Findings Of Fact Based upon my observation of the witnesses and their demeanor while testifying, documentary evidence received and the entire record compiled herein, I hereby make the following relevant factual findings. Respondent is a certified general contractor and has been issued license number CG CA03134. During November of 1978, Respondent, doing business through the entity of Creative Home Design, Inc., entered into a contract with Dr. Stephen Silverstein to construct a residence in Boca Raton, Florida, for the sum of $180,000. Respondent received from Dr. Silverstein a total of $140,500 for the construction he performed on the Silverstein residence. (Stipulation by the parties) Additionally, Dr. Silvertstein paid certain liens which were filed with regard to the construction performed by Respondent on his residence, to wit: P.N.A. Drywall: $5,260.00 (Petitioner's Exhibit 2) Pentagon Diversified: $3,801.34 (Petitioner's Exhibit 3) American Lumber: $8,217.50 (Petitioner's Exhibit 4) Lone Star Industries, (Petitioner's Exhibits 7 and 8) Inc. $1,293.50 Mack Industries: $4,604.29 (Petitioner's Exhibits 9 and 10) Smith and DeShield: $ 600.00 (Petitioner's Exhibit 11) Certain contractors furnishing labor and materials for the Silverstein residence based on contracts entered into by wit: Respondent also filed liens, to A. A. Marini Septic Tanks, Inc.: (Petitioner's Exhibit 21) $1,700.00 Delano Pools, Inc.: (Petitioner's Exhibit 20) $4,539.00 William D. Adeimy, Inc.: 3/ (Petitioner's Exhibit 16) $3,183.75 Climate Control Services: (Petitioner's Exhibit 17) $1,882.50 Ballavia Construction (Petitioner's Exhibit Company: 24) $5,446.00 Temperature Control: (Petitioner's Exhibit 18) $ 678.00 J. Griffin Painting: (Petitioner's Exhibit 23) $3,795.00 Central Systems, Inc.: $1,018.80 (Petitioner's Exhibit 19) Dr. Silverstein also entered into another contract for the sale of the residence being built by the Respondent whereby Dr. Silverstein agreed to sell the residence to Respondent's son, Joseph Roberts, for the sum of $210,000. (TR pages 5-6) On February 15, 1980, a notice of code violation was issued by the building official for Palm Beach County, Florida stating that the pool which was installed at the Silverstein residence was not completely enclosed by a fence or dense hedge as required by Section 500.14F of the Palm Beach Zoning Code. Respondent has failed to correct that violation. Respondent completed the Silverstein residence to a degree of completion where it could be occupied and he could move into the residence with his family. Thereafter, Dr. Silverstein eventually filed suit and was awarded a judgment evicting Respondent from the residence. (Petitioner's Exhibit 12) Respondent's son, Joseph, failed to consummate the agreement to purchase the residence. Respondent and his family vacated the Silverstein residence and, in the process, removed certain fixtures attached to the residence including carpeting, appliances, door knobs, air conditioning and air handlers, the sprinkler system, light fixtures, vanities, a whirlpool tub, washer, dryer, air conditioning vents, bidet, sprinkling pump timer, and a drop-in range. (TR pages 23-28, 128- 130, and 98-100) Dr. Silverstein filed a claim of loss with his insurance company and was paid a settlement for the loss, which included the certain charges for reinstallation and the reconnection of the various fixtures which had been removed for a total sum of $24,252.02. (Petitioner's Exhibit 13, TR 25-28) The Respondent's Position Respondent contended that he was authorized to occupy the Silverstein residence and this contention is not really in dispute herein. However, it later became necessary for Dr. Silverstein to evict the Respondent and his family from the residence when it became apparent that his son, Joseph Roberts, would not consummate the agreement to purchase the residence of Dr. Silverstein. Respondent admits to taking the fixtures and other items referred to hereinabove. Respondent was without authority to do so. Respondent contends that the various liens which were referred to hereinabove were not valid inasmuch as more than one year had elapsed during the time the work was performed and no claim of lien had been filed within that one- year period. Thus, Respondent contends the claims of lien were defective. Respondent offered no proof of payment of the various claims of lien. Additionally, Respondent states that several of the contractors did not perform work and therefore there were no amounts due and owing those companies. Specifically, Respondent contends that Marini Septic Tank did not install the septic tank but a former affiliate did and that there was an attempt to bill him twice. Additionally, Respondent contends that he paid Ballavia Construction Company for the amount claimed in cash, however he had no receipts or other documentary evidence to substantiate that transaction. As relates to the claim of Griffin Painting, Respondent contends that he paid all amounts due and owing them save $660.00. Respondent failed to introduce evidence to corroborate his claim in that regard and it is therefore rejected. Finally, Respondent furnished releases of liens and an invoice of the claim referred to hereinabove from Climate Control Services, Inc. indicating that they were paid in full. Documentary evidence received and testimony introduced herein substantiates Respondent's position and it is found that he, in fact, paid Climate Control Services, Inc. in full for the services they rendered. (Respondent's Exhibits, 4, 6, and 10) As noted hereinabove, it is found that the Respondent paid the amount due and owing William D. Adeimy, Inc., and a release of lien from that entity was received herein. (Respondent's Exhibit 3)
Recommendation Based on the foregoing findings of fact and conclusions of law, it is hereby RECOMMENDED that the Respondent's certified general contractor's license number CG CA03134 be revoked. RECOMMENDED this 24th day of May, 1985, in Tallahassee, Florida. JAMES E. BRADWELL Hearing Officer Division of Administrative Hearings The Oakland Building 2009 Apalachee Parkway Tallahassee, Florida 32301 (904) 488-9675 Filed with the Clerk of the Division of Administrative Hearings this 24th day of May, 1985.
Findings Of Fact On April 23, 1980, the county applied to DER for a permit to place approximately 334,000 cubic yards of sand along the southern 2.4 miles of the eastern shoreline of Key Biscayne to create an additional recreational beach for public use and to control beach erosion. The northern limit of the Project area is the southern boundary of Crandon park, the southern limit is the Cape Florida Lighthouse, and the seaward limit is the "design toe of fill", which results in establishing a new mean highwater line at approximately the 1913 shoreline. No fill will be placed along a 1600-foot area along the shore between 1500-feet and 3100-feet north of the lighthouse, where accretion has occurred since 1913. The re-nourished beach is proposed to average approximately 100 feet in width. On October 15, 1980, DER issued a letter of Intent to deny the requested permit. There are approximately 45 acres of sea grass within the Project Area which are proposed to be covered with sand as a result of the project. Sea grass is a major marine resource in Florida, and the anticipated loss of these 45 acres is one of the primary reason DER proposed to deny the permit application. Transects made by the County in December of 1977, and March of 1978, showed that the sea grass in the Project Area varies in density from "sparse" in approximately half of the Project Area to "dense" in approximately ten percent of the Project Area, with the remainder being considered being "medium" in density. Approximately 25 percent of the area to be filled is barren bottom. Sea grasses serve several important functions in the marine ecosystem. They are a vital and productive link in the marine food chain. By cycling energy from the sun into digestible plant material, sea grasses provide food for various organisms which, in turn, are eaten by other organisms in the food chain. Sea grasses assist in maintaining good water quality by causing a baffling effect which improves clarity, and by assimilating the potentially harmful nutrients from the water column. Sea grass roots bind sediments on the sea bottoms, thereby detering erosion. Additionally, sea grass beds function as prime nursery habitat for juvenile fish and other young marine animals as well as spawning grounds for various marine species. Sea grass beds further provide areas for concealment protection and feeding for all types of marine-creatures. Two types of marine sea grasses predominate in the area off Key Biscayne: Syringodium filiforme, or "manatee grass", and Thalassia testudinum, or "turtle grass". The sea grass beds proposed to be filled by this project are dominated by Syringodium filiforme, a long, slender grass which, when compared to turtle grass, offers less refuge to smaller marine animals because its leaves are slender and round and it does not occur in dense groups. In addition, Syringodium filiforme is not as good a soil stabilizer as turtle grass, due primarily to its root structure. It also offers comparatively less surface area for the attachment of epiphytes and algae. A significant portion of the sea grasses in the northern part of the Project Area are ephemeral: that is, they have grown in since 1967, and could very likely be destroyed during a major storm event. It is unlikely that they will be in place for sufficient periods of time to become a major influence on the grain size of the sand in the area, nor will they have a major influence on the long-term sediment dynamics of the area. The 45 acres of sea grass in the Project Area constitute only about two percent of the approximately 2,000 areas of sea grass habitat located immediately to the east of the Project Area. In addition, there are approximately 150,000 acres of sea grass beds lying within that portion of Biscayne Bay in Dade County, Florida. There is an almost solid belt of turtle grass beginning on the offshore or ocean-side of Key Biscayne extending southward of Key West out to the Merquesas Islands and, with a slight break, to the Dry Tortugas. Unlike Syringodium filiforme, turtle grass serves as a true nursery ground for marine organisms in their early life stages. The portion of the sea grass community proposed to be filled in the Project Area is not a good nursery ground, primarily because of the small amount of turtle grass present. The turtle grass beds present in the Project Area do not constitute a mature stable community comparable to those located slightly farther offshore Key Biscayne. These better turtle grass beds have longer blades that do not show wear from wave action and are covered with epiphytes and other marine organisms. Further, unlike the turtle grass in the Project Area, these beds are dense, with little open space between them, and have little or no other plants growing with them. The sea grass beds in the Project Area are simply not qualitatively as rich as these adjacent beds. These offshore sea grass beds serve as true nursery grounds for marine life. Shrimp and certain game and commercial fish, as examples, are located primarily in nursery grounds in Biscayne Bay and Hawk Channel, where there are more mature and stable turtle grass communities. In light of the extent and condition of the sea grasses in the fill area and the associated sea grass communities both inshore and offshore Key Biscayne, taken together with the design of the overall project as hereinafter described, the total effect of the proposed fill on marine life should be inconsequential. The sand to be placed in the Project Area will be dredged from a borrow area located approximately one mile south of Key Biscayne. This site was selected by the United States Army Corps of Engineers. A consultant retained by the County has recommended that certain portions within this borrow area not be used, and that other areas adjacent thereto be utilized if necessary. This modified borrow area falls within the area described in the County's permit application for the source of the fill material. The depth of the sand above the substrate in the borrow area ranges from 1.0 to 9.5 feet, with a substantial portion of the area having in excess of a five-foot depth of sand. Assuming sand will be removed to a depth of five feet, the sand will be taken from approximately a 2,000 by 1,000-foot site. If done in this manner, only about one-third of the borrow area designated by the Corps of Engineers and modified by the County's consultant will be utilized. The entire borrow area designated by the Corps of Engineers contains approximately one million cubic yards of sand. There are no known corals or hard-bottom communities within the proposed borrow area. In addition, there appear to be very few benthic organisms in this area, which is comprised primarily of shifting sand. The benthic organisms that do exist in the area will, of course, be removed during dredging. However, the borrow area can reasonably be expected to repopulate with these organisms as soon as the dredging operation is concluded. Further, the area from which the fill is proposed to be obtained is well removed from any areas of persistent sea grass cover. There are only five or six patches of sea grass in the borrow area, the largest being approximately 12 feet across. These patches do not contain turtle grass and may be easily avoided during dredging. The record in this case clearly establishes that use of the sand from the borrow area should not have an adverse impact on the environment surrounding that area. The sand proposed to be placed on the beach is similar in grain size and composition to the sand that is on the existing beach, owing probably to the fact that it was at one time located on the beach and has been removed through the process of erosion. This sand is of such quality that there should be only minimal turbidity occurring during the dredging operations. There are very small quantities of fine material within the borrow area, and the chemical and physical composition of the sand there closely matches the chemical and physical composition of the sand on the beach. As stipulated by the parties, it is not anticipated that any turbidity problems will result from a physical or chemical breakdown of the material after it is deposited on the beach, and it is also not anticipated that significant long-term turbidity will result from the actual fill being placed on the beach because of the small quantity of fine material contained in the fill. The sand is proposed to be dredged from the borrow area by means of a hydraulic dredge, and transported in a sand/water mixture via pipeline to the Project Area. The sand will be placed on the beach by a method known as longitudinal diking, which permits most of the sand to precipitate before the water returns to the ocean, thereby keeping most of the sand in the Project Area and reducing the impact on receiving waters. The 45 acres of sea grass in the Project Area discussed above will not be covered immediately by fill. This acreage figure represents the total area of sea grass that will be covered after the fill has reached the "theoretical- toe of fill". The theoretical design profile of the beach cannot be achieved immediately because it is not possible to operate the necessary equipment below the waterline. The project design calls for fill to be placed on the beach in a different configuration than will ultimately be obtained, and allows natural wave action to reshape the sand to achieve the design profile. It is anticipated that the entire process will take approximately two years. This is not a unique process, in that the Crandon Park beach immediately north of the Project Area was renourished in a similar fashion in 1969. The Crandon Park design profile was achieved in 1971, and the record establishes that sea grasses offshore Crandon Park were not adversely affected by the sand placed on that beach. Further, no additional fill has been placed on Crandon Park beach since its original renourishment in 1969, and that beach is still very close to the original design profile. The design profile for Crandon Park beach is identical to that proposed for the Project Area. Accordingly, once the design profile for this project is achieved, the greater weight of the evidence in this cause establishes that the sand in the renourished area should not migrate beyond the design toe of fill. A rock structure referred to as the "terminal groin" is proposed to be constructed in connection with the project at the lighthouse at the southern extremity of the beach. The purpose of the terminal grain is to retain the sand placed along the beach. This structure will extend seaward approximately 350 feet, with a top width of seven feet, and top elevations ranging from plus 2.6 feet mean low water at the most seaward location, to plus 7.0 feet mean low water at the beach. The County proposes to modify the slope of the groin to create additional intertidal and subtidal habitat by placing native limestone boulders along the entire 350-foot length of the south side of the groin. By making this modification, approximately 7,000 square feet of subtidal rock habitat will be provided. In addition, this modification will create approximately 36,750 cubic feet of void space for potential marine habitat. The approximate cost of this structure is $200,000. The terminal groin will provide a type of rocky habitat which naturally existed in the Biscayne Bay area, but which has been largely eliminated by man-made improvements. This type of habitat, of course, will not duplicate the type currently provided by the 45 acres of sea grass proposed to be covered by fill. Specifically, rocky habitat does not serve the nursery and breeding functions which sea grasses provide. Further, it neither contributes food stuff by way of primary productivity nor cycles energy into the marine ecosystem in the same manner as sea grasses. The County, in fact, had at one time considered replanting sea grass to mitigate for the loss of the grass communities in the Project Area, but abandoned that alternative in view of the existing large areas of sea grass adjacent to the project, and the fact that the barren bottoms in the Project Area and in adjacent areas have occurred as a result of high wave energy. As a result, it was felt that any attempt to replant the sea grasses by way of mitigating the effect of the proposed project would be unsuccessful. With a properly designed terminal structure, the renourished beach should last approximately 30 years. The rate of erosion on the beach when the project is concluded should approximate 15,000 cubic yards per year. Accordingly, it is unlikely that the beach would require renourishing in less than ten years following the project. As noted above, the Crandon Park beach was restored in excess of 12 years ago, has not been renourished, and still is very close to the original design profile. Sea turtles nest at Bill Baggs State Park and at Crandon Park. The record in this case establishes that these turtle nests can be fairly easily found and relocated. The Corps of Engineers has a turtle protection program with the U.S. Fish and Wildlife Service under which contractors on beach renourishment projects are required to relocate turtle nests, utilizing persons licensed by the Florida Department of Natural Resources. Dade County also has a turtle relocation program which is currently being utilized in Crandon Park. The record in this case does not establish that the proposed beach renourishment project will adversely affect the nesting of sea turtles within either the Project Area or areas adjacent thereto. Extensive erosion has occurred on the beaches on the eastern shore of Key Biscayne. It is currently not possible, for example, to walk from one end of the beach on Key Biscayne to the other without climbing seawalls and jetties, since portions of the beach are completely under water at all times except during extremely low tidal periods. A substantial portion of the project Area is completely submerged even during low tide. The Hearing Officer personally viewed the extent of the erosion in the Project Area. The placement of fill in the northern 1.2 miles of the project will create public access between Bill Baggs State Park and Crandon Park, which is maintained by Dade County. The project will also create a public beach where currently none exists eastward of the proposed erosion control line for the northern 1.2 miles of the project. Beach renourishment will provide support for and stabilize the restored beach on Crandon Park, thereby enabling that beach to last longer, and will also provide erosion control for the entire length of the eastern shoreline of Key Biscayne. The project, as designed, will protect against a ten-year storm of 24-hour duration, thereby helping to diminish serious injury to property and persons by reason of violent storms. Additional protection will also be provided to the Cape Florida lighthouse, a State historical landmark. Although not a hurricane surge protection project, the beach renourishment program will provide some degree of protection from hurricanes. More protection is provided to upland structures by increasing the distance between them and adjacent water bodies. Pursuant to Section 161.053, Florida Statutes, the Department of Natural Resources has determined that severe beach erosion has occurred along the southern 2.4 miles of Key Biscayne, and that the beach either has been or will be destroyed in the immediate future unless a publicly financed program is undertaken. In 1978, and in 1979, the Florida Legislature appropriated funds for the project, and additional funding has also been approved by the Governor and Cabinet. Tourism is Florida's largest industry. In 1980, approximately 35.9 million visitors spent $17 billion in the State of Florida, generating $785 million in tax revenues and supplying employment for 535,000 people directly employed in the tourist industry. There are primarily four reasons that visitors come to the State of Florida: (1) rest and relaxation; (2) beaches; (3) climate; and (4) other attractions, primarily manmade. Over 60 percent of the visitors to Florida have indicated that beaches are their primary reason for visiting the State of Florida. In 1980, 12.6 million tourists visited Dade County. Of these, 10.3 million were domestic tourists, and 2.3 million were international tourists. these tourists spent a total of $9.5 billion in Dade County, making the tourist industry by far Dade County's largest single industry, directly accounting for 25 percent of employment in Dade County. In 1950, over $4.77 million were collected in the taxable areas of Dade County by imposition of a resort tax of two percent on hotels and motels for transients. Tourism on Key Biscayne contributed approximately $300,000 to the Dade County resort tax collection, which is 6.2 percent of the total tax collection for 1980. 57.2 percent of the domestic tourists in Dade County came to Dade County because of the beaches. Tourists visiting other sections of Dade County used the beaches on Key Biscayne because they are very convenient and pleasing. During the course of this proceeding, the deposition of Dr. Anitra Thorhaug was taken by Petitioners, and the parties have requested that the Hearing Officer, pursuant to the provisions of Rule 28-5.208, Florida Administrative Code, and Rule 1.390, Florida Rules of Civil Procedure, determine a fair and reasonable expert witness fee to be paid to Dr. Thorhaug for her deposition. Having considered the submissions of the parties on this issue, including the actual time spent in deposition of two hours and 55 minutes, and the total time of 4.5 hours devoted by Dr. Thorhaug to the taking of her deposition, it is determined that a reasonable fee for her services is $350.
The Issue This case concerns proposed amendments to Respondent's Rule 16N-22.009, The issues for determination are, 1) whether Petitioner has standing to challenge the proposed amendments, and 2) whether the amendments are an invalid exercise of delegated legislative authority. More specifically, the following issues are raised by the pleadings and presentation of the parties: Whether the rule amendments exceed the agency's grant of authority by creating a "no entry" or "motorboat prohibited zone", and by extending that zone into the right of way of the Intracoastal Waterway Channel. Whether the agency materially failed to follow rulemaking procedures prescribed by Section 120.54, F.S., by substantially revising the proposed amendments after a challenge had been filed, and by preparing an inadequate economic impact statement; and Whether the amendments are arbitrary and capricious because they are unnecessary or unrelated to manatee protection.
Findings Of Fact Petitioner, Gerald M. Ward, is a registered engineer residing in Riviera Beach, Palm Beach County, Florida. He owns a 30-foot Columbia sailboat, with motor power. He uses the boat for recreational purposes exclusively. Since 1973, the boat has been berthed at Old Ship Marina, within the slow speed zone of the existing rule, but approximately one mile outside of the proposed motorboats prohibited zone. Petitioner does not live on, nor own any real property abutting the proposed motorboat prohibited zone. Since 1979, Rule 16N-22.009, F.A.C. has provided two speed zones for operation of motor boats between November 15 and March 31 in Palm Beach County: an idle speed zone in all waters within one-half mile of the discharge of the Florida Power and Light Riviera Beach Power Plant, including the Intracoastal Waterway; and a slow speed zone for all inland waters lying between one-half mile and one and one-half miles of the power plant discharge, including the Intracoastal Waterway. These zones are within Lake Worth, the body of water between West Palm Beach and Palm Beach and extending both north and south. The changes proposed for Rule 16N-22.009, F.A.C., would create a third zone, "motorboats prohibited", in a much smaller area within the current idle speed zone, and in and immediately adjacent to the power plant discharge canal. The full text of the Department of Natural Resources (DNR) proposed rule was published in the Florida Administrative Weekly, Volume 15, No. 38, September 22, 1989, as follows: 16N-22.009 Palm Beach County Zones Amended. For the purpose of regulating the speed and operation of motorboat traffic between the dates of November 15 and March 31 of each year, the Palm Beach County zones are amended as follows: IDLE SPEED ZONE-All waters lying within one-half mile of the discharge of the Florida Power and Light Riviera Beach Power Plant including the Intracoastal Waterway, except those waters posted as a "Motorboats Prohibited Zone" as described in paragraph (c) below. (c) MOTORBOATS PROHIBITED ZONE - All waters lying within Lake Worth, commencing at a point exactly 300 feet north of the Riviera Beach Power Plant discharge canal and easterly to within 100 feet of the westernmost boundary of the Intracoastal Waterway, lying within Township 42 South and Range 43 East, running southerly to a point exactly 300 feet south of the abovementioned discharge canal and easterly to the westernmost boundary of the Intracoastal Waterway lying within Township 43 South and Range 43 East. The precise boundaries and effective period of the zone will be posted each year between November 15 and March 31 (see accompanying map for exact locations). (Emphasis in original denotes new text). No map was published. Sometime between September 22nd and October 16, 1989, DNR staff realized that the description of the proposed zone was defective. It failed to "close", and therefore did not adequately describe the area. At the public hearing on the proposed rule amendments, on October 16, 1989, Department staff person, Karen Lewis announced the need to make a technical change to the proposed amendments; she provided the attendees a copy of the revised description and a map depicting the zone. These changes were incorporated into the record of the rulemaking proceedings. On November 3, 1989, the DNR, Division of Law Enforcement, published a "notice of change" in the Florida Administrative Weekly, Volume 15, No. 44. The notice affected several other rules establishing zones in other counties, and the following text was published for proposed Rule 16N-22.009, F.A.C.: * * * 2. For proposed rule 16N-22.009, Palm Beach County Zones the word "amended" has been deleted from the title, and subsection (1)(c) has been corrected to read as follows: (c) MOTORBOATS PROHIBITED ZONE - All waters lying within Lake Worth, commencing at a point exactly 300 feet north of the northeast corner of the Riviera Beach Power Plant discharge canal, thence easterly to a point 100 feet west of the western boundary of the Intracoastal Waterway channel, lying within Township 42 South and Range 43 East; thence running southerly parallel to and 100 feet west of the western boundary of the Intracoastal Waterway channel for a distance of 700 feet to a point within Township 43 South and Range 43 East; thence westerly to the shoreline to a point 300 feet south of the southeast corner of the discharge canal; thence northerly 300 feet to the southeast corner of the discharge canal; thence westerly 150 feet, northerly 100 feet, and easterly 150 feet to the northeast corner of the discharge canal (inclusive of the entire waterbody comprising the Riviera Beach Power Plant discharge canal); thence northerly 300 feet to the point of origin. The precise boundaries and effective period of the zone will be posted each year between November 15 and March 31. The words "(see accompanying map for exact locations)" have been removed from subsection (1)(c). * * * A map depicting the three zones in Lake Worth was published at page 5144 of the Nov. 3rd Florida Administrative Weekly. The Intracoastal Waterway is a federal Corps of Engineers project extending the Atlantic coast length of Florida. In Palm Beach County the waterway consists of a main channel approximately 125 feet wide with 187.5 feet of right of way on each side. The waterway runs north and south in the waters of Lake Worth, hugging the mainland coast, east of Riviera Beach. The waterway is regulated by the Florida Inland Navigation District (FIND). An easement for maintenance of the project was granted by Chapter 13664, Laws of Florida (1929), and by a conveyance from the Trustees of the Internal Improvement Trust Fund to the United States, dated June 8, 1942. Petitioner has suggested, but failed to prove, that FIND has withheld necessary permission for DNR to establish its zone within a portion of the right of way. Maintenance or repair of a property owner's facilities is exempt from the prohibition of the motorboat prohibited zone. Rule 16N-22.003(3), F.A.C. The Department has received no objection nor written comment from the U.S. Army Corps of Engineers and U.S. Coast Guard, and its comment from FIND was simply that the draft map was inconsistent with the text of the September 22, 1989 version of the proposed rule. The Department has consistently intended that the zone extend into the right of way, but not into the waters of the Florida Intracoastal Waterway channel. The revised description of the boundaries of the zone, published on November 3rd, plainly effectuates that intent. There are no marinas in the area of the proposed motorboat prohibited zone. There is an existing dock owned by the U.S. Coast Guard within the zone, but arrangements have been made with the Coast Guard regarding their non-use of the dock during the posted months. The proposed zone is a very small area within an already limited speed zone. There is ample room for motorboats to navigate east of the zone, within the right of way, in the channel of the Intracoastal Waterway, and in the wide waters of Lake Worth lying east of the waterway. The proposed motorboat prohibited zone will not interfere with navigation or boats engaged in interstate commerce. The zone will be marked by signs installed by the department during the relevant months. While the exact type of marker has not been established, they will be obvious to boaters and will be easily removed by department staff. The increase in signs will not automatically increase boating accidents. In the record there are two versions of an economic impact statement accompanying the proposed rule. They do not materially differ; the revised version simply provides an expanded narrative without altering the estimated costs or the underlying conclusions. The Department estimates the cost of signs to be approximately $125.00 each, for four; and an additional $320.00 each for the pilings, for a total quantifiable cost of $1780.00. This is for signs to be attached to a piling structure. The department is currently investigating the possibility of using buoys which would be cheaper to install and remove. The $1780.00 is a one-time cost and the department anticipates that installation and removal each year will be routinely accomplished by existing field staff who are already working in that area. The zone will be enforced by the Florida Marine Patrol who already enforces the existing zones. Any associated increase in law enforcement costs will be absorbed into the existing operating budget. No small nor minority businesses are operating in the area within the proposed zone and no evidence was presented to disprove the department's estimate of no cost to those groups or to competition and open market for employment or to persons directly affected by the proposed action. The stated purpose of the proposed rule is for ". . . regulating the speed and operation of motorboat traffic to needed protection for the Florida manatee." (Notice of proposed rulemaking published in the Florida Administrative Weekly, Volume 15, No. 38, September 22, 1989.) The manatee is an endangered species, one of the original species identified in the Federal Endangered Species Act. Its estimated population is approximately 1,200 for the entire United States; many of whom are found in the waters of Florida. In 1978, the Florida Legislature passed the Manatee Sanctuary Act declaring the state to be a refuge and sanctuary for manatees. The act has also been amended at least three times since 1978, giving the department additional authority to protect the species. Motorboats kill, maim and disturb manatees. In the past five years there has been an 85 percent increase in the incidents of manatee deaths from collision with vessels. In 1988, 133 manatees were found dead in Florida; 43 were determined to have been killed by boats. In 1989, those figures had both been surpassed at the time of the hearing in this case. Since 1978, there have been 12 boat-related manatee deaths in Palm Beach County, including two deaths in 1988. No deaths have been observed this year. Manatees congregate in the winter months in the Florida Power and Light Riviera Beach power plant discharge canal and surrounding waters. The warm waters there are a refuge. Each year their numbers fluctuate according to the weather conditions. In warmer years fewer numbers are observed, and the totals range from a maximum one-day count of 60 in 1983-84, to 277 in 1987-88. The proposed rule is reasonably expected to fulfill the purpose of protecting the manatee. Prohibiting motorboat traffic in the limited area immediately in and surrounding the discharge canal will not only prevent deaths and harassment in that area, but will also keep the motorboats from scattering the animals into the busier, highly trafficked area further east and in the channel of the Intracoastal Waterway.
Findings Of Fact Respondent, Department of Community Affairs, is the state land planning agency charged with the responsibility of administering the provisions of Chapter 380, Florida Statutes, and the regulations promulgated thereunder. The Department has the authority to appeal to the Florida Land and Water Adjudicatory Commission any development order issued in an area of critical state concern pursuant to Sections 380.031(18), 380.032, and 380.07, Florida Statutes. At all times pertinent to this proceeding and to DOAH Case Number 93- 7165DRI, Petitioner, Fred Snowman, owned the real property known as Lot 75, Matecumbe Ocean Beach subdivision, Lower Matecumbe Key, in Monroe County, Florida (the subject property). A building permit issued by Monroe County, described below, for this property was the subject of DOAH Case Number 93- 7165DRI (the underlying proceeding.) The lot is approximately 100 feet wide and, at different points, between 200 and 225 feet deep. The subject property is bounded on the landward side by U.S. 1 and fronts the Atlantic Ocean in an area known as Matecumbe Beach. Matecumbe Beach is a known resting and nesting habitat for marine turtles. This building permit constituted a development order on property within the Florida Keys Area of Critical State Concern. On September 30, 1993, Monroe County issued to Mr. Snowman, as the owner and general contractor, building permit number 9330008850, which authorized the construction on the subject property of a single-family residence containing 2,472 square feet of heated and cooled area, 1,568 square feet of porches, 1,435 square feet of storage enclosure below base flood elevation, and a swimming pool. The authorized construction was to be consistent with the building site plan, which was also approved by Monroe County. On November 18, 1993, the Department timely appealed the subject building permit to the Florida Land and Water Adjudicatory Commission (FLWAC) pursuant to Section 380.07, Florida Statutes. FLWAC referred the matter to the Division of Administrative Hearings where it was assigned DOAH Case Number 93- 7165DRI. A formal hearing was conducted in DOAH Case Number 93-7165DRI in Key West, Florida, on June 30, 1994. Following the formal hearing, the parties were afforded the opportunity to file post-hearing submittals. Thereafter, a recommended order was entered which recommended that FLWAC enter a final order that dismisses the Department's appeal. After the entry of the recommended order, the Department voluntarily dismissed its appeal. FLWAC subsequently entered a final order of dismissal. Petitioner, Fred Snowman, was the prevailing party in DOAH Case Number 93-7165DRI. SMALL BUSINESS PARTY The issue as to whether Petitioner is a "small business party" as defined by Section 57.111(3)(d), Florida Statutes, was disputed by the Department in this proceeding. The parties stipulated that Mr. Snowman meets the remaining criteria contained in Section 57.111, Florida Statutes, for an award of attorney's fees and costs. The following testimony elicited by Petitioner's counsel of the Petitioner was the sole evidence pertaining to the number of employees of the Petitioner: Could you tell us a little bit about your business? What's the nature of your business? Primarily I'm a speculation - spec builder and general contractor in the Florida Keys, and have been since 1973. Q. How many employees do you maintain on a regular basis? A. I mainly have subcontractors. Occasionally when I have a job, I hire for that particular job. But I'm the sole proprietor and I'm the employee. (Transcript, page 9, lines 12-22.) While the foregoing testimony establishes that as of May 15, 1995, Petitioner was the sole proprietor and sole employee of his business, it does not establish that Petitioner had fewer than 25 employees in 1993 when the Department initiated its actions against him. 1/ The following testimony elicited by Petitioner's counsel of the Petitioner pertains to his net worth: Q. What is your net worth? Let me ask you this. Does your net worth exceed a million dollars? A. No. Q. Less than a million dollars? A. Yes. (Transcript, page 9, line 23 through page 10, line 3) The following testimony elicited by Respondent's counsel of the Petitioner on cross examination also pertains to his net worth: Q. When you're identifying your net worth, what exactly are you considering? A. Well, net worth is all my assets minus my liabilities. Q. All of your personal assets? A. Which are far and few between (sic) today. Q. Do you have business assets? A. No. Q. Do you own any property? A. Lot 75. Q. Any property other than Lot 75? A. I own three lots, small lots in Plantation Key. Q. Are they developed or undeveloped? A. No, they're undeveloped. Q. Do you know how much they're worth? A. They're valued at fifteen thousand per lot. Q. They're not on the water? A. Not on the water. Q. Lot 75, do you know what that property's worth? A. That property is worth about a hundred and seventy-five thousand. Q. Without the house on it? A. Without the improvements, yes. Q. How about in its improved condition? A. I would say, in the improved condition, with this home, it would be about five hundred thousand. Q. Okay. Other than the real estate, do you have any personal or business investments, stocks or -- A. No. Q. No? A. Just my condo. (Transcript, page 10, line 8 through page 11, line 13.) There was no other evidence presented as to Petitioner's net worth. While the foregoing testimony establishes that as of May 15, 1995, Petitioner had a net worth of less than two million dollars, it does not establish that his net worth was below that figure in 1993 when the Department initiated its actions against him. SUBSTANTIAL JUSTIFICATION The Department's appeal initially raised several issues. All issues in the underlying proceeding but one were voluntarily dismissed by the Department either prior to the hearing or at the hearing. The only issue litigated at the formal hearing in DOAH Case Number 93-7165DRI was the appropriate setback from the portion of the beach-berm complex located on the subject property known to serve as an active nesting or resting area of marine turtles. Pertinent to this proceeding, Section 9.5-345(3)(f), Monroe County Code, provides: f. No structure shall be located within fifty (50) feet of any portion of any beach-berm complex which is known to serve as an active nesting or resting area of marine turtles, terns, gulls or other birds; There was no dispute in Case 93-7165DRI that the turtle nesting setback applied to Mr. Snowman's property. The dispute was how to apply the setback. There was a bona fide factual dispute as to the extent of the beach berm complex on the subject property that should be considered to be "beach berm complex which is known to serve as an active nesting or resting area of marine turtles" within the meaning of the setback ordinance. The Department established that it followed its standard procedures in deciding to appeal the subject development order. The Department maintains a field staff in the Florida Keys that routinely reviews development orders issued by Monroe County for consistency with the land development regulations, the Monroe County comprehensive plan, and Chapters 163 and 380, Florida Statutes. The permit package typically reviewed, and reviewed in this case, includes the permit, a permit conditions sheet, surveys, and site plans. The Department staff usually reviews a biological survey or habitat evaluation index, reviews the County's entire file, reviews aerial photographs and conducts a field assessment. In this case, the Department also looked at records of the Department of Natural Resources and of the Save A Turtle volunteer environmental group. In this case, the Department conducted a field assessment of Mr. Snowman's lot and measured the point it considered to be the landward extent of the turtle nesting setback line. Kate Edgerton, an experienced biologist employed by the Department, measured the point the Department asserted was the landward extent of the turtle nesting setback line. Ms. Edgerton made a good faith assessment of the beach berm complex and considered the property to contain one beach berm complex. (Transcript, DOAH Case 93-7165DRI, page 166, line 17.) Ms. Edgerton testified in the underlying proceeding that she considered herself bound by the definitions in the Monroe County land use regulations and that she believed herself to be applying the pertinent definition when she measured the setback line. (Transcript, DOAH Case 93- 7165DRI, page 163, lines 20-23.) Following field staff review, a report is prepared and forwarded to Tallahassee for review by additonal staff, including the Department's administrator of the critical state concern program. Department staff in Tallahassee review the field staff report and participate in formulating a recommendation as to whether to appeal the permit. The appeal decision is then made either by the Department Division Director or by the agency head. Each material step in the Department's customary practice of reviewing permits was followed in reviewing the subject permit. Section 9.5-4(B-3), Monroe County Code, contains the following definition of the term "beach berm" that was found to be pertinent to the underlying proceeding: (B-3) "Beach berm" means a bare, sandy shore- line with a mound or ridge of unconsolidated sand that is immediately landward of, and usually parallel to, the shoreline and beach. The sand is calcareous material that is the remains of marine organisms such as corals, algae and molluscs. The berm may include forested, coastal ridges and may be colonized by hammock vegetation. The term "berm" is identified in the Monroe County comprehensive plan as . . . a mound or ridge of unconsolidated sand that is immediately landward of, and usually parallel to, the shoreline and beach. A berm is higher in elevation than both the beach and the area landward of the berm. At the formal hearing in the underlying appeal, there was conflicting evidence as to the extent of the beach berm complex on the subject property. The Recommended Order found that there were two distinct ridges located on the subject property. The issue of whether both ridges could be considered part of the "beach berm complex" was one of first impression. Succinctly stated, it was the position of the Department in the underlying appeal that both ridges were in an area of potential habitat on a beach that is known habitat and it asserted the position that both ridges should be considered to be one beach berm complex. The Department asserted the position that the setback should be measured from the landward extent of the second ridge (the more landward of the two ridges). Monroe County had measured the setback from the landward extent of the first ridge. Mr. Snowman agreed with the County's determination of the setback. Mr. Snowman presented evidence that the County had, for several years, applied the setback from the landward extent of the first ridge and argued that, based on the foregoing definitions each ridge should be considered to be a separate beach berm, but that only the first should be considered to be a beach berm. The Department presented evidence that the County had applied the setback provision in an inconsistent manner by measuring from the crest of berms in some cases and measuring from the landward extent of berms in other occasions. The Recommended Order rejected the Department's position and concluded that the definition of "beach berm" contained in Section 9.5-4(B-3), Monroe County Code, and the description of "berm" in the comprehensive plan were unambiguous. Although the Department argued that other provisions of the code and comprehensive plan supported their construction of the setback requirement, it was concluded that the issues should be resolved based on the unambiguous definition of "beach berm". It was also concluded that no deference should be afforded the Department's construction of the term "beach berm" because there is a plain and unambiguous definition of the term that is a part of the Monroe County Code. It was observed that "[w]hile a greater setback may better serve the goals of the comprehensive plan, as argued by the Department, the imposition of a greater setback requirement should come from a change in the Monroe County Code." This observation was made because the Department had found support for its interpretation of the setback requirement from other parts of the code and comprehensive plan. This case involved bona fide disputed issues of material fact and legal issues that were of first impression. It is found that those issues, although resolved against the Department following the formal hearing, were of sufficient merit to substantially justified the Department's actions in initiating the underlying appeal.
The Issue The issue to be determined in these consolidated cases is whether the U.S. Army Corps of Engineers (“Corps”) and the City of Sarasota (“City”) (sometimes referred to as “the Applicants”) are entitled to the proposed joint coastal permit, public easement, and sovereign submerged lands use authorization (referred to collectively as “the Permit”) from the Department of Environmental Protection (“DEP”) and the Trustees of the Internal Improvement Trust Fund to dredge sand from Big Sarasota Pass and its ebb shoal and place the sand on the shoreline of Lido Key.
Findings Of Fact The Parties Petitioner Siesta Key Association, Inc. is a Florida Not for Profit Corporation, with its principal place of business in Sarasota. The organization has approximately 1,425 members and represents the interests of those who use and enjoy Siesta Key’s beach and waters. A substantial number of its members have substantial interests in the use of the beach and adjacent waters. Petitioner Michael S. Holderness is a resident and property owner on Siesta Key. Mr. Holderness has substantial interests in the protection of his property and the use of the beach at Siesta Key and adjacent waters. Petitioner Save Our Siesta Sands 2, Inc. is a Florida Not For Profit Corporation, with its principal place of business in Sarasota. The organization has over 700 members and was formed in opposition to the current dredging proposal. A substantial number of its members have substantial interests in the use of the beach at Siesta Key and adjacent waters. Petitioners Peter van Roekens and Diane Erne are residents and property owners on Siesta Key. They have substantial interests in the protection of their properties and the use of the beach at Siesta Key and adjacent waters. Respondent City of Sarasota is an incorporated municipality in Sarasota County. It is a co-applicant for the Permit. Respondent Corps is the federal agency responsible for the Lido Key Hurricane and Storm Damage Reduction Project first authorized by Congress in 1970. Under this Project, the Corps has conducted periodic maintenance, inlet dredging, surveys, and bypassing to protect Lido Key’s shoreline. The Corps is a co-applicant for the Permit. Respondent DEP is the Florida agency having the power and duty to protect Florida’s air and water resources and to administer and enforce the provisions of chapters 161, 373, and 403, Florida Statutes, and rules promulgated thereunder in Titles 62 and 62B of the Florida Administrative Code, which pertain to the permitting of construction activities in the coastal zone and in surface waters of the state. DEP acts as staff to the Board of Trustees of the Internal Improvement Trust Fund. Intervenor Lido Key Residents Association is a Florida Not for Profit Corporation incorporated in 1980 and with its principal place of business in Sarasota. The organization represents the interests of regular users of Lido Key Beach. A substantial number of its members have substantial interests in the use of the beach at Lido Key and adjacent waters. The Project Area Lido Key is a 2.6-mile-long, manmade barrier island constructed in the 1920s, located on the Gulf of Mexico and within the City of Sarasota. North of Lido Key is New Pass, a navigation channel that separates Lido Key from Longboat Key. South of Lido Key is Big Sarasota Pass and the ebb shoal of the pass. Further south is Siesta Key, a natural barrier island. Sediment Transport In the project area, sand generally drifts along the various shorelines from north to south. There can be sand drift to the north during some storm events, currents, and tides, but the net sand drift is to the south. It is sometimes called “downdrift.” Whatever downdrift conditions existed 100 years ago, they were substantially modified by the creation of Lido Key. For decades, the shoreline of Lido Key has been eroding. Since 1964, the Corps has periodically dredged New Pass to renourish the shoreline of Lido Key. The City has also used offshore sand to renourish Lido Key. These renourishment projects have not prevented relatively rapid erosion of the shoreline. A 2.4-mile-long segment of the shoreline of Lido Key has been designated by DEP as “critically eroded.” The Big Sarasota Pass ebb shoal has been growing and now has a volume of about 23 million cubic yards (“cy”) of sand. The growth of the ebb shoal is attributable to the renourishment projects that have placed over a million cy of sand on Lido Key and Longboat Key. The growth of the ebb shoal has likely been a factor in the southward migration of the main ebb channel of Big Sarasota Pass, closer to the northern shoreline of Siesta Key. Most of the west-facing shoreline at Siesta Key has experienced significant accretion. It is unusually wide for a Florida beach. It was named the best (“#1”) beach in the United States by “Dr. Beach,” Dr. Steven Leatherman, for 2011 and 2017. The Project The federally-authorized Lido Key Hurricane and Storm Damage Reduction Project includes the use of New Pass as a supplemental sand source for renourishing Lido Key. However, the use of New Pass is the subject of separate DEP permitting. The project at issue in this proceeding only involves the renourishment of Lido Key and is named “Lido Key Beach Renourishment and Groins.” The Applicants conducted a study of the ebb shoal to determine whether it could be used as a permanent sand source to renourish Lido Key. The study consisted of an environmental feasibility study and an inlet management program for Big Sarasota Pass and New Pass with alternative solutions. The application for the Permit was a response to this study. The proposed sand source or borrow areas are three dredge “cuts.” Cuts B and D are within the ebb shoal. Cut C extends through the ebb shoal and partly into Big Sarasota Pass. Cut C generally follows an existing “flood marginal channel.” The sand from the cuts would be placed along the central and southern 1.6 miles of Lido Key to fill a beach “template.” The design width of the renourished beach would be 80 feet. The initial placement would be wider than 80 feet to account for erosion. The Permit would have a duration of 15 years. The Applicants’ intent is to initially place 950,000 cy of sand on Lido Key. After the initial renourishment, sand would be dredged from one or more of the three designated cuts about every five years to replace the sand that eroded away, and would probably be on the scale of about 500,000 cy. The numerical modeling of the proposed project assumed the removal of up to 1.3 million cy of sand from the three cuts. One of DEP’s witnesses testified that the Permit authorizes the removal of up to 1.732 million cy of sand. The record does not support that testimony. The Applicants did not model the effects of dredging 1.732 million cy of sand from the ebb shoal and pass. There is insufficient evidence in the record to support an authorization to remove more than 1.3 million cy of sand. Although the total volume of sand in the three cuts is 1.732 million cy, it is reasonable for the dimensions of the cuts and the proposed easement that is based on these dimensions to contain more material than is authorized to be removed, so as to provide a margin to account for less-than-perfect dredging operations. Therefore, it is found that the Permit authorizes up to 1.3 million cy of sand to be removed from the designated borrow areas. The findings of fact and conclusions of law in this Recommended Order that address the expected impacts of the proposed project are based on this finding. The Permit also authorizes the construction of two rubble mound groins at the southern end of Lido Key to stabilize the beach and lengthen the time between renourishment events. The groins are designed to be semi-permeable so that they “leak” sand. There are no seagrasses in the renourishment area and mostly scattered and thin patches of seagrass near the dredge cuts. The Permit requires mitigation for the potential direct impacts to 1.68 acres of seagrasses. To offset these impacts, the Applicants propose to create 2.9 acres of seagrass habitat. The seagrass habitat would be established at the Rookery at Perico Seagrass Mitigation Basin in Manatee County, about 16 miles north of Big Sarasota Pass. The Permit incorporates the recommendations of the Florida Fish and Wildlife Conservation Commission regarding protections for turtles, nesting shorebirds, and manatees. The Permit requires regular monitoring to assess the effects of the project, and requires appropriate modifications if the project does not meet performance expectations. Project Engineering The Corps’ engineering analysis involved three elements: evaluating the historical context and the human influences on the regional system, developing a sediment budget, and using numerical modeling to analyze erosion and accretion trends near the project site. A principal objective of the engineering design for the borrow areas, sand placement, and groins was to avoid adverse effects on downdrift, especially downdrift to Siesta Key. The Corps developed a sediment budget for the “no action” and post-project scenarios. A sediment budget is a tool used to account for the sediment entering and leaving a geographic study area. The sediment budgets developed by the Corps are based on sound science and they are reliable for the purposes for which they were used. The post-project sediment budget shows there would be minimal or no loss of sediment transport to Siesta Key. Petitioners did not prepare a sediment budget to support their theory of adverse impact to Siesta Key. Petitioners object to the engineering materials in the Permit application because they were not certified by a Florida registered professional engineer. DEP does not require a Florida professional engineer’s certification for engineering work submitted by the Corps. As explained in the Conclusions of Law, Florida cannot impose licensing conditions on federal engineers. Ebb Shoal Equilibrium Petitioners’ witness, Dr. Walton, developed a formula to estimate ebb shoal volume equilibrium, or the size that an ebb shoal will tend to reach and maintain, taking into account bathymetry, wave energy, tides, adjacent shorelines, and related factors. In an article entitled “Use of Outer Bars of Inlets as Sources of Beach Nourishment Material,” Dr. Walton calculated the ebb shoal equilibrium volume for the Big Sarasota Pass ebb shoal as between 6 and 10 million cy of sand. The ebb shoal has been growing and is now about 23 million cy of sand, which is well in excess of its probable equilibrium volume. The volume of sand proposed to be removed from the ebb shoal is only about six percent of the overall ebb shoal volume. Dr. Walton’s study of the use of ebb shoals as sand sources for renourishment projects supports the efficacy of the proposed project. Modeling Morphological Trends The Corps used a combined hydrodynamic and sediment transport computer model called the Coastal Modeling System, Version 4 (“CMS”) to analyze the probable effects of the proposed project. The CMS model was specifically developed to represent tidal inlet processes. It has been used by the Corps to analyze a number of coastal projects. Dr. Walton opined that the CMS model was inappropriate for analyzing this project because it is a two-dimensional model that is incapable of accounting for all types of currents and waves. However, a two-dimensional model is appropriate for a shallow and well-mixed system like Big Sarasota Pass. Dr. Walton’s lack of experience with the CMS model and with any three-dimensional sediment transport model reduced the weight of his testimony on this point. Petitioners contend that the CMS model was not properly calibrated or verified. Calibration involves adjustments to a model so that its predictions are in line with known conditions. Verification is the test of a model’s ability to predict a different set of known conditions. For calibrating the hydrodynamic portion of the model, the Corps used measurements of water levels and currents collected in 2006. The model showed a 90-percent correlation with water surface elevation and 87-percent correlation to velocity. Dr. Walton believes a model should exhibit a 95-percent correlation for calibration. However, that opinion is not generally accepted in the modeling community. Model verification, as described by Dr. Walton, is generally desirable for all types of modeling, but not always practical for some types of modeling. A second set of field data is not always available or practical to produce for a verification step. In this case, there was only one set of sea floor elevations available for verification of the CMS model. It is the practice of DEP in the permitting process to accept and consider sediment transport modeling results that have not been verified in the manner described by Dr. Walton. The Corps described a second calibration of the CMS model, or “test of model skill,” as an evaluation of how well the CMS model’s sediment transport predictions (morphological changes) compared to Light Detection and Ranging (“LIDAR”) data collected in 2004. The CMS model successfully reproduced the patterns of erosion and sediment deposition within the area of focus. Petitioners’ expert, Dr. Luther, testified that, over the model domain, the CMS model predictions differed substantially from LIDAR data and believes the discrepancies between the model’s predictions and the LIDAR data make the model’s predictions unreliable. Modeling sediment transport is a relatively new tool for evaluating the potential impacts of a beach renourishment project. Renourishment projects have been planned, permitted, and carried out for decades without the use of sediment transport models. Now, modeling is being used to add information to the decision-making process. The modeling does not replace other information, such as historical data, surveys, and sediment budgets, which were heretofore used without modeling to make permit decisions. Sediment transport is a complex process involving many highly variable influences. It is difficult to predict where all the grains of sand will go. Sediment transport modeling has not advanced to the point which allows it to predict with precision the topography of the sea floor at thousands of LIDAR points. However, the CMS model is still useful to coastal engineers for describing expected trends of accretion and erosion in areas of interest. This was demonstrated by the model’s accurate replication of known features of the Big Sarasota Pass and ebb shoal, such as the flood marginal channels and the bypassing bars. The CMS model’s ability to predict morphological trends assisted the Applicants and DEP to compare the expected impacts associated with alternative borrow locations on the ebb shoal and pass, wave characteristics, and sediment transport pathways. Together with other data and analyses, the results of the CMS model support a finding that the proposed dredging and renourishment would not cause significant adverse impacts. The Applicants extensively analyzed sediment transport pathways and the effects of alternative borrow areas on sediment transport to Siesta Key. Petitioners’ hypothesis is not supported by engineering studies of equivalent weight. The more persuasive evidence indicates that sediment transport to downdrift beaches would not be reduced and might even be increased because sediment now locked in the ebb shoal would reenter the sediment transport pathways. In addition, the proposed dredging may halt the southward migration of the main ebb channel of Big Sarasota Pass, and thereby reduce erosive forces on the interior shoreline of north Siesta Key. Wave Energy Petitioners assert that the proposed dredging would result in increased wave energy on Siesta Key because the diminished ebb shoal would no longer serve as a natural buffer against wave energy from storms. They conducted no studies or calculations to support this assertion. Because the proposed dredging would remove a small percentage of the total ebb shoal volume, the ebb shoal would remain a protective barrier for Siesta Key. Wave energy reaching the shorelines along Big Sarasota Pass or within Sarasota Bay would continue to be substantially reduced by the ebb shoal. The predicted increase in wave energy that would occur as a result of the project could increase the choppiness of waters, but would not materially increase the potential for wave-related erosion. Petitioners conducted no studies and made no calculations of their own to support their allegation that the project would significantly increase the potential for damage to property or structures on Siesta Key due to increased wave energy. To the extent that Petitioners’ expert coastal engineer opined otherwise, it was an educated guess and insufficient to rebut the Applicants’ prima facie case on the subject of wave energy. Groins Petitioners contend that the two proposed groins would adversely impact the beaches of Siesta Key because the groins would capture sand that would otherwise drift south and benefit Siesta Key. However, the preponderance of the evidence shows the groins would not extend into or obstruct the sand “stream” waterward of the renourished beach. The historic use of groins to capture downdrift resulted in adverse impacts to adjacent beaches. However, the use of groins in conjunction with beach renourishment to stabilize a renourished beach and without obstructing downdrift is an accepted practice in coastal engineering. The proposed groins would not obstruct longshore sediment transport and, therefore, would not interfere with downdrift to Siesta Key. Public Interest - General Section 373.414(1) requires an applicant to provide reasonable assurance that state water quality standards will not be violated, and reasonable assurance that a proposed activity is not contrary to the public interest. However, if the proposed activity significantly degrades or is within an Outstanding Florida Water (“OFW”), the applicant must provide reasonable assurance that the proposed activity will be clearly in the public interest. Sarasota Bay, including Big Sarasota Pass and portions of Lido Key, have been designated as an OFW. Therefore, the Applicants must demonstrate that the proposed project is clearly in the public interest. In determining whether an activity is clearly in the public interest, section 373.414(1)(a) requires DEP to consider and balance seven factors: Whether the activity will adversely affect the public health, safety, or welfare or the property of others; Whether the activity will adversely affect the conservation of fish and wildlife, including endangered or threatened species, or their habitats; Whether the activity will adversely affect navigation or the flow of water or cause harmful erosion or shoaling; Whether the activity will adversely affect the fishing or recreational values or marine productivity in the vicinity of the activity; Whether the activity will be of a temporary or permanent nature; Whether the activity will adversely affect or will enhance significant historical and archaeological resources under the provisions of section 267.061; and The current condition and relative value of functions being performed by areas affected by the proposed activity. DEP determined that the project is clearly in the public interest because it would improve public safety by providing protection to Lido Key upland structures from storm damage and flooding, protect and enhance wildlife habitat, and provide beach-related recreational opportunities; and it would create these public benefits without causing adverse impacts. Public Interest - Safety Petitioners contend that the proposed project would adversely affect public health, safety, welfare, or the property of others because it would interrupt downdrift and substantially reduce the storm protection provided by the ebb shoal. As found above, the preponderance of the evidence does not support this contention. Public Interest - Conservation of Fish and Wildlife Petitioners contend that the proposed project would adversely affect the conservation of fish and wildlife, including endangered or threatened species. The Permit application materials provided evidence that the proposed project would have no effects, or only minimal temporary effects, on water quality, temperature, salinity, nutrients, turbidity, habitat, and other environmental factors. That was sufficient as a prima facie showing that the project would not adversely affect the conservation of fish and wildlife because, if environmental factors are not changed, it logically follows that there should be no adverse impacts to fish and wildlife. Therefore, as explained in the Conclusions of Law, the burden shifted to Petitioners to present evidence to show that adverse effects to fish and wildlife would occur. It was not enough for Petitioners to simply contend that certain fish species were not adequately addressed in the application materials. With the exception of Dr. Gilmore’s field investigation related to the spotted seatrout, Petitioners conducted no studies or field work of their own to support their allegations of adverse impacts to fish and wildlife. Dr. Gilmore discovered that spotted seatrout were spawning in Big Sarasota Pass. Such spawning sites are not common, are used repeatedly, and are important to the conservation of the species. Spotted seatrout spawn from April through September. The record does not show that the Florida Fish and Wildlife Conservation Commission, the U.S. Fish and Wildlife Service, or the National Marine Fisheries Service were aware that Big Sarasota Pass was a spawning area for spotted seatrout, or considered this fact when commenting on the project. The spotted seatrout is not a threatened or endangered species, but DEP is required to consider and prevent adverse impacts to non-listed fish species, as well as recreational fishing and marine productivity. If the proposed project would destroy a spotted seatrout spawning area, that is a strong negative in the balancing of public interest factors. The Applicants do not propose mitigation for adverse impacts to spotted seatrout spawning. Seagrass sites close to the spawning area are used by post-larval spotted seatrout for refuge. The likely seagrass nursery sites for seatrout spawning in Big Sarasota Pass are depicted in SOSS2 Exhibit 77. The proposed seagrass mitigation at the Perico Rookery Seagrass Mitigation Basin, over 16 miles away, would not offset a loss of this refuge function because it is not suitable as a refuge for post-larval spotted seatrout. The spawning season for spotted seatrout occurs during the same months as turtle nesting season, and DEP argued that the turtle protection conditions in the Permit to limit lighting and prohibit nighttime work, would also prevent adverse impacts to the spotted seatrout. However, spotted seatrout spawning is also threatened by turbidity and sedimentation in the spawning area and adjacent seagrasses. The spotted seatrout spawning area is in the area where dredge Cut B is located. If Cut B were dredged during the spawning season, it would likely disrupt or destroy the spawning site. Reasonable assurance that the proposed project would not disrupt or destroy the spawning site requires that Cut B not be dredged during the spawning season. Seagrasses that are likely to provide refuge to post- larval seatrout are near the most eastern 1,200 feet of Cut C. Reasonable assurance that the proposed project would not disrupt or destroy the refuge function requires that the most eastern 1,200 feet of cut C not be dredged during the spawning season. In summary, the proposed project would adversely affect the conservation of fish and wildlife unless dredging was restricted during the spotted seatrout spawning season, as described above. Public Interest – Navigation, Flow of Water, and Erosion Petitioners contend that the proposed project would adversely affect navigation, the flow of water, and would cause harmful erosion to Siesta Key, but Petitioners conducted no studies or calculations to support this assertion. The preponderance of the evidence shows that no such adverse impacts would occur. Public Interest – Recreational Values Petitioners contend that the proposed project would adversely affect fisheries and associated recreation because of harm to spotted seatrout and other fish species. As found above, the preponderance of the evidence shows the project would adversely affect the spotted seatrout, an important recreational fish species, unless dredging was restricted during the spawning season. Public Interest - Value of Functions Petitioners contend that the proposed project would adversely affect the current condition and relative value of functions being performed by areas affected by the proposed project because dynamic inlet system would be disrupted. As found above, the preponderance of the evidence shows the project would not adversely affect the coastal system. However, it would adversely affect the spotted seatrout spawning and refuge functions provided by Big Sarasota Pass unless dredging was restricted during the spawning season. Mitigation If a balancing of the public interest factors in section 373.414(1)(a) results in a determination that a proposed project is not in the public interest, section 373.414(1)(b) provides that DEP must consider mitigation offered to offset the adverse impacts. Although the Perico Rookery at Seagrass Mitigation Basin is within the OFW and the same drainage basin, it does not fully offset the adverse impacts likely to be caused by the proposed project. The mitigation would not offset the loss of spotted seatrout spawning and refuge functions. The mitigation for the loss of spotted seatrout spawning and refuge functions is unnecessary if the impacts are avoided by restricting dredging during the spawning season as described above. Design Modifications Petitioners contend that the Applicants did not evaluate the alternative of taking sand from offshore borrow areas for the renourishment. The record shows otherwise. Furthermore, as explained in the Conclusions of Law, the Applicants were not required to address design modifications other than alternative locations for taking sand from the ebb shoal and Big Sarasota Pass. Consistency with the Coastal Zone Management Program Petitioners contend that DEP failed to properly review the Permit for consistency with the Florida Coastal Zone Management Program (“FCZMP”), because DEP failed to obtain an affirmative statement from Sarasota County that the proposed project is consistent with the Sarasota County Comprehensive Plan. The State Clearinghouse is an office within DEP that coordinates the review of coastal permit applications by numerous agencies for consistency with the FCZMP. It is the practice of the State Clearinghouse to treat a lack of comment by an agency as a determination of consistency by the agency. With respect to this particular project, the State Clearinghouse provided a copy of the joint coastal permit application to the Southwest Florida Regional Planning Council (“SWFRPC”) for comments regarding consistency with local government comprehensive plans. SWFRPC submitted no comments. In a letter dated June 26, 2015, the State Clearinghouse reported to the Corps that “at this stage, the proposed federal action is consistent with the [FCZMP].” In a written “peer review” of the proposed project produced by the Sarasota Environmental Planning Department in October 2015, some concerns were expressed, but no mention was made of inconsistency with the Sarasota County Comprehensive Plan. Sarasota County sent a letter to DEP, dated August 24, 2016, in which it requested that the Corps prepare an Environmental Impact Statement (“EIS”) for the project. Sarasota County did not indicate in its letter to DEP that the proposed project is inconsistent with any policy of the Sarasota County Comprehensive Plan. Petitioners assert that the proposed project would be inconsistent with an environmental policy of the Sarasota County Comprehensive Plan that Petitioners interpret as prohibiting the proposed dredging. The record contains no evidence that Sarasota County believes the proposed project is inconsistent with this particular policy or any other policy of its comprehensive plan.
Recommendation Based on the foregoing Findings of Fact and Conclusions of Law, it is RECOMMENDED that DEP issue a final order approving the proposed agency actions, but only if the joint coastal permit is modified to prohibit dredging operations in Cut B and the most eastern 1,200 feet of Cut C during April through September. If this modification is not made, it is recommended that the proposed agency actions be DENIED; and The joint coastal permit be modified to clarify that it authorizes the removal of up to 1.3 million cy of sand. DONE AND ENTERED this 8th day of May, 2018, in Tallahassee, Leon County, Florida. S BRAM D. E. CANTER Administrative Law Judge Division of Administrative Hearings The DeSoto Building 1230 Apalachee Parkway Tallahassee, Florida 32399-3060 (850) 488-9675 Fax Filing (850) 921-6847 www.doah.state.fl.us Filed with the Clerk of the Division of Administrative Hearings this 8th day of May, 2018. COPIES FURNISHED: Kirk Sanders White, Esquire Florida Department of Environmental Protection Mail Station 35 3900 Commonwealth Boulevard Tallahassee, Florida 32399-3000 (eServed) Kent Safriet, Esquire Hopping Green & Sams, P.A. Post Office Box 6526 Tallahassee, Florida 32314 (eServed) Alexandrea Davis Shaw, Esquire City of Sarasota Room 100A 1565 1st Street Sarasota, Florida 34236 John R. Herin, Jr., Esquire Gray Robinson, P.A. Suite 1000 401 East Las Olas Boulevard Fort Lauderdale, Florida 33301 (eServed) Eric P. Summa U.S. Army Corps of Engineers Post Office Box 4970 Jacksonville, Florida 32232 Martha Collins, Esquire Collins Law Group 1110 North Florida Avenue Tampa, Florida 33602 (eServed) Thomas W. Reese, Esquire 2951 61st Avenue South St. Petersburg, Florida 33712-4539 (eServed) Richard Green, Esquire Lewis, Longman & Walker, P.A. Suite 501-S 100 Second Avenue South St. Petersburg, Florida 33701 (eServed) Kevin S. Hennessy, Esquire Lewis, Longman & Walker, P.A. Suite 501-S 100 Second Avenue South St. Petersburg, Florida 33701 (eServed) Christopher Lambert, Esquire United States Army Corps of Engineers 701 San Marco Boulevard Jacksonville, Florida 32207 (eServed) Lea Crandall, Agency Clerk Department of Environmental Protection Douglas Building, Mail Station 35 3900 Commonwealth Boulevard Tallahassee, Florida 32399-3000 (eServed) Noah Valenstein, Secretary Department of Environmental Protection Douglas Building 3900 Commonwealth Boulevard Tallahassee, Florida 32399-3000 (eServed) Robert A. Williams, General Counsel Department of Environmental Protection Legal Department, Suite 1051-J Douglas Building, Mail Station 35 3900 Commonwealth Boulevard Tallahassee, Florida 32399-3000 (eServed)
The Issue Whether 1800 Atlantic Developers is entitled to a DER fill permit and water quality certification for the creation of a sand beach, approximately 500' long X 100' wide, requiring placement of 2,620 cubic yards of fill, 2,200 yards of which would be waterward of mean highwater (MHW), off Key West, Florida.
Findings Of Fact The Proposal By its initial application in April 1985, 1800 Atlantic proposed to place 4,100 cubic yards of fill (manufactured sand) along approximately 460 feet of eroded shoreline facing the Atlantic Ocean and fronting its 168-unit condominium (still under construction) in Key West, Florida. In connection with this project, 1800 Atlantic also proposed a 200 foot jetty at the east property line; a second and smaller jetty (if needed) at the west property line; a 400 foot long (10' high and 20' wide) fishing pier on the western property line; and a 50 x 50 foot art display platform seaward of the new beach. Approximately one and one-half acres would be filled of which 0.9 acres would be below the MHW line. The "proposed use" for the new beach was designated "private multi- dwelling." By affidavit Atlantic 1800 certified that it was record owner, lessee, or easement holder of the project site. 1/ (Atl.Exh.1) On May 7, 1985, 1800 Atlantic revised its application by submitting a new plan view to Teryl Kranzer, DER's field biologist. The modification tapered the beach fill into the shoreline toward the western property line and reduced the size of the westernmost jetty. (Atl.Exh.4) On May 10, 1985, DER sent a "Completeness Summary" to 1800 Atlantic, asking for additional information to complete the application. (DER Exh.5) On June 18, 1985, 1800 Atlantic responded to DER's Completeness Summary by submitting the additional requested information to Douglas L. Fry, Environmental Supervisor of DER's South Florida District. Revised drawings were submitted eliminating the east jetty from the project. The volume of beach fill material was indicated as 2620 cubic yards--420 above MHW, and 2200 below MHW. (Atl.Exh.5) On July 1, 1985, DER sent another Completeness Summary to 1800 At1antic seeking still more information to make the application complete. (DER Exh.6) t 20, 1985, 1800 Atlantic supplied the additional information and modified its proposal by eliminating the art display platforms the fishing pier and the west jetty. The beach fill was also modified by tapering the fill from the corner of the existing seawall at the east property line into the existing shoreline on the west property line. Total beach fill volume was shown as 2700 cubic yards--300 above MHW and 2200 below. The proposed dry beach extended 70 feet seaward (the June 18, 1985 submittal showed an 80 foot wide beach) and the toe of the fill extended 100 feet seaward of the MHW line. In response to DER's inquiry about public access, Edward Swakon, 1800 Atlantic's consulting engineer, stated: will be no provision made to assure perpetual public access to the project area. As we previously stated, the applicant has no intentions of prohibiting public access, however, you should be aware that the appli- cant is the owner of the submerged land and that no guaranteed public access is assured. (Atl.Exh.7) Mr. Swakon, on behalf of 1800 Atlantic, then addressed each of the permitting criteria of Section 403.918(2)(a), Florida Statutes (1985), though contending that they did not apply to the project: project will not affect the public health, safety, welfare or the property of others. On the contrary, as a result of this project the tax base of the City of Key West will be improved and therefore benefit the residents of the community. The beach fill will provide an added degree of protection to the upland development, thereby reducing the potential claims to the Federal Flood Insur- ance Program. In addition, the project provides a beach for 168 residents of the upland development and their many guests. This reduces the impact on the already over crowded public beaches in Key West. project will not adversely effect the conservation of fish and wildlife within the immediate vicinity. The area to be filled is devoid of significant vegetation. It is our opinion that the placement of this fill would result in an imperceptible impact to the marine resources. There are no endan- gered or threatened species or habitats located within the area to be filled. project will not adversely effect navigation, the flow of water or cause harmful erosion or shoaling. On the contrary, the placement of this material will improve the overall shoreline conditions. The filling will not cause any erosion or shoaling in the vicinity. the fill area is barren, it is our opinion that this project will have no impact on fishing, recreational values and/or marine productivity in the vicinity of the project. project will be permanent in nature will be no impact to historic or archeological resources. Id. t 26, 1986, DER received the August 20, 1986 submittal of 1800 Atlantic and the application became complete. r 5, 1985, the District Manager of DER's South Florida District in Fort Myers noticed his intent to deny the permit application. According to Douglas Fry, DER's supervisor of the District's dredge and fill section, the denial was based on information that he had received: I expected that the project would degrade both general water quality standards as established in the intent, including turbidity, biological integrity, transparency, other things noted as well as degradation of fish and wildlife standards as encompassed in part of the public interest requirements; I felt that the project would be contrary to the public interest. (Tr.546) the months that followed, 1800 Atlantic pursued the matter with various DER personnel, including Mr. Fry; Ms. Kranzer, the District biologist who performed the initial biological and water quality appraisal for the project; Steven J. Fox, Director of the Division of Environmental permitting, and William Hennessey, Deputy Director, both located in Tallahassee and supervisors of district permitting operations 2/ and Kenneth L. Echternacht, a DER hydrographic engineer in Tallahassee. Negotiations ensued, various modifications were proposed. Ms. Kranzer, the DER field biologist who had conducted the initial environmental evaluation in May 1985, and had recommended denial in September 1985, never submitted a new report evaluating the subsequent modifications, although she did discuss changes with other DER staff members. At the time she evaluated the project, it had already been modified once--cubic yardage had been reduced; the fishing pier, art platform and both jetties had been eliminated. t of negotiations between DER and 1800 Atlantic, DER reversed its initial position and, on March 27, 1986, gave notice of its intent to issue a permit for the revised project. The proposed permit incorporated changes agreed to by 1800 Atlantic. These changes required that the waterward 1/3 of the fill volume consist of coarse sand or sand aggregate no finer than 2mm in diameter; that approximately 10 percent of the sand range in size from 2mm to 6mm in diameter; and that 1800 Atlantic conduct a seagrass monitoring program for the duration of the permit. These changes were meant to resolve DER's concern that the fill material might migrate seaward and smother offshore seagrass beds. The area below the MHW line to be covered by the fill (approximately 1/2 acre) remained the same as indicated in the last drawings submitted by 1800 Atlantic on August 20, 1985. (Atl.Exh.7) l 1985, the City (of Key West) and the Coalition (Florida Keys Citizens Coalition) timely requested an administrative hearing to challenge proposed issuance of the permit. R had announced its intention to grant the permit, Mr. Fry, DER's District environmental dredge and fill supervisor continue to have concerns about the project: . . . I did not believe that the project still was clearly in a public interest, and that I did not see that the project had been modified enough to eliminate the destruction of aquatic habitat. I was concerned that the project did not encompass any mitigation to offset those, that damage. I was concerned that we had not received reasonable assurances that the project was clearly in the public interest. I was concerned that we had not received reasonable assurances that the beach fill would stay in place, thereby contributing to future degradation, and I had experienced some concerns regarding cumulative impact. (Tr.547) These concerns prompted representatives of DER and 1800 Atlantic to meet in Tallahassee on Friday, June 20, 1986. This was three working days prior to final hearing. Neither the City nor the Coalition were aware off or invited to, the meeting. s meeting, DER and 1800 Atlantic agreed to certain additional project modifications. One addition required construction of a small terminal jetty or groin on the western end of the project to stabilize the fill and replace rocky habitat to be covered by the fill. The specifications for this groin were not subsequently calculated or submitted at hearing. 1800 Atlantic proposes to "field engineer" the groin within these parameters: It would be designed to contain the fill or it would be designed in the field when the material was in place and would be designed with specifications that the rocks really didn't come any higher than the fill itself and would be adjusted so as to allow for some movement of sediment back and forth between it so as to minimize any down drift concerns that might exist. (Tr.121) l hearing, DER and 1800 Atlantic reduced this addition to writing as one of several proposed conditions to the DER permit. These conditions, ostensibly providing precision and specificity to the project changes described at hearing, were received over objection as part of DER's post-hearing Exhibit No. 7. The particular condition describing the groin-type structure to be built at the west end of the beach fill provides in pertinent part: Prior to construction of the beach fill, the permittee shall submit approximately dimen- sioned sketches of the structure, for review, modification as necessary, and approval by [DER]. (DER Exh.7) DER and 1800 Atlantic thus propose that specifications and drawings for this coastal structure be submitted, reviewed, and approved sometime in the future, after the requested permit is issued. The need for specifications is acknowledged, yet submittal and review is put off until after a permit is issued. Hence, detailed specifications for the structure remain unknown or ill- defined; scrutiny of those specifications by the City and Coalition is threatened; APA 3/ processes are frustrated. e which DER and 1800 Atlantic agreed to at the Friday meeting was to taper the toe of the fill on the western one-half of the fill area to more closely match the contour of the existing shoreline. 1800 Atlantic's engineer sketched this change, free-hand, while testifying at final hearing. Hence, it also remains ill-defined and uncertain. Like the groin, this change was reduced to writing and received as part of DSR post-hearing Exhibit No. 7. And like the groin, before construction but after the permit is issued, 1800 Atlantic is to submit a "fully dimensioned and scaled plan view of the revised beach fill limits for review, modifications as necessary, and approval" by DER. (DER Exh.7) The procedural shortcomings of such a procedure have already been noted. e which DER and 1800 Atlantic agreed to at the Friday meeting concerned off-site mitigation. As explained at final hearing, 1800 Atlantic would purchase an upland site equal in size to the area to be covered by the proposed fill and excavate it to tidal or subtidal elevations. (The upland mitigation site could be located as far as Big Pine Key (35 miles away) or elsewhere in the Florida Keys.) If this mitigation measure could not be accomplished prior to placement of the fill, a bond to assure its performance would be posted with DER. But this mitigation measure, when later reduced to writing and received as post-hearing DER Exhibit No. 7, became something quite different. The post-hearing exhibit specified that the upland mitigation site would be at least twice the size of (not equal in size to) the proposed one-half acre fill project. Moreover, the mitigation site was to be inspected and approved by DER prior to placement of the fill. If the mitigation site was not approved prior to filling, a bond (of unknown amount) would be posted to assure purchase and the excavation. With this condition, as with those already mentioned, critical features were left to future review and approval by DER, and so placed beyond the scrutiny of the other parties to this proceeding. The specific nature and location of this mitigation site is not known; neither is the amount of the bond to be posted if filling precedes mitigation. Whether the mitigation will, in fact, offset any loss of plant, fish, and wildlife habitat eliminated by the proposed fill is, likewise, unknown. Finally, the written condition, to the extent it doubles the size of the mitigation site presented at final hearing, is rejected as an unauthorized attempt to present new and additional evidence after the close of evidentiary presentation. (DER Exh.7) s other on-site mitigation measures were agreed to at the Friday meeting. As explained at hearing, algae-covered rocks within the fill area would be moved to a non- vegetated part of the submerged land; a Halodule grass bed within the fill area would be relocated waterward of the fill area; the toe of the proposed fill would be staked prior to construction; and fill placement would occur only during periods of low tide. When later reduced to writing as a post-hearing exhibit, these conditions generally conformed to their description at final hearing. Effect of Fill Project on Fishing or Recreational Values; Navigation; Marine Productivity; and Conservation of Fish and Wildlife t site is located on the southern shoreline of Key West on a narrow strip of beach known as Rest Beach, which includes a 2900 foot shoreline between Bertha Street to the east and White Street Pier to the west. The pier, a 950-foot long solid fill structure, is located 2400 feet west of the project site. Directly west of White Street Pier is another public beach (1400 feet long) known as Higgs Beach. With the exception of the submerged lands at the project site, to which 1800 Atlantic asserts titled all of the submerged lands adjacent to Rest Beach are publicly owned. (Atl.Exh.2-I; DER Exh.4) s at the project site are part of the navigable open waters of Hawk Channel and the Straits of Florida (Atlantic Ocean), designated by DER as Class III waters. On May 8, 1985, the waters in the area of the project (within the boundaries of the Florida Keys Special Waters), were also designated (by rule) as "Outstanding Florida Waters"--thereby imposing DER's most stringent level of protection from degradation of water quality loss of fish and wildlife habitat, and reduction in marine productivity. (Rule 17-3.041(4)(i); DER Exh.4) t site is bordered on the east by Bertha Street, which ends at a seawall facing the ocean. South Roosevelt Boulevard begins at the end of Bertha Street and parallels the shoreline east of the site. A public boat ramp is located on South Roosevelt Boulevard just east of Bertha Street. Just east of the ramp is a long curving jetty or groin at the southern end of a 3350-foot long public beach known as Smathers Beach. This public beach is within a few hundred feet of the project site. (Atl.Exh.6; DER Exh.4) o the west of the project site is an undeveloped parcel of land consisting largely of mangroves separated from the ocean by a sandy berm. Although the berm has been overwashed and tidal connections have opened in the past, no tidal connection was apparent at the time of final hearing. In some places the berm may have been artificially altered west of this undeveloped wetland site. Other residential condominiums are located on uplands to the west. d directly landward to the project site is a 168-unit, four story L-shaped condominium owned and developed by 1800 Atlantic. Recreational facilities, such as a swimming pool and club house, overlook the ocean. A third wing of the condominium (parallel to and abutting Bertha Street) was still under construction in July, 1985. s not the first time a permit has been sought to create or restore a beach at the site. In 1979, the trusteeship of Eugene J. Weiss, a 1800 Atlantic's predecessor in title, applied to DER for a similar "beach restoration" permit. He proposed to place (between groins to be constructed at opposite ends of the property) 1750 cubic yards of sand waterward of MHW and 2500 cubic yards landward. The approximate area to be filled was .59 acres waterward of MHW, .80 acres landward. Curtis Kruer then an environmental specialist with DER, performed a biological and water quality appraisal of the project and recommended denial because the fill would bury vegetated benthic communities that provide habitat and nutrients to marine organisms which, in turn, become a food source for a large number of juvenile fish and shellfish. He also was concerned about the short and long-term cumulative biological effects of a number of such projects on the shoreline of Key West. In April 1982, Eugene Weiss withdrew the application. (Coalition Exh. 3) s at the project site are shallows as the bottom slopes gently seaward. At mid-tide, depths of 1.5 feet are found 100 feet seaward of the MHW line. At low tide, the entire fill area is exposed. Even at high tide, water depths in the fill area range from zero (at MHW line) to approximately two feet at the toe of the fill. Because of the shallow depths, the fill project will have no significant adverse effect on navigation. (DER Exh.4; Atl.Exh.5) f stacked but unstabilized railroad ties separates the upland area (where the condominium and associated structures are located) from the beach slope. The narrow, graveled beach slope contains a mix of sand, rock, rubble and beach plants. Several distinct zones of seawrack are found on the beach slope: Thalassia at the lower portion of the beach face and Sargassum at the base. (Atl.Exh.15, 16) t 100 feet seaward of the MHW line, which includes all of the fill area, consists of small rubble embedded with calcareous sediments. The rubble consists of chunks of limestone rock and pieces of concrete less than two feet in size. Scattered among the rubble is anthropogenic debris such as bottles, asphalt and cast iron pipe. (Tr.130) f the limestone rock and rubble found on the submerged project site are residential lag from a fill at the site prior to or during the early 1960s. The boundaries and extent of the prior fill have not been established. It appears, however, to have consisted of a mix of carbonate particles ranging from silt and clay to the rocks, rubble and coarse sand now found on the project site. The fill material on site is what remains from the earlier artificial fill. e rock and rubble in the littoral zone provide attachment sites for various green, brown, and red algae such as Laurencia, Caulerpa, Cymopolia, Digenia, Batoptiora, Padina, Halimeda, Neomeris and Congia. These algal species play a positive role in the marine environment. The near shore contains a coarse sandy-shell substrate. (DER Exh.4; Atl.Exh.16) f seagrasses grow on, and immediately seaward of, the fill site. These include Cuban shoalweed (Halodule wrightii) and turtle grass (Thalassia testudinum). Some patches of seagrass are found as close as 30 feet from the MHW line. 4/ Approximately 95 feet seaward, cuban shoalweed becomes dominant; turtle grass coverage increases as one travels seaward from the site. Some cuban shoalweed patches are dense and healthy, with blades sometimes two feet in length. There is a patch of cuban shoalweed on the eastern portion of the project site. Although 1800 Atlantic has agreed to dig-up and transplant this seagrass to unvegetated portions of its property seaward of the toe of fill, the success of such a transplanting is not assured. Unvegetated bottoms can usually be explained by environmental factors. (DER Exh.4; Atl.Exh.16) s communities play a beneficial role in the marine environment. They provide habitat, feeding, and nursery areas for aquatic organisms. They supply primary nutrients as well as perform nutrient uptake and removal functions. The proposed fill would adversely impact the seagrass communities on the site--by smothering or burying any seagrasses not successfully transplanted. Moreover, the site, once converted to sandy beach for the use of owners and guests of the adjacent condominiums, could no longer support seagrass communities. r shore zone of seagrass and algal communities, adversely impacted by the proposed fill, constitutes a productive shallow water habitat that supports a variety of juvenile fish and crustaceans. These include hares, banded tulip shells, nerites, xanthid crabs, blue crabs, lizard fish, barracuda, parrotfish, killifish, needlefish, grey snapper, sergeant major, tomtates, hermit crabs, shore crabs and blue crabs. c macrofaunal species and diverse species of crustaceans live in the sediment of the in-shore rocky algae and seagrass communities. These species include Scyphoproctus, Notomastus hemipodus, Capitella capitata, Pulliella, Capitomastus, Capitellidae, Chaetozone, Tharvz annulosus, Caulleriella, Carilleriella bioculate, Glyceridae papillosa, Axiothella, Ceratonereis, Nereis Succinea, Nereis Rava, Nereis caudata, Onuphis magna, Protoariciinae, Proscoloplos, Cirrophorus lyriformis, Hasmineira elegans, Jasmineira bilobata, Fabricia, Augeneriella, Faebicola, Minuspio, Prionospio heterobranchia, Prionospio steenstrupi, Nerinides goodbody, Brania clavata, Exogone dispar, Exogone naidina, Odontosyllis, Sphaerosyllis labyrindiophia, Streptosyillis, Typosyllis hyalina, Typosyllis regulata, Typosyllis alternata, Typosyllis prolifera, Langerhansia cornuta, Langerhansia ferrugina, Syllida bansei, Terebella turgidula, Streblosoma hartmanae, Streblosoma abranachiata, Streblosoma, Pista palmata, Arca, Chjione caniculater, Tellina iris, Melita dintata, Elasmopus, Melito, Melita nitida, Rudilembordes, Dexamine, and Erichsonella filiformis. (Coalition Exh. 6) g at the site took place as recently as June 1986. Three petite ponar samples were taken in seagrass beds 150-160 feet seaward of the shoreline; three were taken in the rubble zone just seaward of the toe of the proposed fill; and two were taken in seagrass beds off nearby Smathers Beach. As measured by the Shannon Weaver Species Diversity Index, the level of species diversity in the rock rubble just seaward of the toe of fill was 2.19; in the seagrass beds farther offshore, 4.71; and in the seagrass beds off Smathers Beach, 4.76. A diversity of 4 is in the upper range of food habitat. Although diverse species of benthic organisms are found on the site, the level of diversity is substantially less than the high levels found in the thicker seagrass immediately seaward of the project site. (Atl.Exh.16) t Beach area (including the project site), provides a valuable habitat for migratory birds, wading birds, and shore birds. It is one of the last major stretches of uninterrupted shallow water bird habitat in Key West. Ms. Francis Hamer, a local resident and bird watcher for over 40 years, visits the area regularly. One of her favorite vantage points is on White Street Pier; from there, using a telescope, she observes birds feeding and wading along the Rest Beach shoreline. Although most of the birds she sees gather at the western end of Rest Beach, she has seen sandpipers, including the least sandpiper, twelve species of herons, including the yellow crowned night heron and the blue heron in the vicinity of the project site. When asked where would one go to see Sandpipers if the Rest Beach habitat was eliminated she replied, "I don't know of any other place in Key West." (Tr.645) Ms. Kranzer, the DER biologist, and Mr. Kruer, the U.S. Army Corps of Engineers' biologist, have visited the site many times over the years and observed numerous wading and shore birds in the area. Ms. Kranzer photographed eight herons in the fill area at one time. 5/ Mr. Kruer has observed the little blue heron, the great egret, the cattle egret, the white ibis and the laughing gull, numerous shore birds. The proposed fill would adversely impact this valuable feeding ground for birds. The shallow algae and rubble zone, which supports the crabs and marine organisms which nourish bird life, would be replaced with beach sand. It is also likely that increased recreational use of the beach would drive off bird life. e many natural areas typical to the Florida Keys which, as DER and 1800 Atlantic contend, are more valuable than the project site in biological productivity, and as nursery and feeding grounds for fish, marine life, and wildlife. Nevertheless, this fact does not negate the substantial benefits which the site now provides to juvenile fish, crustacenas, benthic marine organisms, and bird life. l placement of the fill will have no impact on mobile organisms able to retreat to safer waters. Benthic and other organisms on the site which are relatively immobile would be destroyed by the fill. The number killed would be a relatively small fraction of the total of such organisms along the Key West shoreline, and their loss--alone--would not affect the marine environment to an extent which is quantifiable. Effects of the Proposed Fill on Water Quality Standards; Public Health, Safety or Welfare; Significant Historical and Archeological Resources; Endangered Species or their Habitats d project will not adversely affect public healthy safety, or welfare; significant historical and archeological resources; or endangered species or their habitats. (Neither the City nor the Coalition presented any affirmative evidence establishing adverse effect.) l the project degrade or cause violations of DER water quality standards for Outstanding Florida Waters. See Rules 17-3.051, 17-3.061, and 17- 3.121, Fla.Admin.Code. Turbidity will be minimal, since filling would take place at low tide and turbidity curtains will be used. The loss of algae at the site would not cause significant degradation of water quality. (Algae covered rocks would be moved outside the fill area.) c contends that water quality would actually be enhanced by the proposed fill. The seagrasses seaward of the site have beneficial effects on water quality, but their sediment beds are shallow. 1800 Atlantic contends that the finer particles of its fill material, dispersed by waves, would provide needed sediment to the offshore seagrass beds. This ostensible benefit is problematic. The study performed to support this contention did not sufficiently investigate or explain how seagrass beds beyond the reach of nearby beaches (and their sediment) could flourish. Dense and healthy seagrass offshore has not been shown to be endangered due to shallow sediment. It is clearly less than certain that just the right amount (too much would smother, too little would have no effect) of just the right kind of fill (only the fines are needed, not the large or coarser particles) would be delivered to offshore seagrass by natural forces. Impacts on Erosion, Shoaling and Sand Migration h and shoreline at the project site are relatively stable and in equilibrium; no greater erosion is occurring than at other unfortified shorelines in the Key West area. The coarse material and rubble that line the bottom of the site act as a "natural seawall" or armor which prevents or slows down erosion. (Tr.249) Removal of the existing rubble, as proposed, would eliminate this "natural armor." (Tr.260) e in the vicinity at the site faces south to south- southeast. This exposure is relatively windward with respect to winter storms. Gentle prevailing east to southeast winds, however, produce low-energy waves that approach the shore and generate longshore currents moving east to west. (Atl.Exh. 15) f a shallow limestone ridge offshore the Atlantic shoreline in Key West, waves reaching the shore are ordinarily well-dampened. Although subject to storm and hurricane attack by high energy waves, the southern shoreline is characterized as "low-energy." (Atl.Exh.15) vicinity of the project site on the southern shoreline, there is no natural onshore supply of sediments to beaches from offshore. The beaches at Smathers Beach and at the project site (which have been narrowed by erosion over the last 25 years) are artificial, composed of limestone fragments derived from quarries. The fill was placed at both beaches sometime prior to 1962. s have undergone gradual erosion. Fine sand and silt from the beach material is carried seaward, with no natural offshore sediment to replace it. The proposed fill will provide, at least temporarily, an added degree of protection to the upland development by widening existing upland between the condominium and the sea. It will not, however, prevent continued erosion. Over time, it too, will be dispersed by wave action and longshore drift to shorelines to the west. The fill would also temporarily stabilize the public sidewalk and street to the east of the site, currently being undermined. Protection of the public sidewalk and boat ramp from erosion, however, is part of public road maintenance duties. c has neither alleged nor shown that its upland condominium, still under construction, is endangered by erosion or high-energy wave action. Nor has it shown that there are no reasonable methods of supplying an "added degree of protection" to the upland development, methods not requiring elimination of productive habitat for fish, marine life, and wildlife. s net east-to-west longshore transport of sediment along the southern shoreline of Key West. Two groins at Smathers Beach (to the east) and the nearby public boat ramp have, to some extent, interrupted the normal longshore sand transport from the east. As a result, the effects of erosion are more pronounced on the eastern portion of the site, causing a shoreline "discontinuity." Although the proposed fill would partially eliminate this discontinuity, it has not been shown that the discontinuity is a serious problem. While it may trap floating debris, this was not a significant problem in July 1985, when Ms. Krenzer, the DER biologist, inspected the site. Moreover, the proposed groin near the west property line (to stabilize the fill material) would--in itself--add a new shore discontinuity, and may cause more discontinuity to the west if it interrupts the normal longshore movement of sand. (DER Exh.4) s finer than 200 microns tend to move in suspension, while grains finer than 40 microns cause turbidity. Grains coarser than 200 microns tend to move along the sea bottom when sufficient wave or current energy is present. Analysis of onshore and offshore sediment indicates that not much material coarser than 200 microns is moving offshore into seagrass beds seaward of the project site. Most of the material larger than 200 microns found in the seagrass beds is being produced there naturally. d that the proposed fill would migrate seaward and smother offshore seagrasses, seeks a condition (to which 1800 Atlantic has agreed) requiring that the seaward one-third of the fill volume consist of coarse sand no finer than two millimeters in diameter. The evidence is insufficient, however, to eliminate the possibility that constant wave action could gradually pulverize the coarse limestone into smaller particles that, when dispersed, could smother seagrass beds directly offshore and southwest of the site. 0 Atlantic has selected fill material with settling characteristics compatible with the existing beach material on site, placement should not cause an increase in turbidity. Although 1800 Atlantic posits that just enough of the fine sediments would migrate seaward to nourish grassbeds, leaving the coarse material to migrate westward by longshore drift, these results are not assured. Winter storms and high energy waves could remove and disperse even coarse material seaward or pulverize it into smaller particles for wider dispersion. Dispersion of the coarser sand to the west by longshore drift could result in shoaling which would block periodic tidal connections which occur between the sea and the mangrove covered wetlands. n structure toward the west boundary--designed to stabilize and hold the fill material in place--may contribute to erosion to the west by interrupting natural longshore transport. The wisdom of such an artificial structure ("field designed" on-site), which may interrupt the natural longshore transport of beach sands, is doubtful. Even 1800 Atlantic's own experts criticize it. y 1982, the U.S. Army Corps of Engineers completed a "Feasibility Report for Beach Erosion Control" with an accompanying Environmental Impact Statement. This report proposed a beach restoration program on the southern shore of Key West consisting of construction of a level beach berm, four feet above MHW and 100 feet wide along the 3,000 foot length of Smathers Beach; and a beach 25 feet wide along 2,370 feet of shoreline east and 3,400 feet west of Smathers Beach. 1800 Atlantic's proposed fill falls within the boundaries of this proposed beach restoration program. y is the local sponsor of the beach erosion control project described in the Feasibility Report. As late as August 1985, the Mayor of the City sent a letter to DER's dredge and fill supervisor confirming the City's continued support for the overall beach renourishment project. Although 1800 Atlantic suggests otherwise, the City's support of a comprehensive publicly financed beach restoration project along its southern shores (which presumably would assure public access to the restored beaches) is not necessarily inconsistent with its opposition to a relatively small fill project undertaken primarily for the private benefit of the owners, guests, and tenants of an adjacent condominium. h 1981, the Governor of Florida expressed written support for the Corps of Engineers' beach restoration project, but recommended that, in order to protect the marine environment, "any future beach renourishment be done in an environmentally sensitive manner. (Atl.Exh.19) The Governor's endorsement of the public beach restoration program does not, however, equate to his endorsement of the particular and more limited private beach project at issue. Even if it did, a gubernatorial expression of support cannot supplant DER's duty to exercise its regulatory authority in accordance with Chapter 403, Florida Statutes (1985). h fill project proposed by 1800 Atlantic was designed to be consistent with the overall U.S. Army Corps of Engineers beach restoration project described in the Feasibility Report. It should be noted, however, that the Corps project was criticized by federal environmental agencies for adverse impact on seagrass beds and fish and wildlife resources. (Atl. Exh.19, Appendix 3.) c has already received a coastal construction permit for its proposed project from the Florida Department of Natural Resources ("DNR"). This permit, however, was issued by another state agency exercising regulatory authority under a different statute, with different criteria for issuance. Cumulative Impact e no similar applications for beach fill projects in the Lower Keys pending before DER, although inquiries have been made by a nearby landowner. least the last two years, DER has not issued a permit in the Keys for a fill project similar to the one proposed by 1800 Atlantic. l may be placed on submerged lands (not previously conveyed to private ownership) without the consent of the Governor and Cabinet, sitting as the Board of Trustees of the Internal Improvement Trust Fund--the owner of sovereignty lands. The Trustees have not approved an application to place beach fill on sovereignty lands in the Florida Keys for the last three years. Nor are there any pending applications for approval to do so. (As already noted, except for the project site, all remaining submerged lands in the Rest Beach area are publicly owned.) h serves as the staff for and makes recommendations to the Trustees, has a general policy of opposing the creation of unnatural beaches in the Keys on publicly owned submerged lands. As stated by Casey Fitzgerald, Chief of DNR's Bureau of State Lands Management: [Mr. Fitzgerald] A. So in a general sense, our recommendations would typically be negative, unless shown for some public interest purpose that it should be otherwise. Q. By that latter comment, do you mean, in connection with, for example, an overall publicly sponsored beach restoration project? A. That would be one example, yes. (e.s.) (Atl.Exh.20; p.8) Whether the Proposed Fill Would be Clearly in the Public Interest y for a DER permit, 1800 Atlantic must provide "reasonable assurance that the project will be clearly in the public interest." Section 403.918(2), Fla.Stat. (1985). In deciding whether a project is "clearly in the public interest," several statutory criteria must be considered and balanced. The issue though broadly phrased--is fundamentally a factual one, and must be decided on a case-by-case basis. 6/ Section 403.918(2)(a) Fla.Stat. (1985). d in light of the seven statutory criteria, it must be concluded that the applicant has failed to show that the proposed fill would be "clearly in the public interest." t should not cause violations of water quality standards or significantly degrade state waiters. Neither should it adversely affect (1) the public health, safety, or welfare, or the property of others; (2) endangered or threatened species, or their habitats; (3) navigation or the flow of water; or (4) significant historical material and archaeological resources. Nevertheless, the project will adversely affect the conservation of fish and wildlife, fishing or recreational values, and marine productivity in the vicinity. The site, which would be permanently covered with beach sand, now provides viable intertidal marine habitat and a feeding ground for migratory, shore and wading birds. It supports numerous species of juvenile fish and crustaceans, a diverse benthic and algae community, and patches of seagrass which benefit water quality and enhance the ecology of the marine environment. This shallow water habitat, gently sloping to the sea from an extended unfortified shoreline, is a diminishing resource in Key West. The existence of other submerged areas which are more biologically productive and support an even greater diversity of marine life do not diminish the positive value of the undisturbed project site to the marine environment. r adverse environmental impacts could occur. The proposed groin could cause increased erosion on property to the west by interrupting longshore sand drift. Shoaling could block tidal connections which periodically occur in the adjacent mangrove wetlands. Fill sands, pulverized and dispersed seaward by hurricanes or violent winter storms, could smother offshore seagrasses. y for the fill project has been shown. Though erosion has occurred over the last 25 years, the shoreline is stable, in equilibrium, and protected by a "natural armor" of coarse material and lag rubble. 1800 Atlantic has neither alleged nor asserted that the structural integrity of its upland condominium (still under construction) is threatened. The proposed fill would widen the upland between the condominium and the sea, providing an added degree of protection. While this benefits the upland structures, it is a benefit which would seemingly result whenever a fill project converts submerged land (seaward of a structure) to dry upland. Further, no necessity for an expanded private beach has been shown since there is a convenient 3000 foot public beach within a few hundred feet of the site. n measures proposed by 1800 Atlantic are insufficient to offset the known and potential adverse effects. These measures are vague, ill- defined, and uncertain. The design of the groin is left to "field engineering;" the adequacy of other mitigation measures is left to future review and decision by DER. The specific location and nature of the upland mitigation site (to be converted to submerged lands) is unknown, as is the amount of the bond to be posted if the beach fill project precedes mitigation. n expanded beach would provide recreational benefits to the owners, guests and tenants of the upland condominium, it has not been shown that similar benefits would inure to the general public. 1800 Atlantic does not guarantee that the public will have access to the beach. (It asserts only that any right of access which the public may have will not be infringed.) 1800 Atlantic's affidavit of ownership, which must be taken as true, asserts ownership of the submerged lands presumable by previous conveyance from the Trustees of the Internal Improvement Trust Fund. It is entirely possible that 1800 Atlantic, as owner of the submerged lands and upland beach, could deny access to the general public. 1800 Atlantic has not shown that the general public has any existing right to enter upon and use the submerged lands and existing beach. By promising no greater access right than the public now has, and by failing to show that the public has any existing right to enter and use the submerged lands and shoreline, 1800 Atlantic has failed to demonstrate that its beach project would provide recreational opportunities to the general public. c benefit asserted by 1800 Atlantic is that the fill would eliminate an existing shoreline discontinuity, a discontinuity that has not been shown to be a significant problem. 1800 Atlantic would replace it with a new discontinuity created by a proposed groin at the west end of the property--a groin with uncertain effects on the shoreline to the west. Another claimed benefit is that needed sediment--of the correct quality and quantity--would be contributed to offshore seagrasses; but whether this would actually occur is uncertain. c also points out that its privately funded beach restoration project is consistent with and falls within the boundaries of a proposed public beach restoration project proposed by the U.S. Army Corps of Engineers, supported by the Governor, and sponsored by the City. Any public benefit to be derived from this consistency is also doubtful. It was not shown that the Corps of Engineer's project involving Smathers Beach and Rest Beach has been finally approved and funded, or when (if at all) it would take place. Federal environmental agencies have pointed out the adverse environmental effects of such a project. A main benefit of the Corps project--expanded beach recreational opportunities for the general public--has not been shown to be a benefit which would result from 1800 Atlantic's fill project. , 1800 Atlantic has not affirmatively shown that, on balance, its proposed fill would be clearly in the public interest. The fill would have significant adverse environmental impacts--some certain, others possible. Measures offered to mitigate these impacts are vague, ill-defined, and inadequate. While benefits would inure to private upland owners, guests, and tenants, benefits to the general public are illusive or inconsequential. No necessity for the project has been shown, alternate methods of providing additional protection to the condominium may be available. A Corps of Engineers' beach restoration project for the entire area has been proposed and studied. While such a project would have adverse environmental effects at the 1800 Atlantic site, increased beach recreational opportunities would benefit the general public. 1800 Atlantic has not shown that its beach project would confer a like benefit.
Recommendation Based on the foregoing, it is RECOMMENDED: that the application for a fill permit and water quality certification filed by 1800 Atlantic be DENIED, based on failure to provide reasonable assurances that the project is clearly in the public interest. DONE and ORDERED this 3rd day of September, 1986, in Tallahassee, Florida. R. L. CALEEN, JR. 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 3rd day of September, 1986.
The Issue The ultimate issue is whether the Applicant, Florida-Georgia Venture Group, is entitled to development orders for its proposed development of regional impact, Hunter's Ridge, in Flagler County and the City of Ormond Beach, Florida.
Findings Of Fact The Petitioner is Florida-Georgia Venture Group, 402 Clifton Avenue, Holly Hill, Florida 32117, and its authorized agent is Thomas L. Durrance, Managing Partner. The Hunter's Ridge project lies within the jurisdiction of both the Northeast Florida Regional Planning Council (NEFRPC) and the East Central Florida Regional Planning Council (ECFRPC) and underwent concurrent review. The Hunter's Ridge project as proposed in this proceeding is a proposed planned unit development located in the unincorporated area of Flagler County and in the City of Ormond Beach on approximately 5,037 acres. The portion of the Hunter's Ridge project located in the unincorporated area of Flagler County consists of approximately 3,800 acres, of which 1,940 acres will be preserved as conservation area. The portion to be developed in the unincorporated area of Flagler County is approximately 1,860 acres, consisting of 1,702 residential units, plus commercial, recreational, and other uses. The portion of the Hunter's Ridge project located in the City of Ormond Beach consists of approximately 1,237 acres, of which 327 acres will be preserved as conservation area. The portion of the property in Ormond Beach to be developed is approximately 910 acres, consisting of 982 residential units, plus commercial, recreational, and other uses. Of the residential units to be developed in the City of Ormond Beach, 109 residential units were approved by the Department of Community Affairs (DCA) under a preliminary development agreement. The Board of County Commissioners of Flagler County held a public hearing on the DRI/ADA on July 13, 1989, which was continued to October 12, 1989, to November 2, 1989, to January 11, 1990, and to January 25, 1990. On January 25, 1990, the Board of County Commissioners of Flagler County passed and adopted a Development Order for the Hunter's Ridge DRI, which Development Order was recorded in Official Records Book 0423, Page 0669 through 0728, Public Records of Flagler County, Florida. The City Commission of the City of Ormond Beach held a public hearing on the DRI/ADA on August 15, 1989, which was continued to September 5, 1989, to September 19, 1989, to October 3, 1989, to October 17, 1989 and to January 30, 1990. At the public hearing on January 30, 1990, the City of Ormond Beach adopted Resolution 90-20 denying the DRI/ADA for the portion of the Hunter's Ridge DRI located in the City of Ormond Beach. The DCA, pursuant to Section 380.07, Florida Statutes, and Rules 42- 2.002 through 42-2.011, Florida Administrative Code, timely filed a Notice of Appeal and Petition for Administrative Hearing with the Florida Land and Water Adjudicatory Commission (FLWAC), whereby DCA appealed the Development Order adopted by the Board of County Commissioners of Flagler County. The Applicant, pursuant to Section 380.07, Florida Statutes, and Rules 42-2.002 through 42-2.011, Florida Administrative Code, timely filed a Notice of Appeal and Petition for Administrative Hearing with FLWAC, whereby the Applicant appealed the denial of approval by Ormond Beach. This cause came before FLWAC on May 22, 1990, for consideration of the Appeals and the Petitions for Administrative Hearing; FLWAC ordered that this matter be forwarded to Division of Administrative Hearings (DOAH) for assignment of a hearing officer and further proceedings. At the Administrative Hearing conducted by DOAH, on December 5-7, 1990, the Applicant amended its DRI/ADA to reduce the size of the project and to reallocate land uses, densities, and other components of the project. The current scope of the project is reflected in Florida-Georgia Exhibits 1-5, 9, and 14. As amended by the Applicant, the proposed project now consists of the following uses in Flagler County: 11.61 acres of Village Retail Office; 5.71 acres of Village Office; 16.68 acres of Light Industrial; 197.18 acres of Village Services/Recreational; 90.89 acres of Parks and Schools; 64.52 acres of Multi-Family Residential (with Upland Buffer); 259.34 acres of Wetlands; 146.93 acres of Roads, Drainage, and Retention; 52.90 acres of Lakes; 130.00 acres of Golf Course; 57.25 acres of Utility Easement; and 130.00 acres of Single Family Residential. The total number of dwelling units permitted in the County is 220 townhouses and villas and 145 apartments and condominiums. As amended by the Applicant, the proposed project now consists of the following uses in the City: 192.00 acres of Village Services/Recreational; 30.61 acres of Parks and Schools; 14.51 acres of Multi-Family Residential (with Upland Buffer); 174.54 acres of Wetlands; 110.95 acres of Roads, Drainage, and Retention; 28.65 acres of Lakes; 17.32 acres of Utility Easement; and 341.42 acres of Single Family Residential (with Upland Buffer). The total number of dwelling units permitted in the City are 932 single family units and 50 townhouses and villas. Generally speaking, the portions of the development within the County which are to be developed are in Township 41 South, Range 31 East, Section 22 and the east half of Section 21; Section 15 and the east half of Section 16, with the exception of a golf course in Section 15, constitute an area that, if it is to be developed in the future, will require a substantial deviation approval from all concerned agencies. Pursuant to stipulation of the Applicant and Flagler County, an area approximating Section 15 and the east half of Section 16 will be redesignated under the Flagler County Comprehensive Plan as Agricultural, with a permitted residential density of not more than one unit per five acres. Pursuant to stipulation, Sections 17 and 20 and the west halves of Sections 16 and 21, along with most of the portions of Sections 29 and 30 north of State Road 40, will be deeded to a public or public interest agency, with the Applicant retaining the right to conduct silviculture with best management practices except in those wetland areas of the property designated for conservation. The parties, with the exception of Citizens, have stipulated that Florida-Georgia Exhibit 5 constitutes the necessary affordable housing conditions for the project. The affordable housing provisions of the proposed project are consistent of the requirements of Chapter 380, Florida Statutes, Rule 9J-2, Florida Administrative Code, and the State Comprehensive Plan. The affordable housing conditions adequately address affordable housing needs of the project consistent with all local government, state, and regional requirements and regulations. The Applicant, the Florida Audubon Society, Flagler County and the City of Ormond Beach, have stipulated that the conditions contained in their Joint Stipulation, filed as Florida-Georgia Exhibit 9 satisfactorily resolve all issues concerning wetlands, wildlife habitat, and endangered species. The soils on the project will support the proposed development. During review of the DRI/ADA by the RPCs, Volusia County submitted comments and recommendations to ECFRPC. The comments and recommendations of Volusia County were considered by ECFRPC when it adopted its recommended conditions of approval. The conservation area proposed by the Applicant represents a significant contribution to conservation and wildlife. The proposed Development Orders and Conditions of Approval adequately address the regional impacts of the project on the environment and natural resources. The proposed Development Orders and Conditions of Approval include measures intended to address impacts upon, and to protect, the Little Tomoka River. The proposed Development Orders and Conditions of Approval provide for preservation and conservation of wetlands. The proposed Development Orders and Conditions of Approval provide flexibility for protection of environmentally sensitive areas. The proposed plan of development reflects a development that provides adequate environmental protection. The proposed project will have no adverse environmental impacts in the City of Ormond Beach. The proposed Development Orders and Conditions of Approval provide protection for the Little Tomoka River, preventive measures regarding stormwater discharge and stormwater treatment, and mitigative, water quality treatment methods in the surface drainage system, if any degradation is found at a later date. The proposed Conditions of Approval require that all construction within the project be protected against flooding. The project has sufficient safeguards to prevent construction within flood prone areas. Minimum floor elevations for flood plain purposes will be controlled by FEMA flood plain designations and by local rules and regulations, and will be established on a case by case basis for the Hunter's Ridge project. The proposed Conditions of Approval addressing transportation impacts and facilities are consistent with the provisions of Chapter 380, Florida Statutes, with the provisions of Rule 9J-2, Florida Administrative Code, and with the State Comprehensive Plan. The proposed Conditions of Approval ensure that the Hunter's Ridge project will not have an adverse impact on regionally significant roadways, including State Road 40. The proposed Conditions of Approval will ensure that the regional highway network will function at the desired level of service during the project buildout. The proposed Conditions of Approval are consistent with the provisions of Section 380.06(12), Florida Statutes, relating to transportation impacts. The proposed Conditions of Approval adequately address the transportation concerns of Flagler County. The proposed Conditions of Approval adequately address the transportation impacts on the City of Ormond Beach. The proposed Conditions of Approval dealing with public facilities are consistent with the provisions of Chapter 380, Florida Statutes, consistent with the provisions of Rule 9J-2, Florida Administrative Code, and consistent with the State Comprehensive Plan. If the conditions for providing public facilities are not met by the Applicant, development must cease. The proposed Conditions of Approval dealing with public facilities are consistent with the concurrency requirements of Chapter 380, Florida Statutes. The proposed Development Orders and Conditions of Approval adequately address the regional impacts of the project on public services and facilities. The proposed plan for development of the Flagler County portion of the project provides for all required public facilities and services. The Applicant will have to subsidize any deficits in providing public services. The Applicant has agreed to make contributions intended to assist Flagler County in providing public services to residents of areas outside of the Hunter's Ridge project. Solid waste is not an issue in Flagler County. The proposed Conditions of Approval for the Flagler County portion of the project provide three options for wastewater treatment. The proposed Conditions of Approval for the Flagler County portion of the project require that the project must stand on its own and must provide water supply and wastewater treatment without cost to the rest of the residents of Flagler County. The Flagler County portion of the project requires 1,200 to 1,500 dwelling units to provide a self-contained, self-supporting, self-sufficient development which will not require subsidy by other Flagler County taxpayers. The good mix of land uses contained in the proposed plan for development will help the tax base of Flagler County and avoid a deficit during the buildout of the project prior to construction of 1,200 to 1,500 dwelling units. The tax base, the values, and the assessments for the proposed project will provide sufficient funds to support the development. The proposed Conditions of Approval for the Flagler County portion of the project provide for voluntary contributions by the Applicant in excess of what is required by local ordinance. The dedication and donation of the golf course and conservation areas to Flagler County are voluntary contributions by the Applicant. The Ormond Beach portion of Hunter's Ridge project will not require a separate police patrol zone. The Ormond Beach Police Department can provide acceptable response times for the portions of the project within the City. The public safety site to be dedicated by the Applicant will benefit the City and the Police Department and will be helpful in rendering public safety services to the citizens of Ormond Beach. The Ormond Beach portion of Hunter's Ridge project will provide needed revenue to provide needed Police Department services. The Ormond Beach Police Department can adequately provide public safety services for the Hunter's Ridge area and respond to public safety needs within a reasonable amount of time. The City of Ormond Beach is capable of providing potable water service to the project. Impact fees generated by the project will be sufficient to fund water supply and wastewater capital facilities needed to serve the project. The City has adopted the West Ormond Plan to provide utilities to the Hunter's Ridge project. The Applicant has dedicated to the City a westerly wellfield site which will be needed for the entire city in the future, even if the Hunter's Ridge project is not developed. The City of Ormond Beach does not lose money on water and sewer fees. If the homes built in the Ormond Beach portion of the Hunter's Ridge project approximate the assessed values of existing homes within the city, there will be no revenue strain on the operating budget of the City of Ormond Beach. The average sale price for homes in the Hunter's Ridge project will be higher than the current average sale price within the City of Ormond Beach. The Hunter's Ridge project will not place an economic strain on the City of Ormond Beach. Future growth in the City of Ormond Beach will pay for itself in terms of capital needs. The fiscal problems of the City of Ormond Beach are not unique, but are similar to those occurring throughout the state. Increased property values from the Hunter's Ridge project will help the city's fiscal problems in the long run. The City of Ormond Beach has a great deal of ad valorem capacity to meet service needs and operating budgets. The Hunter's Ridge DRI will make significantly more contributions to public services and facilities than traditional subdivisions. The reduced project as proposed for approval in this proceeding contributes a greater amount of money toward public facilities. The public safety site to be dedicated in the Ormond Beach portion of the project is adequate to serve the fire fighting needs of the project and the surrounding areas. The public safety site to be dedicated in the Ormond Beach portion of the project gives the city flexibility in providing fire fighting services if the road network connecting the project with Shadow Crossings and Breakaway Trails is in place and will enable the city to better serve Shadow Crossings and Breakaway Trails. The roadway network for the Hunter's Ridge project will provide interconnections with Shadow Crossings and Breakaway Trails for the provision of police, fire, and emergency services. The Hunter's Ridge project will have no impact on solid waste in the City of Ormond Beach. The Hunter's Ridge project will have no impact on the vehicular needs of the City of Ormond Beach Department of Public Works. The Hunter's Ridge project will have no adverse impact on road maintenance in the City of Ormond Beach. The proposed Hunter's Ridge DRI is consistent with the requirements of Chapter 380, Florida Statutes, the requirements of Rule 9J-2, Florida Administrative Code, and the requirements of the State Comprehensive Plan. The Hunter's Ridge DRI meets all regional requirements. The Hunter's Ridge DRI does not represent "leap frog development," nor does it constitute "urban sprawl." The density of 982 dwelling units for the Ormond Beach portion of the Hunter's Ridge project is consistent with the State Comprehensive Plan and the requirements of Chapter 380, Florida Statutes. Reducing the density proposed for the Ormond Beach portion of the project from 982 residential units to 882 residential dwelling units would not necessarily be considered an improvement to furthering the plan concept. The Hunter's Ridge DRI is consistent with the plans and policies of the Regional Planning Councils. As to the portions within Flagler County, the Hunter's Ridge DRI: Is consistent with the provisions of Chapter 380, Florida Statutes; Is beneficial to Flagler County; Is consistent with the Flagler County Comprehensive Plan; Is consistent with the NEFRPC report and recommendations; Is superior to existing zoning; Provides better development and more planning opportunities than non- DRI approaches to development; and, Provides adequate controls for the development of Hunter's Ridge. The Ormond Beach portion of the project: Is consistent with the provisions of Chapter 380, Florida Statutes; Is consistent with the Ormond Beach Comprehensive Plan and all City ordinances and regulations; Adequately mitigates against adverse impacts through the Conditions of the proposed Development Order. To the extent that the opinions of some witnesses, primarily Mr. Grace and Mr. Shearer, have not been adopted in these Findings of Fact, they are deemed to be unreliable or lacking in substantial weight or persuasive value.
Recommendation Based upon the foregoing Findings of Fact and Conclusions of Law, it is RECOMMENDED that the Florida Land and Water Adjudicatory Commission enter a Final Order and therein: Adopt the development order with conditions as set forth in the Joint Stipulation of Florida-Georgia Venture Group and the City of Ormond Beach. Adopt the development order with conditions as set forth in the Joint Stipulation of Florida-Georgia Venture Group and Flagler County. DONE and ENTERED this 21st day of March, 1991, in Tallahassee, Florida. DIANE K. KIESLING Hearing Officer Division of Administrative Hearings The DeSoto Building 1230 Apalachee Parkway Tallahassee, FL 32399-1550 (904) 488-9675 Filed with the Clerk of the Division of Administrative Hearings this 21st day of March, 1991. APPENDIX TO THE RECOMMENDED ORDER The following constitutes my specific rulings pursuant to Section 120.59(2), Florida Statutes, on the proposed findings of fact submitted by the parties in this case. Specific Rulings on Proposed Findings of Fact Submitted by Florida-Georgia Venture Group Each of the following proposed findings of fact is adopted in substance as modified in the Recommended Order. The number in parentheses is the Finding of Fact which so adopts the proposed finding of fact: 1-5(1-5); 12-14(6-8); 16- 19(9-12); 20(18); 22-25(19-22); 27-38(23-34); 40-89(35-83); 91(84); 92(85); 94(86); 97(87(; and 98(88). Proposed findings of fact 26, 39, 90, 93, 95, and 96 are subordinate to the facts actually found in this Recommended Order. Proposed findings of fact 6-11 and 21 are unnecessary. Proposed finding of fact 15 is irrelevant. Specific Rulings on Proposed Findings of Fact Submitted by Department of Community Affairs Each of the following proposed findings of fact is adopted in substance as modified in the Recommended Order. The number in parentheses is the Finding of Fact which so adopts the proposed finding of fact: 8-12(13-17). Proposed findings of fact 1, 2, and 13-17 are subordinate to the facts actually found in this Recommended Order. Proposed findings of fact 3-7 are unnecessary. Specific Rulings on Proposed Findings of Fact Submitted by the City of Ormond Beach 1. Proposed findings of fact 1, 8, 10-17, 21, 33-36, 38-40, 43, 46, and 49 are subordinate to the facts actually found in this Recommended Order. Proposed findings of fact 2-7, 19, 20, 22, 23, 37, 47, 48, and 50 are irrelevant. Proposed findings of fact 9, 18, 24-32, 41, 42, 44, 45, 51, and 52 are unsupported by the credible, competent and substantial evidence. Specific Rulings on Proposed Findings of Fact Submitted by the Citizens for Ormond Beach 1. Proposed findings of fact 7, 9-11, 13-19, 21-25, 35, 47, and 49-52 are subordinate to the facts actually found in this Recommended Order. Proposed findings of fact 8, 12, 20, 26-32, 34, 42, and 57 are irrelevant. Proposed findings of fact 33, 36-39, 43-46, 48, and 53-56 are unsupported by the credible, competent and substantial evidence. Proposed findings of fact 1-6, 40, and 41 are unnecessary. COPIES FURNISHED: J. Doyle Tumbleson, Attorney at Law Kinsey Vincent Pyle Professional Association 150 South Palmetto Avenue, Box A Daytona Beach, FL 32114 Fred S. Disselkoen, Jr. Attorney at Law City of Ormond Beach Post Office Box 277 Ormond Beach, FL 32175-0277 Gerald S. Livingston Attorney at Law Post Office Box 2151 Orlando, FL 32802 Timothy Keyser, Attorney at Law Post Office Box 92 Interlachen, FL 32148 Jonathan Hewett Attorney at Law Central Florida Legal Services, Inc. 216 South Sixth Street Palatka, FL 32177 David Russ, Senior Attorney Julia Johnson, Attorney Department of Community Affairs 2740 Centerview Drive Tallahassee, FL 32399-2100 Charles Lee Senior Vice President Florida Audubon Society 1101 Audubon Way Maitland, FL 32751 Linda Loomis Shelley Attorney at Law Dixon, Blanton & Shelley 902 North Gadsden Street Tallahassee, FL 32303 Noah McKinnon Attorney at Law 595 West Granada Avenue Ormond Beach, FL 32075 Douglas M. Cook, Director Planning and Budgeting Florida Land and Water Adjudicatory Commission Executive Office of the Governor The Capitol, PL-05 Tallahassee, FL 32399-0001
The Issue The issue for determination at the final hearing was whether the Petitioner Blaha possessed the requisite standing to maintain this action and if so, whether the Applicant Aquarina Developments, Inc., established by a preponderance of the evidence entitlement to a permit from the Coastal Construction Control Line ("CCCL") which would authorize construction of the following: (1) twelve above-ground balconies extending five feet over the CCCL; (2) two roof overhangs extending approximately one foot over the CCCL; (3) two dune walkovers and four decks providing elevated beach access; and (4) a temporary fence extending no more than five feet beyond the CCCL. At the final hearing, the Respondent Aquarina Developments, Inc., (hereafter "Aquarina" or "Applicant") offered Respondent's Exhibits 1-16, which were admitted into evidence. Edward Fleis, Howard J. Teas, Bert Leltz and Ross Witham testified on behalf of the Respondents. Peter Pritchard, Rob Lee and Georges Blaha testified for the Petitioner. Additionally, public comment was taken as provided at Section 120.57(1)(b)(4), Florida Statutes. A Proposed Recommended Order has been submitted by the Respondent Aquarina Developments, Inc. To the extent that the proposed findings submitted by Respondent are not reflected in this Order, they are rejected as unsupported by the weight of credible evidence or as being immaterial to the results reached.
Findings Of Fact By application No. 775-020.61 filed on July 1, 1981, Respondent Aquarina requested a coastal construction permit for construction of portions of twelve cantilevered balconies, two roof overhang sections, a temporary construction fence, four elevated wooden decks, and two dune crossovers, all seaward of an established coastal construction control line ("CCCL") in Brevard County, Florida. The purpose of the proposed structures is to enhance utilization of the beach by residents of Aquarina's PUD located between the Atlantic Ocean and Mullet Creek, a tributary of the Indian River in South Brevard County, while at the same time inhibiting the deleterious effects of unrestrained pedestrian and vehicular access across the beach dune on the property. Respondent Aquarina's project is located on the barrier islands separated from the mainland by the Indian River, thirteen miles south of Melbourne and five miles north of Indian River County. Aquarina proposes to develop a condominium community approved as a PUD by Brevard County, with a projected population of 3,400 persons including 1,600 residential units, a commercial area, and 500 hotel rooms. The project includes at least two condo- mini urn buildings located entirely landward of the CCCL except for the following specific portions: Twelve cantilevered balconies ex- tending approximately five feet beyond the CCCL but not touching the ground; Two roof overhang sections extending approximately one foot beyond the CCCL; Two beach-dune walkover structures to be constructed a maximum of seventy- five feet seaward of the CCCL, which are to provide controlled beach access; Four elevated wooden observation decks constituting integral parts of the walkover structures; A temporary construction fence extending no more than five feet beyond the CCCL. On or about November 20, 1981, the Department indicated its intent to recommend to the Executive Director the issuance of the Applicant's coastal construction permit. After the granting of a requested extension of time, Petitioner Blaha filed objections and a Petition for the Initiation of Formal Proceedings under Section 120.57, Florida Statutes. The Petition raised three issues: Whether construction of the proposed minor structures seaward of the CCCT would harm sea turtles inhabiting the area at issue; Whether a new CCCL should have been set based on changing conditions in the area; Whether the additional shading caused by the proposed structures would harm the dune vegetation system. At the beginning of the hearing, the Hearing Officer heard argument and received evidence on the issues raised by the Motions to Dismiss filed by the Department and the Applicant. The Respondent's Motions raised three issues: Whether the Petitioner had standing to initiate this cause; Whether the alleged impact that the Applicant's proposed coastal construction would have on sea turtles lies within the jurisdiction of the Department and the Hearing Officer under Chapter 161 of the Florida Statutes; and Whether the exact configuration of the CCCL is a proper subject for consi- deration at a hearing challenging the proposed issuance of a coastal construction permit. Petitioner Blaha admitted that he did not live on the beach at issue and in fact lived on the west side of State Road A1A, three miles to the north of the Applicant's proposed project. The Petitioner stated that he was the Director of the Space Coast Branch of Friends of Animals, an environmental organization concerned about wildlife, although not representing the organization in this proceeding, and that he had a general interest in protecting the beach from erosion, a problem affecting everyone on the barrier island. In response to the argument that Petitioner Blaha had no special interest differing in kind from the interests of the general public, the Petitioner alleged that he runs on the beach and observes the sea turtles, arguing that this evinces a more than average interest in protecting the beach and its wildlife. The Hearing Officer also heard argument on whether the Department has jurisdiction to consider potential impacts on the nesting habitats of sea turtles from proposed coastal construction, under Chapter 161, Florida Statutes. Petitioner Blaha urged that although Section 161.053, Florida Statutes and the rules promulgated thereunder do not address sea turtles and their protection, the statute should be so interpreted. The Department responded that any jurisdiction it may have over sea turtles would be reposited in its Marine Resource Division, not in the permitting procedures for a coastal construction permit. In addition, federal laws protect endangered sea turtles, and the federal government has primary jurisdiction over the regulation of the nesting habitats of such sea turtles. Similarly, the Applicant and the Department pointed out that the Petitioner's criticism of the placement of the present CCCL falls outside the scope of a hearing on the issuance of a coastal construction permit, since Section 120.54, Florida Statutes provides for rulemaking proceedings for those attempting to change a rule established CCCL and Rule 16B-33.10, Florida Administrative Code, contains provisions for CCCL revisions or modifications on application of a riparian owner of property at or on the CCCL. Petitioner Blaha is not a riparian property owner and this was not a proceeding under Section 120.54, Florida Statutes. Respondent Aquarina established that it had taken and would continue to take all reasonable actions necessary to ensure the protection of sea turtles that inhabit the site through public relations campaigns and public advertisements to educate the public and especially the residents of the PUD and through architectural design efforts and dareful construction practices that will limit the impact of the proposed development on sea turtles and their nesting habitats. Moreover, to the extent that the development might have an impact on sea turtles, the source of the impact would not primarily be the structures at issue in these proceedings, but the buildings, parking lots, and other human habitation lying landward of the CCCL. The proposed temporary construction fence to be placed five feet beyond the CCCL will help conserve the dunes by limiting the potential impact of construction, and the Respondent Aquarina has agreed to restore that affected area to its natural state upon the completion of construction. Most importantly, the proposed dune crossovers will protect the dunes from the destruction that is occurring in the dunes to the north of the project and on the project site itself because of unrestrained pedestrian and vehicular traffic over and/or through the dunes and the accompanying destruction of dune vegetation in those areas. The dune crossovers are wooden walkways on raised pilings designed to have as little contact with the dunes as possible, with railings to restrain pedestrians from straying away from this direct access from the condominiums to the beach. The crossovers will make it unnecessary and undesirable for residents and visitors to create alternative foot paths through the heavy dune vegetation to the beach. Coupled with the educational program already being implemented by Aquarina, the dune crossovers should help to conserve the dunes. The Respondent Aquarina established that the incremental shading caused by the proposed roof overhangs extending about one foot beyond the CCCL and the cantilevered balconies extending approximately five feet beyond the CCCL would not significantly add to the shading from the buildings themselves, which lie entirely landward of the CCCL. The evidence showed that even the impact of the shading from the landward buildings would have no significant impact on the dune vegetation system or increase the rate of erosion or deterioration of the dune. See Rule 16B-33.02(23)(b), Florida Administrative Code. The additional impact from the minor structures for which the Respondent Aquarina seeks its permit should be minimal.
Recommendation Based on the foregoing Findings of Fact and Conclusions of Law, it is RECOMMENDED: That the Respondent Department of Natural Resources, through its Executive Director, grant the requested construction control permit to the Applicant Aquarina Developments, Inc., subject to the conditions stated in the proposed permit (No. BE-80), the draft of which was attached to the Department's letter of November 20, 1981, notifying Petitioner Blaha of the Department's intent to issue the requested permit. DONE and ORDERED this 25th day of October, 1982, in Tallahassee, Florida. SHARYN L. SMITH, Hearing Officer Division of Administrative Hearings The Oakland Building 2009 ApA1Achee Parkway Tallahassee, Florida 32301 (904) 488-9675 Filed with the Clerk of the Division of Administrative Hearings this 25th day of October, 1982. COPIES FURNISHED: Georges Blaha 280 Flamingo Drive Melbourne Beach, Florida 32951 Deborah A. Getzoff, Esquire Assistant Department Attorney Department of Natural Resources 3900 Commonwealth Boulevard Tallahassee, Florida 32303 Clifford A. Schulman, Esquire GREENBERG TRAURIG ASKEW HOFFMAN LIPOFF QUENTEL & WOLFF, P.A. 1401 Brickell Avenue Miami, Florida 33131 Henry Dean, Esquire General Counsel Department of Natural Resources 3900 Commonwealth Boulevard Tallahassee, Florida 32303 Elton Gissendanner, Executive Director Department of Natural Resources 3900 Commonwealth Building Tallahassee, Florida 32303
Findings Of Fact Upon consideration of the oral and documentary evidence adduced at the hearing, the following relevant findings of fact are made: On March 26, 1991 Venice applied to the Department for a CCCL permit to construct a 475 foot wooden retaining wall seaward of the coastal construction control line and to place a shell road immediately adjacent to, and landward of, the retaining wall from approximately 100 feet south of Granada Avenue to approximately 50 feet south of Ocala Street on Venice's right-of-way of The Esplanade in Venice, Florida. The Petitioners Roy B. and Patricia B. Olsen are residents of Venice, Florida and reside at 304 Ocala Street. They own Lot 1, The Esplanade, which is immediately east and south of the southern terminus of the proposed retaining wall. Petitioner, Nina Howard is a resident of Venice, Florida and resides at 721 Ocala Street. Ms. Howard's residence is located to the south and across Ocala Street from the site of the proposed retaining wall. Intervenors, Roger and Irene Fraley are residents of Venice, Florida and reside at 221 The Esplanade South, which is immediately landward (east) of the site of the proposed retaining wall. Intervenors, Howard and Evelyn Barbig are residents of Milton, Florida but are owners of lot 4, The Esplanade South, located north of the Fraleys' property and immediately landward (east) of the site of the proposed retaining wall. The Petitioners oppose the granting of the CCCL permit. The Petitioners have expressed their opposition to the granting of the CCCL permit based upon their belief that the construction of the proposed retaining wall will have adverse impacts to the beach dune areas and to the adjacent properties. Specifically, it is their belief that the construction of the proposed retaining wall will accelerate the erosion of the beach dune areas and the adjacent properties. The Petitioners disagree with the conclusion reached by the Department in the final order that, "the activities indicated in the project description are of such a nature that they will result in no significant adverse impacts to the beach dune areas or to the adjacent properties." Intervenors, Fraley and Barbig are in favor of the issuance of the CCCL permit because it will prevent seasonal erosion which results in exposure of, and damage to, the sewer line along The Esplanade, and will provide public access over the shell road within the right-of-way of The Esplanade for those properties between Granada Avenue and Ocala Street that do not have public access from time to time due to the seasonal erosion. On April 17, 1991 the Department advised Venice that the CCCL permit application was determined to be incomplete, and advised Venice of those things needed to make the application complete. Subsequent to this letter, the Department determined that, although the application was not an emergency, it did deserve "fast tracking", and assisted Venice in bringing the application to a "complete" status. On April 25, 1991 the Department issued a Final Order administratively approving CCCL permit number ST-820 for the construction of a wooden retaining wall and shell access road as described in Venice's application. On April 26, 1991 the Department issued a Notice to Proceed Withheld to Venice, which advised Venice not commence construction of the project authorized by the permit until certain permit conditions had been met. This notice also gave notice to those whose substantial interests would be affected by the proposed project of their right to a formal hearing. An engineering assessment was made for this project, and although not a formal written engineering assessment, the engineering assessment did consider all conditions of adverse impacts. In making this assessment, the Department considered and reviewed available aerial photographs, photographs taken of the area of the proposed project site and erosion tables concerning the area. A formal written engineering assessment is not required by statute, rule or Department policy. This assessment also indicated that there are severe impacts due to winter storm events which contribute to the seasonal profile changes. The seasonal beach profile is depicted by the build up of the beach (sand) during the summer months and the removal (erosion) of beach (sand) during the winter months. However, due to an inlet, a major rock-out cropping and the rock grain structures located in the vicinity of the proposed site, there is a limitation on the natural movement of sand along the coast which prevents natural renourishment and results in severe erosion in the area of the proposed site during the winter months. This erosion during the winter months causes the sewer pipes along The Esplanade to be exposed and sometimes broken, and prevents access over the right-of-way of The Esplanade to certain properties located along The Esplanade between Granada Avenue and Ocala Street. The wooden retaining wall is designed to retain sand just landward of the wall and allow a shell access road to be placed on the right-of-way of The Esplanade. The wooden retaining wall will be constructed as follows: (a) 8" x 20' wooden piling will be placed on 6' center and driven to an approximate depth of -14.00 (NGVD); (b) 2" x 8" planking will be attached to the landward side of the piling from the top of the piling (+7.0 NGVD) to a depth of appropriate 7 feet (0.00 NGVD); (c) with a filter "x" cloth covering the planking on the landward side. At the time of the application, the existing beach was +5.0 (NGVD) which would leave approximately 2 feet of the retaining wall exposed on the seaward side. The purpose of the retaining wall is to protect the shoreline in the immediate vicinity of The Esplanade and thereby protect the sewer line and access road which are landward of the seaward (west) right-of-way line of The Esplanade. The proposed wooden retaining wall is to be located as far landward as possible, and will be the minimum size and configuration to protect the sewer line and the shell access road along The Esplanade right-of-way. The retaining wall is designed to be temporary in nature in that its design will not allow it to survive under a major storm event. In that regard, the retaining wall comes within the definition of a minor structure as defined by rule and does not require a formal written review. The access road will enable Venice to establish a public road on public right-of-way for ordinary and emergency utilization by the residents and Venice. Previous attempts by Venice to protect the sewer line by "shoring up" the area with sand bags have proven unsuccessful. A wooden retaining such as the one proposed would be the next logical step to prevent the exposure and damage to the sewer line and still be consistent with the coastal armoring policy adopted by the Governor and Cabinet in December 1990. Dr. Al Deveraux, Bureau Chief, Control Engineering, personally viewed the site prior to approval of the project and waived compliances with certain provisions of the application. There is sufficient competent substantial evidence to establish that: erosion is occurring in the area of the proposed site without the presence of the proposed retaining wall; without the proposed retaining wall, Venice will be unable to prevent that erosion, particularly during the winter storm events, which will result in exposure and damage to the sewer line and lack of public access to certain properties located along The Esplanade between Granada Avenue and Ocala Street; and upon construction of the retaining wall, the beach dune area and the adjacent properties to the south of the proposed project will experience some increase in erosion above that presently occurring, but it will be minimal and will not have a significant impact on the area. The application submitted by Venice was processed and approved in accordance with statutes, rules and Department policy. There is sufficient competent substantial evidence to establish that granting CCCL permit number ST-820 and constructing the retaining wall and access road as set forth in Venice's application would be in the best public interest. The Petitioners' expert witness on coastal engineering concluded that there would be substantial erosion of the beach dune area and adjacent properties south of the proposed retaining wall as a result of constructing the retaining wall. However, this conclusion was not supported by competent substantial evidence. Special permit condition 1 requires Venice to provide the Department with a Sea Turtle Protection Plan approved by the Florida Marine Research Institute in St. Petersburg, Florida. This special condition takes into account the Department's policy for the protection of sea turtles as described in Rule 16B-33.005(9), Florida Administrative Code. The project is consistent with the thirty-year erosion projection and is not located seaward of that line.
Recommendation Having considered the foregoing findings of fact and conclusions of law, it is, accordingly recommended that the Department enter a Final Order issuing CCCL permit number ST-820 to the City of Venice, Florida subject to all the special conditions contained therein, and adding one other special condition requiring the City of Venice, Florida to monitor the beach dune system and adjacent properties south of the project site on a semi-annual basis for a period deemed necessary by the Department, and report any accelerated erosion that might occur in that area to the Department for review and action. RECOMMENDED this 27th day of December, 1991, in Tallahassee, Florida. WILLIAM R. CAVE Hearing Officer Division of Administrative Hearings The DeSoto Building 1230 Apalachee Parkway Tallahassee, FL 32399-1550 (904) 488-9675 Filed with the Clerk of the Division of Administrative Hearings this 27th day of December, 1991.
