The Issue The central issue in this case is whether the Department of Environmental Protection (Department) should approve a permit for the applicant, Indian River County (County), to install a prefabricated erosion prevention reef (PEP reef) off the coast of Vero Beach, Florida.
Findings Of Fact The Department is the state agency charged with the responsibility of reviewing and approving permits such as the one at issue. The County is a governmental entity and is the applicant which has requested a permit for an experimental project to be located in Vero Beach, Florida. The Petitioners oppose the proposed project. The project at issue is the installation of a PEP reef system to be located between approximately 300 feet south of reference monument R-80 to approximately 300 feet south of reference monument R-83, in Indian River County, Florida. Because of the uncertainty as to the performance of the proposed project and the potential that it may cause adverse impacts to the coastal system, the Department classified the project as experimental pursuant to Chapter 89-175, Section 27, Laws of Florida. In making its preliminary approval for the permit, the Department required special permit conditions to safeguard the coastal system and marine turtles. Additionally, the Department specified both preconstruction and post installation monitoring and testing. The term of the permit is limited to five years, including three years to monitor the project's impacts. A PEP reef is a prefabricated erosion prevention product installed as a breakwater off the shore. In this case, the product measures approximately twelve feet long and six feet high. The base of the product (which is conically shaped) is approximately 15 feet tapering to a one foot crest at the top. The PEP unit is a proprietary product of a company called American Coastal Engineering (ACE). The County proposes to contract with ACE for the manufacture and installation of the units. It is proposed that the PEP units would be installed in an alignment parallel to the beach for a total, though not continuous, length of 3000 feet. The proposed location for the PEP reef in Vero Beach is in an erosion area as identified by the Department's Beach Restoration Management Plan. Historically, the subject beach has experienced a steady and continuous erosion which has been exacerbated during storm conditions. The proposed site is suitable for the experimental nature of this project. At least one past storm event caused substantial damage to the beach front at the project site. Walkways, utilities, and other public improvements were substantially damaged. Past efforts to curb the erosion have proved unsuccessful. Such efforts included beach renourishment, and the installation of seawalls or bulkheads. Future beach renourishment is undesirable for the project site due to the lack of compatible sand, and its high cost. More important, however, are concerns over the negative environmental impacts to nearshore reefs which could result from a large scale renourishment project. For over ten years the County has sought a solution to the erosion that has plagued the project site. To that end, the County established a special committee, the Beach and Shore Preservation Advisory Committee, to review options available and to recommend long-term solutions to the County. In June, 1993, the County contracted with Petitioner Walther to prepare a map of the nearshore hardbottom reef and to evaluate alternatives for beach restoration at the project site. Such work was completed, and recommendations from Mr. Walther were not incompatible with the installation of the proposed reef. The proposed installation should not adversely affect the hardbottom reefs which are in the vicinity of the PEP units. Such hardbottom is considered environmentally sensitive; however, no PEP unit will be placed on the hardbottom or so close to it that it will disturb the organisms located within the hardbottom community. In December, 1993, the County submitted an application for an experimental coastal construction permit to install the PEP reef which is at issue. The PEP units are to be placed in seven to ten feet of water. The PEP reef is designed to reduce wave heights, particularly during a storm event, which should reduce the wave energy and currents in the lee of the structure. While it is hoped the units will deter erosion, they may also cause some accretion to the beach. Whether such accretion would be temporary or long- term is uncertain. As a result of studies performed by the University of Florida under the direction of Dr. Dean, and supported by the County's coastal engineer Mr. Donaldson, it was determined that the PEP units should be installed in shorter lengths (than originally designed) with gaps between each segment. Consequently, the installation proposed by the County is not continuous but is staggered and gapped. The installation proposed by the County is unique in that the coastal characteristics of the area and the proposed design should produce results different from past installations of reef structures in Palm Beach County, Florida. As a result, studies performed by Dr. Dean in connection with a reef installed in Palm Beach County have been discounted as dissimilar to the one proposed in this case. In reviewing the subject permit application, the Department requested additional data which the County retained Dr. Zarillo to gather. Dr. Zarillo performed numerical modeling for the proposed reef system. Based upon Dr. Zarillo's work it is expected that the PEP reef system will have a positive benefit in that wave height and energy is likely to be reduced by the installation of the units. The site for the installation is suited for the proposal and is not within an area that is considered environmentally sensitive. Moreover, the PEP reef itself will add to the development of species since it should develop into a nursery habitat for young fish and other marine organisms. The installation of PEP reefs at other locations have proven to be both successful and unsuccessful. Having considered the studies performed by Dr. Bruno, an expert in coastal engineering and in measuring/modeling coastal processes, it is likely that the proposed project will be similar enough in design to installations reviewed by Dr. Bruno to allow the proposed project to be compared. Dr. Bruno has monitored three installations at three different sites in New Jersey. Each site had different results based upon conditions of each location. One site, expected to be most like the proposed site in Vero Beach, has experienced a reduced rate of erosion. Based upon Dr. Bruno's "real life" experience it is expected that the proposed installation will result in a reduction of wave height on the order of 10 percent to 20 percent. Consequently, the proposed installation should provide a benefit to the control of erosion. The reduction of wave height leads to a reduction in the erosive power of the wave field. Therefore, it is expected to result in a reduced erosion rate behind the PEP reefs. Additionally, Dr. Bruno's assessment of Dr. Zarillo's modeling work suggests that "in theory" the proposed site should experience a reduction in wave height as a result of the proposed installation. As a result, both scientific methods support the proposed project. No scientific study can, however, assure the success of this project. In fact, success may be derived from the value of the data which will be gathered during the monitoring period. Such data may assist in the future design of structures to reduce wave energy. The County's proposed monitoring plan contains detailed and adequate performance criteria to assure that the PEP reef system will be fully evaluated. The County has provided adequate assurance that it will comply with the permit conditions, including the modification or removal of the reef system if directed by the Department. All installation and monitoring as well as removal is to be performed at the County's expense. The PEP reef system will have no appreciable adverse impact on marine turtles. Construction is prohibited during nesting season under the terms of the permit. The PEP reef system will have no adverse impact on swimmers or boaters. The units are to be clearly marked and identified under the terms of the permit. No adverse impacts to Petitioners Walther and Clemens should be incurred as a result of the installation of the proposed project.
Recommendation Based on the foregoing, it is, hereby, RECOMMENDED: That the Department of Environmental Protection enter a final order approving the permit requested by the County. DONE AND ENTERED this 16th day of February, 1996, in Tallahassee, Leon County, Florida. JOYOUS D. PARRISH, Hearing Officer Division of Administrative Hearings The DeSoto Building 1230 Apalachee Parkway Tallahassee, Florida 32399-1550 (904) 488-9675 Filed with the Clerk of the Division of Administrative Hearings this 16th day of February 1996. APPENDIX TO RECOMMENDED ORDER, CASE NO. 95-4045 Rulings on the proposed findings of fact submitted by the Petitioner Walther: 1. Paragraphs 1, 3, 4, 6, 7, 8, 9, 10, 12, 13, 16, 17, 26, 29, 42, 44, 47, 50, 51, 59, and 60 are accepted. With regard to paragraph 2, the allegation is hearsay as it relates to the record cited; however, although not stipulated, the record most likely supports the paragraph in substance. Paragraph 5 is rejected as irrelevant. There is no evidence to support the factual conclusion that because another permit holder has failed to remove a reef that the County will similarly default on its obligation to do should the agency order the PEP reef removal. Paragraph 11 is rejected as irrelevant. Paragraph 14 is rejected as irrelevant if it purports to suggest the contracting was improper; this proceeding does not consider the propriety of the contracting process. With the deletion of any emphasis and the last sentence which are rejected as argument, paragraph 15 is accepted. Paragraphs 18 through 24 are rejected as irrelevant or contrary to the weight of credible evidence. Paragraph 25 is rejected as hearsay; it is accepted that Mrs. Clemens opposed the permit and requested a hearing. Paragraph 27 is rejected as an incomplete statement and therefore not supported by the total weight of credible evidence. Paragraph 28 is rejected as irrelevant or contrary to the weight of credible evidence. Paragraphs 30 through 33 are rejected as law not statements of fact. Paragraph 34 is accepted in general terms but not as to the specific measurements cited. Paragraphs 35 through 38 are rejected as contrary to the weight of all credible evidence. It is determined that the site is suitable for a non-biased, comprehensive analysis of the project. Paragraphs 39 through 41 are rejected as contrary to the weight of all credible evidence. Paragraph 43 is rejected as irrelevant. With regard to paragraph 45, it is accepted the reefs may settle but such is expected to be unlikely to impair the overall performance of the structure; therefore, the paragraph, as drafted, must be rejected as contrary to the weight of all credible evidence. Paragraph 46 is rejected as argument or contrary to the weight of all credible evidence. Paragraph 48 is rejected as argument or contrary to the weight of all credible evidence. Paragraph 49 is rejected as unclear or incomplete to stand as a finding of fact or contrary to the weight of all credible evidence. Paragraph 52 is rejected as irrelevant. Paragraph 53 is rejected as incomplete to stand as a finding of fact or contrary to the weight of all credible evidence. Paragraphs 54 through 58 are rejected as irrelevant or contrary to the weight of all credible evidence. With regard to paragraph 61, it is accepted that Dr. Dean envisioned a current being created that would run parallel to the shoreline as a result of the reef installation but otherwise rejected as irrelevant or contrary to the weight of all credible evidence. With regard to paragraph 62, such statement is generally true; however, Dr. Dean did not conduct any sediment transportation test to verify that the structure in an open setting (as opposed to the experimental tank) would transport sediment as inferred. Paragraphs 63 through 67 are rejected as irrelevant or contrary to the weight of credible evidence. Paragraph 68 is accepted as accurate but the agency did not express, and the record does not establish, that there is a concern that the County may not honor its agreement to remove the PEP reef if directed to do so. Paragraph 69 is rejected as irrelevant. Rulings on the proposed findings of fact submitted by the Petitioner Clemens: 1. None submitted. Rulings on the proposed findings of fact submitted by the Respondent Department: All proposed findings of fact adopted by the Department as listed are accepted. See comments below as to rulings on the proposed findings of fact submitted by the County. Rulings on the proposed findings of fact submitted by the Respondent County: 1. Paragraphs 1 through 5, 7 through 15, 17, 20, 21, 23, 24, 26, 27 through 30, 34, 40, 41, 42, 43, 45, and 46 are accepted. With regard to paragraph 6, it is accepted that an extensive renourishment program might damage the sensitive nearshore hardbottom community; otherwise rejected as irrelevant. With regard to paragraph 16, with the deletion of the word "significantly" in the second sentence and the last sentence which are rejected as irrelevant, editorial comment, argument or not supported by the total weight of credible evidence, it is accepted. With regard to paragraph 18, the first sentence is accepted. As to the balance of the paragraph, with the deletion of the word "significantly" and the substitution of "might" for "could", the paragraph is accepted. Otherwise rejected as an inaccurate characterization of the weight of the record. With regard to paragraph 19, the first sentence is accepted. The remainder of the paragraph is rejected as irrelevant. Paragraph 22 is rejected as a compound statement of proposed fact some of which are accurate but which taken in whole constitute argument, unnecessary, irrelevant or not supported by the weight of the credible evidence. Paragraph 25 is rejected as unnecessary or irrelevant. With regard to paragraph 31, with the deletion of the word "significant" in sentence three, the paragraph is accepted. With regard to paragraph 32, with the deletion of the word "significant" in sentence two, the paragraph is accepted. Paragraph 33 is rejected as repetitive, unnecessary or irrelevant. With regard to paragraph 35, the first sentence is accepted. The remainder of the paragraph is rejected as unnecessary, comment, argument, or irrelevant. Paragraphs 36 through 38 are rejected as unnecessary, comment, argument, or irrelevant. The proposed PEP reef should not adversely impact the Vero Beach shoreline. Paragraph 44 is rejected as unnecessary, comment, argument, or irrelevant. With regard to paragraphs 47 through 53, it is accepted that the Petitioners did not establish that they will be substantially affected by the proposed project; however, their conduct does not rise to the level to establish participation in the administrative process was for an improper purpose. Consequently, the paragraphs are rejected as argument, irrelevant or contrary to the weight of the credible evidence. COPIES FURNISHED: Steve Lewis, Esquire John W. Forehand, Esquire LEWIS, LONGMAN & WALKER, P.A. 215 S. Monroe Street, Suite 702 Post Office Box 10788 Tallahassee, Florida 32302 Kevin S. Hennessy, Esquire LEWIS, LONGMAN & WALKER, P.A. 2000 Palm Beach Lakes Boulevard Suite 900 West Palm Beach, Florida 33409 Michael P. Walther 1725 36th Avenue Vero Beach, Florida 32960 Adele Clemens 3747 Ocean Drive Vero Beach, Florida 32963 Thomas I. Mayton, Jr. Dana M. Wiehle Assistants General Counsel Department of Environmental Protection 3900 Commonwealth Boulevard Tallahassee, Florida 32399-3000 Virginia B. Wetherall Secretary Department of Environmental Regulation Douglas Building 3900 Commonwealth Boulevard Tallahassee, Florida 32399-3000 Kenneth Plante General Counsel Department of Environmental Regulation 3900 Commonwealth Boulevard Tallahassee, Florida 32399-3000
Findings Of Fact Nannette K. Scoggins is the owner of the real property located at 5622 Gulf Drive, Holmes Beach, Florida in Manatee County. Nannette K. Scoggins' property, the petitioner's property, 5624 Gulf Drive, and the other adjacent property, 5620 Gulf Drive, are zoned as "A-1 Hotel-Motel" under the City of Holmes Beach Zoning Ordinance. On November 13, 1983, Mrs. Scoggins submitted to DNR an application for a permit for construction seaward of the coastal construction control line (control line). The proposed project, known as Jansea Place, would consist of two multifamily dwellings, four units to a building, divided by a swimming pool. A portion of the most seaward building would extend a maximum of 57 feet seaward of the control line. By letter dated July 11, 1984, DNR notified petitioner that the department was considering the permit application. The petitioner responded by letter dated July 18, 1984, objecting to any construction seaward of the control line. On October 1, 1984, petitioner received notification that DNR intended to recommend approval of the permit. The permit was scheduled for a vote by the Governor and Cabinet on October 16, 1984. The staff of DNR recommended approval of the permit. By telegram dated October 15, 1984, the petitioner requested an administrative hearing, and on October 22, 1984, petitioner filed a petition for a formal administrative hearing pursuant to Section 120.57(1), Florida Statutes. The application for permit No. ME-89 is a complete application for permit to construct seaward of the coastal construction control line. On October 5, 1983, the Superintendent of Public Works of the City of Holmes Beach certified that this project does not violate any ordinance of the City of Holmes Beach. The plans for the proposed project are signed and sealed by an architect registered in the State of Florida, and the submitted plans comply with the design standards established in Rule 16B-33.07, Florida Administrative Code to resist adequately the natural forces associated with a 100-year return interval storm event. The plans, specifications, drawings and other information submitted to DNR with the application for permit to construct seaward of the coastal construction control line are complete and accurate, and meet the requirements of DNR for that purpose. Under the provisions of Rule 16B-33, Florida Administrative Code, the application was determined to be complete on August 6, 1984. The proposed construction is located landward of an existing vertical concrete bulkhead. The seawall was built jointly by the Scoggins and Mr. McLean, who owns the property immediately to the south of the Scoggins' property. The seawall was built after the hurricane of 1972 because the existing dune system had been destroyed. Since that time, the mean high water line has continued to encroach landward to the point where it is now east of the wall. However, the seawall is not necessary for the protection of the proposed building. Although the seawall would fail under the direct impact of a major hurricane, the proposed building is adequately designed to withstand the impact erosion, the wave loads, the winds, and the water forces associated with a major hurricane. The necessity and justification for the project's location in relation to the control line is stated in the application, and petitioner has not challenged the necessity or justification. The City of Holmes Beach Zoning Ordinance requires that the buildings be separated by a minimum of 30 feet. Since the proposed buildings are separated by 30 feet, the proposed seaward building is located as far landward as possible without violating the zoning ordinance. Erosion and structural damage occurred as a result of Hurricane Agnes in 1972 and the "No Name" storm in 1982 in the area between 1,000 feet south of the Scoggins' property and 500 feet north of the Scoggins' property. Although the beach was fairly stable from 1974 to 1979, the beach began to erode in 1980. When the seawall was built in 1974, the dune line was even with the seawall. However, as can be seen from a comparison of the photographs taken in June of 1979 with those taken in early 1985, the beach has eroded since June of 1979 and the dune line is now several feet landward of the seawall. The DNR recommendation for approval of the Scoggin's permit application was based upon historical erosion data for the period between 1940 and 1974, which was the most recent data available that could be used to review the project. Mr. Clark stated that the application was recommended for approval based on the design of the proposed building and its alignment with existing structures built seaward of the control line. The proposed project is located landward of a line of existing structures. Although the adjacent properties have been affected by erosion, there was no evidence presented to show that the existing structures located seaward of the control line have been unduly affected by erosion. In 1974, when the seawall was being constructed, the worker building the seawall dug up part of the petitioner's property and destroyed the sea oats he had planted. However, the proposed project has a driveway encircling the building which would provide vehicular access to the seawall if necessary. The proposed project will partially obstruct petitioner's view to the southwest. However, there was no evidence presented that petitioner's property or the other adjacent property, would be adversely affected in any other way by the proposed project. There was no evidence presented that the proposed project would be affected by, or have an effect on, beach or coastal erosion. The proposed project would have no effect on the beach dune system.
Recommendation Upon consideration of the foregoing, it is recommended that DNR issue Permit Number ME-89 to Nannette K. Scoggins. DONE and ENTERED this 28th day of June, 1985, in Tallahassee Leon County Florida. DIANE A. GRUBBS 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 28th day of June, 1985.
The Issue Whether the Petitioners, and each of them, have standing to bring the instant action before the Division of Administrative Hearings. Whether the 5500 North Corporation has meets the requirements set forth in Section 161.053, Florida Statutes, and Rule 16B-33, Florida Administrative Code, for obtaining a permit to construct a structure seaward to the coastal construction control line (CCCL).
Findings Of Fact The Department of Environmental Protection, f/k/a Department of Natural Resources, is the state agency charged with the responsibility of regulating coastal construction under Chapter 161, Florida Statutes. 5500 North Corporation (Respondent/Applicant) is the owner of the property located at 5600 North Atlantic Avenue, Cocoa Beach, Brevard County, Florida 32931. 5500 North Corporation submitted an application for a coastal construction control line (CCCL) permit to build on the vacant portion of its property, a seven (7) story building, along with required access drives and parking, as an addition to the Cocoa Beach Days Inn Hotel complex. The site of the proposed Days Inn Tower fronts on the Atlantic Ocean and is located three (3) miles south of Port Canaveral, near DNR survey monument R-16. The application and attached document were compiled and submitted to the Department of Environmental Protection by Plata Engineering, Inc., and consisted of the following documents: Application to the Department for the proposed construction of the building, consisting of three pages, front and back, six pages total. A legal description of the property, and a Warranty Deed for the property demonstrating ownership in 5500 North Corporation. Reduced certified survey of the site, showing control lines and other required information. Reduced Site Plan prepared by Plata Engineering, Inc. Section C - which is a section through the site plan, showing the dune configuration in relation to the proposed building and the construction control lines. A depiction of a section through the proposed building and some of its structural elements. Full size drawing of the proposed site. Turtle assessments form with attached lighting specifications of the manufacturer, and aerial of the site attached. Structural Design Calculations. Complete set of Building Plans, dealing with floor planning, and the structural elements of the calculations that were submitted with the structural calculations. The application was deemed complete, and on May 20, 1993, the Department issued a proposed Final Order issuing Permit Number BE-760 for the proposed structure. Standing of Petitioners Petitioner, Carole Pope, resides in the City of Rockledge, Brevard County, Florida. She is the owner of Lot 11, Block 101 of the platted subdivision known as Avon-By-The Sea which is located in unincorporated Brevard County, north of the existing north boundary of the City of Cocoa Beach. A duplex dwelling unit is located on the parcel. Petitioner occupies one unit annually during the summer. Petitioner Pope's property is not adjacent to the property where the proposed Days Inn Tower is to be located. The property is located approximately three blocks directly north of the proposed building and measures 475 feet east- west by 50 feet north-south and is bounded on the east by the Atlantic Ocean. Petitioners, Hugh and Cora Harris, own property located at Lot 13 of replat of Blocks 104 and 105, Avon-by-the Sea, in the unincorporated land of Brevard County, which borders on the City of Cocoa Beach. Petitioners' property is located across Young Avenue, and north of the property owned by 5500 North Corporation. The Harris's property contains a single family dwelling unit and is adjacent to the property were the proposed Days Inn Tower is to be located. Petitioners, Patricia A. and Eugene A. Wojewoda, own a unit at the Cocoa Beach Towers, a multi-family condominium, which is located north of the property owned by 5500 North Corporation, across Young Avenue, in the City of Cocoa Beach. The Wojewoda's unit is located on property which is adjacent to the property where the proposed Days Inn Tower is to located. Petitioners Wojewodas are Real Estate Brokers and owners of Professional Touch Realty, Inc. One of their four offices is located at 108 Young Avenue, immediately across the street and north of the subject property. Petitioners, Howard and Martha Crusey, own a unit, which they rent out, in the Cocoa Beach Towers, which is located north and adjacent to the property owned by 5500 North Corporation. Petitioners reside at 430 Johnson Avenue in Cape Canaveral, Florida. The Department sent out a notice for public comment to each of the immediate adjacent property owners. Existing Uniform and Continuous Line of Construction As part of the application process, the Department made a determination of the existing line of uniform and continuous construction. The existing line of uniform and continuous construction is a theoretical line that goes from the most seaward extent of the two adjacent structures, where adjacent structures exist, and extends north and south along the seaward edge of the structures. In the instant case, there is historical development of major habitable structures on either side of the parcel for which the proposed building is being constructed and which are co-terminus with the prior CCCL. The footprint of the proposed Days Inn Tower does not extend seaward of the existing uniform and continuous line of construction, although a new structure (Discovery Beach) north of the Cocoa Beach Towers has been constructed landward of the current CCCL. The existing structures, which form the existing line of uniform and continuous construction, have not been unduly affected by erosion. The property was purchased by 5500 North Corporation in 1988. The property was commercially developed with the existing hotel buildings between 1959 and 1962, and the site has been operated as a hotel since that time. The footprint of the building was set by the engineers based on the parking requirements of the City of Cocoa Beach, and environmental concerns. It was determined that if the parking were located on the seaward side of the building, there would be drainage problems, and the need for a storm water treatment system for the parking lot. With the parking lot located landward of the proposed building, there will be no drain off to the side areas, but rather drain off would be to the middle of the property where the exfiltration system is located. The parking lot located landward of the proposed building meets the City of Cocoa Beach parking requirements and the drainage requirements. When siting the footprint of the proposed building, the engineers also took into consideration the fact that if the parking were located on the seaward side of the proposed building, the headlights would shine out to the beach and possibly impact sea turtles nesting. The applicants stated that construction seaward of the control line or 50-foot setback is considered necessary for reasonable use of the property, for the following reasons: The proposed building is basically an addition to a completion of the original concept of the overall hotel complex that was never completed in the past due to either financial or room availability need. The proposed placement seaward of the CCCL can be attributed to the configuration of the existing on-site buildings and the require- ment to satisfy the City of Cocoa Beach's extensive parking and limited access point requirements that have been subjected to this proposed site development. Please note that the proposed building is not being placed seaward of the existing line of continuous construction that has been established by the adjacent buildings to the north and the south. The Department determines necessity based upon the impacts the proposed structure will have on the active beach, and the dune system, and the neighborhood properties including the subject property, how the property is zoned, and whether it is situated behind the existing continuous line of construction. It is the Department's opinion that if the proposed building is in compliance with the standards established in Chapter 16B-33, F.A.C., the necessity of the proposed building has been justified. Impacts to the Beach-Dune System The greater weight of evidence supports the conclusion that the shoreline fronting the site of the proposed Days Inn Tower is stable. This section of the coastline has historically been accretional, and still continues to be accretional. There exists adequate evidence of current littoral trends. There exists accepted methodologies for determining evidence of expected wind, wave, hydrostatic and hydrodynamic forces associated with the design storm event which was presented in 5500 North Corporation's application for CCCL permit. Based on the 1989 Brevard County Study conducted by Olsen and Associates, Inc., there is no erosion at the location of the proposed building, instead the shoreline is prograding seaward instead of landward. Therefore, the shoreline is at least stable or accretional. Based on its in-house analysis, the Department of Environmental Protection conservatively adopted an erosion rate of one foot per year, which is considered a relatively minor erosion rate. Based on the Department of Environmental Protection's projection of the erosion for the area being one foot per year, the location of the proposed building lies well in excess of 200 feet landward of the thirty-year seasonal high water line. Although the proposed structure extends 118 feet seaward of the CCCL, the setback of the proposed building from the existing dune line is significant; therefore, there was no evidence of a threat of impact on the beach, to the beach or dune system as a result of the construction at the specific site. There are existing devices (i.e., an existing fence on the property which funnels people into boardwalks so that people cannot walk uncontrolled on the beach dune system) implemented in Brevard County and specifically on the site which will help manage people impacts as well. The setback between the dune and the proposed construction qualitatively relates to the ability of the site to recover after a one-hundred year storm. If a structure is located too far seaward, either immediately adjacent to or on top of the dune, it would inhibit the natural storm recovery process. The proposed building is set a significant distance landward of the dune formation itself, so there will be adequate room for the dune to recover in the future should there be a one-hundred year storm event. The proposed structure is located at a sufficient distance landward of the beach-dune system to permit natural shoreline fluctuations and to preserve the dune stability and the natural recovery following storm induced erosion. The proposed construction will not have a cumulative impact that will threaten the beach or dune system or its recovery potential following a major storm event. low. Impacts to Adjacent Property Owners The probability of potential impacts to adjacent property owners is One reason the proposed building will not have adverse impacts to adjacent properties is that the proposed building is located significantly landward, and does not go further seaward than the existing line of construction. The adjacent buildings were constructed landward of the previous CCCL. The nature of the design associated with the particular project or the structural components of the design also minimize the impact to the parcel and to adjacent parcels. The first feature of the design of the proposed building is that the major habitable floors of the building are above the elevation of the one- hundred year storm and wave activity on top of the storm surge, so they will not be impacted by the water height or the wave activity of the storm. The second feature of the design of the proposed building is that everything below the habitable floors is designed to break away and lie down during any impact by wave activity, which allows the storm to go through the building rather than having those forces exerted on the building itself. The frangible driveway is designed so that the individual stones will fall as the grade falls, and most of them will end up buried in the event of a storm. The third feature of the design of the proposed building is that the building is elevated on a pile foundation which is sunk to a depth which is sufficient to accommodate for the anticipated erosion of a one-hundred year storm, and the pile caps are sunk well into the ground so that they do not contribute to erosion. Therefore, the building has been designed to withstand the one-hundred year storm, and the dynamics of the storm are allowed to go through the building and to be dissipated, in contrast to endangering the building or endangering adjacent properties. Due to the fact that the proposed building is "super-elevated and the portions that are actually impacted by the one-hundred year storm being frangible," the proposed building will not impact the adjacent properties. The proposed Days Inn Tower would serve to protect the adjacent Cocoa Beach Towers, and Petitioner Harris's property, by blocking the impact of a storm coming from the southeast. The proposed structure is designed so as to minimize any expected adverse impact on the beach dune system or adjacent properties or structures and is designed consistent with Section 16B-33.005, Florida Administrative Code. The proposed building meets the requirements of Chapter 161, Chapter 16B-33, Florida Administrative Code. Structural Design of Proposed Building The applicant provided adequate engineering data to the Department concerning the construction design of the building. The structure is designed in accordance with the minimum building code adopted for the area pursuant to Section 553.70-553.895, Florida Statutes. The proposed building is designed in accordance with the local code, and, in the opinion of the structural engineer who designed the building, either meets or exceeds the required codes. The proposed building is designed in accordance with Section 6, American National Standards/American Society of Civil Engineering 7-88 (July 1990) "Minimum Design Loads for Buildings and Other Structures", and has a minimum basic wind speed of 110 miles per hour. The proposed building is designed so that the building and its components will not become airborne missiles. The plans for the windows and doors require that they meet the 110 miles per hour wind loads. The proposed building is made of concrete reinforced masonry, and does not have bricks or attached masonry which could detach in a storm and become airborne. There are no substantial walls or partitions to be constructed below the level of the first finished floor, except for the elevator and stairs, seaward of the CCCL. The walls on the first floor are frangible walls which are designed to resist the 110 mile per hour wind pressure, but they lie down or collapse into the erosion hole created under wave surge pressure. The frangible walls are made of 4-inch thick concrete with reinforcing rods inside them, and are cut into 4 foot by 4 foot panels. The Department of Environmental Protection requires that any walls constructed below the one-hundred year storm surge plus storm wave elevations be frangible walls. The structural design considered the hydrodynamic loads which would be expected under the conditions of a one-hundred year storm event. The calculation for wave forces on building foundations and building superstructures is based on minimum criteria and methods given in professionally recognized documents accepted by the Bureau of Coastal Engineering and Regulation with the Department. The structural design considered hydrostatic loads which would be expected under the conditions of maximum water height associated with a one- hundred year storm event. The calculations for hydrostatic loads considered the maximum water pressure resulting from a fully peaked, breaking wave superimposed on the design storm surge. Both free and confined hydrostatic loads were considered in the design calculations. Hydrostatic loads which are confined were determined using the maximum elevation to which the confined water would fully rise if unconfined. Vertical hydrostatic loads were considered as forces acting both vertically downward and upward; however, there is no action upward because the maximum water level is at midlevel of the first floor and does not reach the second floor. The structural design considered the hydrodynamic loads which would be expected under the conditions of a one-hundred year storm event. The calculations for hydrodynamic loads considered the maximum water pressure resulting from the motion of the water mass associated with a one- hundred year storm event. Full intensity loading was applied on all structural surfaces above the design grade which would effect the flow velocities, which are above the first floor and are not reached by the wave surge. The proposed building is elevated on, and securely anchored to, an adequate pile foundation in such a manner as to locate the building support structure above the design breaking wave crests or wave uprush as superimposed on the storm surge with dynamic wave set up of one-hundred year storm. The piling foundation is designed to withstand anticipated erosion, scour, and loads resulting form a one-hundred year storm, including wind, wave, hydrostatic and hydrodynamic forces, and the pile caps are located below the erosion line as indicated by the Department's information and graphs. The elevation of the soil surface used in the calculation design grade is less than that which would result from the anticipated beach and dune erosion due to the one-hundred year storm event. The erosion calculations for foundation design account for all vertical and lateral erosions and scour producing forces. The pile caps are set below the design grade which includes localized scour, and are designed for the erosion of soil during the one-hundred year storm event. The piles are driven to a penetration which achieves adequate bearing capacity taking into consideration the anticipated loss of soil above the design grade, based on information provided by the geotechnical engineer's recommendation and the Department's requirements. The design plans and specifications submitted as part of the permit application for the proposed Days Inn Tower are in compliance with the standards established in Rules 16B-33, Florida Administrative Code. Turtle Impacts There is a two prong test which the proposed structure must meet to determine if the proposed building would have an adverse impact on nesting sea turtles. First, the proposed structure must not occupy marine turtle habitat, and second, the proposed structure's lighting must be adequate to eliminate adverse impacts to marine turtles. The effects of pedestrian traffic or flashlights on the beach are not considered by the Department when reviewing a permit application for adverse impacts to the marine turtles. The proposed building is sited significantly landward of the nesting beach, which is evidenced by the 75-foot wide dune stretch; therefore, it is not anticipated that the structure will result in any direct mortality of any marine turtle, nor would the building result in the degradation of the marine turtle nesting habitat. The proposed seven story structure will not occupy marine turtle habitat. The permit requirement to do dune restorative work, proposed by the Department, enhances the marine turtle habitat by further building the dune and enhancing the dune. Although the turtles do not nest beyond the dune crest, the dune is an integral part of protecting the habitat. There is a potential that the building, due to its height, could enhance marine turtle nesting habitat by blocking out the ambient glow from the City of Cocoa Beach which would create a dark beach directly in front of the proposed structure which could attract nesting. The applicant submitted a lighting plan to the Department which complied with the guidelines that are established in the information form entitled "Assessment to reduce impacts to marine turtles for lighting to reduce adverse impacts associated with coastal lighting." There are two main components of the lighting plan associated with the proposed building: the parking lot lights and the structural lighting. The parking lot lighting is designed as low-level Ballard-style lighting which is only 48 inches above the grade and emits light in a downward direction which will not be directly visible from the beach. The parking lot lighting design is the type recommended by the Department for parking lots, and is a good lighting design. The Department also recommends that an applicant plant hedges or landscape features to block out parking lights. The applicant is proposing to plant hedges in front of the 18 parking spaces that are on the seaward side of the proposed building. The structural lighting plan does have lighting on the seaward facade of the proposed building, which is not recommended by the Department, but the lights are designed to eliminate or significantly reduce the impact to marine turtles. The lights consist of canister, shielded, down-casting lights on the balconies which house a yellow bug lamp which is less impactive to turtles, and which is acceptable to the Department. The Department issued an approval letter regarding the proposed building to the project engineer which contained permit conditions for the protection of the marine turtles in association with the project. The permit conditions are as follows: No construction, operation, transportation or storage of equipment or materials is authorized seaward of the existing chain link fence located approximately 175 feet seaward of the coastal construction control line. No temporary lighting of the construction area is authorized at any time during the marine turtle nesting season (March 1 through October 31). All permanent exterior lighting shall be installed and maintained as depicted in the approved lighting schematic. No additional permanent exterior lighting is authorized. c All windows and glass doors visible from any point on the beach must be tinted to a transmittance value (light transmission form inside to outside) of 45% or less through the use of tinted glass or window film. Pursuant to the Department's requirements, the proposed construction will not have an adverse impact on nesting sea turtles, their hatchlings, or their habitat. Vegetation Impacts The vegetation patch on the dune system is approximately seventy five feet wide under today's conditions, and is probably growing to some degree. The vegetation system is basically comprised of a low-level dune which is planted both naturally and artificially with indigenous, salt-tolerant type vegetation, and sea oats. The existing line of construction which the proposed building is set behind is well landward of the zone of indigenous vegetation. Special condition #4 contained in the permit issued by the Department requires the applicant to convert some of the existing sodded area between the vegetation limits and the proposed construction to plantings with indigenous vegetation, which will serve to enhance the dune system. The native beach vegetation will be adequately protected by the permit conditions, given the location of the construction. Local Government Approvals On June 3, 1992, the Cocoa Beach Board of Adjustment granted a variance to the CCCL to the 5500 North Corporation for construction of the proposed building. Challenges to decisions of the City's Board of Adjustment is to the circuit court. In the instant case, the time for challenging the decision of the Board has expired. The City of Cocoa Beach Planning Board has the authority to approve site plans for site specific construction. The City's Planning Board has the responsibility of ensuring that the site plan conforms with the Comprehensive Plan and to recommend changes, if needed, to the City Commission. On July 13, 1992, the Cocoa Beach Planning Board voted to approve the site plan for the proposed building submitted by the 5500 North Corporation. The decision of the Planning Board granting approval of the 5500 North Corporation's site plan showed part or all of the building was seaward of the CCCL. The Petitioners did not file an appeal of the Planning Board's decision with the City Commission. Nor did they challenge the Planning Board's action in the circuit court. The 5500 North Corporation was not required to apply to the city commission for an amendment to the Cocoa Beach Comprehensive Plan in order to permit the proposed hotel tower to be located in the designated high hazard area. On July 6, 1993, the Building Official issued a building construction permit to the 5500 North Corporation for the proposed building, which has been subsequently extended for an unknown period of time. There are no other permits or local government requirements which have not been met by 5500 North Corporation. The applicant submitted written evidence to the Department from the City of Cocoa Beach, who has jurisdiction over the project, which stated that the project does not contravene local setback requirements, or zoning and building codes.
Recommendation Based on the foregoing findings of fact and conclusions of law, it is RECOMMENDED that the Department of Environmental Protection issue Permit Number BE-760 to the 5500 North Corporation, subject to the conditions proposed in the proposed Final Order. DONE and ENTERED this 24th day of March, 1994, in Tallahassee, Florida. DANIEL M. KILBRIDE Hearing Officer Division of Administrative Hearings The DeSoto Building 1230 Apalachee Parkway Tallahassee, Florida 32399-1550 (904) 488-9675 Filed with the Clerk of the Division of Administrative Hearings this 24th day of March, 1994. APPENDIX The following constitutes my specific rulings, in accordance with section 120.59, Florida Statutes, on proposed findings of fact submitted by the parties. Petitioners' Proposed Findings of Fact Accepted in substance: paragraphs 1 (in part) 2, 3 (in part), 4, 5, 6, 7, 8 (in part), 10, 12 (in part), 13, 16 (in part), 17, 18, 19, 23 (in part), 24 (in part), 26 (in part), 27 (in part), 29 (in part), 31 (in part), 38 (in part), 49, 51, 63, 68 (in part), 69, 70, 71, 73 (in part). Rejected as against the greater weight of evidence: paragraphs 15 (in part), 16 (in part), 27 (in part), 46, 50 (in part), 82 (in part). Rejected as subsumed, argument or Conclusions of law: paragraphs 1 (in part), 14, 15 (in part), 16 (in part), 21, 23 (in part), 25, 26 (in part), 27 (in part), 28, 29 (in part), 30, 31 (in part), 32, 33, 34 (in part), 35, 36, 37 (in part), 38 (in part), 39, 40, 41, 42, 43, 44, 45, 47, 48, 50 (in part), 52, 56, 57, 58 (in part), 59 (in part), 61, 62, 64, 65, 66, 67, 68 (in part), 72 (in part), 73 (in part), 76, 77, 78, 79, 80, 81, 82 (in part), 83, 84. Rejected as irrelevant or immaterial: paragraphs 3 (in part), 5, 8 (in part), 9, 11, 12 (in part), 20, 22, 24 (in part), 34 (in part), 53, 54, 55, 58 (in part), 59 (in part), 60, 72 (in part), 74, 75. Respondent's Proposed Findings of Fact: Accepted in Substance: paragraphs 1, 2, 3, 4, 5, 6, 7, 8, 9, 10, 11, 12, 13, 14, 15, 16 (in part), 17, 18, 19, 20, 22, 23, 24, 25, 27, 29, 30, 35, 36 (in part), 37, 38, 39, 40, 41, 42, 43, 44, 45, 46, 47, 48, 49, 50, 51, 52, 53, 54, 55, 56, 57, 58, 59, 60, 62, 63, 64, 65, 66, 67, 68, 69, 70, 71, 72, 73, 74, 75, 76, 77, 78, 79, 80, 81, 82, 83, 84, 85, 86, 92, 93 (in part) 94, 95, 96, 97, 98, 99, 100, 101, 102, 104, 105, 106, 107, 108, 109, 110, 111, 112, 113, 114, 115, 116, 117, 118. Rejected as against the greater weight of evidence: paragraph 16 (in part). Rejected as subsumed, argument or irrelevant and immaterial: paragraphs 21, 26, 28, 31, 32, 33, 34, 36 (in part), 61, 87, 88, 89, 90, 91, 93 (in part), 103. COPIES FURNISHED: Virginia B. Wetherell, Secretary Department of Environmental Protection Twin Towers Office Building 2600 Blair Stone Road Tallahassee, Florida 32399-2400 Kenneth Plante Department of Environmental Protection Twin Towers Office Building 2600 Blair Stone Road Tallahassee, Florida 32399-2400 Hugh and Cora Harris (pro se) 208 Young Avenue Cocoa Beach, Florida 32931 Howard and Martha Crusey (pro se) 430 Johnson Avenue, Apartment #304 Cape Canaveral, Florida 32920 Carole Pope (pro se) 715 Rockledge Drive Rockledge, Florida 32955 Patricia and Eugene Wojewoda 830 North Atlantic Avenue Cocoa Beach, Florida 32931 Dana M. Wiehle, Esquire Assistant General Counsel Department of Environmental Protection Twin Towers Office Building 2600 Blair Stone Road, MS-35 Tallahassee, Florida 32399 Wilbur E. Brewton, Esquire Kelly Brewton Plante, Esquire Taylor, Brion, Buker & Greene 225 South Adams Street, Suite 250 Tallahassee, Florida 32301
The Issue The issue is whether the Department of Environmental Protection should approve Petitioner’s application for a coastal construction control line permit.
Findings Of Fact Stipulated Facts2 Petitioner, Beach Group Investments, LLC (Beach Group), is a limited liability corporation under Florida law. Its address is 14001 63rd Way North, Clearwater, Florida 33760. On December 19, 2005, Coastal Technology Corporation (Coastal Tech) on behalf of Beach Group submitted to the Department an application for a CCCL permit pursuant to Chapter 161, Florida Statutes, to construct 17 luxury townhome units in two four-story buildings, a pool, a dune walk-over, and ancillary parking and driveway areas (hereafter “the Project”). The Department designated the application as File No. SL-224. The property on which the Project is proposed (hereafter “the Property”) is located between the Department's reference monuments R-34 and R-35, in St. Lucie County. The Property’s address is 222 South Ocean Drive, Fort Pierce, Florida. The Property is located seaward of the CCCL line established in accordance with Section 161.053, Florida Statutes, and Florida Administrative Code Rule Chapter 62B-33. On April 21, 2006, the application was determined to be complete. By letter dated June 5, 2006, the Department notified Beach Group that the Project appeared to be located seaward of the 30-year erosion projection of the seasonal high water line (SHWL), and that in accordance with Section 161.053(6), Florida Statutes, the staff could not recommend approval of the Project since major structures are seaward of the estimated erosion projection. By letter dated July 7, 2006, and subsequent submittals, Beach Group requested a waiver of the 90-day time period for processing completed applications pursuant to Chapter 120, Florida Statutes, until October 31, 2006. On August 30, 2006, Beach Group submitted a certified engineering analysis of the 30-year erosion projection of the SHWL for the Department's consideration pursuant to Florida Administrative Code Rule 62B-33.024(1). Beach Group's analysis determined that the proposed major structures associated with the Project were located landward, not seaward, of the 30-year erosion projection. The Department also performed its own 30-year erosion projection of the SHWL, and determined that the proposed major structures were located seaward, not landward, of the 30-year erosion projection. The Department asserts that the proposed structures are located between 87 feet and 68 feet seaward of the Department's determination of the 30-year erosion projection. The Department disagreed with Beach Group's analysis because the analysis appeared to be inconsistent with Section 161.053(6), Florida Statutes, Florida Administrative Code Rule 62B-33.024, and the Department's own analysis. The Property is located just south of the Fort Pierce Inlet, and landward of a federally maintained beach restoration project that had approximately 14 years of life remaining under the existing Congressional authorization when the permit was submitted to the Department. By proposed Final Order dated November 1, 2006, the Department provided to Beach Group notice of its intent to deny the permit application. The proposed Final Order was received by Beach Group on November 8, 2006. Beach Group's petition for hearing was timely filed with the Department. Since the Department proposes to deny Beach Group's CCCL permit application, its substantial interests are clearly at issue, and it has standing to maintain this proceeding. On December 11, 2006, the Department issued an environmental resource permit for the Project. The Department denied Beach Group’s permit application because the Project extends seaward of the 30-year erosion projection calculated by the Department and because the Project’s impacts to the beach-dune system had not been minimized. The permit was not denied on the basis of the existence, or absence, of a line of continuous construction in the vicinity of the Project. The 30-year Erosion Projection (1) Background Fort Pierce Inlet (hereafter “the inlet”) was constructed by the Army Corps of Engineers in the 1920’s. The channel of the inlet is protected by two jetties that extend several hundred feet into the Atlantic Ocean. The jetties act as a barrier to the littoral transfer of sand from the north to south that would otherwise occur along the beach in the vicinity of the Property. The jetties cause accretion on the beach to the north of the inlet and erosion of the beach to the south of the inlet. The inlet channel beyond the jetties also restricts the littoral transfer of sand in the area. The deepening and widening of the channel in 1995 likely contributed to the increased erosion observed south of the inlet in recent years. The beach to the south of the inlet, including that portion on the Property, is designated as a “critically eroded beach” by the Department. The inlet is the primary cause of the erosion. Congress first authorized beach nourishment south of the inlet in 1965. That authorization expired in 1986. Congress “reauthorized” beach nourishment south of the inlet in 1996. That authorization expires in 2021, but St. Lucie County has requested that the authorization be extended for “another 50 years.” The first “major” beach nourishment south of the inlet occurred in 1971. Subsequent “major” nourishments occurred in 1980, 1999, 2003, 2004, and 2005. Another “major” nourishment is planned for 2007. There was a “moderate” nourishment of the beach in 1995, which included the placement of geotextile groins on the beach just to the north of the Property. “Small” nourishments occurred in 1973, 1978, 1987, 1989, 1990, 1992, 1994, 1997, and 1998. Cumulatively, the nourishments that occurred between the “major” nourishments in 1980 and 1999 involved approximately 419,000 cubic yards of sand, which is more than the volume involved in several of the “major” nourishments. Beach nourishment south of the inlet has been an ongoing effort since it started in 1971. The more persuasive evidence establishes that the nourishment project that is authorized through 2021 is a continuation of the project started in 1971 rather than a separate and distinct project. Various erosion control efforts have been used south of the inlet in conjunction with the beach nourishment efforts. For example, geotextile groins (which are essentially massive sandbags) have been installed and removed on several occasions since the mid-1990’s in order to “temporarily stabilize the shoreline until such measures could be taken to design, permit and construct a long-term solution”; concrete rubble and other riprap has been placed on the beach over the years (without a permit from the Department) to protect upland structures from erosion; and a "spur jetty" was constructed on the south jetty in an effort to reduce erosion south of the inlet. These efforts have not slowed the pace of the erosion or minimized the need for beach nourishment south of the inlet. Indeed, the need for and frequency of “major” nourishments south of the inlet have increased in recent years. Beach erosion south of the inlet will continue to be a serious problem so long as the inlet exists and the jetties remain in place. There is no reason to expect that the inlet or the jetties will be removed in the foreseeable future and, as a result, beach nourishment south of the inlet will continue to be necessary. The Department has recognized the need for continuing nourishment of the beach south of the inlet, as reflected in both the Strategic Beach Management Plan for the St. Lucie Beaches and the Ft. Pierce Inlet Management Study Implementation Plan. Those plans acknowledge the long-term need for continued nourishment of the beach at a rate of at least “130,000 cubic yards on an average annual basis.” The plans do not, however, guarantee that future beach nourishment in the area will occur at that, or any, rate. (2) Rule Methodology Florida Administrative Code Rule 62B-33.024 contains the methodology for determining the 30-year erosion projection, which is the projected location of the SHWL 30 years after the date of the permit application under review. Where, as here, the beach at issue is subject to an ongoing beach nourishment project, the methodology requires consideration of “pre-project” conditions -- i.e., the conditions that existed before the beach nourishment efforts started -- because those conditions are used to project how the beach will migrate landward in the periods over the next 30 years when there may not be any beach nourishment activity. The coastal engineering experts presented by the parties -- Michael Walther for Beach Group and Emmett Foster for the Department -- used essentially the same methodology to determine the location of the 30-year erosion projection. However, the variables that they used in each step of the methodology differed. Step 1: Locate the Pre-Project MHWL The first step in determining the 30-year erosion projection is to locate the pre-project MHWL. If a pre-project erosion control line (ECL)3 has been established in the area, it is to be used as the starting-point for the determination of the 30-year erosion projection. Otherwise a pre-project survey of the MHWL is to be used as the starting-point. Mr. Walther used a 1997 ECL as the starting point for his analysis. Mr. Foster used a March 2002 survey of the MHWL as the starting point for his analysis because he did not consider the 1997 ECL to be an appropriate pre-project ECL. The March 2002 survey of the MHWL is not itself an appropriate starting point for the analysis. The survey is not a “pre-project” survey, no matter how the project is defined; the survey occurred more than 30 years after the nourishments started in 1971, and three years after the first “major” nourishment pursuant to the Congressional reauthorization of the project. Moreover, as discussed below, there is an appropriate pre-project ECL in the area. There are two lines that might be considered to be a pre-project ECL in this case -- (1) the ECL established in 1997, and (2) the South Beach High Tide Line (SBHTL) established in 1968. The 1997 ECL was established based upon a survey of the MHWL performed on May 5, 1997. The survey occurred two years after a “moderate” beach nourishment and the placement of the geotextile groins on the beach. There was also a “small” nourishment in 1997, but the record does not reflect whether that nourishment occurred before or after the survey. The SBHTL was established based upon a survey of the MHWL between 1966 and 1968, prior to the initial nourishment of the beach south of the inlet. It is approximately 65 feet landward of the 1997 ECL. The SBHTL is the functional equivalent of an ECL, and it roughly corresponds to the “best fit line” for the March 2002 survey used by Mr. Foster as the starting point for his determination of the 30-year erosion projection in this case. The Department contends that the 1997 ECL is not based upon a “pre-project” survey of the MHWL because the applicable beach restoration project south of the inlet began in the 1970’s and has been ongoing since that time. Beach Group contends that the applicable project is the current one that is authorized through 2021, and that the 1997 survey preceded the start of the nourishments authorized by that project. The Department has used the 1997 ECL as the starting- point for determining the 30-year erosion projection in several prior permits in the vicinity of the Project,4 and in an April 9, 1999, memorandum discussing the 30-year erosion projection in the vicinity of monuments R-35 and R-36, Mr. Foster stated that “the ECL represents the pre-project [MHWL].” Mr. Foster no longer considers the 1997 ECL to be the appropriate pre-project MHWL for purposes of determining the 30- year erosion projection south of the inlet. He testified that had he been aware of “the complete background” of the 1997 ECL and the extent of the nourishments in the 1980’s and 1990’s, he would have brought the issue to the Department’s attention so that the Department could consider whether the 1997 ECL or “an earlier prenourishment line” was the appropriate pre-project MHWL. Although it is a close question, the more persuasive evidence presented at the final hearing establishes that the 1997 ECL is not an appropriate pre-project MHWL because the applicable “project” includes the beach nourishment efforts started in 1971 that have continued through the present, even though those efforts were intermittent at times. Thus, the appropriate starting point for determining the location of the 30-year erosion projection is the SBHTL, not the 1997 ECL used by Mr. Walther or the March 2002 MHWL survey used by Mr. Foster. Step 2: Locate the Pre-Project SHWL The second step in determining the 30-year erosion projection is to determine the location of the pre-project SHWL. Mr. Walther located the pre-project SHWL 26.4 feet landward of the 1997 ECL. That is the surveyed distance between the MHWL and SHWL in June 2005. Mr. Foster located the pre-project SHWL at the most landward location that the SHWL was surveyed in March 2002. The line is between 50 and 75 feet5 landward of the “best fine” line used by Mr. Foster as the pre-project MHWL, and it is as much as 25 feet landward of the surveyed location of the SHWL in some areas. Mr. Foster used “an average [of] 50 feet” as the MHWL- to-SHWL distance in his analysis of several prior permits in the vicinity of the Project.6 Mr. Foster testified that the distance between the MHWL and SHWL in this area varies “from the 20s in the immediate post-nourishment situations . . . all the way up to 70-some feet” and that the “the averages gravitate towards 40 feet.” Consistent with that testimony, the distance between the surveyed locations of the MHWL and SHWL depicted on Department Exhibit 6 is approximately 40 feet, on average. The MHWL-to-SHWL distance calculated by Mr. Walther is not a reasonable projection of the pre-project distance because it was based upon survey data taken immediately after a “major” beach nourishment when the shoreline was unnaturally steep and, hence, not representative of “pre-project” conditions. The SHWL located by Mr. Foster is also not a reasonable projection of the pre-project SHWL because it was based upon a March 2002 survey (which is clearly not "pre- project"); because it used the most landward surveyed location of the SHWL rather than a “best fit” line or an average of the distances between the surveyed MHWL and SHWL; and because it runs across areas of well-established dune vegetation. In sum, the MHWL-to-SHWL distance calculated by Mr. Walther (26.4 feet) is too low, whereas the distance resulting from Mr. Foster's siting of the SHWL based on the March 2002 survey (50 to 75 feet) is too high. Those distances are essentially endpoints of the range observed in this area, as described by Mr. Foster. A more reasonable estimate of the pre-project MHWL-to- SHWL distance is approximately 40 feet. See Findings 51 and 52. Thus, the pre-project SHWL is located 40 feet landward of and parallel to the SBHTL. That line is not depicted on any of the exhibits, but on Petitioner’s Exhibit 37, it roughly corresponds to a straight line between the points where the red- dashed line intersects the Property’s north and south boundaries. Step 3: Calculate the Erosion Rate The third step in determining the 30-year erosion projection is to calculate an erosion rate. The erosion rate used by Mr. Foster was -7 feet per year (ft/yr). That rate was calculated based upon an average of the shoreline change data for monument R-35 for the period from 1949 to 1967. The rate would have been higher had Mr. Foster averaged the rates for the nearby monuments.7 The erosion rate used by Mr. Walther was -4.9 ft/yr. That rate was calculated based upon an average of the shoreline change data for monuments R-34 to R-39 over the period of 1930 to 1968. An erosion rate of -7 ft/yr south of the inlet was referenced in permit applications submitted by Mr. Walter’s firm, Coastal Tech, for several shore protection structures south of the inlet; was used by Mr. Foster in his review of several prior CCCL permit applications south of the inlet; and was included in reports on the inlet prepared by the Army Corps of Engineers over the years. An erosion rate of -3.3 ft/yr was used and accepted by the Department in its review of another permit application in the general vicinity of the project.8 That erosion rate was based upon data from the period of 1972 to 1994, which is after the beach nourishment started south of the inlet. It is not entirely clear why Mr. Foster chose to use a data set starting in 1949, particularly since his report stated that the “1928-30 survey already shows significant erosion occurring south of the inlet.” His testimony did not adequately explain the choice of that data set. The use of a longer data set is typically more appropriate when calculating a historical rate. In this case, however, the use of the shorter period of 1949-68 is reasonable because the 1930-49 erosion rate was considerably lower than the 1949-68 rate,9 which has the effect of skewing the erosion rate calculated for the longer period of 1930-68. The higher erosion rate calculated by Mr. Foster also better takes into account the increased frequency of the nourishments in recent years as well as the continued need for shore stabilization in the area. In sum, the higher erosion rate of -7 ft/yr calculated by Mr. Foster using the 1949-68 data set better reflects the historical post-inlet, pre-nourishment erosion rate than does the lower erosion rate calculated by Mr. Walther. Step 4: Determine the Remaining Project Life The fourth step in determining the 30-year erosion projection is to determine the “remaining project life” of the “existing” beach nourishment project. It was stipulated that there are 14 years remaining until the currently authorized federal beach restoration project expires. It is reasonable to expect that beach nourishment south of the inlet will continue well beyond the expiration of the current federal project, but there were no other funded and permitted projects in place at the time Beach Group’s permit application was filed. Potential future beach nourishment projects are not considered “existing” under the rule methodology in Florida Administrative Code Rule 62B-33.024 unless they are funded and permitted at the time the application at issue is filed. Mr. Walther used the 14-year remaining life of the existing federal project in his calculation of the 30-year erosion projection, as did Mr. Foster. The “remaining project life” applicable to this case is 14 years, notwithstanding the likelihood of continued beach nourishment in the area beyond the expiration of the existing project. Step 5: Calculate the 30-year Erosion Projection The final step in determining the location of the 30- year erosion projection is a calculation using the variables determined in the previous steps. The calculation is as follows: first, the remaining project life determined in step four is subtracted from 30; then, that result is multiplied by the erosion rate determined in step three to get a distance; and, finally, the SHWL is moved that distance landward of its pre-project location determined in step two. Subtracting the remaining project of 14 years from 30 equals 16 years. Multiplying 16 years by the erosion rate of -7 ft/yr equals 112 feet, which means that the 30-year erosion line is located 112 feet landward of the pre-project SHWL (or 152 feet landward of the SBHTL). That line is not depicted on any of the exhibits, but it roughly corresponds to a straight line than runs across the Property parallel to the SBHTL just landward of the “conc. pad” and “existing conc. Pile caps (typ)” shown on Petitioner’s Exhibit 37. The line is 25 to 30 feet seaward of Mr. Foster’s 30-year erosion projection depicted on that exhibit. (3) Ultimate Finding Regarding the Location of the Proposed Structures in Relation to the 30-year Erosion Projection The Project includes major structures seaward of the 30-year erosion projection, as determined above. Impacts of the Project on the Beach-Dune System The Project includes 17 luxury town home units in two four-story buildings, a pool and spa, landscaping, and an elevated dune walkover. The units will range from 2,700 to 4,400 square feet of living space and are projected to be offered for sale in the $1.5 to $2.5 million range. Beach Group’s principal, Harold Seltzer, testified that the Project is sited as far landward as possible to allow for the development of all 17 units while still complying with the local setback and height restrictions; that the Project’s financial viability depends upon it being developed as proposed; and that the Project cannot be redesigned and remain financially viable. The CCCL permit application included a letter from the City of Ft. Pierce confirming that the Project is consistent with the applicable local development codes. Mr. Seltzer testified that the Project’s local development approvals expired in September 2006 because the CCCL permit had not been issued, and that Beach Group is having to go back through the local permitting process. The seaward extent of the Project is the 1978 CCCL, which is approximately 250 feet seaward of the current CCCL. The buildings on the adjacent properties are also located on the 1978 CCCL. The Project does not extend further seaward than the nearby development, including the structures authorized by the Department in File Nos. SL-162 and SL-173.10 The seaward boundary of the Property is the SBHTL. That line is approximately 295 feet landward of the MHWL established in June 2005, and as noted above, it is approximately 65 feet landward of the ECL established in 1997. The adjacent properties are developed with multi-story residential buildings. There is a densely vegetated dune feature in front of the building to the south of the Property. There is some vegetation, but no discernable dune in front of the building to the north of the Property. The Property as a whole is sparsely vegetated, but there are areas of “prolific vegetation” on the Property. The seaward extent of the vegetation on the Property roughly corresponds to the location of the 1978 CCCL. There are several mature sea grape clusters in the vicinity of that line. The beach in front of the Property is devoid of vegetation. It has a steep slope immediately landward of the water line; a wide (approximately 270 feet) expanse of relatively flat beach; and a gently sloping dune feature that starts just landward of the Property’s seaward boundary, crests approximately 30 feet farther landward, and then gradually slopes downward across the Property all of the way to State Road A1A. The dune feature on the Property is the frontal dune. It is the first mound sand located landward of the beach that has sufficient vegetation, height, continuity, and configuration to offer protective value. The crest of the frontal dune is seaward of the vegetation line on the Property, and ranges in height from +9.7 to +12.2 feet NAVD.11 The seaward toe of the dune is shown on the topographic survey for the Property at elevations ranging from +7.27 to +7.85 feet NAVD. Similar elevations occur on the landward side of the dune crest, just landward of the 1978 CCCL. The vegetation on the Property extends landward of the 1978 CCCL and landward of the line shown on the topographic survey of the Property as the “approximate location of sparse grass and ground cover.” The landward extent of the vegetation does not in and of itself define the landward extent of the dune; changes in the slope of the ground must also be considered. The more persuasive evidence establishes that the landward toe of the frontal dune is landward of the 1978 CCCL, but not as far landward as suggested by Department witness Tony McNeal.12 The landward toe of the dune on the Property is best defined by the elevations landward of the dune crest similar to the elevations shown for the seaward toe of the dune. The Project extends into the frontal dune on the Property, and it will requires minor excavation of the frontal dune, primarily in the area of the proposed pool. All aspects of the project, except for the proposed dune walkover, will be landward of the crest of the frontal dune and the mature sea grape clusters located on the dune. There will be no net excavation on the Property as a result of the Project. The sand excavated for the pool will be placed on-site, and additional beach-compatible sand will be used as fill for the site. Overall, the Project will result in the net placement of approximately 66 cubic yards of sand on the Property. The proposed structures will be elevated on piles, which will allow the beach-dune system to fluctuate under the structures during storm events. The finished floor elevation of the proposed structures is approximately +8 feet NAVD, which is slightly higher than the elevations associated with the toes of the frontal dune. The Project will not destabilize the frontal dune, even though it will encroach into the dune. The impacts of the Project on the beach-dune system will be mitigated by the placement of additional sand into the beach-dune system, as described above. The Project’s impacts will be further mitigated by the enhancements to the frontal dune described in the permit application. Mr. Walther testified that the frontal dune on the Property could “very easily” be enhanced to be of comparable height and magnitude of the dunes on the adjacent properties. The permit application proposes enhancements to the frontal dune as part of the Site Landscaping Plan for the Project. The proposed enhancements include increasing the crest of the dune to a height of +15 feet NAVD, and extensive planting of the dune with sea grapes, beach morning glories, and sea oats. The plantings would extend from the 1978 CCCL to the seaward toe of the existing frontal dune. The dune enhancements proposed in the permit application should be included as a specific condition of the CCCL permit for the Project, if it is approved.
Recommendation Based upon the foregoing findings of fact and conclusions of law, it is RECOMMENDED that the Department issue a final order denying Beach Group’s application for a CCCL permit. DONE AND ENTERED this 19th day of April, 2007, in Tallahassee, Leon County, Florida. S T. KENT WETHERELL, II Administrative Law Judge Division of Administrative Hearings The DeSoto Building 1230 Apalachee Parkway Tallahassee, Florida 32399-3060 (850) 488-9675 SUNCOM 278-9675 Fax Filing (850) 921-6847 www.doah.state.fl.us Filed with the Clerk of the Division of Administrative Hearings this 19th day of April, 2007.
Findings Of Fact On 24 July 1979 the Board of County Commissioners of Palm Beach County adopted Resolution R-79-887 petitioning the TIITF to establish an erosion control line (ECL) extending from South Lake Worth Inlet to the northern city limits of Delray Beach in conjunction with a beach restoration project in the same area. The project as then proposed encompassed extension of the south jetty at the Inlet 170 feet, construction of eight groins at 400-foot intervals commencing just south of the Inlet, and widening the beaches by 500 feet with 150 feet above the mean high water and 350 feet below mean high water, for a distance of approximately 4.8 miles. The restoration project is proposed to be accomplished with sand from a borrow area located approximately one-half mile off shore. The project is designated "Ocean Ridge-Briny Breezes" beach restoration project. SLWID objected to the project and, following conferences between Palm Beach County, SLWID and DNR the County amended its project to exclude property owned by SLWID from the ECL and beach restoration projects with the restoration of the beach to commence 300 feet south of the Inlet and continue for 2.6 miles to the town of Briny Breezes. Extension of the jetty and installation of groins were deleted. Palm Beach County's proposed beach restoration project was authorized by the U.S. Congress and the U.S. Army Corps of Engineers in House Document 164 (Exhibit 5). The proposed "Ocean Ridge-Briny Breezes" beach restoration project was designed in accordance with the criteria set forth in Exhibit 5. The project is designed to restore the severe beach erosion that has occurred in the 2.6-mile project area and to provide the affected uplands protection against the ten-year design storm event. The ten-year design storm event implies a 3.8-foot storm surge with up to eight-foot waves superimposed thereon. The proposed ECL has been surveyed by Palm Beach County along the mean high water line in the proposed area. Over 60 percent of the ocean front property owners have approved the establishment of the ECL in conjunction with a beach restoration project by executing letters of consent. Following notice by DNR a public hearing was held on February 13, 1980, to receive evidence relative to the necessity and propriety of the proposed beach restoration project and the proposed location of the ECL. The Hearing Officer's report (Exhibit 28) concluded that there is a definite need to restore the proposed area where severe beach erosion has occurred and the establishment of the ECL would accomplish the purpose stated in Section 161.161, Florida Statutes. Approval of the project was recommended. The staff of DNR approved the project and prepared the agenda item for the next meeting of the TIITF in which this project was to be considered for final approval. Prior to this meeting of the TIITF, SLWID filed its initial Request for Formal Proceeding and the item was removed from the TIITF agenda and referred to the Division of Administrative Hearings. The beach erosion in the project area has been documented by Palm Beach County, DNR and the U.S. Army Corps of Engineers. Much of the erosion in the northernmost mile of the project has involved the beach above high water, as well as the offshore beach, while the erosion in the southern 1.6 files of the project has predominantly been offshore. During the period 1955-1981 approximately 1.6 million cubic yards of sand has been lost in the project area. Beach erosion determinations are made by calculating both onshore and offshore changes in the beach profile. Significant offshore erosion will lead to onshore beach recession by storm-generated waves. A gradually sloping beach is a natural absorber of wade energy and the most effective. Since maximum wave height is a function of the depth of the water, waves rapidly dissipate when they reach shoal water. With offshore erosion and the resulting deeper water near the shore, incoming waves can be higher and will impact on the upland area with greater force than would occur with a gradually sloping beach. There is a net annual littoral drift of 200,000 cubic yards of sand southward in the project area. Prior to the construction of the Inlet this drift replaced sand lost during storms, thus creating a dynamic beach which receded and was augmented from time to time. The installation of the jetties disrupted this littoral flow and caused the sand to build up on the beach north of the jetty while starving the beach south of the jetty. This problem was partly corrected by the erection of a sand transfer plant on the north jetty which pumped some of this sand across the Inlet to the beach south of the Inlet. The sand transfer plant was not operated during WWII due to the fuel shortage and severe erosion occurred in the project area. Following WWII the sand transfer plant was replaced in operation, sand was dredged from the Inlet and deposited on the beach south of the Inlet and the beach in the project area was largely restored. In 1967 the north jetty at the Inlet was extended and the sand transfer plant was moved eastward some 130 feet. This plant is a fixed plant consisting of a suction line on a boom which dredges sand to be pumped south of the Inlet only from the area that can be reached by the boom. Although capacity of the plant is adequate to pump the sand needed to replace in the project area that sand intercepted by the jetty, due to the limitation of the plant to reach a larger area there is insufficient sand available for the plant to pump to capacity. As a result, even if the plant operated all the time and there was sand available to pump, there would still be a net loss of sand in the project area (Exhibit 21). During recent winter storms property-threatening beach erosion has occurred to beach property in the project area. Some of the property owners have erected bulkheads and seawalls and others are proceeding with plans to do so. In some places in the north portion of the project area there is no exposed beach at high water. In the southern portion of the project area the offshore erosion will, if left to continue, result in severe damage and loss of upland beach if impacted with seas commensurate with a ten-year design storm event. This erosion, both on and offshore, will, if uncorrected, result in a calculated total of 134 feet of beach recession for the ten-year design storm event. This could result in the inundation of S.R. A1A, which runs near the beach in the northern portion of the project area. S.R. A1A is the primary north-south highway east of the Intracoastal Waterway and the evacuation route to the bridges to the mainland in the event evacuation of the beach is necessary in a hurricane situation. The proposed beach restoration project is designed to replace sand lost offshore and onshore erosion in the the project area and provide a sloping beach to absorb wave impact. It will not accelerate erosion. The proposed restoration of the beach will protect property and structures in the project area against the forces associated with a ten-year design storm event. Addition of the 1.5 million cubic yards of sand in the project area will result in some sand infiltration of the Inlet. This was calculated at 8,000 cubic yards the first year, 6,000 cubic yards the second year and 4,000 cubic yards per year thereafter. This will result in insignificant shoaling in the Inlet but will require infrequent maintenance dredging. It will not adversely impact the tidal prism in the Inlet or materially increase the maintenance of the Inlet. Heavy storms result in immediate loss of sand from the upland beach. Most of this sand is deposited in the offshore beach and is returned to the upland beach by the normal action of waves and tides. Approximately ten percent of the sand so removed from the upland beach is not returned but is lost.
Findings Of Fact Petitioner, Roland Peterson, is the owner of Lots 4, 5 and 6, Block 7, Vilano Beach, in an unincorporated area of St. Johns County, Florida. Vilano Beach lies just eastward of the City of St. Augustine, Florida, and north of St. Augustine Inlet. The three lots are adjacent to each other. By applications dated June 7, 1985 petitioner sought the issuance of three coastal construction control line permits by respondent, Department of Natural Resources, Division of Beaches and Shores (Division), to authorize construction seaward of the coastal construction control line or setback line on Lots 4, 5 and 6. More specifically, petitioner sought approval to construct a beach-side snack bar with associated beach walkover, driveway and attached decks on Lot 4, and single family residences with associated dune walkover; driveway and attached decks on Lots 5 and 6. These applications were assigned Application Numbers SJ 220, SJ 221 and SJ 222 by the Division. They were deemed to be complete on August 6, 1985. After evaluating the three applications, the Division formulated recommendations to deny the requested permits. These recommendations were adopted by the Governor and Cabinet sitting as head of the agency at its November 5, 1985 meeting. Notice of such intended action was previously forwarded to petitioner on October 23, 1985. Said notice prompted the instant proceeding. As grounds for denying the permits the Division concluded that the three projects were located seaward of the seasonal high- water line and were therefore prohibited by a law, the projects lay in an area "highly vulnerable" to a major storm; and the cumulative impact of locating these and other structures further seaward could be expected to adversely impact the beach and dune system of the Vilano Beach area. The parties have stipulated that the Division has properly calculated the seasonal high water line in the questioned area, and that petitioner's three projects lie seaward of that line. The parties have also stipulated that the three projects lie seaward of the frontal dune within the meaning of Subsection 161.053t6)(a)1., Florida Statutes (1985).
Recommendation Based on the foregoing findings of fact and conclusions of law, it is RECOMMENDED that application numbers SJ 220, SJ 221 and SJ 222 filed by Roland Peterson to construct various structures on Lots 4, 5 and 6, Block 7, Vilano Beach in St. Johns County, Florida, be DENIED. DONE and ORDERED this 14th day of May, 1986, in Tallahassee, Florida. DONALD R. ALEXANDER, Hearing Officer Division of Administrative Hearings The Oakland Building 2009 Apalachee Parkway Tallahassee, Florida 32399 (904) 488-9675 Filed with the Clerk of the Division of Administrative Hearings this 14th day of May, 1986.
The Issue The issues to be determined is whether the City of Destin (“City”) has demonstrated its entitlement to place dredged material from the maintenance dredging of the East Pass (“East Pass” or “inlet”) entrance channel conducted pursuant to the Consolidated Joint Coastal Permit and Sovereign Submerged Lands Authorization, Permit Number: 0288799-003-JC (“Permit”), in the swash zone east of East Pass in accordance with the Notice to Proceed (“NTP”); and whether the Inlet Management Plan referenced in the NTP is an unadopted rule as described in section 120.57(1)(e), Florida Statutes.
Findings Of Fact Based upon the demeanor and credibility of the witnesses, the stipulations of the parties, and the evidentiary record of this proceeding, the following Findings of Fact are made: The Parties Petitioners, David H. Sherry and Rebecca R. Sherry, own Unit 511 at the Surf Dweller Condominium, 554 Coral Court, Fort Walton Beach, Florida. The Surf Dweller Condominium, which is on Santa Rosa Island in the unincorporated community of Okaloosa Island,1/ fronts the Gulf of Mexico, and straddles DEP Reference Monument R-7, which is between three and four miles west of DEP Virtual Monument V-611, and is between five and six miles west of the west side of East Pass. The Sherrys use the beach at their condominium on a daily basis for fishing, crabbing, swimming, walking, running, and general recreation. They also walk or run from Monument R-7 along the beaches to East Pass, and occasionally drive to and use the beaches on the east side of East Pass. Petitioner, John S. Donovan, owns Units 131 and 132 at the El Matador Condominium, 909 Santa Rosa Boulevard, Fort Walton Beach, Florida. The El Matador Condominium is on Okaloosa Island, fronts the Gulf of Mexico, and is approximately five miles west of Monument V-611, and is more than six miles west of the west side of East Pass. Mr. Donovan generally walks the beaches west of his condominium, but does occasionally walk along the beach to Monument V-607, which is the location of a seawall constructed by the Air Force on sovereign submerged lands to protect an Air Force tracking facility. Intervenor, Thomas Wilson, resides at 856 Edgewood Drive, Charleston, West Virginia, and owns a secondary residence at 1530 Miracle Strip Parkway, No. 101-B, Fort Walton Beach, Florida, in the vicinity of Monument R-14. Mr. Wilson uses and enjoys the gulf-front beaches between his property on Okaloosa Island and East Pass. Petitioners’ stated injuries are related to the allegation that the lateral movement of sand from the East Pass areas of influence is from east to west. Placing dredged material in the eastern disposal site would allegedly deprive the beaches in front of their property -- beaches that are miles from the nearest area of influence or spoil disposal site -- of their natural sand supply by cutting off what they allege to be the natural sand flow, causing the beaches in front of their properties to eventually erode. Petitioners alleged no immediate environmental injuries associated with the NTP. Petitioners’ stated objective in this case is to have any sand dredged from East Past to be placed on the western disposal areas at all times. The City is the applicant for the Permit and the NTP, and abuts the east side of East Pass. DEP is an agency of the State of Florida pursuant to section 20.255, Florida Statutes. DEP is the permitting authority in this proceeding and issued the NTP at issue in this proceeding to the City. The NTP was issued on February 2, 2018, without notice of rights language regarding the right to request a hearing or time limits for doing so. Petitioners received a copy of the NTP on October 1, 2018, and filed a challenge more than 14 days later, on November 30, 2018. East Pass Prior to 1928, the connection from Choctawhatchee Bay to the Gulf of Mexico flowed through what is now Old Pass Lagoon. After a storm in 1928, a high-tide breach of the shoreline near the current location of East Pass was formed. In 1929, a record rain event caused waters to rise in Choctawhatchee Bay. Residents of the area dug a relief channel at roughly the present location of East Pass. The waters releasing through the more hydraulically efficient flow path from Choctawhatchee Bay established a channel, which quickly enlarged to become the prominent inlet to the Gulf of Mexico. The permanent channel, now known as East Pass, is the only navigable passage from Choctawhatchee Bay and the Intercoastal Waterway to the Gulf of Mexico between Panama City, Florida, and Pensacola, Florida. East Pass separates the gulf-fronting beaches of the City to its east from the beaches owned by the United States as part of Eglin Air Force Base to the west. The entrance to East Pass is protected by two boulder-mount jetties: a 3,860 foot- long jetty on the west side of the inlet and a 1,210 foot-long jetty on the east side of the inlet. East Pass is an ebb tide dominated inlet, with a sizable amount of sediment moving in and out. When outgoing tidal flow moves though the constriction formed by the jetties, flow velocities are accelerated. When the water, and any entrained sediment, passes the jetties, flow tends to spread out to the east, west, and south, and naturally loses velocity. When the outgoing tidal waters reach a critical velocity where they can no longer carry the sand, the sand drops out of suspension, which forms the ebb shoal. Essentially, the ebb shoal is a large, semi-circular sandbar extending from the mouth of East Pass that was created by the ebb tide carrying sediments south. East Pass is a highly dynamic inlet system. There are processes spurred by the configuration and location of East Pass, tides, waves, and storms that have resulted in currents running to the east and west that change on a frequent basis. The Physical Monitoring Plan (“PMP”), which is part of the Permit, and thus, not subject to challenge in this case, established, for the period of 1996 through 2007, “a trend of west to east longshore transport, resulting in net gain immediately west of [East Pass] and a significant loss of sand along Holiday Isle east of [East Pass].” The PMP further established that a “drift nodal point” existed at East Pass. Longshore transport at uniform coastal locations is generally in one direction. However, when there are wave events coming from varying angles, and where beach contours are not parallel and uniform, or even linear, it is common for transport reversals to occur. The point at which those reversals occur is referred to as a nodal point. That point can be where east and west transport converges, or where it diverges. The shoreline in the vicinity of East Pass has exhibited “quite a few” nodal points over the past decade, resulting in frequent drift reversals and sand transport to the east and the west. The evidence as to the existence and effect of the East Pass drift nodal point, and its affect on the lateral transport of sand in the area, including the East Pass areas of influence, was substantiated by testimony and other evidence introduced at the final hearing. The testimony and evidence that there is no consistent direction of lateral sand transport in the vicinity of East Pass, and no predominant lateral current transporting sand in a westerly direction, is accepted. Evidence to the contrary was not persuasive. East Pass includes a federal navigation channel. The federal navigation channel requires routine maintenance to prevent it from shoaling. On an average, East Pass is dredged in two-year intervals. The last time that East Pass was dredged was in December of 2013. It has now shoaled with sand and become very hazardous for marine traffic. In December of 2018, the City declared a state of emergency relating to the navigational hazards caused by the accumulation of sand in the navigation channel. The Permit On February 26, 2015, DEP issued the Permit, which authorized the City to perform “periodic maintenance dredging of the federally authorized East Pass and Destin Harbor and navigation channels.” The Permit will expire on February 26, 2030. Notice of the issuance of this Permit was published in the Destin Log, a newspaper of general circulation, on December 24, 2014. No challenge to the issuance of the Permit was filed. As it pertains to the issues in this proceeding, the Permit provides that “Dredged material from . . . maintenance dredging activities will be placed in the swash zones of the beaches east and west of East Pass, as specified in the East Pass Inlet Management Plan.” The specific beach spoil placement sites are, as relevant to this proceeding, located “west of East Pass . . . between [DEP] reference monuments V-611 and V-622; and on 2 beach sites situated east of East Pass . . . from R-17 to R-20.5 and from R-23.5 to R-25.5.” Those areas correspond to what have been identified as the “areas of influence,” which are the beach areas east and west of East Pass that are affected by tidal forces generated by the inlet. The specified beach spoil placement sites, being conditions of the unchallenged Permit, are not subject to challenge in this case. The Permit establishes the criteria by which specific work is to be authorized. Specific Condition 5 provides, in pertinent part, that: 5. No work shall be conducted under this permit until the Permittee has received a written notice to proceed from the Department for each event. At least 30 days prior to the requested date of issuance of the notice to proceed, the Permittee shall submit a written request for a Notice to Proceed along with the following items for review and approval by the Department: * * * Prior to the second dredging event authorized under this permit, and each subsequent event, the Physical Monitoring Data, as specified in Specific Condition 9, shall be submitted to select the appropriate placement locations. Specific Condition 9 provides that: Following the initial placement of material on Norriego Point, fill site selection shall be supported by the latest physical monitoring data over a minimum of five years in accordance with the adopted East Pass Inlet Management Implementation Plan (July 24, 2013). All physical monitoring shall be conducted in accordance to the Approved physical monitoring plan dated August, 2014. A notice to proceed for specific projects shall be withheld pending concurrence by the Department that the data support the proposed placement location. The purpose of Specific Condition 9 is to identify, using supporting monitoring data from the eastern and western areas of influence, the “adjacent eroding beach” most in need of sand from the inlet. The requirement that physical monitoring data be used to determine which of the beach spoil placement sites identified in the Permit’s Project Description will receive the spoil from any particular periodic dredging event was to implement section 161.142, Florida Statutes. That section mandates that “maintenance dredgings of beach-quality sand are placed on the adjacent eroding beaches,” and establishes the overriding policy of the state regarding disposition of sand from navigational channel maintenance dredging. East Pass Inlet Management Implementation Plan The East Pass Inlet Management Implementation Plan (“East Pass IMP”) was adopted by Final Order of DEP on July 30, 2013.2/ The East Pass IMP was not adopted through the rulemaking procedures proscribed by chapter 120, Florida Statutes, or DEP rules. Despite a comprehensive Notice of Rights advising persons whose substantial interests could be affected of the means by which the East Pass IMP could be challenged, it was not. There are 44 maintained inlets in Florida. About half have individual inlet management plans. The East Pass IMP is not applicable to any inlet other than East Pass. The East Pass IMP does not require that any quantity of dredged material from the dredging of East Pass be placed at any particular location other than as established in the Permit. Rather, the disposal site is to be determined on a case-by-case basis based on the best monitoring data available for the beaches in the area of influence of East Pass. The critical element of the IMP, and that in keeping with the statutory requirement that sand be placed on “adjacent eroding beaches” is the “strategy” that “the recent erosion of adjacent beaches observed over a minimum of five years shall define the placement need in terms of location and volume.” The East Pass IMP, being applicable only to East Pass, is not of “general applicability.” Furthermore, the East Pass IMP does not implement, interpret, or prescribe law or policy. The Notice to Proceed On January 30, 2018, the City filed its Request for Notice to Proceed (“Request”). The Request addressed the criteria in Specific Conditions 5 and 9 of the Permit. Upon review, DEP determined the conditions of the Permit were satisfied and issued the NTP on February 2, 2018. The analysis of data submitted as part of the Request was designed to show areas of erosion and accretion within the eastern and western areas of influence in order to identify “critically eroded beaches.” The shoreline of Santa Rosa Island to the west of East Pass has historically been stable. To be sure, as is the case with any shoreline, there will be some areas of erosion and some areas of accretion. After Hurricanes Ivan and Opal, areas of Santa Rosa Island experienced erosion. DEP declared the shoreline to be critically eroded after the 2004-2005 hurricane seasons, which prompted Okaloosa County to commission a study to monitor the health of the Monuments R-1 through R-16 beach segment, a segment that includes Petitioners’ residences. Despite the fact that no post-storm beach restoration occurred in the area, the beach recovered naturally and gained sand following the post-storm recovery. In addition, Santa Rosa Island is known for “beach cusps,” which are crenulate3/ shapes along the shoreline. Depending on the season and storm conditions, those beach cusps can have a localized erosive effect on the beach, but those tend to be seasonal. They do not negate what the evidence shows to be the overall stable to accretional conditions of the beaches west of East Pass from Monument V-622 to Petitioners’ residences. Mr. Trammell offered testimony, including a discussion of photographic evidence, demonstrating the beaches west of East Pass have large dunes; multiple dune lines; tall, and thick vegetated dunes indicating established dune growth; pioneering vegetation indicating active, healthy dune growth and accretion; partially buried signs indicating dune advance; and broad and expansive beaches. Those features are indicative of a stable and accretional shoreline. Mr. Trammell’s testimony as to the western spoil disposal site was convincing and is accepted. At present, the Santa Rosa Island shoreline is not deemed by DEP to be “critically eroded.” The photographic evidence supports the data collected over time for the beaches west of East Pass, and the testimony offered at the final hearing, which collectively establishes, by a preponderance of the evidence, that the beaches to the west of East Pass are stable and accretional, are not subject to erosion caused by East Pass, and are not “adjacent eroding beaches” as that term is used in section 161.142. The shoreline east of East Pass, including the eastern area of influence and the proposed dredge material disposal sites at Monuments R-17 to R-20.5 and R-23.5 to R-25, except for the area immediately abutting the eastern jetty, is highly erosional. Mr. Trammell offered testimony, including a discussion of photographic evidence, demonstrating the beaches east of East Pass exhibit the following signs of significant and ongoing erosion: extensive dune erosion; exposed sea oat roots; reduced beach elevation; reduced beach width; crenulate bays; newly built dune walkovers that replaced old walkovers claimed by erosion; dune walkovers in close proximity to the shoreline indicating that the shoreline had receded to the walkover; and beach scarping at the shoreline indicating active erosion. Mr. Trammell’s testimony as to the eastern spoil disposal sites was convincing and is accepted. The eastern areas of influence are currently designated to be “critically eroded” by DEP, a designation maintained for more than 10 years. The photographic evidence supports the data collected over time for the beaches east of East Pass, and the testimony offered at the final hearing, which collectively establishes, by a preponderance of the evidence, that the beaches to the east of East Pass are critically eroded, a condition that is influenced by East Pass and or its navigational channel, and are “adjacent eroding beaches” as that term is used in section 161.142. Data in Support of the NTP The data submitted by the City to DEP in support of the Request included monitoring data for the eastern beach placement areas from the West Destin Four-Year Post-construction Monitoring Report and earlier annual post-construction reports covering the period from October 2012 to July 2017, and additional data from the Holiday Isle Emergency Beach Fill Two-Year Post-construction Report. DEP was also provided with historical monitoring data for the area west of East Pass, including the Western Beach Monitoring Report, which covered 2006 to 2017, and the Potential Borrow Area Impact Report, which included data from 1996 through 2012. DEP has also received recent profile data from April 2019. These reports, and the data contained within them, cumulatively provide more than 20 years of survey date, and demonstrate convincingly that the shoreline to the west of East Pass has been stable or accreting, and the areas to the east are eroded. The data submitted in support of the Request was sufficient to meet Specific Condition 9 that fill site selection be supported by the latest physical monitoring data over a minimum of five years in accordance with the East Pass IMP. Petitioners argue that the City failed to comply with the PMP, which requires, among other things, that the analysis of the dredged material disposal area include “preconstruction survey data and the most recent survey conducted at least five years prior.” The PMP establishes that “[p]reconstruction surveys shall be conducted no more than 90 days before construction commences. A prior beach monitoring survey of the beach and offshore may be submitted for the pre-construction survey if consistent with the other requirements” of the PMP. The City submitted a prior beach monitoring survey of the beach and offshore that is consistent with the PMP. Petitioners argue that the City violated a temporal limitation which provides that the City “may submit a prior beach restoration monitoring report for the west or east beach areas (Walton-Destin or Western Destin Beach Restoration Project) if the monitoring data is collected within 1 year of the proposed maintenance dredging event and if consistent with the other requirements of this condition.” Petitioners acknowledge in their PRO that the beach restoration monitoring report was timely when the Request for NTP was submitted. The information contained therein was sufficient to support the notice of proposed action on the NTP. The otherwise compliant data is no longer within one year of the proposed dredge. In that regard, the litigation in this case, initiated by Petitioners, has been ongoing for almost one year. Work authorized by the NTP cannot go forward when subject to challenge. If the PMP, which is not a rule, is unreasonably read so as not to account for delay caused by litigation, such delay becomes a tool for use by, and a reward for, a person dissatisfied with DEP’s outcome. In this case, the NTP was lawfully issued pursuant to compliant data, surveys, and analysis. As with any permit or license subject to a third- party challenge, the terms of the NTP are tolled pending Petitioners’ litigation, and do not become a ground for denial of the otherwise compliant Request. See § 120.60(1), Fla. Stat. (“An application for a license must be approved or denied within 90 days after receipt of a completed application unless a shorter period of time for agency action is provided by law. The 90-day time period is tolled by the initiation of a proceeding under ss. 120.569 and 120.57. Any application for a license which is not approved or denied . . . within 45 days after a recommended order is submitted to the agency and the parties, . . . is considered approved unless the recommended order recommends that the agency deny the license.”).4/ Furthermore, DEP has now received recent profile data from April 2019. The evidence establishes that the data provided to DEP as part of the Request includes the latest physical monitoring data over a period of greater than five years, and that the data collection met the standards for conducting physical monitoring. Fill Site Selection The NTP authorized “placement of dredged material in the swash zone east of East Pass.” In accordance with the Permit, that authorized area extends eastward from R-17 to R-20.5 and from R-23.5 to R-25.5, in Holiday Isle. The evidence is persuasive that placing dredged material on the eastern side of East Pass would not result in erosion on the western side of East Pass. Dredged material placed in the western beach placement area, and in the “shadow” of the western jetty, will tend to remain in that area. It would take a very long time, if at all, for that material to migrate further to the west. However, dredged material placed to the east of East Pass would, if the lateral shoreline drift is east to west as asserted by Petitioners (though not supported by a preponderance of the evidence as set forth in paragraphs 11 through 13), be introduced into the ebb shoal and likely move faster to the west as opposed to it being placed directly at the base of the west jetty. As such, placement of the dredged material on the eastern beach placement areas would, more likely than not, accomplish the beach effect objectives set forth in the Petition. The Eglin AFB Beach Restoration Project Petitioners relied heavily on photographs taken in 2010 and 2019 from roughly the same location in the vicinity of Monuments V-607 to V-608 to demonstrate that the beaches of Santa Rosa Island are eroding. The area depicted is outside of the area of influence of East Pass, and outside of the western beach placement area under the Permit. Those photographs depict a wide expanse of beach in 2010, with a seawall well upland from the shore in 2010. Then, in 2019, a photograph depicting the same stretch was offered that showed the same seawall, now at or below the water line. The photographs were, ostensibly, designed to depict naturally occurring erosion in the area. Mr. Clark testified that the seawall and boulder mound structure depicted in both photographs protect an Air Force mission-critical tracking facility. The seawall was originally constructed in 1979 after Hurricane Frederick, was constructed at that time to extend into the water, and was maintained in that configuration through the 1990s. One could not walk around the original seawall. Rather, for most of its history, passage around the seaward side of the seawall could only be accomplished by swimming or wading. The original seawall was damaged by Hurricane Opal, and destroyed by Hurricanes Ivan and Dennis in 2004 and 2005. The Air Force, needing to reconstruct the wall, applied for and received a joint coastal construction permit, allowing the structure to be constructed on sovereign submerged land below the line of mean high water. The seawall was rebuilt and, as stated by Mr. Clark, “it was in the water.” In 2010, the Air Force performed the small Eglin Air Force Base Beach Restoration Project, which placed artificial fill in front of the seawall, thereby creating a temporary beach. That beach fill project was “a one-shot deal,” did not involve any subsequent maintenance, and is now essentially gone, as was expected. Mr. Clark was neither surprised nor concerned with the fact that the area returned to what he described as its natural state, with the seawall below mean high water. The 2019 photograph was presented as evidence of erosion caused by East Pass. That was not the case. Rather, the 2010 photograph was evidence of an artificial and singular event, and the 2019 photograph depicts the natural state of the shoreline. Rather than depicting erosion, the 2019 photograph depicts a return to the stable shoreline that exists all along Santa Rosa Island to the west of East Pass. The photographs of the site of the 2010 Eglin Air Force Base Beach Restoration Project do not support a finding that the beaches of Santa Rosa Island are anything but stable, if not accretional, nor do they support a finding that the beaches of Santa Rosa Island are eroding. Ultimate Factual Conclusion Specific Condition 9 of the Permit requires the location of the spoil disposal be supported by the latest physical monitoring data over a minimum of five years in accordance with the East Pass IMP and the PMP. The greater weight of the competent substantial evidence establishes that the City submitted physical monitoring data consistent with the requirements of Specific Condition 9. The greater weight of the competent substantial evidence establishes that the eastern areas of influence of East Pass, including the beach disposal areas at R-17 to R-20.5 and R-23.5 to R-25.5, are critically eroded, a condition influenced if not caused by the East Pass, and constitute East Pass’s “adjacent eroding beaches.” Evidence to the contrary was not persuasive. The greater weight of the competent substantial evidence establishes that the western areas of influence of East Pass, including the beach disposal areas at Monuments V-611 to V-622, are stable, if not accreting, and are not East Pass’s “adjacent eroding beaches.” Evidence to the contrary was not persuasive. The greater weight of the competent substantial evidence establishes that the City met the standards for the NTP as proposed for issuance by DEP on February 2, 2018. Evidence to the contrary was not persuasive. Thus, the NTP should be issued.
Recommendation Based on the foregoing Findings of Fact and Conclusions of Law, it is RECOMMENDED that the Department of Environmental Protection enter a final order: Approving the February 2, 2018, Notice to Proceed for the maintenance dredging of East Pass as authorized pursuant to Consolidated Environmental Resource Permit and Sovereign Submerged Lands Authorization No. 50-0126380-005-EI and State- owned Lease No. 0288799-003-JC, subject to the general and specific conditions set forth therein; and Denying the City of Destin’s Motion for Attorney’s Fees, Expenses and Costs pursuant to section 120.595(1). DONE AND ENTERED this 14th day of October, 2019, in Tallahassee, Leon County, Florida. S E. GARY EARLY Administrative Law Judge Division of Administrative Hearings The DeSoto Building 1230 Apalachee Parkway Tallahassee, Florida 32399-3060 (850) 488-9675 Fax Filing (850) 921-6847 www.doah.state.fl.us Filed with the Clerk of the Division of Administrative Hearings this 14th day of October, 2019.
The Issue The issues to be resolved in this proceeding concern whether the Department of Environmental Protection (DEP) has jurisdiction over the activities encompassed by Permit Application BA-475 (Amended) and, if so, whether issuance of the permit complies with the applicable provisions of Section 161.053, Florida Statutes, and Chapter 62B-33, Florida Administrative Code.
Findings Of Fact Undisputed Facts: The following relevant facts are established by stipulation or admission and are not disputed. The proposed project is landward of the seasonal high waterline within thirty (30) years of December 1996; The project will not interfere with public access; The project will not result in the net excavation of in situ sandy soils seaward of the coastal construction control line (CCCL); Any sandy soil or material excavated for the proposed project seaward of the control line will remain seaward of the control line or setback and be placed in the immediate area of construction; The proposed project complies with the structural provisions of Rule 62B-33.007(2), Florida Administrative Code; The proposed project complies with Rules 62B-33.007(3)(a) through (d) and (f) through (h), Florida Administrative Code. Additionally at hearing, the Petitioners and Intervenor announced that they would not present any evidence on the issue of adverse impacts on marine turtles. Accordingly, impacts on marine turtles are not at issue in this proceeding. Project Description: RHE has proposed constructing a restaurant, pool, deck and stormwater basin within the Boardwalk Beach Resort on Panama City Beach, in Bay County, Florida. The Boardwalk Beach Resort consists of four (4) multi-story hotels with six hundred (600) rooms all together, several pools, boardwalks extending the length of the property and approximately seventeen hundred (1,700) to eighteen hundred (1,800) feet of beach front property. The project site is between Thomas Drive to the north and the Gulf of Mexico to the south. On July 23, 1996, RHE applied to the Department for a CCCL permit to construct, seaward of the interim line established by the emergency Order of October 16, 1995, the restaurant, swimming pool and deck. Part of the proposed deck was located seaward of the coastal construction setback line. On December 9, 1996, the Department issued a permit to RHE to construct the restaurant building with an attached deck fifteen (15) feet landward of the location originally proposed by RHE, as well as for construction of the swimming pool. On December 16, 1996, the Department issued to RHE an Amended CCCL permit authorizing construction of a restaurant building located five (5) feet landward of the location originally proposed by RHE, as well as a deck re-designed so that it would be structurally independent of the restaurant, a swimming pool and a dune enhancement plan which would restore the sandy dune seaward of the pool and restaurant location to its pre-hurricane Opal condition and elevation. The Amended permit would require re-vegetation of the dunes at the site with native plants to secure the dunes from erosion. Both the original and the Amended permits authorized the removal of the stormwater drainage pipe that carried stormwater onto the beach that had caused erosion of the beach near the project area. On January 9, 1997, the Petitioners timely filed a Petition challenging the Department’s decision to issue the Amended permit. On February 7, 1997, the Department established a new CCCL line for Bay County that was farther landward than either the old coastal construction setback line or the interim line established in the October 1995 emergency order. The project authorized by the Amended permit would thus be located entirely seaward of the newly established CCCL for Bay County. As of February 7, 1997, the date the new line was established, RHE had not begun working on the foundation or continued construction above the foundation for any of the structures authorized by the Amended permit. The Department determined that the project did not meet the requirements of Section 161.053(9), and Rule 62B-33.004(1), Florida Administrative Code, so as to qualify for an exemption from complying with the newly established CCCL for Bay County, as the project was not “under construction” at the time the new CCCL was established. The beach and dunes system is wide and the dune system is a significant one, with elevations of fourteen (14) to sixteen (16) feet NGVD, with a wide dune crest. The dry sandy beach in front of the site, even after hurricane Opal struck, remained approximately one hundred twenty-five (125) feet wide. From 1855 to 1934 the shoreline of the site was mildly accretional. Thereafter, until 1955 accretion was less significant, but from 1955 to 1976 became significant. From February 1992 through April 1995, the project site experienced a period of mild erosion. Accordingly the long-term data shows, in essence, that the shoreline is relatively stable at the site. Hurricane Opal caused the dune to erode or retreat landward by approximately a distance of fifteen (15) feet. Hurricane Opal was a major magnitude storm with one hundred twenty-five (125) mile per hour sustained winds and one hundred forty-four (144) mile per hour measured gusts when it came ashore in the vicinity of the proposed site. The dune portion of the proposed site now essentially mimics the pre-Opal conditions. Following hurricane Opal the applicants spent approximately Four Hundred Thousand Dollars ($400,000.00) in dune restoration along the entire shoreline of the resort property, some seventeen hundred (1,700) to eighteen hundred (1,800) feet of shoreline. That dune restoration work was permitted by the Department. There is now little native salt-tolerant vegetation on the site in its natural pre-construction condition. An existing stormwater drainage pipe and catch basin extend onto the beach seaward of the location of the proposed restaurant. The existing pipe and basin have caused erosion of the beach and the sand dune system on the project site. Under the amended permit proposal the stormwater pipe and basin would be removed. All of the proposed structures authorized by the Amended permit would be landward of the pre-Opal coastal construction control line. The proposed pool will be located landward of the dune crest and fifty-five (55) feet landward of the toe of the dune. The proposed restaurant would also be located landward of the dune crest and two hundred five (205) feet landward of the mean high waterline. The original design of the project was for a much larger, three story restaurant. The original pool design called for a one hundred twenty foot pool extending from in front of the Comfort Inn to beneath the proposed restaurant, in effect being located on the first floor of the restaurant. At DEP’s request the size of the pool was reduced by fifty percent (50%) and it was relocated into the shadow of the Comfort Inn next door so that it will no longer serve as an integral part of the restaurant. Pool depths were also reduced to three (3) feet at DEP’s request. The pool, at DEP’s request, will now be constructed of Gunnite concrete material and will be frangible, that is, it will be designed to break up in storm-surge or storm-waves. This will serve to decrease the erosion which could be caused by storm-waves flowing over and around the pool structure. The same is true of the restaurant deck, which at DEP’s request has been re-designed to be separate from the restaurant and also designed to fail in storm conditions. The frangibility of the deck, as now proposed, will retard erosion during storm conditions, as the stormwater or waves will demolish the deck and remove it rather than scouring the sand dune around it. The Department also requested that the existing stormwater drain pipe and catch basin be removed and such a removal has been made a condition of the subject permit. This will require that the applicant design and build a new stormwater system. The applicant has agreed to this condition and the others referenced above. Vegetation: Construction of the proposed project will not result in the removal or destruction of native vegetation. There is no such vegetation on the site where the construction will take place. Thus, construction of the project will not result in removal or destruction of native vegetation which will either cause de-stabilization of a "frontal, primary or significant dune" or cause a significant adverse impact to the beach and dune system due to increased erosion by wind or water. A special condition of the proposed amended permit requires that the applicant submit a dune enhancement plan for restoration of the dunes seaward of the pool and restaurant to its pre-hurricane Opal condition, including re-vegetation. Such a plan was submitted by the applicant and it includes the planting of sea oats on one (1) foot centers. The planting of sea oats as part of the dune enhancement plan will constitute a significant improvement to the native vegetation situation at the site. Disturbance of Sandy Soils: The project will not result in the removal or disturbance of in situ sandy soils of the beach and dunes system to such a degree as to have an adverse impact on the system. That is, the existing ability of the system to resist erosion during a storm will not be reduced. The proposed project will not result in the removal or disturbance of in situ sandy soils of the beach and dune system to such a degree as to cause adverse impact to those systems by lowering existing levels of storm protection to upland properties and structures. All the sandy material excavated for the pool and the stormwater basin will be placed seaward of these structures on the dune in the immediate area of the construction and seaward of the CCCL. The additional sand to be placed on the dune as part of the dune enhancement plan will, in fact, enhance the ability of the system to resist erosion during the storm. The ability of the dune to resist storm erosion is primarily a function of the quantity of sand within the dune system. The additional sand to be placed on the dune as part of the dune enhancement plan will enhance the protection of upland properties and structures including those of the Petitioners and Intervenor. Excavation of the stormwater basin will not destabilize the dune on the project site. The applicant is moving the stormwater basin landward by twenty (20) feet which will minimize the potential impacts of the basin on the dune system. The preponderant evidence establishes that the structure of the pool and pool deck will not cause an increase in structure-induced scour of such a magnitude as to measurably affect shoreline change rates. Scour caused by the pool will not significantly interfere with the beach-dune system's ability to recover from a coastal storm. The frangible design of the pool decreases the likelihood that it will cause any scour. It will break up in a storm so that any scour caused by the pool would be minimal. Any scour caused by the pool would not disturb the topography or vegetation such that the coastal system would become unstable or suffer catastrophic failure. Scour would have no measurable effect. The proposed restaurant and deck will not cause an increase in structure-induced scouring during a storm of such a magnitude as to have a significant adverse impact. The restaurant and deck will be constructed on piles. Scouring around piles, in a storm situation, is very localized and insignificant. By constructing the restaurant and deck on piles at the design elevation, storm-surge and storm-waves will pass under the deck and restaurant. The restaurant and deck are located a sufficient distance landward of the beach and frontal dune to permit natural shoreline fluctuations. The structures will be built on pilings and will be elevated above the storm-surge; thus they will not interfere with shoreline fluctuations. The restaurant and deck are located a sufficient distance landward of the beach and frontal dune so as to preserve and protect beach and dune system stability, in terms of the lack of interference with such. Other structures in the area are seaward of the proposed restaurant and deck, including Pineapple Willies Restaurant, located eleven hundred feet to the west. Those structures have not caused instability of the beach during hurricane Opal. Typically, existing structures do not cause instability of the dune systems. The restaurant and deck are located a sufficient distance landward of the beach and frontal dune so as to allow for natural recovery to occur following storm-induced erosion. Natural recovery commonly occurs under pile-supported elevated structures which is not the case with “slab-on-grade” structures which are not elevated. The pool and pool deck will permit natural shoreline fluctuations, will preserve and protect beach and dune stability, and will allow recovery after a storm because they are designed as frangible structures that will fail and disintegrate in a storm situation. Thus they will not appreciably affect the beach-dune system. Line of Construction: Most coastal construction in Bay County extends out to the pre-Opal CCCL while some construction extends beyond it. Throughout Bay County the line of construction is the pre-Opal CCCL. The line of construction is determined by the most seaward extent of similar existing structures in the immediate area of the proposed structure under consideration in a CCCL permit application. The proposed pool is landward of the line of construction determined by existing pools within the boardwalk beach resort. There are a number of existing multi-story structures to the east of the proposed restaurant that are located out to the pre-Opal CCCL. That pattern of construction continues to the east of the proposed restaurant. Approximately one thousand (1,000) feet to the east of the proposed restaurant is an existing multi-story major structure that is built out to the pre-Opal CCCL. The beach in the area of the project is highly developed with commercial and condominium buildings. Within eleven hundred to twelve hundred feet to the west of the proposed restaurant there is another major structure built out to the pre-Opal CCCL. Just beyond that structure are a number of additional major structures, including Pineapple Willie's Restaurant, that are constructed out to the pre-Opal CCCL. The multi-story major structures to the east and west of the proposed structure are within the immediate area of the restaurant. The proposed restaurant is located landward of the line of construction established by these major structures within its immediate area. That line of construction is the pre-Opal CCCL. DEP did not consider major structures more than one thousand (1,000) feet from the proposed restaurant when it determined the line of construction for the restaurant. It is DEP’s policy when reviewing CCCL applications not to consider structures more than one thousand (1,000) feet from a proposed structure when determining the line of construction. The one thousand (1,000) foot limit DEP uses to determine the line of construction is not embodied in a rule. There was no preponderant coastal engineering or other scientific evidence which justifies the one thousand (1,000) foot limit DEP imposes when it determines the line of construction. It was appropriate to consider the existing structures referenced above in assessing the line of construction for this amended permit application and considering those lying just beyond the one thousand (1,000) foot distance, because those existing structures dominate the coastal processees in the region and only lie just beyond one thousand (1,000) feet to the east and twelve hundred (1,200) feet to the west. If the Department had considered the above-referenced existing major structures just beyond one thousand (1,000) feet of the proposed restaurant, it would have been shown that the proposed project was landward of the thus established line of construction. No preponderant evidence was offered to explicate why the one thousand (1,000) foot limit was automatically adhered to in this situation. Moreover, the line of construction is not a prohibition in and of itself but rather is only one of several criteria that must be balanced in determining whether or not to approve a CCCL permit application. Projects have been approved seaward of the line of construction in the past. Minimization The location of the swimming pool at the most practicable landward location, the reduced size of the pool, as well as its frangible design and limited depth, has minimized its impact. The placing of the excavated material in the pool’s immediate area and the restoration of the dune in front of the pool and deck have minimized the impacts of the pool and deck. The construction of the restaurant on pilings with its design elevation above storm-surge and storm-wave elevations, together with locating it behind the dune crest and away from the active beach, has minimized the impact of the restaurant. The deck is on pilings as well, elevated above storm-surge and storm-wave levels. It will be physically separate from the restaurant and its design frangibility (so that it will fail in a storm) results in its impact being minimized. The stormwater basin is located as far landward as practicable. Its location and the placing of the materials excavated for the basin on the dune immediately adjacent to the basin has minimized the impact of the proposed stormwater basin on the beach-dune system. The restaurant, pool, deck, and stormwater system will not have a significant adverse impact to the beach-dune system. The restaurant will not adversely affect exiting shoreline change rates, will not significantly interfere with recovery following a storm, and will not disturb topography or vegetation such that the system will become unstable or suffer catastrophic failure. Cumulative Impacts The proposed project will not have an unacceptable cumulative impact. There are no other proposed similar projects to take into account and a cumulative impact assessment has shown there to be no adverse cumulative impact. No evidence was offered to show that an unacceptable adverse cumulative impact in terms of existing or other proposed projects will result. Positive Benefit The proposed project will have a net positive benefit on the beach-dune system. The removal of the slab-on-grade constructed building will have a beneficial impact because it will reduce the chance of storm erosion to the beach-dune system posed by such structures. The existing stormwater pipe and catch basin which cause erosion would be removed, resolving that erosion problem. Stormwater will now be retained in a new stormwater basin designed to serve 1.7 acres and it will not flow onto the beach for any rainfall event up to a one hundred year design storm. The new stormwater system is designed to recover quickly after a storm event and to treat stormwater. The removal of the stormwater pipe and catch basin, and the installation of the new stormwater basin will have a positive benefit to the beach-dune system. The new stormwater system complies with Special Permit Condition 7. Moreover the applicant will restore the dune seaward of the project to its pre-hurricane Opal condition and will plant sea oats, on one foot centers, throughout the restoration area in accordance with Special Permit Condition 1.8. Such restoration of the dune and vegetation will benefit the beach-dune system. The natural recovery process will take several decades without the placement of sand in the dune restoration project. The dune enhancement plan submitted by the applicant, in order to comply with Special Permit Condition 1.8, exceeds the requirements of that condition since it places more sand on the dunes than necessary to achieve pre-Opal conditions. Testimony of expert witness Michael Walhter, which is accepted, establishes that restored beaches and dunes function much like natural ones in storm events even though they can be somewhat inferior in resistance to storm-surge and waves since the sand is not as compacted at first. This dune enhancement plan, however, exceeds the permit requirements by placing more sand than necessary on the dunes to achieve pre-Opal conditions. The Interim CCCL On October 16, 1995, the DEP issued its emergency Order establishing an interim CCCL for Bay County one hundred feet landward of the pre-Opal CCCL. The Department established that interim line in order to regulate coastal development in the wake of Hurricane Opal. In 1978 the Legislature established criteria to be used by DEP in establishing or re-establishing all CCCL’s. They are thus to be established to define that portion of a beach-dune system subject to severe fluctuations from a one hundred year storm event. At the time of Hurricane Opal, DEP had not re-established the Bay County CCCL using a one hundred year storm event criterion. The interim CCCL for Bay County established by the above-referenced emergency Order did not utilize nor was it based on the statutory one hundred year storm event criterion. All twenty-three (23) other CCCL’s that have been established based on the statutory one hundred year storm event criterion were established by rule. As of January 15, 1997, the applicant had received all governmental approvals necessary to begin construction of the proposed project except for that which is the subject of this proceeding. On January 22, 1997, DEP by letter advised the applicant to cease and desist construction of the project. On February 7, 1997, the Department by rule then taking effect established a new CCCL.
Recommendation Having considered the foregoing Findings of Fact, Conclusions of Law, the evidence of record, and the candor and demeanor of the witnesses, it is, therefore, DETERMINED: That the Department of Environmental Protection has jurisdiction over the proposed project and that it is, therefore, recommended that a Final Order be entered granting the Respondent, Resort Hospitality’s CCCL application consistent with the terms and conditions espoused by the Final Order of December 17, 1997, Respondent’s Exhibit 2 and the project plans depicted in Respondent’s Exhibits 3 and 4. DONE AND ENTERED this 30th day of January, 1998, in Tallahassee, Leon County, Florida. P. MICHAEL RUFF Administrative Law Judge Division of Administrative Hearings The DeSoto Building 1230 Apalachee Parkway Tallahassee, Florida 32399-3060 (850) 488-9675 SUNCOM 278-9675 Fax Filing (850) 921-6847 Filed with the Clerk of the Division of Administrative Hearings this 30th day of January, 1998. COPIES FURNISHED: Bram D. Canter, Esquire 103 North Meridian Street Tallahassee, Florida 32301 Thomas I. Mayton, Jr., Esquire Department of Environmental Protection 3900 Commonwealth Boulevard, Mail Station 35 Tallahassee, Florida 32399-3000 Thomas G. Tomasello, Esquire 1315 East Lafayette Street, Suite B Tallahassee, Florida 32301 Neil H. Butler, Esquire Butler and Long, P.A. Post Office Box 839 Tallahassee, Florida 32302-0839 Kathy Carter, Agency Clerk Office of General Counsel 3900 Commonwealth Boulevard Mail Station 35 Tallahassee, Florida 32399-3000 F. Perry Odom, Esquire Office of General Counsel 3900 Commonwealth Boulevard Mail Station 35 Tallahassee, Florida 32399-3000
Findings Of Fact On September 23, 1983, Hollywood submitted a permit application to DNR for construction of the proposed project which is the subject matter of this proceeding. DNR designated that permit application as Permit Application 50-41. The proposed project is actually the first phase of a two-phase project, Phase II of which has already been permitted by DNR. Phase I, which is the subject of Permit Application 50-41, consists of an extension of existing Surf Road in the City of Hollywood, an extension of an existing asphalt boardwalk, construction of a parking area with landscaped island, swale, and associated lighting. The excavated fill removed from the site of Phase I is to be used in the construction of a dune which is encompassed within Phase II of the project. The properties on which Phase I and Phase II are to be constructed are owned by the City of Hollywood and are located seaward of the Coastal Construction Control Line and landward of the Erosion Control Line. The Summit Condominium is a condominium development located west of South Surf Road in the City of Hollywood, and is directly adjacent and contiguous to the property upon which the aforementioned project is to be constructed. Petitioner is the builder and developer of the Summit Condominium and, in addition, is the fee simple owner of approximately 15 units in that development. Phase I of the proposed project, which is the permit application at issue in this proceeding, provides for the construction of a 121-space public parking area which will be approximately 62 feet wide and 605 feet long, and will extend approximately 95 feet seaward of the Coastal Construction Control Line. The parking lot will be constructed with a six-inch limerock base over a six-inch crushed limerock subbase, and will be surfaced with a one and one-half- inch asphalt wearing course. The parking lot is designed with a definite landward slope, so that stormwater will sheet flow across the parking lot away from the dune system. There is no evidence of record in this proceeding which would in any way justify a conclusion that stormwater runoff from the parking lot area will have any adverse effect on the dune system seaward of the lot. Stormwater runoff once it has left the parking lot surface will be collected in a swale and drainage ditch system located landward of the paved parking lot surface. The drainage ditch will be composed of sandy material presently located on the site and is designed on a 1.2 to 1 slope. In addition, Wedelia is to be planted in and around the drainage ditch system in order to stabilize the slopes of the ditch. The ditch and swale system is designed to allow most stormwater runoff to percolate into the soil, with any excess being collected in the ditch itself and transmitted in a northerly direction. A drainage calculation study prepared in conjunction with this proceeding demonstrates that the drainage capacity for the proposed ditch meets minimum standards contained in the South Florida Building Code, as applied by the City of Hollywood. As the ditch fills with stormwater, the water will flow in a northerly, shore parallel direction to Jefferson Street, which is located north of both the proposed project and the Summit Condominium. From Jefferson Street, runoff from the project site will flow westerly to Highway A-1-A where an existing stormwater sewer system is located. If for some reason that system proves insufficient to handle runoff, the runoff will then travel across A-1-A into the intracoastal waterway. There is no competent evidence of record in this proceeding to demonstrate that stormwater runoff from the project site will, under any conditions, flow onto Petitioner's property. Phase I of the project has been designed to minimize the potential for the creation of aerodynamically or hydrodynamically propelled missiles in the event of a major storm. The asphalt surface of the parking lot is designed to break into chunks which will settle into the sand or water when exposed to wind and water forces. The parking meters are set four feet into the ground which reduces their potential to act as missiles, but even should the beach recede to the point where the meters are installed, evidence of record in this proceeding establishes that they will fall to the base of the eroded dune wall and will be washed out to sea rather than be propelled shoreward either by water or air. Various storm surge computer models for pre- and post-construction conditions at various locations on the property were performed. The result of these models shows that there will be no difference in impact on the beach dine system and adjacent property between the pre- and postconstruction profiles in the event of a ten-year storm. Further, computer models actually showed that there will be less erosion for the post-construction profile than for the preconstruction profile in the event of a twenty-year storm surge. In the event of a fifty-year or greater storm event, the beach profile for both pre- and postconstruction in the project area would be inundated, so that the impact of such a storm will be the same with or without the proposed construction. Evidence of record does, however, establish that based upon postconstruction conditions as proposed in the permit application it would take a greater storm to erode material from the postconstruction profile, thereby establishing that the proposed project will afford greater protection than existing topography. It appears from the record in this proceeding that Hollywood's Permit Application 50-41 is complete, and that DNR has in its possession all information necessary and required by law for the processing of the permit application. Engineering plans submitted in support of the application for Phase T have been signed and sealed by a professional engineer registered in the State of Florida.
Recommendation RECOMMENDED That a Final Order be entered by the State of Florida, Department of Natural Resources, granting the requested permit. DONE AND ENTERED this 25th day of October, 1983, at Tallahassee, Florida. WILLIAM E. WILLIAMS 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 25th day of October, 1983. COPIES FURNISHED: Steven L. Josias, Esquire Donald J. Dooty, Esquire 3040 East Commercial Boulevard Fort Lauderdale, Florida 33308 Deborah A. Getzoff, Esquire Assistant General Counsel Department of Natural Resources 3900 Commonwealth Boulevard Tallahassee, Florida 32303 Leonard Lubart, Esquire Post Office Box 2207 Hollywood, Florida 33022 Elton J Gissendanner, Director Department of Natural Resources Executive Suite 3900 Commonwealth Boulevard Tallahassee, Florida 32303
