The Issue The preliminary issue in this case is whether the South Florida Water Management District (District) has jurisdiction over the Petition for Formal Administrative Hearing (Petition) filed by the Save the Manatee Club (Club)--i.e., whether the Petition was timely or, if not, if the District has jurisdiction under principles of equitable tolling or excusable neglect.
Findings Of Fact On October 11, 1999, Hidden Harbor filed with the District an application for an Environmental Resource Permit (ERP) to construct and operate a surface water management system serving a proposed residential development in Lee County, Florida. In January 2001, the Club sent an email to the Florida Wildlife Conservation Commission (FWCC) stating that it was concerned about Hidden Harbor's Application No. 991011- 13, as it might impact an area the Club would like to see as a manatee sanctuary, and was requesting copies of all FWCC documents relating to the permit. FWCC forwarded a copy of this email to the District on January 19, 2001. At the time, the Club's internet website gave the address of its main office in Maitland, Florida, as the Club's official mailing address. On April 9, 2001, the Club opened a Southwest Florida regional satellite office in Estero, Florida, and installed Laura Combs as Regional Coordinator in charge of that office. Responsibility for monitoring the Hidden Harbor application was delegated to Combs and the satellite office. Nonetheless, the Club's website continued to give the address of its main office in Maitland, Florida, as the Club's official mailing address. Combs's prior work experience with the Club was as assistant director of governmental relations in Tallahassee, Florida. In that position, she tracked legislation and actions of the Governor and Cabinet that were of interest to the Club. She had no role in the filing of petitions for administrative hearings on actions of governmental agencies. Combs's education included a bachelor's degree in English and a master's degree in urban and regional planning. She did not have specific legal education in the filing of petitions for administrative hearings on actions of state governmental agencies. On May 30, 2001, the District mailed to the Club at its Maitland office address a letter enclosing the "District's staff report covering the [Hidden Harbor] permit application [No. 991011-13]" and notifying the Club that the "recommendations as stated in the staff report [to grant the attached draft permit] will be presented to our Governing Board for consideration on June 14, 2001." The Club also was advised: Should you wish to object to the staff recommendation or file a petition, please provide written objections, petitions and/or waivers (refer to the attached "Notice of Rights") to [the District's deputy clerk]. The "Notice of Rights" addresses the procedures to be followed if you desire a public hearing or other review of the proposed agency action. You are advised, however, to be prepared to defend your position regarding the permit application when it is considered by the Governing Board for final agency action, even if you agree with the staff recommendation, as the Governing Board may take final agency action which differs materially from the proposed agency action. The Notice of Rights stated that it was intended to conform to the requirement of Section 120.569(1), Florida Statutes, to "inform the recipient of any administrative hearing or judicial review that is available under this section [120.569(1)], s. 120.57 or s. 120.68." It cautioned: Please note that this Notice of Rights is not intended to provide legal advice. Not all the legal proceedings detailed below may be an applicable or appropriate remedy. You may wish to consult an attorney regarding your legal rights. The Notice of Rights included a section entitled "Petition for Administrative Proceedings," which stated in pertinent part: A person whose substantial interests are affected by the South Florida Water Management District's (SFWMD) action has the right to request an administrative hearing on that action. The affected person may request either a formal or an informal hearing, as set forth below. A point of entry into administrative proceedings is governed by Rules 28-106.111 and 40E-1.511, Fla. Admin. Code, (also published as an exception to the Uniform Rules of Procedure as Rule 40E-0.109), as set forth below . . .. Formal Administrative Hearing: If a genuine issue(s) of material fact is in dispute, the affected person seeking a formal hearing on a SFWMD decision which does or may determine their substantial interests shall file a petition for hearing pursuant to Sections 120.569 and 120.57(1), Fla. Stat. or for mediation pursuant to Section 120.573, Fla. Stat. within 21 days . . . of either written notice through mail or posting or publication of notice that the SFWMD has or intends to take final agency action. Pertinent to this case, the Notice of Rights included a verbatim reproduction of Florida Administrative Code Rule 28- 106.201, addressing required contents of a petition to initiate proceedings involving disputed issues of material fact. Rules 28-106.111, 40E-1.5111, and 40E-0.109 were not reproduced in the Notice of Rights. It is not clear from the evidence when the letter dated May 30, 2001, with attachments (the Notice Correspondence), was received in the Club's Maitland office. It was not date-stamped, as time-sensitive correspondence normally would be. Apparently, it was decided to forward the Notice Correspondence to the new satellite office in Estero for handling. Combs received the forwarded Notice Correspondence in early June 2001. This was the "first time [Combs] had been through this type of process." Combs reviewed the Notice Correspondence, eventually focusing on paragraph 1.a. of the "Petition for Administrative Proceedings" section of the Notice of Rights. She did not read any of the cited statutes and rules except for the rules reproduced verbatim as part of the Notice of Rights. Combs made conflicting statements regarding her understanding of the District's administrative process. However, it appears that she understood that the Club could file a petition within 21 days of receipt of the Notice Correspondence, or within 21 days of the "final" action of the District's Governing Board. She testified that, because the Notice Correspondence did not bear a date-stamp, it was unclear when the first 21-day time period began or ended; as a result, she decided to wait until the District's Governing Board took "final" action and file a petition within the second 21-day time period. Combs appeared at the meeting of the District's Governing Board on June 14, 2001, and spoke in opposition to issuance of the draft permit. Notwithstanding the Club's opposition, the Governing Board decided to issue the draft permit. Combs does not have authority to file petitions for administrative hearings on District actions. She consulted with her supervisor, Patricia Thompson, and they made a recommendation to the Club's governing board, which has ultimate authority to file petitions. Prior to Combs's involvement in the Hidden Harbor application, the Club had staff legal counsel, who could be consulted with respect to the filing of petitions and would advise the Club's governing board. However, the Club did not have staff legal counsel at the time of Combs's involvement and through the time of filing of this petition. (The Club now again has staff legal counsel.) Neither Combs nor Thompson saw any need to consult an attorney. It is not clear when the recommendation of Combs and Thompson was presented to the Club's governing board or when the Club's governing board made its decision to file the Petition. Neither Thompson nor any member of the Club's governing board (nor anyone else who may have participated in the decision to file the Petition) testified. Several (according to Combs, approximately 12) times after the District's Governing Board's meeting on June 14, 2001, Combs telephoned the District's offices to obtain a copy of the District's Governing Board's "final" action when it was reduced to writing. It is not clear from the evidence why several telephone calls were required. Eventually, on June 26, 2001, Combs received a copy of the permit issued to Hidden Harbor; there was no Notice of Rights attached. On July 17, 2001, the Club filed its Petition challenging the permit issued to Hidden Harbor. In the meantime, Hidden Harbor had obtained a final development order from Lee County in reliance on the Club's failure to petition for an administrative hearing. The Club is not a newcomer to Florida's administrative process. It can be officially recognized that the Club has participated in numerous proceedings before DOAH. At least one of those cases involved issues similar to those presented for determination in this case. See Conclusion of Law 32, infra.
Recommendation Based upon the foregoing Findings of Fact and Conclusions of Law, it is RECOMMENDED that the South Florida Water Management District enter a final order dismissing the Petition. DONE AND ENTERED this 6th day of December, 2001, in Tallahassee, Leon County, Florida. _________________________________ J. LAWRENCE JOHNSTON Administrative Law Judge Division of Administrative Hearings The DeSoto Building 1230 Apalachee Parkway Tallahassee, Florida 32399-3060 (850) 488-9675 SUNCOM 278-9675 Fax Filing (850) 921-6847 www.doah.state.fl.us Filed with the Clerk of the Division of Administrative Hearings this 6th day of December, 2001. COPIES FURNISHED: Cindy L. Bartin, Esquire Post Office Box 861118 St. Augustine, Florida 32086 Martha M. Collins, Esquire 233 3rd Street North, Suite 100 St. Petersburg, Florida 33701 Keith W. Rizzardi, Esquire South Florida Water Management District 3301 Gun Club Road West Palm Beach, Florida 33406-3089 Frank R. Finch, Executive Director South Florida Water Management District Post Office Box 24680 West Palm Beach, Florida 33416-4680
The Issue As stated by the Hearing Officer the issue in this case is whether the District should issue a surface water management permit to Russell E. and Marilyn F. Scott, and Caloosa Television Corporation for the construction and operation of a surface water management system to serve a television signal tower and control building in Southeast Lee County, Florida. There are no significant water resource impacts related to the management of surface water by the proposed project. The harm at issue in this case is the potential for wood storks and other wading to strike the tower and guy wires which are not structures related to management and storage of waters. The parties disagree as to whether the District has jurisdiction to consider the bird impacts related to collisions with the tower and guy wires, and if so, whether the tower and guy wires will have a significant adverse impact on the water resources of the state through a reduction of wood storks, an endangered species, and other wading birds which through feeding on fish remove biomass from such water, thereby maintaining water quality. In determining jurisdiction in this case, the parties disagree on the meaning of "works" and "surface water management system" as used in Chapter 373, F.S. and Rule 40E-4, F.A.C. The petitioners argue that since one set of guy wires will be placed across one end of the cypress wetland located on the subject property, the entire project including the guy wire and tower is a "works" and part of the surface water management system, which is subject to the permitting jurisdiction of the District. The District and respondent Caloosa Television Corporation contend that the tower and guy wires are not structures related to surface water management and are not "works" nor part of the surface water management system, and therefore, bird mortality, as a result of hitting the tower and guy wires, is not subject to the permitting jurisdiction of the District. FINDINGS ON EXCEPTIONS At the Governing Board meeting of October 6, 1988, the petitioners waived Findings of Fact exceptions 1 and 2 of Petitioners' Exceptions to Finding of Fact, Conclusions of Law, and Recommended Order. Therefore, Findings of Fact exceptions 1 and 2 are rejected. The petitioners' exceptions 1, 2, and 3 to Conclusions of Law of the Recommended Order are rejected as set forth in the District's Response To Exceptions Filed by Petitioners filed on September 27, 1988, and attached hereto as Exhibit B and made part of this Final Order. The Governing Board accepts the exceptions filed by the District and the respondent, Caloosa Television Corporation, as set forth herein under Conclusions of Law.
Findings Of Fact On or about September 14, 1987, Caloosa filed Application Number 09147- B, for a surface water management permit, with the District. This application was for the construction and operation of a surface water management system to serve a 1249 foot high television transmission tower and control building in southeast Lee County, Florida. The proposed location of Caloosa's project is approximately one mile north of the boundary of the Corkscrew Swamp Sanctuary, which is owned and operated by Audubon, and specifically, approximately two and one-half miles north of a wood stork colony located within the Sanctuary. This rookery is the largest rookery of wood stork, a federally endangered wading bird, in the United States. The project site is 60 acres in size, and approximately square in shape. It is improved agricultural land, with a circular cypress wetland of about 5.5 acres located near the center of the site. Extending outward from the cypress wetland are two ditches, one running due east and the other due west. The existing surface water flow varies with the seasons and intensity of storm events. During dry seasons, the rainfall runoff flows into the cypress wetland and percolates into the ground. However, during wet seasons, water builds up in the cypress wetland and flows into the two ditches. In larger storm events, the project site is entirely under water, and sheet flows occur to the southwest. The proposed project should have a negligible impact on the existing surface water system since the total impervious area will only be approximately one acre, or 1.7 percent of the total project area of 60 acres. The project consists of a radio tower and guy wires, a 3150 square foot control building, fill pad and parking area, guy wire anchor slabs, and approximately 1650 feet of lime rock road with an equalizer culvert to maintain existing flow. Three sets of six guy wires will extend from the 1249 foot high tower and connect to the ground at anchor slabs located near the edge of the project site. The entire project is located outside of the limits of the existing wetland, but one set of guy wires does cross the western edge of the cypress wetland. Caloosa proposes to use the tower as a "community tower" which will be capable of supporting more than one transmitting antennae. In addition to Caloosa's antennae, the tower will be able to support up to five commercial radio stations and up to sixty two-way communication antennae. Caloosa has had contacts from several commercial radio stations and governmental agencies which have expressed interest in co-locating their antennae on Caloosa's tower. After review of this application, District staff advised Caloosa, on November 23, 1987, that it was recommending approval of the application since it was felt that any impact from the project on wood storks would not result from the construction and operation of this project. At hearing, the District supported the issuance of this permit, but urged that the tower and guy wires are not a part of the surface water management system over which the District has any permitting jurisdiction. Audubon timely filed its request for a hearing on the District's intent to issue this permit, and at hearing opposed the issuance of this permit to Caloosa, urging that the tower and guy wires were an integral part of the surface water management system, and therefore subject to the District's permitting jurisdiction. The wood stork and other wading birds are an important link in the biological and ecological chain. They are the main mechanism for removing certain species of fish from ponds, lakes and waters of the state. If there is no predation by wading birds, then an increase in the biomass of the water system would be expected, water quality would decrease, and fish kills would result. Ponds that receive biomass reduction by wading birds have a reduction in fish biomass of approximately 75%, with no loss in species, while ponds that do not receive wading bird predation lose almost all individual aquatic animals through reduced water quality resulting from retention of up to 94% of the biomass from dead fish. The reduction in biomass is in direct proportion to the number of birds feeding in a pond, and therefore a 5% reduction in birds will result in a 5% lessening of the biomass reduction. Water quality will be reduced by a lowering of oxygen levels in such waters due to the excessive retention of nutrient laden biomass. During the nesting season, wood storks feed in various ponds and wetland areas that surround the rookery. Their primary feeding areas are within ten miles of the rookery. The proximity of these sites allow the birds to make several flights per day between the colony and the feeding site, and to do so with less energy expended than with feeding sites that are farther away. Caloosa's project site is located between the rookery and a primary feeding area to the north that is within ten miles of the rookery. The proximity of this feeding area allows the birds to fly low, at tree top level, to the site, without the use of thermal updrafts that they use to attain altitudes of up to 5000 feet when traveling greater distances. Thus, if the tower is built, it would be likely that wood storks would fly in the direction of, and at the height of, the tower to reach this primary feeding area. However, it was not established how many such birds actually feed in this nearby area, or how many fish are in these ponds and wetlands. The wood stork colony at Corkscrew Swamp Sanctuary has been experiencing a decline in productivity from approximately 6000 nesting pairs in 1960 and 1966, there has been a steady decline in the number of nesting pairs in the colony, and in 1987, there were no nesting pairs in the colony. During 1988, 750 nesting pairs have been observed. The steady decline in the wood stork colony population is the result of already existing developmental pressures and changes in drainage patterns which have adversely affected the birds' feeding habitats. For nesting to be successful, two adult birds are required per nest during the nesting season, which usually occurs from November to March. This allows one adult bird to be away from the nest obtaining food while the other adult keeps the nest warm and safe from predators. If a nest is left unattended through the loss of one adult bird, it is likely that the entire nest will be lost since the fledglings are very vulnerable throughout the nesting season to predators and changes in temperature. There are usually two or three fledglings per nest. For this reason, the loss of five adult birds per year, for example, results in a total loss to the colony of between ten to fifteen fledglings. This loss compounds each year, as birds lost one year are not available to reproduce in following years. Generally, transmission towers can pose a hazard to birds due to the potential for collisions. Illuminating such towers at night does not decrease this danger since the birds are simply attracted to lights. Strobe lighting has also been tried, but it appears that birds ignore, or are not deterred, by strobes. In this case, Caloosa has agreed to accept conditions placed upon the approval of this project by the Lee County Board of Zoning and Adjustments on March 16, 1987, which include placement of aircraft warning balls on the guy wires and the tower itself, habitat improvement including the creation of a wetland and a wildlife through way, if necessary, and commencement of a monitoring system to identify any problems with wood stork mortality as soon as possible. A very extensive study of bird kills and transmission towers was conducted over a thirty year period involving the WCTV tower in Tallahassee, Florida. The WCTV tower was found to kill 3.9 wading birds per year on average. Based in part upon this data, the U.S. Fish and Wildlife Service concluded that wood stork collisions with the tower will not result in significant mortality, and an "incidental take" of five wood storks per year should result. This is a level of mortality which is noteworthy, since any loss to an endangered species is significant, but is clearly below that which would cause jeopardy to the species. Although Audubon correctly pointed out that the conditions present in the WCTV study do not exactly match those present in this case, such as the fact that there are almost three times as many wading birds in the area of the Caloosa tower as were in the area of the WCTV tower, as well as the differences in the geographical relationship of the tower to nearby wading bird colonies and feeding areas, nevertheless, the WCTV study is relevant and should be considered by the District since it is the most exhaustive study of its kind ever conducted. Caloosa presented evidence of a study it conducted over approximately a one month period in May and June, 1988, of a comparable existing radio tower, the WHEW tower, located near the subject property to the east. Although substantial wood stork and other wading bird activity was observed around the WHEW tower, there were no collisions of wood storks with this 1010 foot high tower. While not a scientific study in the strictest sense, and although it was not conducted for as extensive a period as the WCTV study, nevertheless, the District should consider the WHEW study conducted by Caloosa since it involves a comparable tower in close proximity to the subject property, and the person who conducted the study for Caloosa and who testified at hearing, Robert E. Gatton, appeared particularly credible. The Federal Communications Commission has approved the location of Caloosa's tower. I5. The Florida Game and Fresh Water Fish Commission has recommended that the proposed location for Caloosa's tower be changed to an alternate site which would present a less serious obstacle to the Corkscrew wood stork nesting colony and other wading birds. This recommendation is based on the policy that the mortality of even one wood stork is too much and may present a danger to the population of the wood stork rookery. It was not shown, however, that a basis in fact exists for concluding that the loss of five or fewer wood storks per year would present such a danger. The Commission's recommendation is also based upon a concern that transmission towers will proliferate in the area, and thereby further interfere with the flight paths of wood storks and other wading birds to their feeding locations. However, the fact that Caloosa is seeking to construct a "community tower" to be shared with several governmental agencies, as well as broadcasting stations, will actually serve to decrease this potential proliferation. While there is a potential for wood storks or other wading birds in the area to be killed or injured by striking Caloosa's tower or the guy wires while in flight, the extent of this danger is speculative, but would not appear to exceed five wood storks per year. Under these circumstances, there would not be a significant threat to the population, or continued viability, of the Corkscrew rookery. It has not been shown, by the evidence in this record, that any loss of wood storks and other wading birds caused by this project will result in fish kills through a significant reduction of predation and the resulting failure to remove accumulated biomass in ponds and waters in the area. It was not demonstrated that a fish kill will, or is even likely, to occur. While the loss of five wood storks would result in a certain amount of biomass not being removed from the area's wetlands, nothing in the record suggests that this amount will have an adverse impact on the state's water resources or will otherwise be significant. Therefore, any relationship between the tower proposed by Caloosa and impacts associated with biomass accumulation is purely speculative and de minimis. Fish kills occur naturally as water levels in seasonal marshes and ponds lower in the dry season. The water quality impact of such kills is relatively short-lived, lasting up to two months or until the next wet season begins, at which time water quality parameters return to normal. The evidence produced at hearing does not establish that the project and its surface water management system will have any significant or measurable effect on drainage of surface water runoff from the subject property, or on adjacent properties. The drainage system proposed by Caloosa will utilize the existing ditches and the natural cypress pond on the property. It was established that the post-construction effect of the project on drainage would be insignificant. There are, therefore, no drainage impacts associated with this project.
Recommendation Based upon the foregoing, it is recommended that the District enter a Final Order approving Caloosa's application for surface water management permit number 09147-B, subject to the conditions, agreed to by Caloosa, which were imposed by the Lee County Board of Zoning and Adjustment in its approval of this proposed development. DONE AND ENTERED this 29th day of August, 1988, in Tallahassee, Leon County, Florida. DONALD D. CONN Hearing Officer Division of Administrative Hearings The Oakland Building 2009 Apalachee Parkway Tallahassee, Florida 32399-1550 (904) 488-9675 Filed with the Clerk of the Division of Administrative Hearings this 29th day of August, 1988. APPENDIX TO RECOMMENDED ORDER, CASE NO. 88-5578 Rulings on Audubon's Proposed Findings of Fact: 1. Adopted in Findings of Fact 1, 3. 2-3. Adopted in Finding of Fact 4, but otherwise Rejected as a conclusion of law rather than a finding of fact. 4-5. Adopted in Finding of Fact 5, but otherwise Rejected as unnecessary, irrelevant and as a summation of testimony. 6. Adopted in Finding of Fact 2. 7-8. Adopted in Finding of Fact 7. 9-10 Adopted in Finding of Fact 8. 11. Adopted in Finding of Fact 11. 12-15. Adopted and Rejected, in part, in Finding of Fact 12. Adopted in Findings of Fact 8, 10, but otherwise Rejected as irrelevant and unnecessary. Adopted in Finding of Fact 9. Adopted in Findings of Fact 10, 12, but otherwise Rejected as cumulative and as argument on the evidence. Rejected in Finding of Fact 13, and otherwise as simply a summation of the testimony and argument on the evidence. 20-21. Adopted in Finding of Fact 6. 22-23. Rejected in Findings of Fact 15-17. 24. Adopted in Finding of Fact 15. Rulings on Caloosa's Proposed Findings of Fact: Adopted in Findings of Fact 1, 2. Adopted in Finding of Fact 4. Adopted in Finding of Fact 13. Adopted in Finding of Fact 1. Adopted In Finding of Fact 5. Adopted in Finding of Fact 19. Adopted in Finding of Fact 5, but otherwise Rejected as a conclusion of law and as simply a summation of testimony. Adopted in Finding of Fact 16. 9-10. Adopted in Finding of Fact 12. Adopted in Findings of Fact 12, 13. Adopted in Finding of Fact 11. Adopted in Findings of Fact 4, 15. Adopted in Finding of Fact 6. 15-16. Adopted in Finding of Fact 17. 17. Adopted in Finding of Fact 18, but otherwise Rejected as irrelevant and as cumulative. Rulings on the District's Proposed Findings of Fact: 1-2. Adopted in Finding-of Fact I. 3. Adopted in Finding of Fact 2. 4-5. Adopted in Finding of Fact 3. Adopted in Finding of Fact 4. Adopted in Finding of Fact 3. Adopted in Finding of Fact 8. Adopted in Findings of Fact 12, 14, 16. Adopted in Finding of Fact 12. 11. Adopted in Finding of Fact 13. 12. Adopted in Finding of Fact 16. 13. Adopted in Finding of Fact 15. 14. Adopted in Finding of Fact 11. 15. Rejected as irrelevant. 16. Adopted in Finding of Fact 11. 17. Adopted in Finding of Fact 6. 18-19. Adopted in Finding of Fact 5. COPIES FURNISHED: Charles Lee Senior Vice President Florida Audubon Society 1101 Audubon Way Maitland, Florida 32751 Russell P. Schropp, Esquire Post Office Box 280 Fort Myers, Florida 33902 James K. Sturgis, Esquire Post Office Box 24680 West Palm Beach, Florida 33416 John R. Wodraska Executive Director South Florida Water Management District Post Office Box 24680 West Palm Beach, Florida 33416 =================================================================
The Issue The issue in this case is whether Florida Administrative Code Rule 40E-7.523(2)(c) is an invalid exercise of delegated legislative authority.*
Findings Of Fact The Parties 1. The District is a public corporation existing by virtue of Chapter 25270, Laws of Florida (1949), and operating pursuant to Chapter 373, Florida Statutes, and Title 40E-7, Florida Administrative Code, asa multipurpose water management district, with its principal office in West Palm Beach, Florida. 2. KRVSA is a Florida corporation whose members are substantially affected by the rule in question. 3. Phillip B. Griner is an individual who holds a Special Use License to use the Lower Reedy Creek Management Area/Rough Island Management Unit Protected Zone. He has been a member of KVSA since its inception in 1998 and was serving on its board of directors at the time of the final hearing.
Conclusions Based upon the foregoing Findings of Fact and Conclusions of Law, the Petition for Administrative Hearing is denied. DONE AND ORDERED this 19th day of December, 2003, in Tallahassee, Leon County, Florida. Pan ate J. LAWRENCE JOHNSTON Administrative Law Judge Division of Administrative Hearings The DeSoto Building 1230 Apalachee Parkway Tallahassee, Florida 32399-3060 (850) 488-9675 SUNCOM 278-9675 Fax Filing (850) 921-6847 www.doah.state.fl.us Filed with the Clerk of the Division of Administrative Hearings this 19th day of December, 2003.
Other Judicial Opinions A party who is adversely affected by this Final Order is entitled to judicial review pursuant to Section 120.68, Florida Statutes. Review proceedings are governed by the Florida Rules of Appellate Procedure. Such proceedings are commenced by filing the original notice of appeal with Clerk of the Division of Administrative Hearings and a copy, accompanied by filing fees prescribed by law, with the District Court of Appeal, First District, or with the District Court of Appeal in the Appellate District where the party resides. The notice of appeal must be filed within 30 days of rendition of the order to be reviewed. 31
The Issue The issues to be resolved in this proceeding are whether the Department should issue a permit to Casetta, and whether the Department should issue a permit to Harbor Point. The two application proceedings were consolidated for hearing purposes. In many respects, common factual and legal issues relate to the two proceedings. For that reason, in the interest of economy of time and space, a single recommended order is being issued with respect to the two proceedings.
Findings Of Fact History of Proceedings In 1974, a prior owner of the property now owned by Casetta filed an application with the Department to entirely fill the pond which is the subject of this proceeding. A final order denying the application was entered by the Department on August 31, 1977. A second application to fill the entire pond was filed with the Department by Casetta's predecessor in 1979. During the pendency of that proceeding, Casetta purchased the property and by stipulation was permitted to be substituted as the Petitioner. The Department gave notice of its intent to deny the second application in February, 1981. Casetta challenged the Department's assertion that it had jurisdiction under the provisions of Chapter 253, Florida Statutes. The matter was forwarded to the Division of Administrative Hearings and given Case No. 81-1082. The matter before the Division has been closed, but it remains as a pending proceeding before the Department. It is being held in abeyance pending the resolution of Casetta's present application. The application involved in this proceeding was submitted to the Department during December, 1981. The City of Riviera Beach, Florida, granted local approval for this application; and on May 18, 1982, the Department issued a Notice of Intent to issue the permit. The Department published a notice of its proposed action in the Commercial Record, a Palm Beach County newspaper. The Florida Wildlife Federation and the Property Owners' Association of Singer Island together filed a request for formal hearing with the Department. The Singer Island Civic Association filed a separate request. Counsel for the Wildlife Federation and the Property Owners' Association withdrew during the course of the proceeding. It was indicated that these parties would voluntarily dismiss the requests for hearing, but no such papers were filed. No one appeared on behalf of the Florida Wildlife Federation or the Property Owners' Association of Singer Island during prehearing conferences that were conducted in this matter or at the final hearing. The Executive Director of the Florida Wildlife Federation testified as a public witness at the hearing and indicated that they were not participating in the proceeding as a party. During the pendency of proceedings respecting the Casetta application before the Division of Administrative Hearings, Harbor Point filed an application with the Department to install a culvert which would connect the pond that is the subject of the Casetta application with a pond located on property owned by Harbor Point through a culvert system. Harbor Point sought to have its application considered by the Department as an alternative to the Casetta application. On or about August 2, 1982, the Department issued a Notice of Intent to deny the Harbor Point application Harbor Point thereafter petitioned for a formal hearing. On or about June 4, 1982, the United States Corps of Engineers issued a permit to Harbor Point to construct its proposed culvert system. Description of Property in the Area of Proposed Projects. Casetta is the owner of approximately five acres of land that lie between the Atlantic Ocean and Lake Worth on Singer Island in Palm Beach County, Florida. The property includes a rectangular pond that is approximately three acres in area. This pond will hereafter be referred to as the "Casetta pond." Submerged lands in the Casetta pond were conveyed into private ownership by the Trustees of the Internal Improvement Trust Fund, State of Florida, in 1924. Harbor Point owns land adjacent to Casetta's property to the north. Harbor Point's property includes a pond which is configured in the approximate shape of an hourglass and is approximately one acre in area. A condominium apartment building has been constructed on Harbor Point's property. Harbor Point members own residential units in this facility. The area presently owned by Casetta and Harbor Point was, in its natural condition, a part of the littoral zone, a shallow, submerged area, on the eastern edge of the lake. Lake Worth is an estuarine water body located between the mainland and Singer Island. The littoral zone of such a lake is of fundamental ecological importance. It serves as a habitat for a wide variety of wildlife and serves to maintain water quality in the lake through uptake of nutrients by vegetation that thrives in the area. The natural condition of the area was markedly changed by the construction of State Road A-1-A. The highway separated the area, including what is now the Casetta and Harbor Point properties, to a large extent from the waters of Lake Worth. A culvert was constructed under the highway in the area of what is now the Harbor Point property. This culvert allowed tidal waters from Lake Worth to enter the area, and the area thus remained in a diminished fashion as a littoral zone of Lake Worth. Sometime between 1953 and 1964, landowners in the area constructed dikes which appear to have served as driveways along their northern and southern boundaries. Fill was placed on the Harbor Point property so that a pond was created in its present approximate configuration. The Harbor Point condominium facilities are presently in part set on the filled land. The Harbor Point pond remained connected with the waters of Lake Worth through the culvert system. The Harbor Point pond thus remains subject to tidal influences from Lake Worth. It is an estuarine system which serves as a part of the littoral zone of Lake Worth. The driveway to the condominium, however, completely Separated the Casetta pond from direct interaction with the waters of Lake Worthy. The Casetta pond is presently in an approximately rectangular configuration. Probably as a result of groundwater interaction, it is affected in a minimal manner by tidal influences in Lake Worth. The Casetta pond receives water from runoff and from groundwater interaction. It has become a freshwater body. While the Casetta pond is no longer a direct part of the Lake Worth estuarine system, and while it is by no means in its natural condition, it remains a wetland ecosystem. The pond is surrounded by mangrove communities. There is considerable biologic activity. Many bird species roost in the mangroves and feed in the pond. The mangroves provide shelter for aquatic organisms which are a food source for the birds. The pond does not support a wide diversity of marine plants or animals. A single species of minnow, mosquito fish, exists in substantial quantities These serve as a food source for birds including ducks, herons, egrets, and kingfishers It appears that the Casetta pond has been used in the past as a borrow pit to obtain fill for adjoining properties trenches, which are as much as six feet in depth, have been dug along the northern, southern, and eastern perimeters and across the pond. Because it is cut off from Lake Worth, and because of the ditches that have been cut through it, the Casetta pond is in a very deteriorated condition. While healthy mangroves surround the pond, they are, except to the west, extremely narrow populations due to the sharp banks that have been caused by dredging activity. The mangroves have no room to expand their population and are stressed due to invasion of upland vegetation such as Brazilian pepper. Widgeon grass exists in the lake bottom. Algae, however, has become the dominant vegetation in the pond. From 80 to 90 percent of the pond's bottom is covered by a mat of algae that ranges up to five and one-half inches in thickness. The algae population is increasing rapidly. Widgeon grass populations are being choked off by the algae. Dissolved oxygen levels in the Casetta pond are consistently low, below standards set in the rules of the Department. The oxygen demand of the algae community has depleted dissolved oxygen levels. While the Casetta pond functions as a wetland community, its values are severely reduced, and it appears that water quality in the pond is likely to continue to deteriorate. While by no means in a natural condition, the Harbor Point pond continues to function as a viable part of Lake Worth. This is a result of the pond being connected to the lake through the culvert system. The edges of the pond are populated by mangrove and cord grass communities. Marine species such as mullet are easily observable. Wading birds roost in surrounding vegetation and feed in the pond. The Harbor Point pond is basically a shallow, tidal water body. Water quality in the Harbor Point pond basically mirrors water quality in areas of Lake Worth to the west of Highway A-1-A. The Harbor Point pond has an eastern and western lobe connected by a narrower area, forming an approximate hourglass configuration. The eastern lobe is farthest from the connection to Lake Worth. Water quality in the eastern lobe is generally poorer than water quality in the western lobe and in Lake Worth. The deepest portion of the Harbor Point pond is in the eastern lobe. Wind action cannot serve to fully flush the waters of this area because of its relative isolation from the western lobe. Runoff from the Harbor Point condominium to the east of the pond and from a fire station parking lot to the west enters directly into the Harbor Point pond. It is filtered only by the action of grasses over which it flows. There is no ex-filtration drainage system. The culvert which connects the Harbor Point pond with Lake Worth runs from the western lobe of the pond under Highway A-1-A into Lake Worth. Lake Worth is a Class III water body under the Department's rules. The Parties' Proposals 1. The Casetta Application Casetta is proposing to construct a high-rise condominium on the eastern portion of its property. There is insufficient land on the property as it is presently configured to accommodate needed parking spaces. Casetta proposes to fill in 1.8 acres, or approximately 60 percent of the Casetta pond in order to construct parking facilities. Casetta has proposed to construct a culvert system that would connect the remaining portion of the pond with Lake Worth. The remaining portion of the pond would be regraded and configured. The northern and western boundaries would remain basically in their present configuration The remainder of the pond would be completely modified. A meandering shoreline would be created for an "L"- shaped pond. The bottom would be recontoured so that broader, shallow areas along the shoreline would be created. With the culvert system installed, the reconfigured pond would receive tidal waters from Lake Worth. The pond would effectively become, as the entire area once was, a portion of the littoral zone of Lake Worth. With the meandering shoreline and a gradually sloping bottom, the reconfigured pond would have as much area for littoral zone vegetation to establish itself as the present pond. Casetta proposes to commence construction activities by filling in a portion of the pond and regrading the remainder. The pond would be drained so that the algae that presently exists in large quantities would die and be removed. Clear fill material would be used to grade the pond. An exfiltration system would be created so that runoff that would reach the pond from upland areas would be filtered before it could enter the pond, thus reducing the impact of pollutants from upland runoff. The proposed culvert system would be in three sections. There would be a 35-foot section leading from the pond and slanting gradually downward to a point approximately eight to nine feet under Highway A- 1-A. The second section would be 110 feet long, lying vertically under Highway A-1-A. The third section would be 95 feet long, gradually rising from the second section to the bottom of Lake Worth. The bottoms of the open ends of the culvert in the Casetta pond and in Lake Worth would be at the ordinary low-tide marks. The top would be below the ordinary high-tide marks. Thus, the culvert openings would be exposed at low tide and submerged at high tide. The portion of the culvert under A-1-A would be filled with water at all times. It is necessary to place the culvert at least eight feet under Highway A-1-A in order to avoid utility pipes and cables that lie under the highway. The portion of the pipe under A-1-A would be installed through a boring technique known as "jack and bore." This technique would obviate any need for the closing of traffic on Highway A-1-A. The portion of the culvert in the Casetta pond and in Lake Worth would be installed by digging trenches, laying the pipe, then filling the trenches. Two openings would be made in the pipe at either end of the deep sections. These would be "manhole-type openings that would allow for periodic maintenance. Installation of the portion of the pipe in Lake Worth would be accomplished by building a work platform into the lake from material that is dredged from the trench. Once the pipe is laid, the material from the work platform would be placed back on top of the culvert, and any extra material would be removed from the site. Turbidity screens would be used to surround the project to reduce the short-term impacts of turbidity caused by construction. Once the pond is reconfigured and the culvert is installed, tidal flows would be introduced to the reconfigured pond on a gradual basis in order to observe any problems that might result. Shoreline grasses such as cord grass would be introduced in the shallow areas, and mangroves removed during filling operations would be replanted along the shoreline. This would serve to stabilize the shoreline and to provide the beneficial effects of littoral zone vegetation, including wildlife habitat and water quality benefits. The reconfigured Casetta pond would be approximately 33,000 square feet in area. If the culvert system functions as proposed, the reconfigured pond would become a part of Lake Worth. There are environmental and ecological advantages and disadvantages to the proposal. The disadvantages are rather obvious. One and eight-tenths acres of wetland habitat would be eliminated. While the present Casetta pond is only a marginally valuable wetland, it is not without its beneficent effects as have been described above. Furthermore, during construction, the habitat values of the Casetta pond would be lost, and short-term deleterious water quality impacts would occur in Lake Worth. There are trade-offs. The proposed filling, regrading, and connecting of the ponds to Lake Worth could have substantial positive impacts. The most apparent of these is that Lake Worth would regain 33,000 square feet of littoral zone. Construction activities have removed as much as 75 percent of the Shoreline vegetation that once Surrounded Lake Worth. The littoral zone has been replaced with developments that in ecological terms have negative impacts. Reconnecting the ponds to Lake Worth would be a slight reversal of that trend. Habitat for marine species would be increased, and the "kidney effect" that shoreline vegetation provides would be reestablished. Except during construction, Casetta's proposal would have no adverse water quality impacts upon surrounding waters. Adverse impacts during construction would be minimized by protective techniques that Casetta has proposed, including the use of turbidity screens. Long-term water quality impacts of the proposed project would be positive. Water in the present Casetta pond is of poor quality. The pond does not presently serve any water quality function for Lake Worth, since it is not connected to Lake Worth. Connecting the reconfigured pond to Lake Worth would allow waters from the lake to be purified through nutrient uptake by littoral zone vegetation. In habitat terms, the filling would reduce the total area of wetland habitat. The quality of the habitat would, however, be vastly improved. Rather than an unnatural, stagnant pond which provides habitat for only a few varieties of very common freshwater minnows, a marine habitat would be provided for all manner of creatures that survive in the littoral zone of estuarine water bodies. Bird habitats would not be reduced, since the shoreline of the lake would not be lessened. Thus, while the Casetta proposal would reduce the total size of wetland habitat, it would vastly improve it and would not have a detrimental effect that would be contrary to the public interest. In order for the reconfigured Casetta pond to offer an improved wetland habitat and a positive water quality impact for Lake Worth, it is essential that the proposed culvert system functions so as to allow an unimpeded interchange of water between the reconfigured pond and Lake Worth. If the culvert system does not operate, the result of the proposed project would be merely to lessen wetland habitat. Rather than a three-acre unnatural wetland habitat, there would be a 1.2-acre unnatural wetland habitat. Such an adverse impact upon wildlife habitat would be clearly contrary to the public interest. Furthermore, limited exchange of water between a eutrophic pond and Lake Worth could have an adverse impact upon water quality in Lake Worth so as to result in violations of the Department's water quality standards along the border of Lake Worth. The evidence does not establish that the proposed culvert system will properly function. Casetta had proposed a 36-inch culvert. Robert Snyder, a consulting engineer, was retained to determine the flushing characteristics of the culvert. Snyder calculated that maximum velocities associated with mean or average tides through the culvert system would be 1.89 cubic feet per second. Snyder calculated that this exchange rate would be sufficient to flush sediment and debris that would collect in the culvert. Thus, the culvert would be self- cleaning with only limited maintenance required to keep it open. In calculating the exchange rate, Snyder utilized the wrong formula. He overestimated the exchange rate by a factor of two. If the rate estimated by Snyder is reduced by a factor of two, it is apparent, that the exchange rate would not be sufficient to flush the culvert. Sediment and debris would collect in the pond, and rather regular maintenance would be required. Mechanical means can be utilized to clean a clogged culvert. A culvert of the length and configuration proposed by Casetta is difficult to clean through mechanical processes, however, and the processes themselves increase turbidity in the area. The evidence does not establish that regular maintenance would be sufficient to keep the culvert free of sediment and debris so that there would be a free exchange of water between Lake Worth and the reconfigured pond. When engineer Snyder was made aware of his miscalculations, he proposed reducing the size of the culvert to 24 inches. He testified that this would adequately increase the exchange rate so that the culvert would be selfmaintaining. Snyder's testimony in this regard has not been deemed credible. Given the witness's use of an erroneous formula in calculating exchange rates and another error that he admitted making in calculating scour potential, the witness cannot be considered competent to give expert testimony in these areas. If the culvert system proposed by Casetta allowed for the free exchange of waters between Lake Worth and the reconfigured Casetta pond, the water quality and habitat impacts of the proposed Casetta project would be, on balance, positive. The evidence does not, however, establish that the culvert system would function. It appears likely that the culvert system as proposed would be frequently clogged with sediment and debris, thus preventing the exchange of waters between the reconfigured pond and Lake Worth. The result of the proposed project would therefore be a reduction of wildlife habitat with potentially adverse water quality impacts upon the waters of Lake Worth. 2. The Harbor Point Proposal Harbor Point has proposed to install a culvert system that would connect the Casetta pond in its present configuration with the Harbor Point pond. Since the Harbor Point pond is connected through a culvert system with Lake Worth, the Harbor Point proposal would result in opening the Casetta pond to tidal influences from Lake Worth. Harbor Point has presented no evidence as to construction techniques that would be utilized and has provided no assurance that the construction itself would not result in water quality violations in the Harbor Point pond and in Lake Worth. Opening the Casetta pond in its present configuration to tidal influences would have the positive impact of allowing an exchange of water from the Casetta pond. Water quality in the Casetta pond would inevitably be improved. Given the configuration of the bottom of the Casetta pond, with its deep troughs, a complete exchange of waters would not occur, and water quality in the Casetta pond would be likely to remain poor, albeit improved. The Harbor Point proposal would have short-term and long-term negative impacts upon water quality in the Harbor Point pond and in Lake Worth. Simply opening the Harbor Point pond and Lake Worth to exchange of poor-quality water with the Casetta pond would have a negative impact. As water quality in the Casetta pond improves, this impact will be lessened, but will remain. Furthermore, the proposed culvert would result in poorer flushing of the waters from the eastern extremity of the Harbor Point pond. This would occur as a result of increased water velocities in the western extremity. Water quality in the eastern extremity of the Harbor Point pond is already stressed, and reducing the flushing characteristics of the pond would be likely to result in violations of the Department's water quality standards in the eastern portion of the Harbor Point pond. While the Harbor Point proposal would have the ecologically positive impact of opening the Casetta pond to tidal flows, it would have the negative impacts of reducing water quality in the Harbor Point pond and potentially along the shoreline of Lake Worth. Water quality in the Casetta pond would thus be improved at the expense of water quality in the Harbor Point pond and in Lake Worth. Riparian Rights Harbor Point owns a narrow fringe of the northern border of the Casetta pond. The precise amount of the Casetta pond that is owned by Harbor Point cannot be determined from the evidence, but it is clear that Harbor Point owns some portion of the Casetta pond which may be at one point as much as six feet of the northern portion of the pond. The Casetta pond offers minimal amenity to Harbor Point. The pond is unsuitable for boating, bathing, swimming, or any commercial enterprise. The pond is largely blocked from view by Harbor Point residents by abundant mangrove and upland vegetation. Reconfiguration of the pond as proposed by Casetta would not change the northern boundary of the pond, and it would remain largely blocked from view by Harbor Point residents. To the extent that the Casetta pond provides a view for Harbor Point residents, it is only minimally attractive given the configuration of the pond and given the fact that a high-rise condominium has been constructed on property to the south of the pond. There is no evidence in the record from which it could be concluded that the value of Harbor Point property would be in any way reduced as a result of the projects proposed by Casetta.
Findings Of Fact Based on the stipulations and admissions of the parties, on the exhibits received in evidence, and on the testimony of the witnesses at hearing, I make the following findings of fact. Facts admitted by all parties The water quality standards contained in Rule 17-3.111, Florida Administrative Code will not be violated by this project. There are no aquatic macrophytes located in the area of the proposed project. The proposed project is located within 500 feet of the incorporated municipality of Horseshoe Beach, Florida. The proposed project is located within Class II waters of the State not approved for shellfish harvesting. The project will not adversely affect the conservation of fish and wildlife, including endangered or threatened species, or their habitats. The proposed project will be of a permanent nature. The project will not adversely affect or will not enhance significant historical or acheological resources under the provisions of Section 267.061, Florida Statutes. The rest of the findings The Applicant, Dixie County, applied for a dredge and fill permit to construct a dock which would expand the existing public dock at Horseshoe Beach. In accordance with the revised plans dated October 23, 1986, the proposed facility would consist of a pier 6 feet wide and 120 feet long designed to accommodate six boat slips, each 30 feet wide and 40 feet long. The boundaries of the boat slips will be demarcated by pilings set 10 feet apart. Four of the boat slips would be primarily for the use of commercial fishing boats and commercial shrimping boats. The other two boat slips (the two slips closest to the land) would be reserved for the exclusive use of recreational and other small vessels. By adding a catwalk 3 or 4 feet wide down the middle of the two slips reserved for recreational vessels, the usefulness of those slips to recreational vessels would be greatly enhanced and the narrowness of the resulting slips would preclude their use by large vessels. Adding the two catwalks would be a minor addition to the proposed project which would greatly enhance the usefulness of the project and at the same time avoid the possibility that large vessels in the two slips closest to the land would impede ingress and egress at the nearby boat lift, boat fueling facility, and boat ramp. Adding a reasonable number of permanent trash or garbage containers would also enhance the usefulness of the proposed project and minimize the possibility of improper disposal of trash and garbage which is generated by the normal use of a dock by fishermen and boaters. The proposed project site is located in the Gulf of Mexico at Horseshoe Beach, Florida, and would extend into the waters of the Gulf, which is a tidally influenced water body adjacent to Dixie County, Florida. The water along the shoreline of the area is shallow for a considerable distance waterward, except where basins and channels have been dredged. The Horseshoe Beach area is relatively unpolluted. The existing public dock at Horseshoe Beach is used primarily by recreational vessels, but there is also extensive commercial fishing and Shrimping boat activity in the area. The project is located at the mouth of a canal with direct access to the Gulf. Several commercial fishhouses operate from the canal bank, which generates extensive commercial boat traffic past the proposed project site. Large numbers of commercial shrimp boats presently dock along the canal that ends near the proposed project site. The proposed project requires no dredging. The only filling required by the proposed project is the placement of pilings into the bottom of the Gulf of Mexico. Even though the plans do not specify whether concrete or wooden pilings will be used, this lack of specificity in the plans is irrelevant. Regardless of what types of pilings are used on this project, the filling activity will not violate the water quality criteria contained in Rule 17- 3.051(1), Florida Administrative Code. The placement of the pilings will not adversely affect the public health, safety, and welfare. Further, the proposed project will not adversely affect any property interests of the Petitioners within the scope of Chapter 403, Florida Statutes. The Gulf bottom in the area of the proposed project has already been disturbed. The presently existing suspension of particulate material in the water column, a natural occurrence in the area of the project, results in low visibility which means that seagrass beds and other marine vegetation, which provide shelter and detrital deposits for fish and other marine resources, will not grow. Coast Guard regulations prohibit commercial fishing vessels from depositing materials into the water within three miles of the coast line. Commercial fishing vessels must prominently display a sticker reciting that regulation and it is the practice of commercial fishing vessels operating in the vicinity of Horseshoe Beach to comply with this Coast Guard no discharge requirement by cleaning nets and scrubbing decks outside the three mile limit. It is not the practice of Commercial fishing vessels to deliberately discharge diesel fuel, fish parts or other material into the water while docked. Further, the limited number of commercial fishing vessels which could dock at the proposed facility at the same time cannot reasonably be expected to create discharges in amounts creating a nuisance, posing any danger to the public health safety or welfare, or violating the water quality criteria contained in Rule 17-3.051(1), Florida Statutes. Although small amounts of diesel fuel can become mixed with bilge water and be discharged by automatic bilge pumps while commercial fishing vessels are docked, there is no evidence that this would be in amounts Sufficient to create a nuisance or violate water quality criteria. To the contrary, notwithstanding a large amount of commercial boat traffic past the proposed site and notwithstanding the fact that large numbers of shrimp boats dock up the canal from the proposed site, the water in the area of the proposed site has remained relatively unpolluted. The proposed project will not affect the normal wind and wave action in the area of the proposed project. Such wind and wave action presently results in free exchange between the waters of the open Gulf and the waters near the shore. This free exchange of waters means that any pollutant discharges in the area of the proposed project will be diluted and rapidly dispersed into the Gulf of Mexico. There will be no measurable difference in the wind and wave action, or in the water exchange, after the proposed project is built. No harmful shoaling or erosion is expected to result from construction of the proposed project. Any docking structure extending out into the Gulf of Mexico will obviously have some effect on navigation in the area of the dock, but there is no evidence that the proposed dock will present a hazard to navigation or any significant interference with customary navigation patterns. The distance between the nearest channel marker and the waterward end of the proposed project is more than 200 feet. The angle of the proposed dock and its Spatial relation to the main Horseshoe Beach turning basin cause no impediment to navigation. The placement of Coast Guard Safety lights on the dock would minimize any potential for impeding navigation or posing a danger to the public health or safety during hours of darkness.
Recommendation Based on all of the foregoing, I recommend that the Department of Environmental Regulation issue a Final Order in this case granting the permit applied for by Dixie County. It is also recommended that the permit be made subject to the following additional conditions: That one or more Coast Guard safety lights be placed on the proposed expansion to the dock; That catwalks be added down the middle of the two most landward of the proposed boat slips; and That a reasonable number of trash or garbage receptacles be permanently located on the proposed expansion to the dock to minimize the possibility of trash and garbage being thrown overboard. DONE AND ENTERED this 30th day of October, 1987, at Tallahassee, Florida. MICHAEL M. PARRISH, Hearing Officer Division of Administrative Hearings The Oakland Building 2009 Apalachee Parkway Tallahassee, Florida 32399-1550 (904) 488-9675 Filed with the Clerk of the Division of Administrative Hearings this 30th day of October, 1987. APPENDIX TO RECOMMENDED ORDER, CASE NO. 86-1448 The following are my specific rulings on all of the proposed findings of fact submitted by all of the parties. The paragraph numbers referred to below are references to the paragraph numbers in the parties' respective proposed recommended orders. Ruling on findings proposed by the Petitioners: Paragraph 1: Accepted. Paragraph 2: Accepted. Paragraph 3: Accepted. Paragraph 4: First sentence is rejected as appearing to be more in the nature of an introduction to a discussion of legal issues than a proposed finding of fact. Second and third sentences are rejected as repetitious Paragraph 5: Entire paragraph rejected as unnecessary speculative generalizations in light of the other evidence in this case. Paragraph 6: Entire paragraph rejected as unnecessary speculative generalizations in light of the other evidence in this case. Paragraph 7: Rejected as contrary to the greater weight of the evidence. Paragraph 8: Entire paragraph is rejected as appearing to be more in the nature of an introduction to a discussion of legal issues than proposed findings of fact. Paragraph 9: Entire paragraph rejected as contrary to the greater weight of the evidence; construction of the dock may be expected to bring about some changes in the nature of the boat traffic in the immediate area, but nothing of the nature or magnitude suggested by these proposed findings. Paragraph 10: Rejected as contrary to the greater weight of the evidence. Paragraph 11: First sentence is rejected as contrary to the greater weight of the evidence. Second sentence is accepted in part and rejected in part. Rejected portion is irrelevant. Third sentence is rejected as irrelevant. Fourth Sentence is accepted. Fifth sentence is rejected as contrary to the greater weight of the evidence and as repetitious Sixth sentence is rejected as contrary to the greater weight of the evidence. Paragraph 12: Entire paragraph rejected as contrary to the greater weight of the evidence. Rulings on findings Proposed by the Respondent: Paragraph 1: Accepted. Paragraph 2: Accepted in substance. Paragraph 3: First two sentences accepted in substance. Last sentence rejected as irrelevant. Paragraph 4: Accepted. Paragraph 5: Accepted. Paragraph 6: Accepted. Paragraph 7: Rejected as unnecessary recitation of opposing party's contentions and not proposed finding of fact. Paragraph 8: Accepted in substance. Paragraph 9: Accepted in substance. Paragraph 10: Accepted. Paragraph 11: Accepted in substance. Paragraph 12: Accepted. Paragraph 13: First sentence accepted in substance. Second sentence accepted in part and rejected in part; rejected portion concerns riparian rights, which are irrelevant to whether this permit should be issued. Paragraph 14: Entire paragraph rejected as irrelevant. Paragraph 15: Accepted in substance. Paragraph 16: Accepted. Paragraph 17: Accepted in substance. COPIES FURNISHED: Frederick M. Bryant, Esquire Moore, Williams & Bryant, P.A. Post Office Box 1169 Tallahassee, Florida 32302 J. Doyle Thomas, Esquire County Attorney Post Office Box 339 Cross City, Florida 32628 Ann Cowles-Fewox, Legal Intern Twin Towers Office Building 2600 Blair Stone Road Tallahassee, Florida 32399-2400 Karen Brodeen, Esquire 2600 Blair Stone Road Tallahassee, Florida 32301 Dale Twachtmann, Secretary Twin Towers Office Building 2600 Blair Stone Road Tallahassee, Florida 32399-2400
Findings Of Fact The proposed marina project involves the repair and renovation of a marina which has been in existence since the 1920s. The marina is located in Biscayne Bay within the City of Miami Beach, west of Purdy Avenue where it intersects with 13th Street. Currently, the marina is in a state of disrepair. In 1974, Respondent acquired ownership of the marina which was at that time an operating facility. Thereafter, Respondent began formulating plans to renovate and repair the facility. Respondent obtained estimates from construction firms to make repairs to the facility by replacing or reinforcing deteriorated members, piles, decking and other parts. Respondent plans to remove the existing wooden piers and piles consisting of 35,000 square feet of deck surface area and construct in their stead a facility consisting of only 24,560 square feet of deck surface area. The marina as renovated would not exceed its existing boundaries. In fact, the south pier of the marina will be relocated 40 feet northward of its existing location, which would place it 90 feet from the south property line. The proposed project entails construction of three main piers. The south pier is an L-shaped configuration which would extend westward 416 feet by 10 feet and then northward 304 feet by 10 feet. The north pier, also L-shaped, would extend westward 416 feet by 10 feet and then southward 202 feet by 10 feet. The center pier will have a T-shaped configuration. Its dimensions will extend westward 358 feet by 10 feet. The marina will also have a pier extending both northward and southward, 50 feet by 10 feet each from the center line of the pier. Additionally, the project will contain mooring piles along a canal which extends eastward from the northern perimeter of the marina. When completed, the marina will have accommodations for 161 vessels. The present facility, while it was a fully operating marina, accommodated 135 boats, together with over-the-water facilities constructed on a main center pier. Such facilities included a machine shop and major marina repair facilities, neither of which uses is proposed for the new facility. Construction activity for the proposed project involves no dredging or filling. In addition to reducing deck surface area to 24,560 square fete from the 35,000 square feet contained in the old facility, the proposed project also will contain 409 pilings as opposed to 1,037 in the existing facility. Existing wooden pilings will be removed and will be replaced with concrete pilings. Turbidity curtains will be used during the construction phase to reduce any adverse affect on water quality, which, in any event should be minimal. The concrete pilings will be installed by setting them in a steel template and driving them into the earth at the bay bottom with a hammer. In effect, this construction technique punches a hole straight down into the earth and results in minimal displacement of sediments at the bottom. Respondent also proposes to make certain cosmetic repairs to the sea wall at the present marina where there is some deterioration on the upper edges above the mean high water line resulting from corrosion. Such repairs will be made by welding of steel plate and putting a concrete cap over the top of the existing wall. The waters of Biscayne Bay are classified as Class III waters. There are no Class II waters in the vicinity of the proposed project. The testimony and evidence established that the area in and surrounding the marina facility is not productive in terms of benthic or faunal communities. There is virtually no marine vegetation in the area. The marina itself is almost devoid of any seagrasses, with the exception of several springs of Halophila and Caulerpa. The closest existing grass beds are located approximately 700 to 1,000 feet west of the marina's western perimeter. These grass beds, which include turtle grass and manatee grass, have apparently flourished during the period the existing marina was in full operation. Fouling organisms were found attached to pilings and the seawall areas of the marina. The waters inside the marina, and those in the surrounding area are not suitable as a habitat for breeding, nursery or feeding grounds for fish or other marine life. Studies conducted by Respondent's hydrographic expert indicate that tidal flow in the area of the marina will be enhanced by the renovation of the facility, largely due to reduction in the number of pilings, thereby reducing resistance to tidal flow. The evidence also disclosed that construction of the proposed facility will pose no navigational hazard or serious impediment to navigation in the immediate vicinity. The canal along the northern perimeter of the proposed project varies from 105 feet in width. Apparently only noncommercial boats will be docked in the marina and the canal. A marina has existed at the location of the proposed project for over 50 years, and there is no evidence that has ever created navigational problems within the canal or within the immediate area of Biscayne Bay. Petitioners suggest that the marina will "create a navigational hazard, or serious impediment to navigation..." within the meaning of DER's regulations, specifically Chapter 17-4.29(6)(b), Florida Administrative Code, under the theory that the boats to be accommodated in the facility will result in a general increase in boating traffic in north Biscayne Bay, and would, in addition, adversely affect the public's "navigation" of automobiles across numerous draw bridges whose spans will often be raised to accommodate boat traffic. It does not appear that chapters 253, 258.165 or 403, Florida Statutes, afford DER the authority to consider such factors in determining whether to issue a water quality permit. Even assuming that as a matter of law DER may consider such factors, the evidence presented by Petitioners on this point was vague and speculative. In its Proposed Order of Issuance, DER imposed seven permit conditions which, when combined with the design of the project and the facts set forth above, constitute "reasonable assurance" that the proposed project will not adversely affect water quality. These conditions include the following: Turbidity shall be monitored once daily during periods of water related construction activities at mid-depth 100 ft. upcurrent and 100 ft. down-current of the work area by a person(s) (project monitor) designed by the permittee. Adequate controls are taken during construction so turbidity levels beyond 100 ft. of the construction area in Biscayne Bay do not exceed 50 J.T.U. A pumpout station shall be installed and maintained for the removal of sewage and wastes from the vessels using this facility. No liveaboard vessels shall be docked at this facility unless said vessel has either a Coast Guard approved Marine Sanitation Device or a direct sewage pumpout connection is provided at the liveaboard slip. There shall be no positive drainage of stormwater runoff from the marina parking lot to Biscayne Bay. Fuel storage tanks shall be constructed of non-corrosive materials and located on the upland portion of the site. The fuel storage tanks shall be pressure tested at least once yearly to ensure that they are not leaking. Test reports shall be submitted to DER and the Dade County Environmental Resources Management. Floating oil booms and sorbent materials or equivalent equipment shall be available on site at all times in order to contain and clean up any oil or fuel spills. All marina employees shall be trained in the deployment and usage of the above spill cleanup equipment. The equipment above shall be subject to inspection by all regulatory agencies. At the conclusion of the hearing, it was stipulated among the parties that Petitioner, Izaak Walton League of America, Mangrove chapter, has standing to maintain this action pursuant to Section 120.57(1), Florida Statutes. With respect to Save Our Bay, the evidence disclosed that it is an unincorporated association which was formed for the purpose of preserving the waters of Biscayne Bay for safe navigational use, swimming and fishing, and to enhance the beauty of sunset Island and the venetian Isles, while at the same time protecting the area from the effects of pollution. Members of Save Our Bay own property in the vicinity of the proposed project, and use the waters in that area for swimming, boating and fishing. Their use of the natural resources of Biscayne Bay could be affected by construction of the proposed project. Walton, Save Our Bay and Respondent Turchin have submitted proposed findings of fact in this proceeding. To the extent that such findings of fact are not adopted in this Recommended Order, they have been specifically rejected as being either irrelevant to the issues in this cause, or as not having been supported by the evidence.
The Issue The issues in this proceeding involve whether the Respondent, St. Joe Paper Company ("St. Joe"), is entitled to a "dredge and fill permit" authorizing it to construct a marina for recreational boats, containing 84 boat slips, along the eastern shore of the St. Johns River in St. Johns County, Florida. Embodied within that general consideration are issues involving whether St. Joe, in the construction and operation of the marina, can comply with water-quality parameters embodied in Chapter 17- 3, Florida Administrative Code, for Class III waters of the State, Section 403.918(1), Florida Statutes, as well as the public interest standards of Section 403.918(2), Florida Statutes, and the standard concerning "cumulative impact" embodied in Section 403.919, Florida Statutes.
Findings Of Fact The applicant, St. Joe, seeks to construct and operate a recreational boat marina, consisting of a single, main pier, 12 feet wide and extending some 850 feet waterward in a westerly direction from the shoreline of the east bank of the St. Johns River in St. Johns County, Florida. The main pier will join a terminal pier extending approximately 575 feet in a general north/south direction parallel to the shoreline of the St. Johns River, perpendicular to and abutting the longer main pier. Extended in a landward or easterly direction from the terminal pier structure will be four (4) individual "finger piers" ranging from 119 to 305 feet in length. Located along the individual piers and along a portion of the main pier near the waterward end of it will be 84 slips for recreational-type boats. Additionally, a breakwater system will be suspended along the outer perimeter of the terminal pier and northernmost and southernmost individual piers in order to reduce wave action and its effect on boats in the interior of the marina. Additional details concerning the marina design and operation are contained in the findings of fact below. The Site The site of the proposed marina is on the eastern shore of the St. Johns River in St. Johns County, Florida. At that point, the St. Johns River is almost two miles wide, being approximately 10,000 feet from shoreline to shoreline. The proposed marina site encompasses approximately 1,100 linear feet of river bank frontage. All of the adjacent upland property is owned by St. Joe, and St. Joe owns extensive additional river frontage to the north and south of the marina site. The nearest properties not owned by St. Joe are located 3,500 feet to the north of the site and 1,500 feet to the south of the site. The site is located approximately two miles north of Hallowes Cove, a relatively pristine, diverse and productive marine habitat. The site is characterized, landward of the terminal end of the pier and waterward of the upland, by an unvegetated "near shore area or tidal zone" which extends approximately 50 feet from the mean high-water line of the river to the mean low-water line. Waterward of this zone and extending to a depth of approximately two feet is a system of grass beds, (vallisnerida), commonly known as "tape grass". The grass beds extend approximately 200 to 250 feet from the shoreline. Waterward of the grass beds is an unvegetated area with a gradual slope to a depth of approximately six feet. From the six-foot contour of the river bottom, a relatively precipitous slope begins, extending to depths which exceed 19 feet. In this zone, there are no grass beds. Further waterward and extending beyond the most waterward extent of the the marina site, the river bottom rises somewhat to depths of 13 feet, 12 feet and 11 feet, in the direction of the center of the river. The river bottom substrate in the area of the marina is composed primarily of sand. This includes some shell and other coarse materials, with minor amounts of silt. In fact, organic silt is a very small portion of the bottom sediments, consisting, at a depth of four and one-half feet, of less than 1% silt and at a depth of 15 feet of less than 6% silt content. The present water quality prevailing at the marina site is good, and the benthic habitat in the general area is healthy and diverse. The most landward boat slips proposed at the marina will be located at a distance of approximately 275 feet from the most waterward extent of the grass beds. These most landward slips will be located in depths of approximately eight feet. Access to the marina will be from the north and south in defined channels marked on the west by the end of the individual piers and on the east by channel markers located at the depth contour of minus six feet. That is, the six-foot depth will be the most shallow portion of the channel marked by the channel markers, so that boats will not be permitted to navigate the shallower portion landward of the channel markers insofar as the marina's enforcement program can insure that. The approximate width of the northern channel is 75 feet, and the width of the southern channel is 50 feet. Due to the precipitous drop in depth beyond the contour of minus six feet, the average depth of the channels is 10 to 12 feet. The majority of the boat slips, as well as the basin of the marina, will be located in depths of between 10 and 18 feet. The consultant and expert witness who designed the marina, Erik Olsen, established that the length of the main pier and the location of the most landward of the boat slips and the location of the channel markers are all part of a design and plan intended to insure that marina and boat activity within the marina occur well beyond the extant grass beds and waterward of depths of six feet, to insure that no damage to the grass bed habitat area is occasioned by propeller scouring, "prop-wash", or grounding of boats. Other design measures are also intended to preclude boaters from entering the shallow depths and grass bed areas. Two tiers of signs will be located between the marina basin and the most waterward extent of the grass beds. First, regulatory buoys and signs are proposed to be located at the contour of minus four feet and will establish a "manatee protection zone" landward of that contour. The evidence reveals, however, that a safer contour for the manatee protection zone boundary to be established by the applicant would dictate placing the regulatory warning signs concerning the manatee protection zone at the same contour, minus six feet of water, where the channel markers will be located. This is because the marina will serve boats of up to 4.5 feet in draught. Secondly, a tier of signs will be located approximately ten feet waterward of the most waterward extent of the grass beds warning boaters that aquatic grass beds exist landward of the signs and that prop dredging and boat operation is prohibited. Such warnings at the locations found above should be mandatory conditions to any grant of the permit. A specific, agreed-upon condition is already in the draft permit issued by the Department prescribing the size and lettering of these signs and other design details. A railing will extend, as proposed by the applicant, along the main pier between the slips and the shoreline to discourage boaters from mooring along the main pier, landward of the slips. The evidence establishes that in order to more adequately insure protection of the manatee habitat area and the grass beds, a mandatory condition in boat-slip rental leases should be inserted to absolutely prohibit boaters from mooring along the main pier, landward of the boat slips. Because of the currents and significant water depth prevailing at the marina site, the marina construction will require no dredging nor will operation and maintenance of the marina require any dredging on a continuing basis. Additionally, in the interest of protecting water quality, no fueling facilities or boat fueling will be permitted at the marina at all; and the grant of a permit should be mandatorily conditioned on this basis. Neither will any boat maintenance or repair be permitted at the marina, including no hauling of boats or scraping or painting of boat bottoms. This condition should be clearly pointed out to users of the marina by appropriate warning signs regarding the prohibition against boat maintenance and repair, including warnings concerning the proper methods of disposal of used oil and other petroleum products. The marina will feature pump-out facilities for boat heads and bilges. The pump-out facilities will consist of a central pumping system in which waste is removed from the boats, transported by pipeline to an upland, central waste water collection and treatment system. No holding tanks or other storage of wastes will be located at the piers. The pump-out facility will serve not only the boat heads but also boat bilges in order to prevent contaminants, such as oil and boat fuel from entering the State waters involved. The piers will feature trash collection containers of appropriate number, size and location on the piers so as to provide convenient trash disposal for each boat slip. The piers will also feature plastic modular dock boxes to preclude boaters from randomly storing materials and equipment on the piers. No fish cleaning will be permitted on the piers at all, but rather must be accomplished on the uplands, with disposal of related wastes in the upland collection system. A "no wake" zone will be established in an area extending 500 feet north and 500 feet south of the marina. The "no wake" zone will be marked pursuant to requirements of the Florida Marine Patrol. The marked "no wake" zone should also extend waterward of the farthest waterward extent of the marina, as well as 500 feet north and south of it. Only private, recreational boats will be moored at the marina. All commercial boats will be prohibited. The marina will serve a Yacht Club to be developed by St. Joe in conjunction with the marina. Only members of the Yacht Club and their guests will be permitted to use the marina. This will assist with enforcement of the various conditions on marina operation and maintenance by the owners as to the boat-slip lessees and their guests. This and all other conditions should be enforced by mandatory restrictions in the boat-slip leases. Likewise, the applicant has agreed to permit no "liveaboard" boats at the marina in order to avoid the possibility of sewage or other contaminants entering the State waters from liveaboard boats. The upland facilities will include restrooms, and signs should be appropriately placed on the piers to advise boaters and boat owners and operators of the availability of restroom facilities. The marina will not feature fueling facilities; however, St. Joe will maintain pollution containment supplies and equipment at the marina sufficient to contain any potential fuel or other petroleum spills from catastrophic events, such as the rupture of a boat fuel tank. Expert witnesses for St. Joe established that a "management and operational plan" designed to enforce the provisions enumerated above will be enacted by the applicant. The management and operational plan includes three mechanisms of enforcement: Warning signs. Boat-slip lease agreements which must incorporate all restrictions found to be necessary herein. These will contain an enforcement provision providing for mandatory eviction from use and lease of the marina facilities for any breach of those conditions by lessees or their guests. Management personnel will be employed on the marina property to enforce all restrictions and conditions designed to insure environmentally-safe operation and maintenance of the marina, and such personnel should be employed during all operating hours of the marina, not just during daylight hours, as proposed by the applicant. Signs will be posted at conspicuous locations at the marina and at the upland facilities of the Yacht Club informing boaters of the marina rules and prohibitions. The signage will be visible to Yacht Club members and their guests using the marina, and members' guests will be required, upon mooring at the marina, to register and to review the rules and prohibitions. Boat-slip lease agreements at the marina will incorporate these marina rules and prohibitions. Under the lease agreements, a violation of the marina rules or prohibitions by a member or guest will be considered a breach of the lease and will result in revocation of the lease and removal of the member's boat from the marina. A dock master will be employed at the marina to supervise the operation and maintenance of the marina and will be assisted by dock hands and other personnel in order to see that the conditions and restrictions referenced herein are enforced. The applicant has proposed such personnel being employed during daylight hours. However, in order to insure that the standards for operation and maintenance of the marina and boats using it will be enforced so as to avoid water-quality violations and violations of the public interest parameters delineated below, the permit grant should be conditioned upon such personnel being employed during all operating hours of the marina, whether daylight hours or not. If this is accomplished, the enforcement mechanisms outlined in the management and operational plan will reasonably insure enforcement of the marina's rules, prohibitions and conditions on any grant of the permit and likewise reasonably insure that water-quality and public interest standards are not violated. Upland Facilities The upland and Yacht Club facilities to be developed in conjunction with the marina will be located on approximately seven acres adjacent to the marina site. The Yacht Club and related facilities will include a clubhouse, parking, and a storm water treatment system which will serve the upland facilities. St. Joe has obtained a conceptual permit for the management and storage of surface waters for the proposed upland improvements, including the Yacht Club. It will also seek a permit for the storm water treatment system, itself. St. Joe, through its consultants, has investigated and opined that the installation of the proposed upland facilities are feasible and can comply with applicable regulatory criteria and is pursuing the necessary permits and approvals from local governments and state agencies. It will insure that all such is accomplished prior to initiation of construction of the Yacht Club facilities. The precise configuration and design of all upland facilities will be dictated by applicable local ordinances and the requirements of State regulatory agencies. Marina Impacts The applicant/Respondent and the Petitioners are in essential agreement, through the testimony of their witnesses, regarding the general potential impacts which may be posed by marinas in a general sense, when located in proximity to environmentally-sensitive areas. Concerning anticipated impacts of this marina at the subject site, however, St. Joe presented the testimony of three expert witnesses, as well as a hydrographic study. It was thus established that violations of the pertinent water-quality statute and rules and the public interest standards contained in the statute referenced herein will not be violated. The Petitioners, although presenting both lay and expert testimony regarding the water quality and habitat type and quality in the general area of the site and the general impacts that can be caused by marinas in such areas, presented no expert testimony or studies regarding the anticipated impacts of this particular marina, as designed and configured by the applicant, on the subject site and aquatic habitat. Water Quality Considerations Marinas are potential sources of pollutants which may adversely impact water quality. Different sources at a marina may generate different pollutants; and in this case, testimony addressed these potential pollutant impacts. The totality of the expert testimony taken at hearing establishes that the marina will not likely cause a violation of applicable water-quality standards. One witness for the Petitioners, Bill Watkins, was accepted as an expert in water quality. In describing potential impacts of the marina, however, he only opined that there "could be some effect on water quality"; however, he did not specifically establish adverse effects on water quality which could be anticipated or reasonably expected regarding violations of applicable standards. Mr. Watkins acknowledged: "As to whether or not that degree of pollution, and that's what we're talking about, degree of impact, would be something that would be, have a significant degradation effect, I could not answer without further site specific studies." Mr. Watkins further described the type of site specific information which would be required for him to make a proper assessment of water-quality impacts, including hydrographics and the nature of the sediments existing at the site. Other witnesses for the Petitioners similarly declined to opine regarding violations of the water-quality standards because site specific information was not available to them. Dr. DeMort, for example, explicitly declined to offer an opinion regarding water-quality violations. The opinions and testimony of the expert witnesses on water quality presented on behalf of St. Joe, as well as by the Department, are accepted in establishing that no water-quality violations by the construction and operation of the marina are anticipated. The reasonable assurance that water-quality violations will not occur through the construction and operation of the marina is illustrated by the unrefuted evidence concerning the hydrographics by which the site is characterized. A knowledge of site hydrographics is necessary to accurately determine potential water-quality impacts. A hydrographic study was prepared by St. Joe through the auspices of its consultant, Olsen Associates Incorporated. The experts who prepared that study testified on behalf of St. Joe at hearing, and a Department witness who reviewed the study testified by deposition. None of the Petitioners' expert witnesses addressed the subject of site hydrographics other than to note that they were an important consideration. Mr. Buckingham was accepted as an expert witness in the area of marine engineering with emphasis on hydrographics. He testified regarding the hydrographic study prepared and submitted by St. Joe. The study involved the collection of data at the site, including the gauging of water surface elevations over a two-day period in December of 1988; the comparison of those elevations to predicted elevations based upon historical data; a measurement of current velocities at the site; a dye study to assess the flow regime at the site; and the gathering of depth soundings and sediment samples to confirm the bathymetry and nature of bottom sediments at the site. The hydrographic study also involved the analysis of the data collected at the site. Hydrographics at the site are composed of two components, the transport of a pollutant by advective currents and the dispersion or diffusion of a pollutant within the water column. The physical transport by advective currents dominates the hydrographic circumstance prevailing at the marina site. A pollutant introduced at the site is more likely to be physically transported away from the site, in addition to being merely dispersed through the water column at the site. This is because of the relatively high current velocities prevailing. Both the transport and dispersion components were analyzed in the study to determine the time and distance necessary to reduce an initial concentration of a hypothetical pollutant to 10% of its initial concentration. A pollutant introduced at the site would be reduced to 10% of its initial concentration in less than seven minutes and within 400 feet of the site on the ebb tide and within 300 feet of the site on the flood tide. Moreover, the "plume" of this hypothetical pollutant would occur in a longshore direction parallel to the shore, as opposed to a direction toward the shore and would be of comparatively narrow width (approximately 30 feet). The hydrographics of this site are such that a complete water exchange will occur in 20 to 30 minutes at any point during the tidal cycle. The evidence thus demonstrated that the site is extremely well flushed by tidal currents. In his deposition, Ken Echternacht, of the Department, testified that data in the hydrographic study was realistic in his experience and that he had no questions or concerns regarding the data and methodology used to confirm that data. In addition to Mr. Buckingham's testimony and the study, itself, the testimony of Dr. Echternacht established that flushing is of no concern and is thoroughly adequate at the site. Dr. Echternacht is the Department's hydrographic engineer, whose function is to review all dredge and fill permit applications which may have impacts upon the hydraulics of surface water systems. He has reviewed approximately 1,500 dredge and fill permit applications. His testimony and that of Mr. Buckingham is accepted, as is that of other Department expert witnesses in establishing the excellent flushing characteristics of the site and that the construction and operation of the marina will not adversely affect the present hydrographic situation at the site, as that relates to establishing that no water quality violations will occur. All marinas are potential sources of pollutants. The first to be addressed involves the installation of the pilings themselves during the construction of the marina. This is a potential source of turbidity. Turbidity involves the suspension of bottom sediments and substrate material in the water column, which can pose, among other problems, the retardation of light penetration through the water column which can have an adverse impact on photosynthesis in marine grass beds. In extreme cases, it can cause the destruction of grass beds through killing of the grass by lack of adequate light penetration, as well as the smothering effect of sediments being deposited upon grasses. The method to be used by St. Joe in installing the pilings will be by "jetting" them into the bottom of the river initially and then driving the pilings into the river bottom to the required depth to support the piers. Witnesses for St. Joe and the Department established that this method will constitute an adequate safeguard to be employed during construction to minimize any turbidity. Any temporary or local turbidity caused by the installation of the pilings will be transitory and will pose no significant water-quality violation; however, turbidity curtains will, be employed, if necessary, by the applicant to control any such turbidity during construction. Another potential source of turbidity at a marina involves the dredging, washing or disturbance of the river bottom caused by boat propellers or boat keels. The evidence demonstrated that the risk of such "prop dredging" or wash at this marina will be negligible due to the design features and conditions at the site, including the channels and channel markers, and particularly by the depth of waters prevailing at the site. The marina basin and boat slips are located in water of sufficient depth to prevent prop dredging or wash. The =average depth of the entrance channels is between 10 and 12 feet. Maneuvering within the marina basin will occur in depths of 10 feet or greater. Although the most landward boat slips are located in depths of approximately eight feet, the average depth within most slips is approximately 10 to 12 feet. These depths are based upon the bathymetric survey of the site and confirmed by random soundings performed during the course of the hydrographic study in evidence. Further, these depths are "mean low water" depths. Mean low water reflects the "lowest expected level" within a 29-day tidal epic. The "mean lower low" level is the lowest expected level over the course of a year. That level prevailing at the site, according to the study, is 0.1 feet lower than mean low water. The maximum draught of boats expected to be moored at the marina is 4.5 feet. Thus, the depths in the marina will allow ample clearance between propellers and keels and the river bottom. The required clearance between boat bottoms and propellers and the river bottom can further be assured by proper placement of boats in the boat slips in the leasing process and in the assignment of boat slips to casual, temporary users of the marina. In other words, the larger boats will be assigned to the deeper, more waterward slips. Other measures include warning signs, which should be placed along the six-foot depth contour, along the landward edge of the entrance channels and beyond the waterward extent of the grass beds. This will insure that boaters do not stray into shallow-water, aquatic habitat areas. A second factor in determining the potential for prop dredging at the marina is the nature of the sediments themselves. Four witnesses, including those testifying for the Department and for the Petitioners, established that the sediments at the site are primarily sand-based, with minimal organic silt content. The sandy nature of the sediments minimizes the potential for turbidity caused by prop dredging or prop washing (hydraulic currents created by propeller operation) because sand, by its density, mass and weight, tends to settle out to the bottom much quicker if it is suspended in the water column. Even if prop dredging did occur at the marina, generating turbidity, the high flushing characteristic of the site would quickly transport and disperse any such turbidity and render it undetectable and likely prevent its deposition on the grass beds. A potential source of pollutants at a marina is boat fuel. Expert witnesses for the Department and the applicant established that the design and operational features of the marina, primarily the absence of any fueling facilities, will minimize or eliminate the potential for pollutants generated by fueling operations. Another potential source of pollutants at a marina is waste from boat heads and bilges generated by flushing boat heads or pumping out of bilges with bilge pumps. Expert witnesses for St. Joe, as well as the Department, established that the design and operational features with which this marina will be characterized will minimize or eliminate the potential for such pollutants to be generated because liveaboard boats will be prohibited, and the pumping out of heads and bilges will also be prohibited because of the conditions agreed to by the applicant for a grant of this permit. Another potential source of pollutants at a marina is the use of anti-fouling paint used on the bottoms of boats and the periodic scraping and repainting of boats. Expert witnesses for the Department and the applicant established that the operational features and design of this marina will minimize the potential for pollutants from this source because boat painting, sanding, and scraping and other operations attendant to boat painting will be absolutely prohibited at the marina. Finally, another potential source of pollutants would be trash and garbage materials. The potential for pollution from this source will be minimized by the use of trash containers and dock boxes located at frequent intervals around the piers and boat slips, as well as the instructional signs to be placed on the piers and slips by the applicant and the publication of marina rules in order to inform boat operators and guests of the necessity to dispose of trash in the proper containers. It has thus been established that the design and operational characteristics of the marina and conditions to be imposed thereon will minimize or eliminate the potential for pollutants to be generated and placed in the surface waters at the site. The marina will not occasion violations of applicable water-quality standards. Any pollutants which might be deposited in the surface waters at the site will be quickly transported and dispersed so as to be undetectable at the marina or in the vicinity of the marina because of the critical role played by the hydrographics prevailing at the site. Public Interest Impacts Much of the testimony at hearing regarding impacts upon the various public interest standards, including wildlife and habitats, focused upon the grass beds, and the benthic communities prevailing in deeper water at the site, as well as the fact that the site is used by manatees. Dr. Quinton White was accepted as an expert in biology and biological impacts of marina construction and operation. He testified on behalf of the applicant. His testimony and that of other expert witnesses offered by St. Joe and the Department established that there would be no adverse impact on benthic communities and organisms, including manatees, caused by the construction and operation of the marina. The Petitioners called expert witnesses on the issue of impacts on wildlife. Mike Allen, a Florida Game and Fresh Water Fish Commission staff member, testified that he was not really qualified as an expert in fisheries or benthic communities but, rather, in terms of terrestrial species which are not involved in this proceeding. Lawson Snyder, another Florida Game and Fresh Water Fish Commission staff member, was accepted as an expert in fisheries biology on behalf of Petitioner but testified that the marina's impacts upon fish and wildlife would not be detectable. Jim Valade, a Florida Department of Natural Resources staff member, was also accepted as an expert in marine biology, including fish and manatees, but testified that the permit applicant has taken steps to protect manatees in virtually all aspects and that his department's concerns regarding the safety of manatees have been adequately addressed by the design and proposed operation of the marina. Bill Watkins, a St. Johns River Water Management District staff member, was accepted as an expert in biology, but testified that the design of the marina provides the grass beds "a fair degree of protection" and declined to opine that the marina would have any adverse impacts upon wildlife or fish. Finally, Dr. Carol DeMort, in her deposition, specifically declined to render any opinion regarding adverse impacts upon wildlife or fish. Thus, the evidence adduced by the Petitioners at hearing did not rebut the evidence introduced by the applicant that the marina will have no detectable impacts upon wildlife or habitats involved in the vicinity of the site St. Joe introduced evidence concerning impacts from shading upon grass beds by the marina structures themselves and from turbidity "washed" onto, the grass beds by motorized boats maneuvering in the marina basin. Expert testimony was adduced that established that shading caused by the widest pier, that is, the main pier with a width of 12 feet, would have no adverse impact on the grass beds due to shading. That testimony was unrebutted and is accepted. Two expert witnesses for St. Joe, a marine engineer and a biologist, as well as a Department witness, established that, even assuming that turbidity was generated by propeller action in the marina basin, the turbidity resulting from prop wash would not be transported 275 feet from the marina basin offshore to the :grass beds at the inshore area. They attributed those opinions to the nature of the sediments involved which are not readily suspended, the flushing at the site, the distance between the basin and the grass beds, and the typical extent of prop wash from boats expected to be used at the marina. The Petitioners presented two witnesses, who testified regarding the impacts of prop wash. Mr. Allen, an expert in upland terrestrial species, testified regarding the potential for deposition of sediments on grass beds but also acknowledged that the hydrographics at the site, the distance between the marina basin and the grass beds and other protective measures would minimize this potential. One lay witness for the Petitioners testified to the effect that if a "handful" of boat owners in the marina violated the "no wake" restrictions and accelerated their boats in violation of those restrictions, they would cause turbidity to be placed upon the grass beds. His testimony was contradicted, however, by a marine engineer, who testified that prop wash is a function of many parameters (e.g., the RPM of the engine, the horsepower of the engine, the draught of the boat, and configuration of the propellers, etc.). He established that it would not be reasonable to expect prop wash extending twice the length of a boat. Regarding impacts upon benthic communities at the site, the applicant introduced expert testimony which established that the benthic communities in that vicinity of the marina, including the grass beds, fin fish, shellfish, and other organisms, will not be adversely impacted by the construction and operation of the marina in light of the safeguards which would be imposed upon the permit, as delineated herein. This is primarily due to the absence of significant concentrations of pollutants to be expected and the hydrographics prevailing at the site as that relates to the unlikelihood of boat grounding, prop dredging, and prop wash suspending pollutants and turbidity and depositing them on benthic community habitat areas. Only one of Petitioners' witnesses, Dr. DeMort, testified in her deposition concerning potential impacts upon benthic communities. Dr. DeMort made it clear, however, that she had conducted no investigations and studies necessary to enable her to render an expert opinion on the impacts upon the benthic communities prevailing at the site which might be caused by the marina's construction and operation. Her testimony in this regard only related to marina installation and operation in general and was not related to the specific design characteristics and proposed operational parameters of the subject marina. Manatees are an endangered species. There is much concern about their welfare with regard to the proposed project because all parties acknowledge that the site and the shoreward grass bed areas, particularly, are frequented by manatees, particularly for summer foraging. Manatees tend to forage in shallow waters and associated grass beds. Boats pose definite hazards to manatees and cause significant manatee deaths each year due to impact from boats, as much as 15% to 30% of the known population. In response to this hazard, the U.S. Marine Mammal Commission has recommended that grass beds be protected and that establishment of protective or "no wake" zones in manatee foraging areas be accomplished. In light of such restrictions voluntarily agreed to by St. Joe and its expert testimony in this regard and in light of the manatee education and awareness measures proposed by the applicant, it has been demonstrated that the marina will not have any negative impact on the manatee population in the area. The Petitioners' only expert witness concerning manatees, Jim Valade, indeed, opined that the marina had taken steps to protect manatees "in virtually all aspects". In this connection, the design features in the management and operational plan discussed herein and proposed by the applicant embodies measures to address potential impacts upon manatees which frequent the marina site. These include manatee awareness signs to be posted at the marina; and an additional specific condition has been agreed upon by the Department and the applicant which specifies the size, lettering and other details of the warning signs, and the location of them within the marina, all of which will be included in a plan to be submitted to, reviewed, and approved by the Florida Department of Natural Resources. Additionally, a permanent educational display will be located at the Yacht Club informing boaters who frequent the facility of the presence of manatees in the area and the need to minimize the impact of boats upon manatees. During construction, if a manatee is sited within 100 yards of the marina site, construction activities will cease and not resume until manatees have left the area. A handbook will be prepared concerning manatees and the effect on them of boat operation, which will be distributed to employees of the facility and to Yacht Club members and guests. This requirement and the review of it by Yacht Club members and guests will be an integral requirement in the terms of the slip leases. Additionally, no docking facilities, pilings or cleats will be located along the portions of the piers not containing boat slips in order to discourage boaters from attempting to moor at those locations, which will reduce the number of boats frequenting the marina, as that relates to manatee safety. This portion of the St. Johns River functions as a highly productive juvenile fish nursery and sports fishing area. Therefore, an examination of the marina's potential impacts upon marine productivity, fishing and recreation in the area is an important consideration in this proceeding. The discussion of this potential impact involves the same issues discussed in connection with impacts upon water quality and wildlife habitat; namely, the generation of pollutants and the impacts upon the grass beds and benthic communities directly by boat operation itself. Unrefuted testimony adduced by the applicant and the Department has established that impacts upon the fish population and upon marine productivity, fishing and recreational values will not be adverse. No deliterious effect is likely to be occasioned the fisheries and fish habitat and the habitat of other aquatic organisms in terms of juveniles or adults or to the sport fishing values of the area in which the marina will be located. Indeed, the marina structures and the shade and concealment offered by moored boats will provide additional habitat for juvenile fish, as well as provide an additional source of food because of the "fouling communities" of life forms which will be expected to grow on the pilings. These will serve as food for juvenile fish and some species of adult fish which, in turn, will enhance the food supply of predatory fish operating at an upper level in the food web. The boats and structures themselves also will operate as a source of protection for certain fish populations from predators. The Petitioners produced a fisheries biologist as an expert witness, who testified in this regard; but he acknowledged that he did not know whether noticeable impacts on conservation of fish, marine productivity and recreational values will be caused by the installation and operation of the marina. He testified in a general sense that he feared some negative impacts might result but did not feel that any such impacts would be detectable based upon testimony he heard and deferred to, including testimony that the littoral zone would not be impacted by the marina to any significant degree. He ultimately opined that the marina would likely have little impact on sports fishing. The other witness produced by the Petitioners concerning impacts upon fishing and recreational values was unable to render any expert opinion, by her own admission, because she had conducted no studies or otherwise been provided information regarding the design and proposed operation of the marina. Consequently, the testimony adduced by the applicant as to these parameters is accepted; and it has been established that the marina will not adversely impact fisheries, fish conservation, aquatic habitat, sport fishing, recreational values and marine productivity in the area involved at the project site. Regarding potential impacts upon the public health, safety and welfare and property of others, the applicant and the Department adduced expert testimony that no adverse impact regarding these interests will occur. The testimony of Petitioners' experts similarly establishes that the marina would not pose safety hazards or would otherwise give rise to any noticeable impacts upon the public health, safety, welfare and property of others. Regarding potential impacts upon navigation or the flow of water, St. Joe and the Department introduced expert testimony to establish that the marina would not adversely impact navigation or the flow of water, and it is so found. The Petitioners' introduced no evidence regarding this subject. Regarding potential impacts upon significant historical and archaeological resources, the applicant and the Department introduced evidence that no adverse impact as regards these resource parameters will occur. Although one of the Petitioners, in her testimony, speculated that the marina could "detract" from the William Bartram scenic highway, she was unable to specify how the marina would impact the highway or to what extent the highway was a significant, historical or archaeological resource. It is found that no such adverse impact on the William Bartram scenic highway will occur. Cumulative Impact Regarding cumulative impacts, the applicant and the Department introduced evidence that the marina would not give rise to impacts which, cumulative with the impacts of other marina facilities, would be significant. The evidence establishes that there are six marinas within four miles of this marina site; two upriver, and four downriver. Due to the hydrographic circumstances in the area and the distance of the other marinas from this site, it has been demonstrated that the addition of this marina to the area will not result in any adverse cumulative impacts. Mr. Mike Allen, the expert in upland terrestrial species (not involved in this proceeding), referenced in his testimony the cumulative impacts he feared on sports and commercial fishing. Mr. Allen made it clear, however, that his reference was not to cumulative impacts caused by the marina and existing marinas but, rather, to impacts which could be brought about by many such future facilities located in this particular area. The evidence does not reflect, however, that any other marinas are conceptually contemplated or are the subject of other permit applications for this area for the future. It is thus found that no significant adverse cumulative impacts will be occasioned by the installation and operation of the subject facility.
Recommendation Having considered the foregoing Findings of Fact, Conclusions of Law, the evidence of record, the candor and demeanor of the witnesses, and the pleadings and arguments of the parties, it is therefore, RECOMMENDED that the application of St. Joe Paper Company for the dredge and fill permit at issue be granted, provided that the terms and conditions enumerated in the Department's Intent to Issue, in evidence as St. Joe Exhibit 9, and accepted by the applicant, as well as those conditions found in this Recommended Order to be necessary and supported by the evidence, are incorporated in the permit as mandatory conditions. DONE AND ENTERED this 26 day of October, 1990, in Tallahassee, Leon County, Florida. P. MICHAEL RUFF Hearing Officer Division of Administrative Hearings The DeSoto Building 1230 Apalachee Parkway Tallahassee, FL 32399-1550 (904) 488-9675 Filed with the Clerk of the Division of Administrative Hearings this 29 day of October, 1990. APPENDIX TO RECOMMENDED ORDER IN CASE NO. 89-5053 Applicant's/Respondent's Proposed Findings of Fact 1-53. Accepted, but are subordinate to the Hearing Officer's Findings of Fact on the same subject matter, particularly in those several instances where conditions on the grant of the permit have been recommended to be modified somewhat by the Hearing Officer in light of the totality of the preponderant evidence presented. Rejected, as unnecessary. Accepted. Respondent DER's Proposed Findings of Fact The Department submitted no proposed findings of fact but, rather, adopted those submitted by the applicant/Respondent. Petitioners' Proposed Findings of Fact Petitioners, Hoffert, presented no proposed findings of fact but, rather, a letter in the nature of final argument which has been referenced and discussed in the above Preliminary Statement to this Recommended Order. Petitioners, Cornwell, submitted a post-hearing pleading; but it contained no specific, separately-stated proposed findings of fact, which can be separated from their mere recitation and discussion of testimony in evidence and arguments such that coherent, specific rulings could be made. Petitioners, Cornwell's post-hearing pleading did not conform to the instructions given to them by the Hearing Officer at the conclusion of the hearing concerning the appropriate manner for submission of proposed findings of fact, and they were submitted late. They have been considered in the rendition of this Recommended Order, however, in spite of the fact that they were filed in a tardy fashion. COPIES FURNISHED: Dale H. Twachtmann, Secretary Department of Environmental Regulation Twin Towers Office Building 2600 Blair Stone Road Tallahassee, FL 32399-2400 Daniel H. Thompson, Esq. General Counsel Department of Environmental Regulation Twin Towers Office Building 2600 Blair Stone Road Tallahassee, FL 32399-2400 T. R. Hainline, Jr., Esq. ROGERS, TOWERS, ET AL. 1300 Gulf Life Drive Jacksonville, FL 32207 William H. Congdon, Esq. and Joanne Barone, Esq. Department of Environmental Regulation Twin Towers Office Building Room 654 2600 Blair Stone Road Tallahassee, FL 32399-2400 Barbara Davis Winn 3448 State Road 13 Jacksonville, FL 32259 Mary and Irv Cornwell 2652 State Road 13 Switzerland, FL 32259
