Findings Of Fact Exception to Finding of Fact Number 1 is accepted, but not materially dispositive of the issues presented. Intervenor suggests that the Hearing Officer erroneously found that the dispute arose "when the Board and DNR took a position that Clam Bayou . . . is a part of the Pine Island Sound Aquatic Preserve." The dispute arose when a DNR planning manager took the position that Clam Bayou was in the preserve. (Petitioner's Exhibit #4) This determination was made before the June 12, 1991 Cabinet Meeting, when the Board of Trustees ratified their intent to include Clam Bayou in the preserve when the preserve was created in 1970. This finding was made independently of the Hearing Officer's legal conclusions and, to the extent the Hearing Officer misstated the facts, the misstatement has no bearing on the ultimate issue of whether Clam Bayou is a part of the preserve. Exception to Finding of Fact Number 2 is rejected. The Hearing Officer's findings are supported by competent substantial evidence. (TR 96) Exception to Finding of Fact Number 5 is rejected. The Hearing Officer's findings are supported by competent substantial evidence. (Petitioner's Exhibit #13) Exception to Finding of Fact Number 6 is rejected. The Hearing Officer's findings are supported by competent substantial evidence. Exception to Finding of Fact Number 7 is rejected. The Hearing Officer's findings are supported by competent substantial evidence. (Petitioner's Exhibit #`s 12 and 13) Exception to Finding of Fact Number 8 is accepted to the extent that between 1968 and 1972, Clam Bayou was physically connected to Pine Island Sound via Blind Pass. This exception has been incorporated into revised Finding of Fact 8. Exception to Finding of Fact Number 9 is accepted and the principles set forth in the exception have been incorporated into the amended Finding of Fact 9. Exception to Finding of Fact Number 10 is rejected. The Hearing Officer's findings are supported by competent substantial evidence. 9. Exception to Finding of Fact Number 11 is accepted. 10. Exception to Finding of Fact Number 12 is accepted. 11. Exception to Finding of Fact Number 14 is accepted. 12. Exception to Finding of Fact Number 15 is accepted. 13. Exception to Finding of Fact Number 17 is accepted. Exception to Finding of Fact Number 18 is rejected. The Hearing Officer's findings are supported by competent substantial evidence. (Petitioner's Exhibit #3, 6-A, 6-B and 10-B) Exception to Finding of Fact Number 19 is rejected. The Hearing Officer's findings are supported by competent substantial evidence. (Petitioner's Exhibit #3, 6-A, 6-B and 10-B) Exception to Finding of Fact Number 20 is accepted. EXCEPTIONS TO CONCLUSIONS OF LAW EXCEPTION TO CONSIDERATION OF THE RECOMMENDED ORDER BY THE GOVERNOR AND CABINET Intervenor's exception to consideration of the Recommended Order by the Governor and Cabinet is rejected. The transcript of the June 12, 1991 Cabinet meeting clearly shows the Governor and Cabinet's intent to have the issues in this case determined by a hearing officer. Although Petitioners and Intervenors presented brief oral argument to the Cabinet, no evidence was received and the Cabinet did not review the resolution and legal description, or all of the maps, photographs, or various other exhibits presented at hearing. The Cabinet did not make any findings of fact or conclusions of law with regard to this agenda item, and did not reach a conclusion as to the proper interpretation of the legal description or as to a finding of the actual intent of the Board of Trustees at the time the resolution was adopted. EXCEPTIONS TO OTHER CONCLUSIONS OF LAW Intervenors have asserted several exceptions to the conclusions of law contained in the Hearing Officer's Recommended Order. This order will address those exceptions in the format as presented in Intervenor s exceptions. Ambulatory Boundaries. This exception is rejected without reaching the merits because a conclusion of law as to ambulatory boundaries is not necessary or applicable to the determination of this matter. Clam Bayou's Presence in the Aquatic Preserve in 1970 The "Headlands Rule". This exception is rejected without reaching the merits because, as recognized by the Hearing Officer, a conclusion of law as to the Headlands Rule is not necessary or applicable to the determination of this matter. The Hearing Officer recognized that the headlands rule was never intended to be applied to the aquatic preserve: [S]trict application of the "Headlands Rule" was never intended and should not be applied in this case in construing the entire boundary, else numerous of the coves, inlets, bays, and other water bodies opening into Pine Island Sound would be excluded from the preserve. The evidence ... concerning the Board's intent establishes that such a result was not intended. (Recommended Order, Conclusions of Law, p. 22) The "Separate Name" Theory. This exception is rejected without reaching the merits because a conclusion of law as to a Separate Name Theory is not necessary or applicable to the determination of this matter. Maps of the Preserve. This exception is rejected. There is competent substantial evidence in the record to support the Hearing Officers's conclusion that the intent of the drafters of the legal description was to exclude Clam Bayou from the preserve.
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 therefore, RECOMMENDED that a Final Order be entered by the Respondent agency finding that Clam Bayou and the proposed construction site at issue and referenced in the above Findings of Fact be deemed to be without the boundaries of the Pine Island Sound Aquatic Preserve. DONE AND ENTERED this 9th day of December, 1991, in Tallahassee, Leon County, Florida. P. MICHAEL RUFF Hearing Officer Division of Administrative Hearings The DeSoto Building 1230 Apalachee Parkway Tallahassee, FL 32399-1550 (904) 488-9675 Filed with the Clerk of the Division of Administrative Hearings this 10th day of December, 1991. APPENDIX TO RECOMMENDED ORDER IN CASE NOS. 91-3249R AND 91-3770 Petitioner's Proposed Findings of Fact 1-7. Accepted. 8. Accepted, except that the maps are not exactly identical since Petitioner's Exhibit No. 3 is a stippled or shaded map and the map recorded in the Lee County Public Records at Book 648, page 736, in evidence, is not actually shaded or stippled. 9-29. Accepted. Respondent's Proposed Findings of Fact 1-3. Accepted. Accepted, but not as being materially dispositive of the issues presented. Accepted. 6-12. Accepted. Accepted, but not in itself materially dispositive. Rejected, as not in accordance with the preponderant weight of the evidence. Accepted. 16-17. Rejected, as subordinate to the Hearing Officer's findings of fact on this subject matter. Rejected, as subordinate to the Hearing Officer's findings of fact on this subject matter and not entirely in accordance with the preponderant weight of the evidence. Rejected, as subordinate to the Hearing Officer's findings of fact on this subject matter and not entirely in accordance with the preponderant weight of the evidence. Accepted. Accepted, but not materially dispositive of the issues presented. Accepted, but not materially dispositive of the issues presented and subordinate to the Hearing Officer's findings of fact on this subject matter. Accepted, but not itself materially dispositive of the issues presented. Accepted, but not itself materially dispositive of the issues presented. Accepted. Accepted, but not materially dispositive of the issues presented standing alone. Accepted, but not materially dispositive of the issues presented standing alone. Accepted, but not materially dispositive of the issues presented standing alone. Rejected, as subordinate to the Hearing Officer's findings of fact on this subject matter. Rejected, as subordinate to the Hearing Officer's findings of fact on this subject matter. Intervenor's Proposed Findings of Fact (City of Sanibel) 1-2. Accepted. Accepted, but not materially dispositive in this de novo proceeding. Accepted, but not materially dispositive of the issues presented. Intervenor's Proposed Findings of Fact (Ralph Clark, et al.) Accepted, but not materially dispositive, given the de novo nature of this proceeding. Accepted, but not materially dispositive of the issues presented. Rejected, as not in accordance with the preponderant weight of the evidence. COPIES FURNISHED: Ken Plante, Esq. General Counsel Department of Natural Resources 3900 Commonwealth Boulevard Mail Station #10 Tallahassee, FL 32399-3000 Kenneth G. Oertel, Esq. OERTEL, HOFFMAN, ET AL. 2700 Blair Stone Road P.O. Box 6507 Tallahassee, FL 32314-6507 John Costigan, Esq. Edwin Steinmeyer, Esq. Department of Natural Resources 3900 Commonwealth Boulevard Tallahassee, FL 32399-3000 Robert D. Pritt, Esq. City of Sanibel 800 Dunlop Road Sanibel, FL 33957 Mark A. Ebelini, Esq. HUMPHREY & KNOTT, P.A. 1625 Hendry Street Ft. Myers, FL 33901
The Issue The issue in this case is whether Respondent, the Department of Environmental Protection (DEP), should grant the application of Respondent, Leland Egland, for an Environmental Resource Permit (ERP), Number 44-01700257-001-ES, to fill an illegally-dredged trench or channel in mangrove wetlands between Florida Bay and what was a land-locked lake, to restore preexisting conditions.
Findings Of Fact Since 1988, Applicant, Leland Egland, has resided in a home built on property he purchased in Buccaneer Point Estates in Key Largo, Florida, in 1986--namely, Lots 14 and 15, Block 2, plus the "southerly contiguous 50 feet." A 1975 plat of Buccaneer Point shows this "southerly contiguous 50 feet" as a channel between Florida Bay to the west and a lake or pond to the east; it also shows a 800-foot linear canal extending from the lake or pond to the north. Egland's Lot 14 borders Florida Bay to the west; his lot 15 borders the lake or pond to the east; the "southerly contiguous 50 feet" is between Egland's lots 14 and 15 and property farther south owned by another developer. See Finding 10, infra. Buccaneer Point lots in Blocks 1 (to the east) and 2 (to the west) surround the lake or pond and canal. The developer of Buccaneer Point applied to the Florida Department of Environmental Regulation (DER) in 1977 for a permit to dredge a channel, characterized as a flushing channel for the lake or pond, which was characterized as a tidal pond with replanted red mangroves. (There was no evidence as to the character of this pond before the 1977 permit application or if it even existed.) DER denied the permit application because the: proposal . . . to open a pond to Florida Bay . . . will connect an 800 linear foot dead-end canal. The pond and canal will act as a sink for marl and organic debris which will increase Biological Oxygen Demand and lower Dissolved Oxygen. The project is expected to result in substances which settle to form putrescent or otherwise objectionable sludge deposits and floating debris, oil scum, and other materials, in amounts sufficient to be deleterious. Based on the above, degradation of local water quality is expected. * * * Furthermore, your project will result in the following effects to such an extent as to be contrary to the public interest and the provisions of Chapter 253, Florida Statutes: Interference with the conservation of fish, marine life and wildlife, and other natural resources. Destruction of natural marine habitats, grass flats suitable as nursery or feeding grounds for marine life, including established marine soils suitable for producing plant growth of a type useful as nursery or feeding grounds for marine life. Reduction in the capability of habitat to support a well-balanced fish and wildlife population. Impairment of the management or feasibility of management of fish and wildlife resources. As a result, the proposed channel to Florida Bay was not dredged (although some of the lake side of the proposed channel apparently was dredged before the project was abandoned); the building lots surrounding the lake or pond (now known as South Lake) and canal were sold as waterfront lots on a land-locked lake without access to Florida Bay; and the "southerly contiguous 50 feet" was included with the conveyance to Egland, along with the Lots 14 and 15 of Block 2. The evidence was not clear as to the characteristics of the "southerly contiguous 50 feet" in 1977, or earlier. When Egland purchased his property in 1986, it was a mature mangrove slough with some tidal exchange between the lake and Florida Bay, especially during high tides and stormy weather. Some witnesses characterized the area of mangroves as a shallow creek in that general time frame (from about 1984 through 1988). According to Vince Easevoli, at least under certain conditions, a rowboat could be maneuvered between the lake and Florida Bay using a pole "like a gondola effect." But Egland testified to seeing Easevoli drag a shallow-draft boat through this area in this general time frame, and the greater weight of the evidence was that the mangrove slough was not regularly navigable channel at the time. During this general time frame (the mid-to-late 1980's) several Petitioners (namely, Stanley Dominick, John and Katherine Easevoli, and their son, Vince Easevoli) purchased property on South Lake. All but Vince built homes and resided there; Vince did not reside there until after Hurricane Andrew in 1992, but he sometimes stayed at the residence on his parents' property during this general time frame. In the early 1990's, the slough or creek became somewhat deeper, making it increasingly more easily passable by boat. Large storms such as Hurricane Andrew in 1992 and the "storm of the century" in 1993 may have contributed to these changes, but human intervention seems to have been primarily responsible. In 1994, Egland added a swimming pool south of the residence on his lots. During construction, some illegal filling took place. Several witnesses testified that the illegal fill occurred to the north of the creek, which was not affected. Vince Easevoli's lay interpretation of several surveys in evidence led him to maintain that illegal fill was placed in the mangrove slough and that the creek became narrower by approximately four feet and, eventually, deeper. But no surveyor testified to explain the surveys in evidence, which do not seem to clearly support Easevoli's position, and the greater weight of the evidence was that illegal fill was not added to the creek in Egland's "southerly contiguous 50 feet." At some point in time, hand tools were used to deepen the slough or creek and trim mangroves without a permit to enable a small boat to get through more easily. As boats were maneuvered through, the creek got deeper. Eventually, propeller-driven boats of increasing size were used to "prop- dredge" the creek even deeper. According to Petitioner, Tom Hodges, when he and his wife purchased their lot on the lake in 1994, it was possible to navigate the creek in a 22-foot Mako boat (at least under certain conditions), and their lot was sold to them as having limited access to Florida Bay. (There was evidence that access to Florida Bay could increase the price of these lots by a factor of three.) Petitioners Martha Scott and Marianne Delfino also purchased their property on the lake in 1994. Tom Hodges claimed to have seen manatees in the lake as early as 1994, but no other witnesses claimed sightings earlier than 1997, and the accuracy of this estimate is questionable. Even if manatees were in the lake during this time frame or earlier, it is possible that they used an access point other than the creek. At the southeast corner of South Lake in Buccaneer Point, there is a possible connection to a body of water farther south, which is part of a condominium development called Landings of Largo and leads still farther south to access to Florida Bay near a dock owned by Landings of Largo. While this connection is shallow, it may have been deep enough under certain conditions to allow manatees to pass through. Apparently not with manatees but rather with boaters from the lake in Buccaneer Point in mind, Landings of Largo has attempted to close this access point by placement of rebar; Landings of Largo also has placed rip-rap under its dock farther south to prevent boats from passing under the dock. However, there are gaps in the rip-rap, some possibly large enough for manatees to pass. In approximately 1995 or 1996, Egland observed Vince Easevoli and his father, John Easevoli, digging a trench through the mangrove slough with a shovel and cutting mangrove trees with a saw in Egland's "southerly contiguous 50 feet." Others were standing by, watching. Egland told them to stop and leave.6 These actions made the creek even deeper and more easily navigable by boat, which continued to further excavate the trench by such methods as "prop dredging." In 1997 Hany Haroun purchased property adjacent to South Lake where he lives with his wife, Christine. By this time, Florida Bay was easily accessible by boat from the lake, and Haroun paid $260,000 for the property. He estimated that his property would be worth about $150,000 less without boat access to Florida Bay. In approximately 1997, manatees began to appear in South Lake year round from time to time, especially in the winter months. In 1997, the Hodgeses saw one they thought may have been in distress and telephoned the Save Our Manatee Club and Dolphin Research for advice. Following the advice given, they used lettuce to coax the manatee over to their dock to check its condition and videotape the event. The manatee appeared healthy and eventually departed the lake. On subsequent visits, manatees have been seen and videotaped resting and cavorting with and without calves and possibly mating in the lake. Groups of as many as seven to eight manatees have been seen at one time in the lake. Tom Hodges, Vince Easevoli, and Hany Haroun testified that they have enjoyed watching manatees in the lake since 1997. It can be inferred from the evidence that Elaine Hodges also has enjoyed watching manatees in the lake. There was no evidence as to the extent to which other Petitioners enjoy watching manatees in the lake. In 1997, the ACOE began an investigation of the illegal dredging of Egland's "southerly contiguous 50 feet." According to Egland, he was in communication with ACOE; presumably, he told ACOE what he knew about the illegal dredging on his property. According to Egland, ACOE advised him to place posts in the dredged channel to keep boats out. When he did so, Tom Hodges removed the posts. Egland replaced the posts, and Hodges removed them again. When Egland told ACOE what was happening, ACOE asked him to try reinstalling the posts and screwing plywood to the posts to achieve a stronger, fence-like barrier. Hodges also removed these barriers, and Egland did not replace the posts or plywood barrier again. In 1998, ACOE mailed Egland a Cease and Desist Order accusing him of illegal dredging in his "southerly contiguous 50 feet" and demanding that he restore the mangrove slough to its previous conditions. Egland was angry at being blamed for the dredging and initially disputed ACOE's charges and demands. But ACOE and the United States Environmental Protection Agency (EPA), which accepted the role of lead federal enforcement agency on December 18, 1998, was seeking monetary civil penalties. In addition, Egland received legal advice that, if restoration were delayed, he could be sued for damages by someone purchasing property on the lake or canal in the meantime upon the mistaken belief that there was boat access to Florida Bay. For these reasons, Egland agreed to comply with the Cease and Desist Order. However, ACOE and EPA informed Egland that he might have to obtain a permit from DEP to fill the dredged channel in compliance with the Cease and Desist Order. On May 22, 2000, Egland applied to DEP for an ERP to restore a trench about 100 feet long varying from seven to ten feet in width that was illegally dredged on his property. He estimated that a total of 160 cubic yards of fill would be required, to be spread over approximately 900 square feet. He assured DEP that rip-rap would be used to contain the fill and that turbidity screens would be used during construction. During processing of Egland's application, DEP requested additional information, which Egland provided, and DEP's Environmental Manager, Edward Barham, visited the project site in October 2000. Based on all the evidence available to him at that point in time, Barham viewed Egland's proposed fill project as a simple restoration project to correct illegal dredging and return the mangrove slough to its preexisting condition. For that reason, Barham recommended that DEP process the application as a de minimis exemption and not charge a permit application fee. Subsequently, some Petitioners brought it to DEP's attention that manatees were accessing South Lake through the channel Egland wanted to fill. DEP saw no need to verify the accuracy of Petitioners' information or obtain additional information about the manatees use of the lake because DEP still viewed it as a restoration project. However, DEP decided that it would be necessary to include specific conditions in any ERP issued to Egland to ensure that no manatees would be trapped in the lake or otherwise injured as a result of filling the channel. Primarily due to the need for these conditions, and also because of anticipated opposition from Petitioners, DEP decided to charge Egland a permit application fee and not process the application as a de minimis exemption. DEP staff visited the mangrove slough on numerous occasions between October 2000, and final hearing and observed that the trench continued to get deeper over time as a result of continued prop-dredging and digging. In early August 2001, Tom Hodges observed a man walking back and forth with a wheel barrow between a storage shed on Egland's property and the channel. (Hodges was on his property across South Lake but use of binoculars enabled him to see this.) The next day, Hany Haroun discovered a poured- concrete slab forming a plug or dam in the channel on the lake side. Haroun reported his discovery to Tom Hodges, who investigated with his wife, who took photographs of the structure. At some point, the Hodgeses realized that a manatee was trapped in the lake. The manatee did not, and appeared unable to, use the other possible access point towards Landings of Largo to escape. See Finding 10, supra. The Hodgeses telephoned Barham at DEP to report the situation and complain. Tom Hodges then proceeded to break up the concrete, remove the resulting rubble, and place it on the path to the storage shed, freeing the manatee. The incident was reported in the newspaper the next day and prompted Petitioners to file their Motion to Dismiss and for Other Relief on August 9, 2001. See Preliminary Statement. The evidence was inconclusive as to who poured the concrete, or had it poured, and why. Egland testified that he was in Egypt on an extended trip at the time and denied any knowledge of the concrete plug until he saw the rubble on his property upon his return from Egypt. Egland testified that he saw no "aggregate" in the concrete, which would make it relatively easy to break up, and he suspected that Petitioners were responsible for pouring the concrete in order to publicly make false accusations against Egland. Petitioners denied Egland's accusation. Vince testified that the concrete contained rebar for strength. The evidence was inconclusive as to who was responsible for this incident. As pointed out by Petitioners, DEP did not investigate and does not know whether there is any freshwater upwelling in the lake, whether manatees have mated in the lake, or whether calves have been birthed in the lake. DEP also did not investigate and does not know whether South Lake is unlike other manatee habitat in the area. DEP did not investigate or obtain any information as to how many manatees use the lake, or what manatees use the lake for, in addition to the information provided by Petitioners. Carol Knox, an Environmental Specialist III with the Florida Fish and Wildlife Commission, testified as a manatee expert based on her knowledge of manatees and manatee habitat in the area, as well as the information known to DEP. It was her opinion that, regardless what South Lake might offer manatees in the way of habitat, closing the channel (with the specific conditions required by DEP to protect manatees during the filling itself) would have no adverse impact on manatees because it did not appear that manatees made use of the lake before the channel was dug in 1996 or 1997, and ample other manatee habitat of various kinds continued to be available in the area.7 Based on the testimony of Knox and Barham, and the totality of the evidence in this case, it is found that Egland provided reasonable assurance that his proposed restoration project will not harm or adversely affect manatees or their habitats. Petitioners also questioned Egland's assurances as to water quality. Vince Easevoli, Stanley Dominick, and Hany Haroun testified to their concerns that water quality in the lake will decline if the channel is closed. As Petitioners point out, DEP did not require Egland to provide any water quality measurements. This was because the proposal is reasonably expected to reverse the effects of the illegal dredging on water quality and to return both the water in the lake and canal and the water in Florida Bay to the quality that existed prior to the illegal dredging. Without requiring any water quality measurements, it is reasonably expected that the water quality in Florida Bay would not decline in any respect; to the contrary, if anything, Florida Bay's water quality would be expected to improve by reduction of contributions from the lake and canal. Conversely, water quality in the lake and canal would be expected to decline but not below what it was before the illegal dredging. Petitioners also question DEP's failure to require Egland to provide a survey or stake the area to be filled, so as to ensure against filling too much of the mangrove slough. But the proposed ERP contains a specific condition: "The final fill elevation of the fill shall be at the elevation of the substrate within the adjacent mangrove wetlands." Barham testified persuasively that this specific condition is adequate to provide reasonable assurance. Compliance can be ascertained by simply viewing the site after completion of the restoration project, and compliance can be enforced by requiring removal of excess fill as necessary. The proposed ERP also contains a general condition that the permit does not convey or create any property right, or any interest in real property, or authorize any entrances upon or activities on property which is not owned or controlled by Egland.
Recommendation Based upon the foregoing Findings of Fact and Conclusions of Law, it is RECOMMENDED that the Respondent, the Department of Environmental Protection, enter a final order granting the application of Leland Egland and issuing ERP Number 44- 01700257-001-ES. DONE AND ENTERED this 25th day of November, 2002, in Tallahassee, Leon County, Florida. ___________________________________ J. LAWRENCE JOHNSTON Administrative Law Judge Division of Administrative Hearings The DeSoto Building 1230 Apalachee Parkway Tallahassee, Florida 32399-3060 (850) 488-9675 SUNCOM 278-9675 Fax Filing (850) 921-6847 www.doah.state.fl.us Filed with the Clerk of the Division of Administrative Hearings this 25th day of November, 2002.
The Issue The issue to be determined in this case is whether 1044PVB, LLC (“Applicant”), is entitled to Environmental Resource Permit (“ERP”) No. IND-109-143282-1 from the St. Johns River Water Management District (“District”), authorizing the construction of a surface water management system to serve a proposed residential development in St. Johns County, Florida.
Findings Of Fact The Parties Petitioner Nancy Condron is a resident and landowner in St. Johns County. Her residence is located across Ponte Vedra Boulevard from the Project. Petitioner uses the nearby Guana River Wildlife Management Area for nature-based recreation, including hiking and bird-watching. Applicant is a foreign limited liability company and the applicant for the ERP at issue in this case. The District is an independent special district granted powers and assigned duties under chapter 373, Florida Statutes, including powers and duties related to the regulation of construction activities in wetlands. The Project is within the boundaries of the District. The Project Site The Project site is 17.13 acres located at 1044 Ponte Vedra Boulevard in St. Johns County, Florida. The site currently consists of forested lands on the east and west and pasture areas in the middle. There is an existing trail road that runs the length of the property and a small residence. The site has four small ponds excavated as watering holes, ranging in size from 0.04 to 0.24 acres. There are 4.41 acres of wetlands and other surface waters on the site. There is a 3.49-acre area of mixed forested wetland on the site that continues offsite to the south and west. There are also three isolated wetlands on the site, each less than a half-acre in size. The wetland system adjacent to the Project site flows to the Guana River. The Guana River is a freshwater, Class III waterbody. It is an Outstanding Florida Water, but has been designated by the Department of Environmental Protection as impaired for nutrients. The site is not used by threatened or endangered species for feeding, nesting, or breeding. The Project The proposed Project is a 22-lot, single-family subdivision. The proposed surface water management system for the Project includes curb and gutter paved roadways, storm inlets, concrete pipes, vegetated natural buffers, treatment swales, and a wet detention stormwater pond. The wet detention stormwater pond would discharge into adjacent wetlands that flow to the Guana River. Wetlands The point of discharge from the Project’s stormwater management system is not in the designated Outstanding Florida Water. Applicant proposes to fill the four ponds and the three isolated wetlands. Applicant also proposes to fill 0.28 acres of the larger wetland. The Project includes a number of upland buffers that are a minimum of 15 feet in width and average of 25 feet in width. These buffers are intended to prevent potential adverse secondary impacts to adjacent wetlands. All wetland impacts and mitigation were assessed using the Uniform Mitigation Assessment Method (UMAM) in Florida Administrative Code Rule 62-345. The UMAM assessment takes into consideration the location and landscape support, water environment, and community structure of the wetlands to be impacted. The District also considers the condition, hydrologic connection, uniqueness, location, and the fish and wildlife utilization of the wetlands and other surface waters. The District did not require mitigation for filling the artificial ponds. The District also did not require mitigation for filling the isolated wetlands because each is less than a half-acre in size. As mitigation for filling 0.28 acres of the larger wetland, Applicant would purchase 0.25 mitigation bank credits from the St. Marks Pond Mitigation Bank. The St. Marks Pond Mitigation Bank is located in the same drainage basin as the wetland area that would be filled. The District determined that purchasing the mitigation bank credits would offset the functional loss associated with filling part of the wetland. Two areas on the site where no upland buffers are proposed were assessed for secondary impacts to wetlands in the UMAM evaluation. The mitigation bank credits proposed for the Project would offset all of the adverse, direct, and secondary impacts to wetlands or surface waters associated with this Project. Because direct and secondary impacts would be fully mitigated, the Project would not cause cumulative impacts. Water Quantity A majority of the Project’s stormwater runoff would be conveyed to the wet detention pond. The wet detention pond provides water quantity protection by attenuating the post- development peak rate of discharge. Applicant modeled the pre-development peak rate of discharge and the post-development peak rate of discharge. The modeling indicated that the post-development peak rate of discharge will not exceed the pre-development peak rate of discharge for the 25-year, 24-hour storm event. Section 3.3 of the Applicant's Handbook, Volume II, prohibits a reduction in the 10-year or 100-year floodplain for projects with an upstream drainage basin of five square miles or greater. The proposed Project has an upstream drainage basin of 4.6 square miles, so this criterion is not applicable. Applicant showed the Project would increase offsite flood elevations by only 0.01 feet, which is negligible. The Project would not cause adverse water quantity impacts to receiving waters or adjacent lands. Water Quality Water quality would be managed in the Project through a combination of wet detention pond, swales, and vegetative natural buffers (“VNBs”). The wet detention pond would treat a majority of the runoff from the Project. Section 8 of the Applicant’s Handbook, Volume II, contains presumptive criteria for the design of a wet detention pond. The proposed wet detention pond meets the presumptive criteria. Therefore, the detention pond is presumed to provide reasonable assurance that the water quality of receiving waters will be protected. Applicant is proposing to construct swales at the back of Lots 20, 21, and 22 to treat runoff by infiltration. Section 9 of the Applicant’s Handbook, Volume II, contains presumptive criteria for swale system design and performance. The Project meets the presumptive criteria for swales. Applicant is proposing VNBs on Lots 1 through 14. The use of VNBs is a commonly-used best management practice accepted by the District for treating stormwater runoff. Like swales, VNBs treat runoff by infiltration. Stormwater runoff from the backyards of Lots 1 through 14 would drain to the VNBs. On some of these lots, stormwater runoff from the front yards, side yards, and rooftops would also drain to the VNBs. The lots would be graded so that runoff would sheet flow to the VNBs to maximize their treatment function. The VNBs would have native soils and plants. The VNBs would have Type A soils, which are well-drained soils that provide the highest rate of infiltration and the most permeability. Petitioner contends that, because soil borings were not taken at the location of the VNBs, reasonable assurance was not provided that the VNBs would function as proposed. However, Petitioner did not show that the soils at the VNB locations were unsuitable soils. In addition, Applicant agreed to use Type A soils in the VNBs. Therefore, reasonable assurance that the VNBs would have suitable soils was provided by Applicant. Petitioner referred to a draft rule to support her contention that the proposed VNBs are not properly designed, but the draft rule has no controlling effect and is hearsay. The Applicant’s Handbook does not contain presumptive criteria for VNBs. Applicant demonstrated that the VNBs would infiltrate 80 percent of the runoff from a three-year, one-hour storm event, which is the same treatment efficiency the District requires when swales are used. Reasonable assurance was provided that the VNBs would function as proposed. Because the Project would discharge to wetlands that flow to the Guana River, a waterbody impaired by nutrients, section 2.2 of the Applicant’s Handbook, Volume II, requires Applicant to demonstrate there would be a net improvement in water quality with respect to nutrients. Applicant performed a pollutant loading analysis using the BMPTRAINS model. The BMPTRAINS model is a generally-accepted tool used by stormwater engineers for this purpose. The BMPTRAINS model incorporates the information about the pre- and post-development conditions associated with land use and impervious area. The model accounts for site-specific conditions, including the elevation of the groundwater table and storage capacity of the soil. The design of the surface water management system is then incorporated into the model to estimate the pollutant removal efficiency and estimate the average annual pollutant load that will leave the site. Applicant’s BMPTRAINS modeling indicated that the average annual post-development loading for total nitrogen and total phosphorus would be substantially less than the pre- development loading for those nutrients. Therefore, Applicant demonstrated the Project would result in a net improvement. Operation & Maintenance The Ponte Vedra Beach Preserve Homeowners Association would be the entity responsible for operation and maintenance of the stormwater management system. The wet detention pond, swales, and VNBs would be located within an easement and maintained by the homeowner’s association. Applicant and the Ponte Vedra Beach Preserve Homeowners Association have the ability to accept responsibility for the operation and maintenance of the Project. Public Interest An applicant for an ERP must demonstrate that a proposed project affecting wetlands and other surface waters would not be contrary to the public interest. This determination is made by balancing seven factors found in section 10.2.3(a) through (g) of the Applicant’s Handbook, Volume I. Public interest factor (a) is whether the regulated activity will adversely affect public health, safety, or welfare, or the property of others. There is no aspect of the Project that would affect public health, safety, or welfare, except the potential for flooding. Reasonable assurance was provided by Applicant that the Project would not cause flooding. Factor (b) is whether the regulated activity will adversely affect the conservation of fish and wildlife, including endangered or threatened species or their habitats. The mitigation bank credits offset all of the potential adverse impacts that the proposed project would have on the conservation of fish and wildlife. Factor (c) is whether the regulated activity will adversely affect navigation or the flow of water or cause harmful erosion or shoaling. The parties stipulated that the Project will not adversely affect navigation or cause harmful erosion or shoaling. The record evidence shows the Project will not adversely affect the flow of water. Factor (d) is whether the regulated activity will adversely affect the fishing or recreational values or marine productivity in the vicinity of the activity. The Project would not affect fishing or recreational values in the vicinity. The mitigation bank credits offset all of the potential adverse impacts the proposed project would have on marine productivity in the vicinity. Factor (e) is whether the regulated activity will be of a temporary or permanent nature. The activities are of a permanent nature. The mitigation is also permanent. Factor (f) is whether the regulated activity will adversely affect or will enhance significant historical and archaeological resources. The Project will have no effect on historical and archaeological resources. Factor (g) is the current condition and relative value of functions being performed by areas affected by the proposed regulated activity. The relatively small loss of functional value would be offset by the proposed mitigation. Considering and balancing these seven factors, the Project would not be contrary to the public interest.
Recommendation Based on the foregoing Findings of Fact and Conclusions of Law, it is RECOMMENDED that the St. Johns River Water Management District enter a final order approving the issuance of Environmental Resource Permit No. IND-109-143282-1 to 1044PVB, LLC, with the conditions set forth in the Technical Staff Report dated April 11, 2016. DONE AND ENTERED this 16th day of June, 2016, in Tallahassee, Leon County, Florida. S BRAM D. E. CANTER Administrative Law Judge Division of Administrative Hearings The DeSoto Building 1230 Apalachee Parkway Tallahassee, Florida 32399-3060 (850) 488-9675 Fax Filing (850) 921-6847 www.doah.state.fl.us Filed with the Clerk of the Division of Administrative Hearings this 16th day of June, 2016. COPIES FURNISHED: Karen C. Ferguson, Esquire St. Johns River Water Management District 4049 Reid Street Palatka, Florida 32177 (eServed) Jane West, Esquire Josh Smith, Esquire Jane West Law, P.L. 6277 A1A South, Suite 101 St. Augustine, Florida 32080 (eServed) Eric Olsen, Esquire Amelia A. Savage, Esquire Hopping, Green and Sams, P.A. Post Office Box 6526 Tallahassee, Florida 32314 (eServed) Ann B. Shortelle, Ph.D., Executive Director St. Johns River Water Management District 4049 Reid Street Palatka, Florida 32177 (eServed)
Findings Of Fact Upon consideration of the oral and documentary evidence adduced at the hearing, as well as the Hearing Officer's view of the project site, the following relevant facts re found: Respondent Sunset Realty Corporation initially applied to the Department of Environmental Regulation on March 2, 1979, for a permit to place 54,600 cubic yards of fill adjacent to Three Sisters Island and waterward of the mean high water line in Charlotte Harbor in order to construct a causeway and a sixty-foot bridge from Boca Grande Isles to Three Sisters Island. The applicant Sunset was notified on May 3, 1979, that adverse comments on the project had been received due to its impact upon biological resources. DER suggested that the application be modified by bridging the entire submerged area to alleviate biological and hydrographic concerns. On June 21, 1979, the respondent Sunset filed a revised application which reduced the volume of fill from 54,600 cubic yards to 25,000 cubic yards and extended the bridge from sixty feet to ninety feet long. The Department of Environmental Regulation forwarded to Lee County a summary of the Department's biological and hydrographic report. Additional information was not requested by the County. On October 31, 1979, the Lee County Commission considered the information made available to them from the Department and passed a resolution giving their approval to the first revision of the project by respondent Sunset. Finding that the applicant had not provided reasonable assurance that immediate and long-term impacts of the project would not result in violation of state water quality standards for Class II waters, the Department of Environmental Regulation issued its Intent to Deny Sunset's permit application on March 24, 1980. After a biological and hydrographic study of the project area, Sunset filed a second revision to its project on June 30, 1980. This revised application requested a permit for 10,000 cubic yards of fill and a 120-foot long bridge. In addition, this revision contained plans to install groins at the south end of Three Sisters Island and on Boca Grande Isles, to place riprap along the face of the fill, to remove and relocate existing oyster bars, to maintain turbidity barriers around the project during construction, and to direct stormwater run-off from the concrete bridge to an upland retention area on Three Sisters Island. It was also stipulated by respondent Sunset at the hearing that it would agree, as a condition of the permit, to replant mangrove vegetation along the shoreline of Three Sisters Island. On July 18, 1980, the Department of Environmental Regulation issued a Letter of Intent to Issue the applicant a permit for the revised project. The Department of Environmental Regulation did not seek reapproval of the revised project from the Lee County Commission because the scope and impact of the revised project were substantially reduced. It is not the policy of DER to request a new local approval for reduced projects. All property within the project boundary including submerged lands to be filled is held in fee simple by respondent Sunset. The waters affected by the proposed project are Class II waters, but are unclassified by the Department of Natural Resources as to shellfish harvesting. The nearest Class II waters which thus far have been approved for commercial shellfish harvesting are located approximately one and a half miles north of the project site. The proposed project would involve the destruction and elimination of approximately one acre of productive marine bottoms. The area has an abundance of grass beds and organisms that constitute a viable marine nursery and habitat. The area is not considered a spawning ground for any significant commercial or sport fish species. While the project will eliminate one acre of shallow water and productive bottom resources, the project should have no permanent effect upon the quality of the remaining surrounding waters. Three different species of mangroves vegetate the shoreline and the project would entail the removal of approximately 2/10 acre of mangroves. As indicated above, the applicant has agreed to insert a condition in the permit to revegetate mangroves around the site. The project will also entail the removal of one or two oyster bars. Live oysters can be removed and relocated by the use of floating cages. Relocation of the oysters to the riprapping and bridge pilings should increase their productivity. While the proposed fill will eliminate a wading bird habitat, birds will not otherwise be affected except during the construction of the project. The area around Three Sisters Island is an excellent fishing ground for line and net fishing for trout, red fish, mullet and sheepshead. Concern was expressed by commercial fishermen at the hearing that the bridge would obstruct net fishing, that the construction of the bridge would drive the fish away temporarily and that the fish, being creatures of habit, would not come back. The 120-foot bridge itself would have a minor effect of approximately 2% upon the restriction of flow in the area. A flow resistance is presently caused by the channel itself, a sharp bend in the channel that occurs at a constriction or spit, and the spit itself. The spit severely restricts flow and the channel needs to be enlarged. The remedial measure proposed is to place groins on the spit and on Boca Grande Isles across the spit. This will gradually enlarge the opening and reduce constriction. The placement of groins could provide a 40% increase in flow through the channel, and the increased circulation will improve the overall system. The two groins proposed are 40 feet and 80 feet in length. The groins will intercept the transport of sand and the pass will thereby be enlarged. The groins will be visible to boaters in shallow water and will not be a significant hazard to navigation. Three Sisters Island is a fifteen acre island to be utilized by Sunset Realty Corp. for residential development. Employees of DER who testified at the hearing were not aware of DER ever permitting filling in Class II waters for the purpose of aiding a private development or use. Other regulatory agencies providing comments on the proposed project after its first revision recommended that all fill be deleted from the project plans and that the bridge be constructed so as to span the entire submerged lands and shoreline wetlands. These agencies included the United States Department of the Interior, the Department of the Army, the Florida Game and Fresh Water Fish Commission, the United States Department of Commerce and the United States Environmental Protection Agency. With the exception of Durbin Tabb and Richard Lotspeich, both of whom felt that the destruction of one acre of bottom resources would not be significant to the total system, all other experts in marine biology who testified at the hearing felt that spanning the entire area with a bridge and eliminating the fill would provide a viable alternative to the permanent elimination of wetlands and shorelands. The petitioner Gasparilla Island Conservation and Improvement Association, Inc. is a non-profit, tax exempt corporation which was incorporated in 1971. The qualification for membership is the ownership of real property on Gasparilla Island. Approximately 700 property owners on Gasparilla Island are eligible to be members of GICIA. The actual membership is approximately 446. Twenty-two members own property on Boca Grande Isles, the subdivision closest to Three Sisters Island. Among the purposes of the GICIA are the promotion of Land, water and wildlife conservation uses and purposes in the Gasparilla Island area in Lee County and Charlotte County, Florida, including the preservation of ecology of the area, the protection of fish and shellfish breeding areas, the preservation of wildlife, and the promotion of anti-pollution measures. Members of the association use the proposed project area for recreational boating, commercial fishing, shellfish gathering, swimming, fishing and enjoyment of the natural flora, fauna and wildlife. Association members will be adversely affected by the destruction of grasslands, mangroves and oyster beds. The Organized Fishermen of Florida, Inc. (O.F.F.) is a non-profit corporation with chapters throughout the State of Florida. Its purposes include the protection of the fishing industry of Florida and the promotion and sponsorship of conservation. Some members of O.F.F. regularly fish in the Three Sisters Island area that would be impacted by the proposed project. No evidence was presented at the hearing that the State Board of Directors of O.F.F. officially sanctioned witnesses to appear on behalf of the incorporated Organized Fishermen of Florida. No evidence was presented at the hearing as to the standing or substantial interest of the Florida Division of the Izaak Walton League or Eugene C. Enlow, both listed as Petitioners in the "Amendment of Petition for Formal Hearing." Petitioner Freemen Boynton is the owner of a residence located on Lot No. 98 on Boca Grande Isles. The proposed access bridge and groins are to be constructed on Lots No. 99 and 100 which are contiguous to Mr. Boynton's lot. The groin on Lot No. 99 could cause sand and other debris to accumulate upon Mr. Boynton's riparian property. Petitioner Boynton uses his home on Boca Grande Isles about two and one-half months per year and fishes along the shore, collects oysters, conch and shells and engages in bird watching. He is a member of the Gasparilla Island Conservation and Improvement Association, Inc., and he feels that the proposed project would remove some of the recreational aspects of his property and Three Sisters Island. Petitioner Ralph Cole is 71 years old and has been a commercial fisherman in the Charlotte Harbor area since the age of 12. He fishes the Three Sisters Island area every week. He feels that the area is an excellent fishing ground and that the proposed bridge would be in the way of striking a net.
Recommendation Based upon the findings and fact and conclusions of law recited herein, it is RECOMMENDED that the application of Sunset Realty Corporation for a permit be DENIED insofar as it includes the deposition of 10,000 cubic yards of fill in Class II waters. Respectfully submitted and entered this 24th day of February, 1981, in Tallahassee, Florida. DIANE D. TREMOR 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 24th day of February, 1981. COPIES FURNISHED: Joseph W. Landers, Jr. Ausley, McMullen, McGehee, Carothers and Proctor Post Office Box 391 Tallahassee, Florida 32302 Charles G. Batsel Wotitzky, Wotitzky, Johnson, Mandell and Batsel 201 W. Marion Drive Punta Gorda, Florida 33950 Robert M. Rhodes and Terry E. Lewis Messer, Rhodes, Vickers and Hart Post Office Box 1976 Tallahassee, Florida 32302 Lester E. Durst Farr, Farr, Haymans, Moseley and Emrick Post Office Box 635 Punta Gorda, Florida 33950 Victoria Tschinkel, Secretary Department of Environmental Regulation 2600 Blair Stone Road Tallahassee, Florida 32301 H. Ray Allen Department of Environmental Regulation 2600 Blair Stone Road Tallahassee, Florida 32301
