Findings Of Fact Petitioner is the state land planning agency charged with the responsibility to administer the provisions of Chapter 380, Florida Statutes, and the regulations promulgated thereunder. Petitioner has the authority to appeal to the Florida Land and Water Adjudicatory Commission any development order issued in an area of critical state concern. Monroe County is a political subdivision of the State of Florida, and is responsible for issuing development orders for development in Monroe County. Monroe County issued the development order that is the subject of this appeal. Respondent, Bruce Schmitt, is the owner of real property known as Section 15, Township 66, Range 32, Sombrero Beach Road and Tingler Lane - 88 Tingler Lane, Vaca Key Bright, Florida. Most of Monroe County, including the subject property, is within the Florida Keys Area of Critical State Concern, as designated under Sections 380.05 and 380.0552, Florida Statutes. On May 25, 1993, Monroe County issued building permit number 9320003962 to Bruce A. Schmitt, Owner, and Marathon Woodworking, General Contractor, authorizing the construction of a 4 feet X 140 feet wooden dock with a 4 feet x 40 feet terminus. The site of the permitted dock is on an open water shoreline. Running parallel to this shoreline is a channel that is greater than four feet in depth at mean low tide and is greater than twenty feet in width. The permitted dock will terminate at the edge of that channel in an area that is at least four feet deep at mean low tide and more than 20 feet in width. There are no hard coral bottoms found in the area where the dock will terminate. In the vicinity where Mr. Schmitt proposes to construct his dock, there is a channel that is perpendicular to the shoreline that intersects with the channel that is parallel to the shoreline. This perpendicular channel leads out to deep water. The channel providing access to deep water crosses an area of shallow water, which is an area of flats that is referred to by the Department as a shoal. The water depth of this area at mean low tide ranges between 3.0 and 3.5 feet. The channel running parallel to the shoreline and the channel leading out to deep water are not marked. Boats that use this area traditionally have used the channel that is parallel to the shoreline to access the channel in front of Mr. Schmitt's property that leads to deep water. These boats thereafter access deep water by crossing the area of flats that is referred to by the Department as a shoal. While it was established that boats cannot navigate around the shoal, the dimensions of the shoal were not established. Natural shallow water marine communities, such as seagrasses, exist in the waters in the navigation route for boats that will use the permitted dock. Sea grass beds play an important role in water quality maintenance in the Keys through filtration and nutrient uptake and serve as nursery habitats for fisheries. The cumulative impact of the operation of propeller- driven boats in the Keys results in damage and destruction to shallow water marine communities, such as sea grass beds, through prop dredging. There is evidence of considerable prop dredging of the sea grass beds in the shallow waters offshore of the subject property. Boats have been known to run aground in the flats off Mr. Schmitt's property. Any boat using the permitted dock will have to cross shallow waters with seagrass with water depths of less than four feet at mean low tide. Pursuant to the provisions of Sections 380.05 and 380.0552, Florida Statutes, Monroe County has adopted a comprehensive plan which complies with the Principles for Guiding Development found at Section 380.0552(7), Florida Statutes. Section 380.0552(7), Florida Statutes, requires Monroe County land development regulations to comply with certain principles for guiding development, including the following: (b) to protect shoreline and marine resources, including mangroves, coral reef formations, wetlands, fish and wildlife and their habitat. * * * (e) to limit the adverse impacts of development on the quality of water throughout the Florida Keys . . . Monroe County's Comprehensive Plan, which has been approved by the Department and by the Administration Commission, is implemented, in part, through its adopted land development regulations, codified in Chapters 6 and 9.5, Monroe County Code. Section 9.5-345(m) (2), Monroe County Code, provides as follows: (2) All structures on any submerged lands and mangroves shall be designed, located, and con- structed such that: * * * No structure shall be located on submerged land which is vegetated with seagrasses except as is necessary to reach waters at least four (4) feet below mean low levels for docking facilities; No docking facilities shall be developed at any site unless a minimum channel of twenty (20) feet in width where a mean low water depth of at least minus four (4) feet exists. Section 9.5-4(W-1), Monroe County Code, provides as follows: (W-1) "water at least four (4) feet below mean sea level at mean low tide" means locations that will not have a significant adverse impact on off- shore resources of particular importance. For the purposes of this definition, "off-shore resources of particular importance" shall mean hard coral bottoms, habitat of state or federal threatened and endangered species, shallow water areas with natural marine communities with depths at mean low tide of less than four (4) feet, and all designated aquatic preserves under Florida Statutes, Section 258.39 et seq. Section 2.104, Nearshore Waters, Monroe County Comprehensive Plan, Volume II, Future Land Use Element, provides as follows: The Florida Keys are dependent on nearshore water quality for their environmental and economic integrity. The heart of the Florida Keys economy, the means by which Monroe County exists as a civil and social institution, is based on its unique oceanic character. If nearshore water quality is not maintained, then quality of life and the economy of Monroe County will be directly and immediately impacted. OBJECTIVES 1. To protect, maintain, and where appropriate, to improve the quality of nearshore waters in Monroe County. POLICIES 1. To prohibit land use that directly or indirectly degrades nearshore water quality. * * * To prohibit the development of water dependent facilities, including marinas, at locations that would involve significant degradation of the biological character of submerged lands. To limit the locations of water-dependent facilities at locations that will not have a significant adverse impact on off-shore resources of particular importance. For the purposes of this policy, off-shore resources of particular importance shall mean hard coral bottoms, habitat of state or federal threatened or endangered species, shallow water areas with natural marine communities with depths at mean low tide of less than four (4) feet, and all designated aquatic preserves under Florida Statutes, section 258.39 et seq. There are no channel markers to deep water in the area of the permitted dock that have been approved by the Department of Environmental Protection. There was a dispute in the evidence as to whether marking the channel that has served this area as the access route to deep waters would be appropriate and whether such marking would create a navigational hazard. The conflict in the evidence presented is resolved by concluding that the marking of the channel that serves as the navigation access route for boats that will use the permitted dock is appropriate, will aid navigation, and will not create a navigation hazard. This conclusion is reached, in part, because the channel is well defined by its long-term use and connects with the channel that is parallel to the shoreline at a known point.
Recommendation Based on the foregoing Findings of Fact and Conclusions of Law, it is RECOMMENDED that the Florida Land and Water Adjudicatory Commission enter a final order which conditionally denies Building Permit Number 9320003962, but which authorizes Monroe County to issue that permit once the access channel to deep water has been properly marked and approved by the Department of Environmental Protection. DONE AND ENTERED this 25th day of October, 1994, in Tallahassee, Leon County, Florida. CLAUDE B. ARRINGTON 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 25th day of October, 1994.
Findings Of Fact Max and Anne Makowsky (Respondents Makowsky) are the owners of real property located at Lot 5, Block 35, Venetian Shores Subdivision, Plantation Key, in unincorporated Monroe County, Florida. Respondents Makowsky's property is located in the Florida Keys Area of Critical State Concern. On November 20, 1992, Monroe County, Florida (Respondent County) issued a building permit, Building Permit No. 9230008125, to Respondents Makowsky. The permit authorized Respondents Makowsky to construct and place on their property a boat ramp which measures six feet by thirty feet. Petitioner received a copy of the Building Permit from Respondent County on November 24, 1992. Submerged lands adjacent to Respondents Makowsky's property are owned by the State of Florida. The boundary between the State's submerged lands and Respondents Makowsky's property is the mean high water line. Twenty feet of the proposed boat ramp would extend below the mean high water line. The twenty feet would lie over submerged lands. Chapter 9.5, Monroe County Code, contains Respondent County's Land Development Regulations. Section 9.5-345(m) contains the environmental design criteria applicable to submerged lands in Respondent County. Section 9.5-345(m) provides in pertinent part: All structures on any submerged lands and mangroves shall be designed, located and constructed such that: * * * * No structure shall be located on sub- merged land which is vegetated with sea grasses except as is necessary to reach waters at least four (4) feet below mean low level for docking facilities; No docking facility shall be developed at any site unless a minimum channel of twenty (20) feet in width where a mean low water z depth of at least minus four (4) feet exists. In the permit application, Respondents Makowsky provide that the intended use for the ramp is to launch a windsurfer and a small inflatable boat or dinghy. Respondents Makowsky's dinghy has a motor with a shaft which extends two and one-half feet below the boat's water line. As the proposed boat ramp would allow access to the water via watercraft, the term "docking" facility," as used in Section 9.5-345(m), is applicable to Respondents Makowsky's proposed ramp. The submerged land adjacent to Respondents Makowsky's property is very shallow and heavily populated by sea grass, i.e. turtle grass. The turtle grass areas serve as nursery grounds and provide food and shelter for juvenile fish and invertebrates. These habitat values increase when coupled with the mangrove fringe (the roots of mangroves) located along the area. The mangrove roots also provide food and shelter for the juvenile fish and invertebrates. The turtle grass would be adversely impacted by the ramp itself if the proposed ramp was approved and constructed. The structure itself would shade out the needed sunlight to the grasses underneath the boat ramp, causing those grasses to die. Also, the use of the ramp to dock small boats would adversely impact the turtle grass. The bottom of the submerged land is a very loose, calcarious substrate. Launching a boat would cause the sand to "kick up" (lift up). When the sand comes down, it would settle on the turtle grass and smother it because there would be no way for the turtle grass to clean itself. Further, using a motorized boat, as Respondents Makwosky's, would cause "prop dredging" to occur, harming the turtle grass. In "prop dredging," the motor's propeller would destroy the grasses directly by tearing them up or destroy the grasses over a period of time through siltation after churning up the sand from the substrate. The mean low water depth, i. e., the average mean low tide, at the terminal end of the proposed ramp is less than four feet. In the permit application, the depth at the end of the ramp is indicated to be zero feet mean low water. Petitioner estimates the water depth at low tide as between one foot and two feet. The proposed ramp site is not located at a channel of twenty (20) feet in width where a mean low water depth of at least minus four (4) feet exists. Respondents Makowsky have boat access through a boat basin approximately 320 feet to the southwest of their property. The boat basin is located in their Subdivision. A slip in the boat basin is assigned to Respondents Makowsky and they are entitled to use it.
Recommendation Based on the foregoing Findings of Fact and Conclusions of Law, it is recommended that the Florida Land and Water Adjudicatory Commission enter a final order DENYING Monroe County Permit No. 9230008125. RECOMMENDED this 22nd day of December, 1995, in Tallahassee, Leon County, Florida. ERROL H. POWELL, 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 2nd day of December, 1995. APPENDIX TO RECOMMENDED ORDER, CASE NO. 93-1317DRI Petitioner's proposed findings of fact 1 - 13 have been adopted in substance, although not verbatim, in this recommended order. COPIES FURNISHED: Bob Bradley, Secretary Florida Land and Water Adjudicatory Commission Executive Office of The Governor 1601 Capitol Tallahassee, Florida 32399 Gregory C. Smith, Esquire Governor's Legal Office 209 The Capitol Tallahassee, Florida 32399-0001 James F. Murley, Secretary Department of Community Affairs 2740 Centerview Drive Tallahassee, Florida 32399-2100 Dan Stengle General Counsel Department of Community Affairs 2740 Centerview Drive Tallahassee, Florida 32399-2100 Karen Brodeen Assistant General Counsel Department of Community Affairs 2740 Centerview Drive Tallahassee, Florida 32399-2100 Stephanie Gehres Assistant General Counsel Department of Community Affairs Marathon Regional Service Center Suite 212 2796 Overseas Highway Marathon, Florida 33050 Max and Anne Makowsky 1900 Glades Road, Suite 245 Boca Raton, Florida 33431 Carolyn Dekle, Director South Florida Regional Planning Council 3400 Hollywood Boulevard Suite 140 Hollywood, Florida 33021 James T. Hendrick, Esquire Morgan & Hendrick 317 Whitehead Street Key West, Florida 33041-1117 Bob Herman, Director of Growth Management Monroe County Regional Service Center 2798 Overseas Highway Marathon, Florida 33050-2227
The Issue As to Case 92-1751DRI whether Building Permit No. 9110002865 issued by Monroe County, Florida, to Ronald and Patricia LaCroix as owners and Pierce Construction and Builders as contractor for the construction of a dock is contrary to the provisions of Chapter 380, Florida Statutes, the Monroe County Comprehensive Plan and the Monroe County Land Development Regulations. As to Case 92-3949DRI whether Building Permit No. 9110003422 issued by Monroe County, Florida, to David Goodridge as owner and Pierce Construction and Builders as contractor for the construction of a dock is contrary to the provisions of Chapter 380, Florida Statutes, the Monroe County Comprehensive Plan and the Monroe County Land Development Regulations. As to Case 92-5582DRI whether Building Permit No. 9210004503 issued by Monroe County, Florida, to Dick and Jean Madson as owners and Mark W. Milnes Construction as contractor for the construction of a dock is contrary to the provisions of Chapter 380, Florida Statutes, the Monroe County Comprehensive Plan and the Monroe County Land Development Regulations.
Findings Of Fact Petitioner is the state land planning agency charged with the responsibility to administer the provisions of Chapter 380, Florida Statutes, and the regulations promulgated thereunder. Petitioner has the authority to appeal to the Florida Land and Water Adjudicatory Commission any development order issued in an area of critical state concern. Each appeal in this consolidated proceeding was timely and each involved a development within the Florida Keys Area of Critical State Concern as designated under Sections 380.05 and 380.0552, Florida Statutes. Monroe County is a political subdivision of the State of Florida and is responsible for issuing development orders for development in unincorporated Monroe County. Monroe County issued the development orders that are the subject of this appeal. Respondents, Ronald and Patricia LaCroix, are the owners of real property known as Lot 43 Saddlebunch RV Park on Saddlebunch Key in unincorporated Monroe County. On December 12, 1991, Monroe County issued building permit 9110002865 to Mr. and Mrs. LaCroix as owners and to Pierce Construction and Builders as general contractors, to build a boat dock on the subject property and extending beyond the mean high water mark into a man-made canal. At the point that the boat dock would terminate, the canal is more than twenty feet wide and is more than four feet deep at mean low tide. The canal extends throughout the Saddlebunch RV Park. Respondent, David Goodridge is the owner of real property known as Lots 38 and 39 Saddlebunch RV Park on Saddlebunch Key in unincorporated Monroe County. On March 20, 1992, Monroe County issued building permit 9110003422 to Mr. Goodridge as owner and to Pierce Construction and Builders as general contractors, to build a seawall and boat dock on the subject property and extending beyond the mean high water mark into a man-made canal. At the point that the boat dock would terminate, the canal is more than twenty feet wide and is more than four feet deep at mean low tide. The canal extends throughout the Saddlebunch RV Park. Respondents, Dick and Jean Madson are the owners of real property known as Lot 38, Section D, Sugarloaf Shores subdivision, Sugarloaf Key in unincorporated Monroe County. On May 13, 1992, Monroe County issued building permit 9210004503 to Mr. and Mrs. Madson as owners and to Mark W. Milnes Construction as general contractors, to build a dock and davits on the subject property and extending beyond the mean high water mark into a man-made canal. At the point that the boat dock would terminate, the canal is more than twenty feet wide and is more than four feet deep at mean low tide. The canal extends throughout Sugarloaf Shores subdivision. Monroe County's comprehensive plan, which has been approved by the Petitioner and by the Administration Commission, is implemented through its adopted land development regulations, codified in Chapter 9.5, Monroe County Code. Section 9.5-345(m)(2), Monroe County Code, referred to as the four foot rule, provides as follows: (2) All structures on any submerged lands and mangroves shall be designed, located and constructed such that: * * * No structure shall be located on submerged land which is vegetated with sea grasses except as is necessary to reach waters at least four (4) feet below mean low level for docking facilities; No docking facility shall be developed at any site unless a minimum channel of twenty (20) feet in width where a mean low water depth of at least minus four (4) feet exists; Section 2.104, Nearshore Waters, Monroe County Comprehensive Plan, Volume II, Future Land Use Element, provides, in pertinent part, as follows: The Florida Keys are dependent on nearshore water quality for their environmental and economic integrity. The heart of the Florida Keys economy, the means by which Monroe County exists as a civil and social institution, is based on its unique oceanic character. If nearshore water quality is not maintained, then quality of life and the economy of Monroe County will be directly and immediately impacted. OBJECTIVES 1. To protect, maintain and, where appropriate, to improve the quality of nearshore waters in Monroe County. * * * POLICIES 1. To prohibit land use that directly or indirectly degrade nearshore water quality. * * * To prohibit the development of water dependent facilities, including marinas, at locations that would involve significant degradation of the biological character of submerged lands. To limit the location of water-dependent facilities at locations that will not have a significant adverse impact on off-shore resources of particular importance. For the purposes of this policy, off-shore resources of particular importance shall mean hard coral bottoms, habitat of state or federal threatened and endangered species, shallow water areas with natural marine communities with depths at mean low tide of less than four (4) feet, and all designated aquatic preserves under Florida Statutes section 258.39 et seq. Section 9.5-4(W-1), Monroe County Code, provides as follows: (W-1) "Water at least four (4) feet below mean sea level at mean low tide" means locations that will not have a significant adverse impact on off- shore resources of particular importance. For the purposes of this definition, "off-shore resources of particular importance" shall mean hard coral bottoms, habitat of state or federal threatened and endangered species, shallow water areas with natural marine communities with depths at mean low tide of less than four (4) feet, and all designated aquatic preserves under Florida Statutes section 258.39 et seq. Benthic communities exist in the waters between the two canals and deep water, such as rock-hard bottom, sea grasses, algae, and hard coral. Turtles, manatees, sharks, stingrays, eagle rays, snapper, pink shrimp, mullet, and other marine animals populate the Sound. Sea grass beds play an important role in water quality maintenance in the Keys through filtration, nutrient uptake, stabilization of the bottom, and as a habitat for commercially important species. Neither the canal system for Saddlebunch RV Park nor the canal system for Sugarloaf Shores subdivision has access to deep water without crossing areas of water in Sugarloaf Sound with depths of less than four feet at mean low water. Many of these shallow areas contain sea grass beds. The operation of motor driven boats may result in damage to sea grass beds and shallow water marine communities through prop dredging if boats were to attempt to cross these shallow areas. Although there is evidence of prop dredging in parts of these shallow waters, it was not shown that the damage was done by boats traveling from these canal systems and deep water. Whether boats that may be docked at these sites if these permits are granted will cause damage at some future time to some portion of the shallow waters of Sugarloaf Sound between the canal systems and deep water is speculation. Since 1986, Monroe County has adopted an interpretation of Section 9.5-345(m)(2), Monroe County Code, and of Section 2.104, Nearshore Waters, Monroe County Comprehensive Plan, Volume II, Future Land Use Element, that would permit the construction of each of the subject projects. That interpretation permits the development of marginal seawalls, vertical bulkheads and docks in subdivisions that were under development in 1986 if the proposed structure would terminate in a channel more than 20 feet wide with water more than four feet deep at mean low tide. The structures that are the subject of this proceeding meet that permitting criteria. Monroe County's interpretation of the so-called "four foot rule" is that the rule was intended to restrict the development of boating access facilities in new, undeveloped subdivisions and to regulate proposed expansion of existing marinas and the development of new marinas. Monroe County's interpretation of its rules is that the type development at issue in this proceeding, constructed on an individual family home-site, would have minimal effect on the nearshore water environment of critical state concern. Monroe County considers the subject applications to meet all of its permitting criteria. Respondents presented evidence that several similar projects were permitted at approximately the same time as the subject permits were issued without Petitioner filing an appeal. This evidence was insufficient to establish that Petitioner should be estopped to appeal the subject permits, that Petitioner engaged in selective enforcement of its regulatory power, or that Petitioner otherwise brought the subject appeals for an inappropriate purpose.
Recommendation Based on the foregoing findings of fact and conclusions of law, it is recommended that the Florida Land and Water Adjudicatory Commission enter a final order which affirms Monroe County's decision to issue building permit number 9110002865, and which dismisses the appeal filed by the Department of Community Affairs that is at issue in Case 92-1751DRI. It is further recommended that the Florida Land and Water Adjudicatory Commission enter a final order which affirms Monroe County's decision to issue building permit number 9110003422, and which dismisses the appeal filed by the Department of Community Affairs that is at issue in Case No. 92-3949DRI. It is further recommended that the Florida Land and Water Adjudicatory Commission enter a final order which affirms Monroe County's decision to issue building permit number 9210004503, and which dismisses the appeal filed by the Department of Community Affairs that is at issue in Case No. 92-5582DRI. DONE AND ORDERED this 26th day of January, 1993, in Tallahassee, Leon County, Florida. CLAUDE B. ARRINGTON, 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 26th day of January, 1993. APPENDIX TO RECOMMENDED ORDER TO CASE NO. 92-1751DRI, CASE NO. 92-3949DRI, AND CASE NO. 92-5582DRI The following rulings are made on the proposed findings of fact submitted by Petitioner. The proposed findings of fact in paragraphs 1, 2, 3, 4, 5, 6, 8, 10, 11, and 14 are adopted in material part by the Recommended Order. The proposed findings of fact in paragraph 7 are rejected as being unnecessary to the conclusions reached. The proposed findings of fact in the first two sentences of paragraph 9 are adopted in material part by the Recommended Order. The proposed findings of fact in the last sentence of Paragraph 9 are rejected as being unsupported by the evidence. While the evidence established that damage may result, the evidence did not establish that damage would result. The proposed findings of fact in the first sentence of paragraph 12 are rejected as being unsubstantiated by the evidence since the water in the canals is deeper than four feet. The proposed findings in the second sentence of paragraph 12 are subordinate to the findings made. The proposed findings of fact in the last sentence of Paragraph 12 are rejected as being unsupported by the evidence. While the evidence established that damage may result, the evidence did not establish that damage would result. The proposed findings of fact in paragraph 13 are rejected as being subordinate to the findings made. The proposed findings of fact in the first sentence of paragraph 15 are rejected since the evidence established that Monroe County's interpretation of the four foot rule dates to 1986. The proposed findings of fact in the second sentence of paragraph 15 are rejected as being unnecessary to the conclusions reached. The remaining proposed findings of fact in paragraph 15 are adopted in material part by the Recommended Order. The proposed findings of fact in the first sentence of paragraph 16 are subordinate to the findings made. The proposed findings of fact in the second sentence of paragraph 16 are rejected as being argument. The proposed findings of fact in the final sentence of paragraph 17 (there are two paragraphs 16, the second of which is being referred to as paragraph 17) are adopted in material part by the Recommended Order. The remaining proposed findings of fact in paragraph 17 are rejected as being unnecessary to the conclusions reached. The following rulings are made on the proposed findings of fact submitted by Respondents. The proposed findings of fact in paragraphs 1, 2, 3, 4, 5, 6, 7, 8, 9, 10, 11, 16, and 17 are rejected as being the recitation of testimony that is subordinate to the findings made. The proposed findings of fact in paragraph 12 are rejected as being contrary to the record of the proceedings. The proposed findings of fact in paragraph 13 are adopted in material part by the Recommended Order. The proposed findings of fact in paragraph 14 are adopted in part by the Recommended Order are rejected in part as being subordinate to the findings made. The proposed findings of fact in paragraph 15 are rejected as being unnecessary to the conclusions reached. COPIES FURNISHED: Lucky T. Osho, Esquire Department of Community Affairs 2740 Centerview Drive Tallahassee, Florida 32399-2100 Randy Ludacer, Esquire Monroe County Attorney 310 Fleming Street Key West, Florida 33040 James T. Hendrick, Esquire Morgan & Hendrick 317 Whitehead Street Key West, Florida 33040 William R. Kynoch, Deputy Director Florida Land and Water Adjudicatory Commission Executive Office of the Governor 311 Carlton Building Tallahassee, Florida 32301 Carolyn Dekle, Director South Florida Regional Planning Council Suite 140 3400 Hollywood Boulevard Hollywood, Florida 33021 Robert Herman Monroe County Growth Management Division Public Service Building, Wing III 5825 Jr. College Road Stock Island Key West, Florida 33040 Charles M. Milligan, Esquire Post Office Box 1367 Key West, Florida 33041 David and Florence Clark 4606 Wayne Road Corona Del Mar, California 92625 Edward Warren Werling Post Office Box 1042 Summerland Key, Florida 33042 Theodore W. Herzog, Esquire 209 Duval Street Key West, Florida 33040 Pierce Construction & Builders Route 4, Box 319 Summerland Key, Florida 33042 Dick and Jean Madson Post Office Box 276 Summerland Key, Florida 33402 Mark W. Milnes Route 5, Box 775-G Big Pine Key, Florida 33043 David M. Maloney, Esquire Office of the Governor The Capitol, Room 209 Tallahassee, Florida 32399-0001
The Issue The issue to be determined is whether the applicants, William Guererro and Christina Bang, a/k/a Christina Guerrero (Applicants), are entitled to issuance of a Consolidated Environmental Resource Permit and State Lands Approvals for various structures on the Applicants’ property at 58458 Overseas Highway, Marathon, Florida.
Findings Of Fact The Parties Petitioners Bernard Spinrad and Marian Spinrad are the owners of adjoining parcels of property with the addresses of 58418 and 58420 Overseas Highway, Marathon, Florida. They acquired the property in December 2001. They recently completed construction of two residential structures on the properties. The structure at 58418 Overseas Highway is currently listed for sale. The structure at 58420 Overseas Highway is a vacation rental property. Neither structure is Petitioners’ permanent residence. The DEP is the state agency with the power and duty to regulate activities in waters of the state pursuant to chapter 373, Florida Statutes. The DEP also serves as staff to the Board of Trustees of the Internal Improvement Trust Fund (“Board of Trustees”) to review and act on activities on state sovereignty submerged lands under chapter 253. The Applicants, are the owners of adjoining parcels of property with the address of 58478 Overseas Highway, Marathon, Florida (the Property). They purchased the Property in June 2010. The structures that are the subject of the Permit are to be constructed near or waterward of the shoreline of the Property. The Property The Property is located on Grassy Key, an island in the middle Florida Keys, within limits of the city of Marathon, Monroe County, Florida. U.S. Highway 1 passes through Grassy Key. The Property -- as is that of Petitioners -- is situated between U.S. Highway 1 and the open waters of the Atlantic Ocean. In the early part of the 20th century, a portion of Grassy Key was platted as the Crains Subdivision. The properties owned by Applicants and Petitioners are within the Crains Subdivision. During the periods of time directly relevant hereto, the Property has been owned by Burgess Levine, who owned the property during the period prior to the October 2006, landfall of Hurricane Wilma until June 2010, and by Applicants, who have owned the Property since June, 2010. Grassy Key Grassy Key is three-miles long, and has 6800 feet of beaches, none of which are designated as critically eroded. The island fronts the Atlantic Ocean to the east, and the more protected waters of Florida Bay to the west. The waters along the Atlantic Ocean shoreline of Grassy Key in the area at issue are shallow, with an extremely flat bottom having a very gradual slope of approximately 1 to 30, meaning there is a one foot vertical change over 30 horizontal feet. The mean tide range at the Property is about 1.7 feet. Under normal conditions, the stretch of Grassy Key at issue is fairly characterized as a zero-wave energy shoreline. Waves break well offshore and there is negligible wave energy propagating beyond that point. What shoreline energy exists is produced by small tide currents and wind-shear on the water surface that moves water along the shoreline. The direction of the water movement is dependent on tides and wind direction, with the predominant direction being from north to south. Erosive and other significant changes to the shoreline of Grassy Key, including that stretch fronting the Property, are event driven, meaning when there is a coastal storm that causes a rise in the water level, substantially higher than the astronomical tide, waves can propagate onto the shoreline of Grassy Key. The wind and waves can come from virtually any direction depending on the storm. A storm of greater intensity will create higher energy-wave conditions. Although storm conditions may only occur over 1 to 3 percent of a given year, with the rest of the year having zero-wave energy, on average the coastline may be considered to be of moderate-wave energy. The beach sediment along the Grassy Key shoreline in all areas pertinent hereto consists of calcareous material, made up of the breakdown of corals and coralling algae, with a significant fraction of other detrital marine material. The upper beaches of Grassy Key, including that on the Property, generally consist of coarse, calcareous sand with a small fraction of calcareous silt-size particles. The inter-tidal areas along Grassy Key consist of predominantly fine calcareous sand, with a greater fraction of calcareous silt. Extending out into the nearshore area all along Grassy Key, including that fronting the properties owned by Petitioners and Applicants, the sediment becomes a very fine calcareous sand, with a greater fraction of the material being calcareous silts and clays, and with a substantial amount of organic mud of a marine origin, classified as Islamorada muck. Since at least the 1970s, one wading in the nearshore waters along Grassy Key could expect to sink into the surface muck to a depth of anywhere from six inches to two feet. The depth of muck becomes less as one moves further out and approaches the offshore Thalassia beds. Although some areas offer more resistance than others, it is routine to experience difficulty in walking and wading along the coast of Grassy Key because of the high percentage of clays and silts in the substrate. The band of muck narrows as one proceeds towards the northern stretches of Grassy Key, until one reaches the furthest areas to the northeast where the nearshore transitions to exposed rock and hard bottom. The surface muck that exists in the nearshore waters of Grassy Key, having a sizable component of decaying organic material, gives off an odor of hydrogen sulfide when disturbed that some find to be unpleasant. The odor is a naturally- occurring condition of the sediment, and is common in mucky areas all around the southern coasts of Florida. The suggestion that the shoreline in the vicinity of the Petitioners’ property, and that of Applicants, was a naturally occurring white, sandy beach is contrary to the greater weight of the evidence. To the extent the shoreline at Petitioners’ property may have been temporarily altered by the overwash from Hurricane Wilma as discussed herein, Petitioners’ own post-Wilma man-made efforts at beach stabilization, or the redistribution of sediments occasioned by Hurricanes Isaac and Sandy in 2012, the evidence demonstrates the “mucky” condition described herein to be more consistent with the natural and long-standing conditions of Grassy Key. Thus, as Grassy Key exists in the present time, one may expect to encounter six inches to two feet of loose muck anywhere along the nearshore area. Close to shore of Grassy Key are scattered beds of Halodule, a species of seagrass that tends to emerge and grow in shallow waters. The growth of Halodule is influenced by the nature of the sediments, the salinity temperature, and clarity of the water. Storm events have a significant effect on its growth. Given its transient nature, Halodule may vary in any given area from nonexistent, to spotty, to well-established beds. As one moves further offshore, the Halodule transitions to large, continuous beds of Thalassia. Thalassia grows in deeper water, and is common to a depth of about 12 feet. Being deeper and less affected by storm energy, the line of the Thalassia beds off of Grassy Key has not substantially changed over time. As wind and waves come across the grass beds, and as tides ebb and flow, grass blades are cropped. The amount of grass varies seasonally to a degree. The cropped and dislodged seagrasses, along with other organic material entrained therein, are naturally carried by the tides and wind and stranded along the shoreline. The stranded material is known as wrack, and the line of stranded material is known as the wrack line. Grassy Key is well known for the large seagrass wracks that pile up on the shoreline. A wrack line is a normal and natural occurrence in marine environments like that of Grassy Key, and can be a good indicator of the upper edge of the water action at a particular time. The cropping and dislodging of seagrass is accentuated during major or minor storm events. During Hurricane Rita in 2005, a very large seagrass wrack was blown onto the shoreline of Grassy Key. It was subsequently blown back out to sea by the overwash from Hurricane Wilma. The decomposition of the seagrass and other organic materials creates a significant odor that is not uncommon. That odor of decomposing material is well-recognized as being associated with Grassy Key. Areas along the shoreline of Grassy Key have been used by sea turtles for nesting. However, the nature of the substrate in the area of the Property is not optimal for nesting. Generally, sea turtles require a nesting site with 15 to 20 inches of sand above the water table so as to allow them to dig a suitably deep and dry cavity for their eggs. The natural substrate along the section of Grassy Key at issue is coarser and more difficult to dig into, and does not have the depth of sand for the best chance of a successful nest. Despite the nature of the substrate, Petitioner testified as to her observation of turtle nests along her property in each year from 2006 through 2010. Since the SW Groin, the Mid-bulkhead, and the NE Groin were all in existence and functioning during that period, with work to the SW Groin having been completed by 2008, the preponderance of the evidence demonstrates that those structures have no effect on the success or failure of sea turtles to nest along the property. To the extent nesting has been disrupted since 2011, the most logical inference that can be drawn from the evidence is that such disruption is the result of the Mid-Jetty Extension, which is slated for removal under the terms of the Permit. The preponderance of the evidence demonstrates that the structures and activities authorized by the Permit will have no adverse effect on sea turtles. Hurricane Wilma In October, 2005, Grassy Key was pounded by Hurricane Wilma. The storm passed to the north, and created a substantial storm surge that moved from west to east across Grassy Key. The storm surge created a “ridge and runnel” effect on the Atlantic facing shoreline, with the channelization of the storm tide flow creating erosion and gullies on upland shore-adjacent properties. The storm surge and flooding across Grassy Key caused substantial wash-outs of sand; transported a large volume of sandy, upland sediments into the nearshore waters of the Atlantic Ocean; and created washover “fans” of material along the shoreline of Grassy Key. The effects of the Hurricane Wilma storm surge manifested just north of the Property, became substantial at the Property, and continued south down the shoreline for a considerable distance. At the Property, sand was pushed from 50 to 100 feet waterward from the existing shoreline, and a substantial runout was created running parallel and north of the SW Jetty. The sand pushed into the water buried everything in its path, including seagrasses. In short, the post-Wilma shoreline from the Property south along Grassy Key was left in a completely disrupted state. The nearshore waters fronting the properties owned by Petitioners and Applicants were affected by the deposition of sandy, upland sediments, which temporarily created areas of substantially harder-packed sediment. Over time, as the shoreline equilibrated and the sandy sediment distributed through a broader area, more typical shoreline conditions returned. The photographic evidence demonstrates that the Mid- bulkhead and the SW jetty structures were impacted by the Hurricane Wilma storm surge. In addition, the sandy area between the mid-bulkhead and the SW jetty was pushed seaward from its previous location. The scars from Hurricane Wilma remain evident through the most recent aerial photographs received in evidence. It is visually apparent that seagrass, though reappearing in patches, has not reestablished in the nearshore areas along the affected shoreline of Grassy Key -- including the areas in front of the Property and the property owned by Petitioners -- to the extent that it existed prior to the storm. Post-Wilma Activities When Hurricane Wilma hit, the Property was owned by Burgess Lea Levine. Not long after Hurricane Wilma, Ms. Levine shored up the SW Jetty, and performed work in the “beach” area between the mid-bulkhead and the SW jetty. The photographic evidence also supports a finding that the rock outline of the Mid-jetty was reestablished to its pre-Wilma configuration. The repairs to the SW Jetty resulted in a structure that is virtually indistinguishable in size and shape to the SW Jetty as it presently exists. The wrack line at the beach area after it was “worked” following the passage of Wilma, shows the area in which work was done to be generally consistent with -- though slightly seaward of -- the 2005 post-Wilma shoreline. In 2008, Ms. Levine applied for a series of exemptions and for consent of use for state-owned lands for “shoreline repair, replace earthen ramp with a concrete ramp, repair wood deck, replace mooring piles & maintenance dredge existing channel w/in Atlantic Ocean.” On September 19, 2008, the DEP issued a regulatory authorization and proprietary submerged land approval. The Rights of Affected Parties that accompanied the September 19, 2008, notice provided that “[t]his letter acknowledges that the proposed activity is exempt from ERP permitting requirements” and that “this determination shall expire after one year.” The notice of Rights of Affected Parties did not apply to the proprietary authorization. At some time after issuance of the regulatory authorization, Ms. Burgess initiated additional work to repair the SW Jetty. The photographic evidence, which is persuasive, indicates that the work on the SW Jetty, including the concrete cap, was complete by the end of 2008. When Applicants purchased the Property, the determination of exemption issued in 2008 had, by application of the notice of Rights of Affected Parties, expired. Shortly after the Applicants purchased the property, they had the existing family home demolished. Applicants intend to construct a winter vacation home for their personal use on the property. 2012 Storms In August and October 2012, Grassy Key was subject to event-driven conditions as a result of the passage of Hurricanes Isaac and Sandy. Those storms redistributed large areas of sediments that had been moved offshore by the effects of Hurricane Wilma. The Proposed Permit The February 20, 2013, Permit provides that the structures described herein do not require the issuance of an Environmental Resource Permit, subject to the criteria and conditions in Florida Administrative Code Rule 40E-4.051. The Permit provides that the boat ramp is eligible to use the general permit in Florida Administrative Code Rule 62-330.417, the repair and replacement of the dock is exempt pursuant to section 403.813(1)(b), Florida Statutes, the maintenance dredging of the Channel is exempt pursuant to section 403.813(1)(f), and that the repair and replacement of the NW Jetty, the SW Jetty, and the Mid-bulkhead are exempt because the structures are “historic in nature and pre-dates Department regulations.” In addition to the regulatory authorizations, the Permit granted proprietary authorization by Letter of Consent for the dock pursuant to Florida Administrative Code Rule 18- 21.005(1)(c)4., and for the Channel, the NW Jetty, the SW Jetty, and the Mid-bulkhead pursuant to rule 18-21.005(1)(c)7. The Permit established the mean high-water line as that existing in 1974 and depicted on the “Richmond Survey.” Proprietary authorization for the boat ramp was determined to be unnecessary due to its location above the mean high-water line. Finally, proprietary authorization for the “Sandy Area” or beach between the Mid-bulkhead and SW Jetty was granted by Letter of Consent pursuant to rule 18-21.005(1). On September 20, 2013, the DEP filed a Notice of Additional Grounds for Exemption Determination, in which it found each of the structures subject to the regulatory review to “have only minimal or insignificant individual or cumulative adverse impacts on water resources” and to thus be exempt from the need to obtain an Environmental Resource Permit pursuant to section 373.406(6), Florida Statutes. On December 12, 2013, Applicants filed a Notice of Filing Proposed Changes to the Pending Agency Action in which they agreed to certain additional conditions, and which referenced the October 1, 2013, repeal of rule 40E-4.051, and its replacement by the “Statewide ERP rules.” For purposes of this de novo proceeding, the proposed Permit at issue includes the February 20, 2013, Permit; the September 20, 2013, Notice of Additional Grounds for Exemption Determination; and the December 12, 2013, Notice of Filing Proposed Changes to the Pending Agency Action. The Proposed Structures Groins There has been some confusion relating to the names of the structures that are subject to the proposed Permit. Two of the structures are referred to as jetties, the NE Jetty and the SW Jetty, and the middle structure is referred to as the Mid- bulkhead. A jetty is a navigation structure that is constructed at a barrier inlet. Its purpose is to stabilize the inlet and prevent shoaling by “jetting” current and wave-driven sand further offshore, such that the offshore bar is moved into deep enough water to allow navigation in and out of the tidal inlet, and allowing the tidal current between the ocean and the receiving body of water to keep the inlet scoured and open. There are 48 jetties on the open coast of Florida, none of which are in the Florida Keys. A groin is a structure designed for shore protection purposes. A groin is typically aligned perpendicular to the shoreline, or “shore normal.” The structures identified in the Permit as the NE Jetty and the SW Jetty are clearly groins, and not jetties. The mid-bulkhead is a groin, generally for shore confinement, with a channel-facing bulkhead. For purposes of continuity, the structures will be identified by the names given them in the Permit. Since there is negligible wave energy along the shoreline normal conditions, the groins have little or no day- to-day effect on longshore transport. Under storm conditions, the structures affect longshore transport, as evidenced by accretional “fillets,” and function as shoreline protection and confinement structures. The rock groins provide shelter, habitat and structure for corals, sponges, lobster, and fish in the area. The preponderance of the evidence demonstrates that the groins authorized by the Permit will have no adverse effect on fish and wildlife resources. NE Jetty The NE Jetty was originally constructed in the early 1960s, likely concurrent with the dredging of the navigational channel. The quality of the aerial photographs of the period make it difficult to tell if the NE Jetty was a loosely-placed rock embankment or a more well-designed and constructed structure. However, the fillet of sand accreted to the north of the Channel demonstrates that the jetty was in existence and functioning as a shore-protection structure. By the 1970s, the NE Jetty had become overwhelmed by longshore sediment transport from the northeast. Sediment overtopped the NE Jetty and filled in the landward reaches of the Channel. At that point, ability of the NE Jetty to perform as a shore protection structure was compromised to the point that it could no longer hold the shoreline out of the basin or the landward portion of the Channel. The Mid-bulkhead became the dominant structural control over the shoreline and started to accrete the shoreline to the northeast. At some time between 1977 and 1981, the Channel was maintenance dredged pursuant to a permit issued by the Department of Environmental Regulation, DEP’s predecessor agency. The NE Jetty appeared on the plans for the maintenance dredging. Thus, the most reasonable inference that can be drawn from the evidence is that the NE Jetty was repaired and restored in conjunction with the approved maintenance dredging. By 1981, the NE Jetty had been restored as the dominant shore protection structure north of the Channel, and a fillet of accreted material had been reestablished. The aerial photographs from that period are not sufficiently distinct to determine the precise size, shape, and configuration of the NE Jetty at that time. However, there is no evidence of additional work having been performed on the NE Jetty between 1981 and 1985. By 1985, the NE Jetty existed in substantially the size, shape, and configuration as it existed at the time of Hurricane Wilma. Between 1981 and the 2005 arrival of Hurricane Wilma, the evidence is convincing that the NE Jetty was holding up the shoreline to the northeast and preventing sediment from filling in the upper reaches of the Channel. Although the evidence suggests that the NE Jetty had, by 2005, begun to show its age, the continuous presence of an accretional fillet demonstrates that it continued to serve its function as a shore-protection structure. Although the NE Jetty suffered damage from Hurricane Wilma, it continued to perform its shoreline protection function. Aerial photographs taken in 2009 and 2011 show a relatively distinct structure with a well-defined accretional fillet. Thus, the greater weight of the evidence demonstrates that, at the time of its repair in May 2011, the NE Jetty was a functional groin. The NE Jetty, as repaired in 2011, is of substantially the same size, shape, and location as the structure depicted in aerial photographs taken in 1985, 2009, and early 2011. Although the elevation of the structure was increased over its pre-repair elevation, the increase was that reasonably necessary to prevent the function of the structure from being compromised by the effects of age and weather. The work performed on the NE Jetty, consisting of new rock laid on top of the existing rock, constituted repair and maintenance of the existing structure. Since 2005, and at the present time, the shoreline north of the NE Jetty has reached a state of equilibrium and stability, and is not expected to change significantly from its current condition. The preponderance of the competent, substantial evidence demonstrates that the effect of the NE Jetty on the shoreline and water resources of Grassy Key in the vicinity of the properties owned by Applicants and Petitioners is minimal and insignificant. The sand and sediment accreted to the north of the NE Jetty since 1981 is in the range of 250 square feet. SW Jetty The aerial photographs from 19647/ demonstrate that some form of structure then existed at the location of the current SW Jetty. The structure is indistinct due to what appears to be sidecast material from a small channel in front of the property to the immediate south of the Property. By 1971, the SW Jetty had become more distinct. From that time forward, the SW Jetty, and its accompanying fillet of accreted material, appears in roughly the size and shape of the structure as it appeared immediately prior to the arrival of Hurricane Wilma. The SW Jetty was heavily impacted by Hurricane Wilma. The overwash from the storm created a substantial runout alongside the SW Jetty, and the post-storm aerials suggest that the jetty boulders were undermined and shifted from their more uniform 2003 appearance. Immediately after Hurricane Wilma, the owner of the Property commenced restoration and repair activities. As part of the activities, the SW Jetty was repaired with the addition of boulders, which were often three feet and every now and then as much as four feet across. The boulders, being irregularly shaped, could not be stacked like Legos®, so the repairs were not neatly within the precise pre-Wilma footprint. However, the repaired SW Jetty was substantially in the length and location as existed prior to Hurricane Wilma, though it may have had a slightly wider cross-section. By 2007, the work on the SW Jetty was complete, and it had assumed its present appearance with the addition of a concrete cap. Its appearance -- i.e. length, width, and location -- in 2007 and 2008 was not dissimilar from its appearance in 2003. As repaired, the SW Jetty effectively constitutes the same structure that it has been since its initial construction. From a coastal engineering perspective, the work that was performed on the SW Jetty, consisting generally of new rock laid on top of the existing rock, constituted repair and maintenance of the existing structure. Dr. Lin testified that between 1974 and 2011, the area to the southwest of the southwest jetty was “about equalized,” though it was “accreting a little bit.” Thus, the effect of the SW Jetty on the shoreline of Grassy Key in the vicinity of the properties owned by Applicants and Petitioners from 1974 to 2011 was minimal and insignificant. Dr. Lin testified that, since 2011, the same area had eroded. The only substantive shoreline change that logically accounts for that subsequent erosion is the Mid-bulkhead extension, which is slated for removal under the terms of the proposed Permit. Petitioner testified that she observed no adverse effects from activities on the Property until after February 2011.8/ Since work on the SW Jetty was complete by no later than 2008, Petitioner’s testimony supports a finding that the SW Jetty has had no measurable effect on the water resources in the vicinity of the properties owned by Applicants and Petitioners. The preponderance of the competent, substantial evidence demonstrates that the effect of the SW Jetty on the shoreline and water resources of Grassy Key in the vicinity of the properties owned by Applicants and Petitioners is minimal and insignificant. Mid-bulkhead The structure of the Mid-bulkhead first appeared as part of the sidecast material from the excavation of the navigation channel in 1964. It coalesced into a defined but smaller and more rudimentary structure in the 1971-1972 time period. At that time, it was acting as the predominant shore protection structure due to the overtopping of the NE Jetty with sediment, which also filled in the landward reaches of the Channel. By 1981, after the maintenance dredging of the Channel, the Mid-bulkhead had assumed substantially the size, shape, and location that it has currently. The Mid-bulkhead has a navigation function of protecting the landward extent of the Channel from the collapse of adjacent sand and sediment, and a shore protection and compartmentalization function. Those functions have been consistent since 1981. The Mid-bulkhead appears to have been subjected to the overwash of sand and sediment from Hurricane Wilma, though it maintained its shape and form. The outline of the Mid-bulkhead appears to be more well-defined after the initial post-Wilma repairs. In any event, the configuration and size of the Mid-bulkhead is substantially the same as it had been since 1981. At some point, the interior section of the Mid- bulkhead was topped with soil that is inconsistent with that naturally occurring in the area. That fill was confined, and brought the Mid-bulkhead to a more even grade with the rock outline, but could have had no measurable effect on the shoreline and water resources of Grassy Key in the vicinity of the properties owned by Applicants and Petitioners. The preponderance of the competent, substantial evidence demonstrates that the effect of the Mid-bulkhead is minimal and insignificant. Channel In 1961, the Department of the Army authorized dredging of a navigation channel at the Property. The approved channel was to be 700 feet long, 30 feet wide, and to a depth of five feet below mean low water. The Florida Trustees of the Internal Improvement Fund issued a letter of no objection. By 1964, the Channel that is the subject of this proceeding had been dredged, though not to the 700-foot length approved. Rather, the Channel was dredged to a length of approximately 290 feet. Much, if not all of the dredge spoil was sidecast, creating a rock structure alongside the Channel. Measurements taken during the course of this proceeding demonstrate that the initial dredging resulted in near vertical side slopes, which shows that the bailing of the bedrock was accomplished to the limits. The width of the Channel is from 28 feet to 32 feet wide, which is within an acceptable tolerance of the 30-foot approved width. In 1976, the then-owner of the Property sought a permit from the DEP’s predecessor, the Department of Environmental Regulation, to maintenance dredge the Channel to a dimension of 290 feet long and 30 feet wide, to a depth of minus 8-feet mean high water, and to construct a new rock jetty to extend 230 feet waterward from the existing terminus of the NE Jetty. Given the mean tide range of 1.7 feet at the Property, the depth of the proposed dredging would have been minus 6.3 feet mean low water, or 1.3 feet deeper than originally approved. The permit drawings depict the existing NE Jetty, the Channel boundary, the outline of the Mid-bulkhead, and the sidecast rock structure alongside the southern side of the Channel. The permit was denied. In 1977, the owner of the property reapplied for a permit to maintenance dredge the Channel to a dimension of 290 feet long and 30 feet wide, and to a depth of minus 4.0 feet below mean low water nearshore to minus 6 feet below mean low water at the waterward end. The proposal to construct an extension of the NE Jetty was deleted. The permit was issued, and a severance fee for the dredged material was paid based on a projected 700 cubic yards of material removed. The permit drawings and photographs depict the existing NE Jetty, the nearshore Channel boundary, and the general outline of the Mid- bulkhead. By 1981, aerial photographs demonstrate that the maintenance dredging of the Channel was complete, the NE Jetty was in place and functioning to protect the shoreline as evidenced by the accretional fillet, and the Mid-bulkhead had assumed its approximate current shape and configuration. Although the Channel has varied in depth over the years since the maintenance dredging and Hurricane Wilma, the greater weight of the evidence, including photographic evidence, indicates that the Channel was well-defined and remained navigable during that period. The Channel is an open-water exposed channel. Water in the Channel mixes due to direct tidal flow and the sheet flow of water due to shear wind stress. As water passes over the Channel, it sets up gyre, which is a mixing process. The open- water exposed Channel is subject to a high degree of mixing, even on normal waveless conditions, because of the wind transport of water and the tidal transport of water. The Channel is not a semi-enclosed basin. A semi- enclosed basin does not receive the direct forcing functions that an open-water channel receives. A semi-enclosed basin has no direct connection to open waters, but is connected to open waters by a narrower opening. Although a semi-enclosed basin exchanges water via every tidal cycle, the flushing process is one of slow mixing, in which a little bit of water is added to and withdrawn from the larger basin through the narrow opening during each tidal cycle. In such a case, a flushing analysis may be necessary to determine how much time and how many tidal cycles it may take to effect a complete exchange of the water in the semi-enclosed basin, and thus, for example, to dilute a pollutant to an acceptable level. A flushing analysis is not needed in this case because the Channel is an open-water, openly-exposed location subject to a high degree of mixing under normal day-to-day tidal processes. There is no greater basin connected by a restricting connection as with a semi-enclosed basin. Rather, the Channel has direct exposure to the tides, along with wind shear stress moving the water. The evidence in this case is substantial and persuasive, because the Channel is highly exposed to the open water and the tides, and a well-mixed and well-flushed aquatic system, that a flushing analysis is neither required nor necessary. Dock The dock made its first obvious appearance in 1981. It appears in a consistent shape and appearance through 2011. Aerial photographs taken in 2012, after the maintenance dredging of the Channel was conducted, show the dock had been removed. At the time of the hearing, the Applicants had installed new pilings and vent boards for the replacement dock, but the decking had not been installed. Work to complete the replacement of the dock was halted due to the pendency of the litigation challenging the structures. The proposed dock is less than 500 square feet. It is proposed for non-commercial, recreational activities. It is the sole dock proposed on the Property. The proposed dock will not impede the flow of water or create a navigational hazard. Boat Ramp Since the issuance of the 2008 approval, the boat ramp site was graded and stabilized in limerock material. The concrete ramp was not completed due to the pendency of the litigation challenging the structures. However, Applicants propose to pave the ramp with concrete. Based on Mr. Clark’s observations during his site visits, the boat ramp is landward of the mean high waterline depicted on the survey. The preponderance of the evidence demonstrates that the proposed boat ramp will provide access to the Channel, which provides a minimum navigational access of two feet below mean low water to the ramp. Applicants have agreed to install depth indicators at the ramp to identify the controlling depths of the navigational access. The work on the ramp involves no seagrass beds or coral communities. The ramp as proposed will require no more than 100 cubic yards of dredging. The total width of the ramp is to be 20 feet and the ramp surface will be no wider than 12 feet. Beach Area The area between the SW Jetty and the Mid-bulkhead is an accreted beach-type area that has been confined and protected by the Mid-bulkhead and the SW Jetty. The shoreline landward of the mean high water line, from the dry beach and to the upland, is somewhat steeper than adjacent unprotected shorelines, which is indicative of the grooming of the upper beach sediment and the stability of the shoreline between the Mid-bulkhead and the SW Jetty. As a result of the Hurricane Wilma storm surge, a substantial amount of sediment was swept across the Property and into the Atlantic waters. The beach area was inundated with sand and sediment from the overwash, which appears to have moved the shoreline well waterward of its previous position. Along the northern side of the SW Jetty, a substantial channelized gully was created. The configuration of the shoreline post-Wilma suggests that efforts were made by the then-owner of the Property to fill in the gully on the northern side of the SW Jetty, and to groom and restore the shoreline by redistributing sand and sediment on the Property. It is typical, and allowable under DEP emergency final orders, for affected property owners to redistribute overwashed deposits and place them back within the beach system. In that regard, the DEP encourages the redistribution of clean beach sand back onto the beach. The then-owners of the Property were not alone in taking steps to address the effects of Hurricane Wilma on their adjacent shorelines. The photographic evidence demonstrates that Petitioners engaged in similar restorative activities, which included bringing in material purchased from a contractor to fill in a gully created on their property by the overwash. Observation of representative soil samples from the beach area demonstrate that the soils are consistent with those in the upper beach areas found throughout the area. The only areas of inconsistent soils were found in the interior of the rock structure of the Mid-bulkhead, which contained a four to six-inch layer of soil with a different consistency and darker brown color, and small area of similar soil directly adjacent thereto and well above the mean high water line. The greater weight of the competent, substantial, and credible evidence demonstrates that there was no substantial amount of “fill” from off-site placed on or adjacent to the beach area. Rather, the nature, appearance, and composition of the soils suggests that the temporary increase in the size of the beach area after Hurricane Wilma was the result of grooming and redistribution of sand and sediment pushed onto the Property and into the nearshore waters by the Hurricane Wilma storm surge. In the years since Hurricane Wilma, the influence of normal tidal and weather-driven events has returned the beach area between the mid-bulkhead and the SW jetty to roughly the configuration that existed prior to the passage of Wilma, though it remains somewhat waterward of its pre-Wilma location.
Recommendation Based on the foregoing Findings of Fact and Conclusions of Law set forth herein it is RECOMMENDED that the Department of Environmental Protection enter a final order approving the February 20, 2013, proposed Permit, as conditioned by Applicants’ December 12, 2013, Proposed Changes to the Pending Agency Action. DONE AND ENTERED this 25th day of July, 2014, in Tallahassee, Leon County, Florida. S E. GARY EARLY Administrative Law Judge Division of Administrative Hearings The DeSoto Building 1230 Apalachee Parkway Tallahassee, Florida 32399-3060 (850) 488-9675 Fax Filing (850) 921-6847 www.doah.state.fl.us Filed with the Clerk of the Division of Administrative Hearings this 25th day of July, 2014.
Recommendation Based upon the findings of fact and conclusions of law recited herein, it is RECOMMENDED that petitioner's application for consent of use of sovereignty submerged land for a 9,180 square foot docking facility in Lake Worth be DENIED. Respectfully submitted and entered this 31st day of August, 1983 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 31st day of August, 1983. COPIES FURNISHED: Robert A. Routa, Esquire Roberts, Egan & Routa, P.A. Post Office Box 1386 Tallahassee, Florida 32302 John W. Williams, Esquire Department of Natural Resources 3900 Commonwealth Boulevard Tallahassee, Florida 32303 Dr. Elton J. Gissendanner, Executive Director Department of Natural Resources 3900 Commonwealth Boulevard Tallahassee, Florida 32303
The Issue Whether or not Petitioner is entitled to a dredge and fill permit to construct a dock and seawall by provision of reasonable assurances that the project is in the public interest.
Findings Of Fact On May 8, 1989, the Petitioner, Kathryn Haughney, applied to DER for a permit to construct a dock and seawall on the shore of the Halifax River in Volusia County. The portion of the Haughney property where the dock and seawall would be constructed is separated from the Haughney home by John Anderson Drive, which parallels the river's edge and is separated from the river by a ribbon of undeveloped property at that location and to the south. A house is located at water's edge on the lot to the north of the proposed construction site. The Haughney home itself is set well back from John Anderson drive on the side of the street away from the river. The Halifax River is classified as a Class III water body under DER rules. The particular part of the Halifax River where the Haughney property is located and where the dock and seawall are proposed is also within the Tomoka Marsh Aquatic Preserve, which is an Outstanding Florida Water under DER rules. The dock as proposed by Petitioner will be 320 square feet. DER denied the permit application on July 19, 1990, but in so doing did not deny the application on the basis of the proposed dock, which, because of its dimensions, is exempt from DER permitting requirements. The seawall as proposed is to be 137 feet long. Petitioner applied to extend it 16 feet out into waters of the state at the northern end, gradually increasing to 34 feet into waters of the state at the south end. Additionally, 5 feet of riprap would also extend out into waters of the state along the seawall's entire length. The waters of the state that would be filled by the proposed seawall contain lush wetland vegetation that provides habitat for a number of macroinvertebrate species which are part of the food chain feeding fish and wading birds such as egrets and herons. Fiddler crabs and colonies of mussels have been observed on the site. The area to be filled provides a valuable habitat for fish and wildlife. There was no mitigation offered by Petitioner to make up for the loss of habitat to be occasioned by the proposed construction. Although Petitioner asserted DER had named no "endangered species" and that the Environmental Protection Administration had not designated this area as "endangered," those federal concerns were not at issue. If such federally designated species or location designation existed in the locale, it might militate against granting this application for permit, but in the negative, it is irrelevant. A vertical seawall exists immediately north of Petitioner's shoreline. The shoreline to the south remains undeveloped. (See Finding of Fact 2). Construction of seawalls, especially those that extend out from the existing shoreline, typically causes erosion on adjacent shorelines, and additional seawalls exaggerate wave energy and can have a cumulative erosive effect. The foregoing fact is found in reliance upon the testimony of Don Medellin, an Environmental Specialist II for DER, and Barbara Bess, an Environmental Manager for DER, both accepted as experts in environmental aspects of dredge and fill permits. The assertion that actual erosion on the property to the south has already occurred was contained in a letter from Petitioner's southern neighbor (DER Exhibit 6). Petitioner's representatives objected to consideration of this exhibit as "hearsay." They are correct and current erosion to the south is not found as a fact. Nonetheless, actual erosion in a pocket on the north end of Petitioner's shoreline has been shown by the direct testimony of Emmett and Martha Haughney, who assert that their property is eroding due to the existing seawall and that Petitioner wants a permit for a seawall to alleviate this erosion. Their evidence is confirmed by the personal observations and testimony of Mr. Medellin and Ms. Bess. Further, upon their testimony, it is accepted that this minimal pocket of erosion is most likely due to the existing seawall to the north and that if the Petitioner builds a seawall to the specifications now set out in the permit application, there is potential for similar and perhaps cumulative erosion to the shoreline to the south of Petitioner's lot. Neither the city nor county involved has land use restrictions which would prohibit Petitioner's proposed seawall except that Volusia County advocates riprap requirements if this permit application were granted. In its Notice of Permit Denial, DER advised Petitioner as follows: The Department has determined that the follow- ing changes to the project may make the project permittable: The vertical seawall should be eliminated and replaced with coquina rock riprap revet- ment. The riprap should be located further landward and conform to the slope of the existing embankment. Backfilling on the north property line is acceptable provided the fill area does not extend more than 10 feet westward in the most eroded area. Accordingly, the riprap could extend to the adjacent seawall and gradually extend in a more landward direc- tion to prevent excessive elimination of the littoral zone vegetation. Whatever alternative the applicant elects to choose, the removal or elimination of littoral zone vegetation must be offset in the form of mitigation if the impacts can not be reduced any further. Finally, the agent should eliminate the use of generic drawings which must be continually revised. All drawings should reflect the existing and proposed conditions and the impacts associated with the project. Petitioner's contractor, Andy Harris, testified to other alternatives that could be used by Petitioner in constructing her seawall, but the evidence of Mr. Medellin and Ms. Bess is persuasive that the alternative measures proposed by Mr. Harris would not provide the reasonable assurances the law requires DER to obtain from Petitioner.
Recommendation Upon the foregoing Findings of Fact and Conclusions of Law, it is RECOMMENDED that the Department of Environmental Regulation enter a Final Order affirming its July 19, 1990 Notice of Permit Denial. RECOMMENDED this 25th day of April, 1991, at Tallahassee, Florida. ELLA JANE P. DAVIS, Hearing Officer Division of Administrative Hearings The DeSoto Building 1230 Apalachee Parkway Tallahassee, Florida 32399-1550 (904) 488-9675 Filed with the Clerk of the Division of Administrative Hearings this 25th day of April, 1991. APPENDIX TO RECOMMENDED ORDER, CASE NO. 90-7215 The following constitute specific rulings pursuant to Section 120.59(2) F.S. upon the parties' respective proposed findings of fact (PFOF): Petitioner's letter to Hearing Officer (filed March 22, 1991) The first paragraph complains that a VCR was unavailable in the hearing room so that Petitioner's videotape could not be shown. Petitioner should have made arrangements for showing the tape and did not. Likewise, Petitioner never offered the tape in evidence (for viewing by the Hearing Officer afterwards in preparation of this Recommended Order). Therefore, it very properly was not considered. The next 3 paragraphs refer to the Casden letter (DER Exhibit 6), which is covered in FOF 8-9. The remaining paragraphs are rhetoric and legal argument upon which no ruling need to made under Section 120.59(2) F.S.; however, they are alluded to in the Conclusions of Law. Petitioner's letter to DER Counsel (filed March 25, 1991 by DER, suggesting it was Petitioner's proposed findings of fact) 1-3 For the reasons set out above, the Petitioner's videotape was not considered. The subject of erosion to the degree proved at the hearing is covered in the Recommended Order. 4-5, PS 1-3 Mere rhetoric and legal argument upon which no ruling need be made under Section 120.59(2) F.S.; covered in the Conclusions of Law to the degree appropriate. Respondent's PFOF: 1-11 Accepted as modified to reflect the greater weight of the credible and probative record evidence as a whole. That which is rejected is rejected as not proven or not persuasive. Unnecessary or irrelevant material has likewise been excluded. COPIES FURNISHED: Douglas MacLaughlin Assistant General Counsel Department of Environmental Regulation 2600 Blair Stone Road Tallahassee, Florida 32399-2400 Kathryn Haughney 2301 John Anderson Drive Ormond Beach, FL 32074 Emmett and Martha Haughney 2301 John Anderson Drive Ormond Beach, FL 32074 Carol Browner, Secretary Department of Environmental Regulation 2600 Blair Stone Road Tallahassee, FL 32399-2400 Daniel H. Thompson, General Counsel Department of Environmental Regulation 2600 Blair Stone Road Tallahassee, FL 32399-2400
The Issue The basic issue in Case No. 90-2403 is whether the application of the Petitioner, Ian G. Koblick, for a lease of sovereign submerged lands and an easement for an appurtenant previously filled area should be granted or denied. The Board of Trustees of the Internal Improvement Trust Fund propose to deny the application. The Intervenor, Izaak Walton League, opposes the application and supports the proposed denial. The basic issue in Case No. 91-0258 is whether certain action proposed by the Board of Trustees of the Internal Improvement Trust Fund regarding filled areas in John Pennekamp Coral Reef State Park affects the substantial interests of the Petitioner, Marine Resources Development Foundation.
Findings Of Fact Petitioner Ian G. Koblick is the record title holder of certain real property in Key Largo, Monroe County, Florida, located at 51 Shoreland Drive, where he owns and operates a for profit corporation known as "Koblick Marine Center" and a nonprofit corporation known as "Marine Resources Development Foundation." (MRDF) Petitioner purchased the property in the spring of 1985. Petitioner Koblick's attorney contacted the Division of State Lands on behalf of Petitioner for a sovereignty submerged land lease for two docks and an easement for an appurtenant filled area, the subject of DNR lease file #44001275, in the fall of 1984. As part of the application process, Petitioner's attorney submitted to Respondent's staff a survey of the proposed submerged lands lease area, which contained water depth information. The fill parcels known as "F-7" and "F-8," which are the subjects of the second petition, are not owned by either of the Petitioners. Petitioner has no deeds or conveyances to the lands in the proposed lease and easement area. Petitioner has been using the lands in the proposed lease and easement area continuously since 1985, without consent from the Respondents. At no time has there been any written assurance made by Respondent or its staff that a lease would be issued to Petitioner. The lands within the proposed lease and easement area lie within the boundaries of John Pennekamp Coral Reef State Park. On September 21, 1967, the Respondent Board of Trustees dedicated certain sovereignty submerged lands to the Florida Board of Parks and Historical Memorials. The effect of this dedication was to extend the boundaries of John Pennekamp Coral Reef State Park to the shoreline. The Florida Park Service, part of the Division of Recreation and Parks in the Department of Natural Resources, has continuously managed the Park since then. The Respondent Board of Trustees has not conveyed, alienated, or modified its interest in the lands within the proposed lease and easement area, except for one submerged land lease, #44-39-0784-5E, to Tahiti Village (a predecessor in interest to Petitioner) for a period of five years from August 1, 1978, through July 31, 1983. That lease was for a much smaller parcel of land than Petitioner's proposed lease area and was never renewed. When Petitioner Koblick purchased his property, the two docks and the filled parcel, "F-9", in the proposed lease easement area were already in place. The then existing docks were not those previously consented to by Respondent. After he purchased the property, Petitioner constructed catwalks on the docks and upgraded the electrical system on the fill area without permission from either the Board of Trustees or the Division of Recreation and Parks. Petitioner Koblick is not in possession of any permits giving consent to fill the filled area "F-9" in the proposed lease and easement area. The fill material at filled area "F-9" was placed there between 1964 and 1969, without the consent of the Respondents. Filled area "F-9" has riprap all along its outer edge and tip. This riprap area is currently habitat for a variety of marine plants and animals. Removal of all of the fill material at "F-9" would, of course, destroy that habitat and leave a barren area that might take many years to revegetate. A benthic community eventually would be created in the area from which the fill was removed. Filled area "F-9" also provides protection to the existing shoreline, which includes a seawall, and to a basin that is landward of "F-9." Removal of all of the fill material at "F-9" would reduce the protection to the shoreline and expose the seawall and other shore structures to erosion. Removal of the fill material at "F-9" down to the mean high waterline would not have any demonstrated environmental benefits, but would be a hazard to navigation because at high tide the remaining fill would be difficult to see. The majority of boats docked in the 18 slips in the proposed lease area pay slip rent to Koblick Marine Center. Only three MRDF boats are docked at the docks. A charter boat business, which leases out boats to the public, is also operated at the docks on the proposed lease area. The Intervenor, Izaak Walton League, Mangrove Chapter, is a not for profit Florida corporation which has as its purpose the protection of the state's soil, water, woods, and wildlife. A substantial number of Intervenor's members live near Pennekamp Park and use the park for recreational and educational purposes. Any activity which detracts from, or has a potential for detracting from, the purposes to which the Pennekamp Park is dedicated also detracts from or has a potential for detracting from the recreational and educational interests of the Intervenor's members who live near and use the park. Largo Sound is a manatee habitat. Manatees have been sighted in or near the proposed lease area. Activities in the proposed lease area, which include the discharge of pollutants and boat traffic to and from the docks, have a potential adverse impact on manatees, which are an endangered species. There are benthic communities in the proposed lease area under the mooring areas and where pilings are located. There is no way Petitioner can relocate the docks out of the benthic communities in the proposed lease area. The docks in the proposed lease area shade the benthic communities beneath them. Shading from boats at the docks in the proposed lease area, especially from boats used as residences that rarely leave the docks and from large vessels, damages the benthic communities. Boats docking in the slips in the proposed lease area have caused bare, scoured, concave spots beneath their bottoms. This is due to shading, propeller activity, and grounding of the vessels. Sea grasses and corals have been killed as a result. Boats docking in the proposed lease area have caused prop dredging or grounding damage to benthic communities and corals in Largo Sound, in the slips, just outside the slips, and in the canal adjacent to the proposed lease area. Petitioner Koblick has taken various steps to prevent or minimize the possibility of water pollution from the activities at the proposed lease area. These steps include discontinuing the sale of fuel at the subject docks and adopting strict rules prohibiting the discharge of any pollutants from boats docked at his facility, and prohibiting various activities that might be a source of pollution. These efforts notwithstanding, boats docking in the proposed lease area have discharged oil, pollutants, and bilge water overboard. Further, while water quality samples taken from the proposed lease area show good levels of dissolved oxygen and good levels of nitrates, water quality samples taken from the proposed lease area also reveal the presence of ammonia and pesticides, including endrinosulfan, endrin, and lindane, together with its isomers, at levels which exceed state water quality standards. 3/ Pollutants pose a threat of harm to benthic communities, corals, manatees, and other wildlife. Water depths in the slips and turning basin of the docks in the proposed lease area are shallower than minus four feet in some areas, ranging from minus 1.5 feet to minus 5.3 feet. Boats in those slips for the past five years have had drafts of more than 1.5 feet, some of them having drafts of 3 feet to 3 feet 8 inches. Boating related activities in the proposed lease area contribute to cumulative adverse impacts on Pennekamp Park. If boats were eliminated from the docks in the proposed lease area, the benthic communities would be likely to recolonize in approximately two years.
Recommendation On the basis of all of the foregoing, it is RECOMMENDED that the Board of Trustees of the Internal Improvement Trust Fund enter a final order to the following effect: Dismissing the petition in Case No. 91-0258 as moot; Denying Petitioner Koblick's application for a lease and easement; Ordering Petitioner Koblick to remove all docking structures located on the Respondent's lands; Ordering Petitioner Koblick to pay lease fees in arrears in the amount of $10,202.24; and Ordering that the fill material at filled area "F-9" not be removed. DONE AND ENTERED in Tallahassee, Leon County, Florida, this 17th day of April 1992. MICHAEL M. PARRISH, Hearing Officer Division of Administrative Hearings The DeSoto Building 1230 Apalachee Parkway Tallahassee, Florida 32399-1550 (904) 488-9675 SC 278-9675 Filed with the Clerk of the Division of Administrative Hearings this 17th day of April 1992.
The Issue The issue is whether to approve the City of Gulf Breeze's (City's) application for a Consolidated Wetland Resource Permit and Sovereign Submerged Lands Authorization to conduct a restoration project in Pensacola Bay.
Findings Of Fact Background This dispute involves a challenge by Petitioners to the third phase of a restoration project by the City designed to preserve the Island and protect its historical resources. The project site is located in sovereign submerged lands adjacent to the Island on the southwest side of the Highway 98 Bay Bridge which traverses Pensacola Bay connecting the Cities of Gulf Breeze and Pensacola. The Island is not a true island, but has always been connected to the mainland by a strip of land referred to as an isthmus, which meets the shoreline at Lot 36 of an older subdivision known as the First Addition to Casablanca Parcel No. 1 and platted almost sixty years ago. The isthmus juts out from Lot 36 into Pensacola Bay in a northwesterly direction for several hundred feet before making a 90-degree turn to the southwest where the Island then runs roughly parallel to the shoreline for around a half mile. See Joint Ex. 5-7, 14, and The Island, isthmus, and shoreline form the boundary around a small body of water known as Gilmore Bayou, an ecologically important and pristine salt marsh area. According to aerial photographs, at its widest point, the Island appears to be no more than a few hundred feet wide. Petitioners reside at Lot 37, which is just northeast of the isthmus on the shoreline. The rear part of Lot 37 faces Pensacola Bay and the City of Pensacola to the northwest. Lots 36, 35, and 34 (running to the southwest along the shoreline and facing Gilmore Bayou), are owned by Patricia Moreland, Robert Ozburn, and Intervenor Paul Tamburro, respectively, all of whom testified at the final hearing. Except for Petitioners, the project is supported by virtually all of the residents of the area as well as numerous civic organizations. See Joint Ex. 33. On July 14, 2008, the City filed with the Department its Joint Application for Works in the Waters of Florida, which would allow the City to complete the third phase of the project by (a) planting native submerged vegetation over approximately three acres of sovereign submerged lands, and (b) placing approximately 16,000 cubic yards of fill material and planting native emergent vegetation to stabilize the fill material on sovereign submerged lands at the north end of the Island. See Joint Ex. 3. The Department has authority under chapter 373, Florida Statutes, and Florida Administrative Code chapter 18-21 to approve the application. After an extensive review of the application, on August 9, 2010, the Department issued a Consolidated Notice of Intent to Issue Wetland Resource Permit and Consent to Use Sovereign Submerged Lands, which authorized the proposed project. See Joint Ex. 4. The proprietary authorization (letter of consent) was issued under the authority of rule 18- 21.005(1)(c), which identifies a number of activities that qualify for a letter of consent. In this case, because of the range of proposed activities, the project could qualify for a letter of consent under subparagraphs 8., 15., and 16. of the rule. On September 1, 2010, Petitioners filed their petition challenging the proposed agency action. While their initial pleading raised a number of issues, and cited two rules as a basis for reversing the agency action, these allegations have been substantially narrowed over the course of the proceeding and are now limited to the following: whether the project constitutes management activities associated with the protection of a historic site, thus qualifying for a letter of consent under rule 18-21.005(1)(c)16.; and whether the project unreasonably restricts or infringes upon their riparian rights of navigation, boating, swimming, and view, as proscribed by rule 18-21.004(3)(c). They also question whether Intervenor has standing to participate, but that issue is not dispositive of the primary issues in this case. Petitioners do not contest the issuance of a Wetland Resource Permit. Finally, Respondents and Intervenor question whether Petitioners have standing to initiate this action. The Project Site The project is located on sovereign submerged lands adjacent to the Island, a "naturally occurring sandy beach," as that term is contemplated in rule 18-21.005(1)(c)8. This is true even though portions of the "sandy beach" have eroded over time. The City owns the entirety of the Island. See Joint Ex. 14 and 15. This was not disputed by Petitioners. The Island is a public park, natural preserve, and historic site that is owned and maintained by the City exclusively for public use. Deeds by which the property was conveyed to the City require that it be forever used as a natural preserve and maintained in its natural state. See Joint Ex. 14 and 15. The Island and the area immediately adjacent thereto have a long and significant history dating back to the 1700's. Throughout the 1700's and 1800's, various portions of the Island were used as a careening facility for the repair and maintenance of large vessels. A marine railway was also built. In the late 1800's, a quarantine station was constructed on the Island where people who had contracted yellow fever were isolated. A cemetery exists upon the Island containing the remains of many who perished from the yellow fever epidemic. Also, there were many shipwrecks at the Island, of which some of the remains still exist. Accordingly, there are historic resources and artifacts such as shipwrecks and human remains on and around the Island. The Island has sustained significant erosion over the past 70 years. The northeast shoreline has eroded some 450 to 500 feet during that period of time. There has been a significant loss of vegetation and land mass. Without protection, the Island is in a perilous condition and subject to a permanent breach. The peat bog underlying the Island is vital to the stability of the Island and has been greatly damaged. It requires protective measures, such as those contemplated by the proposed project in order to assure its preservation. Due to the effects of hurricanes and storms, the erosion has substantially increased during the past decade. The erosion has caused the unearthing of and damage to historic artifacts and the salt marsh in Gilmore Bayou. There are clearly visible remnants of the former marine railway on the Island, which are being weakened by current weather events and require protection in order to preserve them. Caskets from the cemetery as well as human bone remains have been unearthed and additional damage will occur without protective restoration efforts. If the erosion continues, there will be more damage to the historic artifacts and the salt marsh will be destroyed. The Project To prevent further erosion and to protect the Island and Gilmore Bayou, the City has applied to the Department for three separate phases of a project to stabilize the shoreline. The first two phases of the project involved the construction of an artificial reef breakwater and the planting of shoreline vegetation. See Joint Exhibit 7a. They have already been approved by the Department and are no longer in issue. The first and second phases were challenged by Petitioners but the cases were eventually settled. See Case No. 09-4870, which involved the second phase. The third phase of the project is being conducted primarily for the maintenance of essentially natural conditions and for the propagation of fish and wildlife. This phase can be described as follows: restoration or nourishment of a naturally occurring sandy beach as contemplated by rule 18-21.005(1)(c)8.; habitat restoration or enhancement as contemplated by rule 18-21.005(1)(c)15.; management activity associated with protection of a park as contemplated by rule 18-21.005(1)(c)16.; management activity associated with protection of a preserve as contemplated by rule 18-21.005(1)(c)16.; management activity associated with protection of a historic site as contemplated by rule 18-21.005(1)(c)16.; and management activity associated with protection of habitat restoration or enhancement as contemplated by rule 18- 21.005(1)(c)16. While the project implicates each of the above provisions, the application and proposed agency action indicate that the letter of consent is granted on the theory that the project is associated with protection of historic sites. See Joint Ex. 4. The third phase is also designed to minimize or eliminate adverse impacts on fish and wildlife habitats and other naturally occurring resources. The project consists of the placement of 16,000 cubic yards of fill material in the area between the existing artificial oyster reef and the shoreline to restore and replace conditions that previously existed. The fill will consist of beach compatible sand that will be approximately six inches to a foot above mean high water. This phase also involves the planting of appropriate native wetland vegetation in the fill area, which will help stabilize the fill. The planting of vegetation in the third phase is separate and distinct from the plantings authorized in the second phase of the project. The project is needed in order to prevent further damage to a public park; public preserve; threatened, endangered, or special concern species of vegetation/habitat; and historic artifacts. These protection efforts were requested and recommended by the Florida Department of State. Petitioners contest only the propriety of the fill materials and the planting of the emergent stabilizing grasses on the fill. The fill portion of the project is located a significant distance from Petitioners' property. The closest portion of the project is estimated to be at least 550 feet from Petitioners' property, while the bulk of the project will take place between some 750 to 1,200 feet from their property. The Proposed Vegetation Planting In the third phase of the project, the City proposes to plant and establish emergent grasses (those that grow in water but partially pierce the surface) and sea grasses, all of which are appropriate native wetland vegetation on the Island. The proposed emergent grasses are Spartina alterniflora (also known as smooth cordgrass) and Juncus roemerianus (also known as black needle rush), which will be used for stabilization of wetlands. The proposed submerged seagrasses are Halodule wrightii (a type of shoal grass) and Ruppia maritime (a type of widgeon grass), which will help stabilize the fill. The smooth cordgrass is native to the Island. It will be planted in the fill area to prevent the fill from eroding. It is expected that once they mature, the height of the plants will not exceed two and one-half feet. Due to the water depth in the area, the shoreline slope, the sediment supply, and the wave action, the smooth cordgrass will not spread outside the proposed project area. Also, it will not interfere with navigation, boating, swimming, fishing, or view. The vegetation will, however, help fishing in the area. The black needle rush is also native to the Island. It will only grow to approximately two and one-half feet in height due to stressful conditions caused by the salt content in the water and wave action. It will not spread beyond the proposed project area and will not interfere with navigation, boating, swimming, fishing, or view. Like the smooth cordgrass, it will enhance fishing in the area. Both Halodule wrightii and Ruppia maritime are native to the Island. Both have slow growth rates, which when coupled with the "high energetics of the system," will hinder their ability to spread outside the project area. Neither seagrass will hinder navigation, boating, swimming, fishing, or view. They will afford a greater opportunity for snorkeling, recreation, and fishing; they will serve as a nursery habitat for finfish and shellfish; they will increase the habitat value of the area; and they will improve water quality. Petitioners submitted no evidence to contradict these findings. They also failed to submit any evidence that the fill material or grasses would spread into any riparian area that might be appurtenant to their Lot 37. The above findings are reinforced by the results of a separate project known as Project Greenshores located across Pensacola Bay from the Island. Project Greenshores involved the restoration of wetlands using dredge material to restore islands that are then protected by the construction of a breakwater and are stabilized by the planting of the same grasses that are proposed for the Island project. The two projects are in relatively close proximity to each other and have essentially the same environment. One difference, however, is that Project Greenshores receives a small source of sediment from stormwater outfalls, which means that it has a higher chance of grasses growing than does the Island. Even with the increased sediment, the grasses at that project have not spread beyond the project area, they have not interfered with navigation, boating, swimming, view, or fishing, and they have enhanced fishing in the area. Historical Artifacts Petitioners contend that the project does not qualify for a letter of consent under rule 18-21.005(1)(c)16. That provision authorizes the Department, acting on behalf of the Board of Trustees of the Internal Improvement Trust Fund, to issue a letter of consent for "management activities associated with . . . historical sites . . . provided there is no permanent preemption by structures or exclusion of the general public." As noted above, the Island has a long and significant history dating back to the early 1700's and there are historic resources and artifacts on the Island. See Finding of Fact 10, supra. When there is an archeological site issue in a permit, the Department typically relies on information from the Division of Historical Resources of the Department of State. See Fla. Admin. Code R. 18-21.004(2)(c)("reports by other agencies with related statutory, management, or regulatory authority may be considered in evaluating specific requests to use sovereignty lands"). Here, the Department relied on information from that agency, which indicates that there are archeological resources at the project site. The Department of State also recommended placing fill over the artifacts to protect them, which will be accomplished by the proposed fill. In addition, the Department relied upon information contained in a survey conducted by Mr. Empie, a registered professional surveyor, to generally show where those artifacts are located. See Joint Exhibit 5, also referred to as the Empie survey. The evidence supports a finding that the project is for management activities associated with historical sites. The record shows that there is strong public support for the project. See Joint Ex. 33. Although many of the artifacts will be covered by the fill, the fill will actually protect them from damage, destruction, theft, and removal. By protecting them, future generations will be able to enjoy the artifacts. No "structures," as that term is defined in rule 18- 21.005(1)(c)16., are part of the project. Therefore, the project will not cause permanent preemption by structures. Contrary to Petitioners' assertion, the project will not exclude the general public from the fill area. The City contemplates that other activities, such as underwater snorkeling, will encourage the public to utilize the project site. The evidence supports a finding that the project qualifies for a letter of consent under this rule. Riparian Lines The Empie survey provides a reasonable depiction of the various riparian lines in the areas adjacent to the proposed project. See Joint Ex. 5. A professional surveyor with the Division of State Lands, Mr. Maddox, agreed that it was a reasonable depiction of the angle of the riparian lines and a "fair distribution of riparian areas," including that of Lot 37. The only property owner adjacent to the Island is Patricia Moreland, who owns Lot 36 and has resided on that parcel since 1956. As noted above, the isthmus meets the northwest boundary line of Lot 36. By executing a Letter of Concurrence, Ms. Moreland conferred upon the City all rights, both proprietary and riparian, that she has with respect to Lot See Joint Ex. 16. Petitioners contend that they own riparian rights appurtenant to their Lot 37, which is to the east of Lot 36. The City and Intervenor dispute this claim and contend that Lot 37 does not adjoin any navigable water and thus there are no riparian rights appurtenant to Lot 37. Assuming arguendo that Lot 37 adjoins Pensacola Bay, it is still separated from the project site by riparian areas appurtenant to the Moreland property (Lot 36) as well as the riparian areas appurtenant to the City property, i.e., the Island and isthmus. The Empie survey, which reasonably depicts the riparian lines in the project area, shows the project site as being approximately 300 feet inside the existing breakwater, which is shown as being no closer than 48.9 feet away from the westernmost riparian line appurtenant to Lot 37. See Joint Ex. The primary portion of the fill site is located around 370 feet from the closest point of the western riparian line appurtenant to Lot 37. Id. No portion of the project is located within 25 feet of the Lot 37 riparian line. Id. Petitioners presented no evidence disputing the riparian areas identified on the Empie survey or otherwise identifying the areas of riparian rights appurtenant to their property. While they engaged the services of Mr. Barrett, a professional land surveyor to prepare a boundary survey, the purpose of the survey was to show that Lot 37 adjoins Pensacola Bay, rather than depicting the riparian areas appurtenant to that lot. See Petitioners' Ex. 1. Infringement on Riparian Rights Rule 18-21.004(3)(c) requires that "activities [in submerged lands] must be designed and conducted in a manner that will not unreasonably restrict or infringe upon the riparian rights of adjacent upland property owners." (emphasis added) Petitioners contend that, even though they do not routinely use their riparian rights, the project will restrict or infringe upon their riparian rights of boating, swimming, navigation, and view. To make this determination, they assert that the appropriate test under the rule is mere infringement, and not "unreasonable" infringement; however, this interpretation is contrary to the plain wording in the rule. The main living floor of Petitioners' residence is approximately 50 feet above sea level. The emergent grasses will be located no closer than 500 feet from the edge of Lot 37 and 600 feet from their residence and are expected to grow only to a height of no more than two and one-half feet. The concern that the grasses will impair Petitioners' view is without merit. Although Dr. Cope initially believed that fill or grass would be placed or planted "all the way up to and abutting our lot 37," this interpretation of the City's plans was incorrect. A photograph taken from his back yard indicated that he could view the northeastern corner of the Island where new vegetation or fill might be placed, but the photograph depicted an area outside of the Lot 37 riparian area. See Petitioners' Ex. 18. While Dr. Cope initially stated that the new emergent grass would "clearly degrade the view from both the house and the shoreline," he later acknowledged that the project would not have any effect upon his view of Lot 37's riparian areas. There are a boathouse and dock in the waters behind Petitioners' house. However, Petitioners submitted no evidence to support their suggestion that the project might cause the water behind Lot 37 to become more shallow and adversely affect boating and navigation. Contrary evidence by the Department and City was unrefuted. Finally, Dr. Cope stated at hearing that he has never been swimming in Gilmore Bayou or Pensacola Bay and has no intention of doing so. His wife offered no evidence that she ever intends to swim in those waters. In summary, the activities undertaken in the project area will not unreasonably restrict or infringe upon Petitioners' riparian rights of swimming, boating, navigation, or view within the meaning of rule 18-21.004(3)(c). Petitioners' Standing Respondents and Intervenor contend that Petitioners lack standing to bring this action for two reasons: that they do not own Lot 37 individually but rather as trustees, and the petition was not filed in that capacity; and that Lot 37 does not adjoin navigable waters. See § 253.141(1), Fla. Stat. ("[r]iparian rights are those incident to land bordering upon navigable waters"). As described by the City's real estate expert, in June 2010, or before the instant petition in this case was filed, the Copes executed two deeds for estate planning purposes, which resulted in "legal title [being] owned part by Dr. and Ms. Cope as to one-half life estate and for Ms. Cope as to one-half for her life estate [and] then the remainder interest is vested in the trustees [of the D. Nathan Cope or Cynthia Russell Cope revocable trust agreements] for the remainder interests." Put in plainer language, this meant that the ownership of Lot 37 is now divided as follows: an undivided 50 percent is owned by the wife as to a life estate and by the wife's revocable trust as to the remainder interest, and the other undivided 50 percent is owned by the wife and husband as to a life estate for the husband's lifetime and by the husband's revocable trust as to the remainder interest. Therefore, there are four entities or persons with an ownership interest in the property: Dr. Cope, Mrs. Cope, Dr. Cope's trust, and Mrs. Cope's trust. The City presented expert testimony regarding the chain of title of Lot 37, beginning in June 1952 when the subdivision was first platted, and running through June 2010, when Petitioners conveyed the property to themselves as trustees of two revocable trusts. According to the expert, the subdivision plat in 1952 reflects a narrow strip of property (described as a hiatus strip) separating the entire subdivision, including Lot 37, from the waters of Gilmore Bayou, Pensacola Bay, and Woodland Lake, a nearby body of water. The strip was a park that was dedicated to the public. See Joint Ex. 1. In 1962, the developer conveyed by quit claim deed the entire strip to the record title holder of each lot in the subdivision. At that time, Lot 37 was owned by the Blaylocks. The expert found that each conveyance of Lot 37 that occurred after 1962, up to and including the Copes' purchase of the property in February 2008, did not include the hiatus parcel. Therefore, he opined that title in the strip property continues to remain with the Blaylocks. Besides his title search, the expert further corroborated this opinion by referring to a topographic survey of Lot 37 prepared in June 2005, see Joint Ex. 2a; a title insurance policy on Lot 37 issued in 2008 when the Copes purchased the property that specifically excludes title insurance for the hiatus parcel; and a recent Santa Rosa County tax bill describing the property without the hiatus parcel. In response, Petitioners contend that the hiatus strip never existed or the 1952 plat is invalid because it failed to comply with section 177.08, Florida Statutes (1951), which required that "all land within the boundaries of the plat must be accounted for either by blocks, out lots, parks, streets, alleys or excepted parcels." Because a dispute over the exact boundary lines of Lot 37 exists, this issue must be resolved in the appropriate circuit court. See § 26.012(2)(g). For purposes of deciding the merits of this case, however, it is unnecessary that this determination be made. Intervenor's Standing Dr. Tamburro currently resides on Lot 34, which faces Gilmore Bayou, and jointly owns the property with his wife. He uses the Bayou to boat and for other recreational purposes. He also uses the Island to swim, walk, and boat. The preservation of the Island is important to him since it serves as a barrier island in protecting his home during storm events. Although Dr. Tamburro's wife did not join in his petition to intervene (but appeared as his counsel), he still has a recognized ownership interest in the property.1
Recommendation Based on the foregoing Findings of Fact and Conclusions of Law, it is RECOMMENDED that the Department of Environmental Protection enter a final order approving the City's application for a Wetland Resource Permit and Letter of Consent to Use Sovereign Submerged Lands. DONE AND ENTERED this 20th day of April, 2011, in Tallahassee, Leon County, Florida. S D. R. ALEXANDER Administrative Law Judge Division of Administrative Hearings The DeSoto Building 1230 Apalachee Parkway Tallahassee, Florida 32399-3060 (850) 488-9675 Fax Filing (850) 921-6847 www.doah.state.fl.us Filed with the Clerk of the Division of Administrative Hearings this 20th day of April, 2011.
