The Issue The issue is whether the Department of Environmental Regulation (DER) should modify permit number 599070329, issued to the City of Boca Raton (City), to allow construction of an approved beach restoration project to commence on May 1, 1988, rather than on June 1, 1988.
Findings Of Fact On November 21, 1986, DER issued number 500970329 to the City for a beach restoration project. Issuance of the permit followed resolution of a dispute between DER and the City of Boca Raton which was the subject of an earlier proceeding before this hearing officer. See, City of Boca Raton, et al., v. Florida Department of Environmental Regulation, et al., DOAH Case number 86-0991 (Final Order of Dismissal rendered November 21, 1986). Although the City maintained in this case that the Coral Reef Society and Sierra Club, who are petitioners here, were intervenors in that prior proceeding through an umbrella organization, Save and Protect our Aquatic Resources and Environment (SPARE), no evidence was adduced supporting that contention. In the 1986 proceeding SPARE alleged that it was "a coalition of various environmental and commercial groups with a common interest in the protection of Florida's unique and fragile aquatic resources" (Amended Petition for Leave to Intervene in Case 86-0991, filed September 2, 1986). The groups which made up the coalition were not identified in that prior proceeding or in this one. SPARE filed a voluntary dismissal in the prior proceeding after learning that DER had decided to support issuance of a permit to the City of Boca Raton. After further administrative proceedings at the federal level, the U.S. Army Corps of Engineers issued a permit to the City of Boca Raton for the beach restoration project on or about January 28, 1988. The project, as currently permitted, involves the placement of approximately 980,000 cubic yards of sand, dredged from offshore, onto 1.45 miles of the City of Boca Raton's beachfront. The project will be constructed within and adjacent to two city Spanish River Park and Red Reef Park, and the waters of the Atlantic Ocean. The mean grain size of the dredged sand to be added to the beach is .32 millimeters. The dredged material is 99.6 percent sand and .4 percent silt or clay. The sand to be pumped onto the beach has characteristics almost identical to the current beach sand. As part of the approval process, the City of Boca Raton received a variance from turbidity standards otherwise applicable to Florida Class 3 waters. Turbidity is, to some extent, an unavoidable by-product of beach renourishment dredging. DER approved a mixing zone of 10,000 feet by 1,000 feet in which state water quality standards for turbidity could be violated during the construction period. The City of Boca Raton has also constructed artificial reefs comprised of natural limestone boulders and a protective groin approximately one-half mile south of the project area. Specific Condition Number Three (3) of the DER permit restricts project construction to the months of June, July, and August. In a letter dated February 12, 1988, the United States Fish & Wildlife Service (the Service) requested that the City of Boca Raton seek a modification of its DER permit to allow construction of the project to begin on May 1, 1988. The Service maintained the modification was important to avoid conflict with the peak nesting season of sea turtles, which are protected species. The Service did not make its request to the City to advance the project start date until February 12, 1988, because the Service was under the impression that the City had already requested permission from DER to commence construction sooner. In May of 1987, the City of Boca Raton had requested that the three month construction restriction of Specific Condition Number Three be deleted completely from the permit. When this request was made, the City of Boca Raton had hoped to begin construction of the project in the fall of 1987, and avoid construction during the sea turtle nesting season. DER's hydrographic engineer, Dr. Kenneth Echternacht, opposed this initial request to delete the construction limitation period. Due to delays in the federal permitting process and other logistical problems, the City of Boca Raton withdrew this earlier modification request. In order to meet the concerns of the Service, the City of Boca Raton applied by letter to DER dated February 22, 1988 for the suggested permit modification. Upon review of additional climatological and wave height data and littoral drift calculations from Dr. Robert Dean of the Costal and Oceanographic Engineering Department of the University of Florida College of Engineering, Dr. Echternacht supported a permit modification which would allow the construction period to begin in March, 1988. DER indicated its intention to grant the modification on March 10, 1988, acknowledging the concern of the Service and finding "the proposed modification is not expected to result in any adverse environmental impact or water quality degradation. " American Littoral Society, South Florida Chapter, and the Sierra Club, Florida Chapter, jointly, and the Coral Reef Society, independently, filed virtually identical petitions on March 22, 1988, objecting to DER's proposed approval of the modification request, and each requested a formal administrative proceeding. Those petitions not only questioned the permit modification, but also sought to reopen the issue whether the beach restoration project should be undertaken at all. During a telephone conference hearing on the City of Boca Raton's motion to strike portions of the petitions, held on April 8, 1988, the issue in this proceeding was narrowed to whether DER's proposed approval of the modification, expanding the construction "window" by one month, was proper. The time for objecting to the entire project has passed and the permit modification proceeding cannot be used to reopen the issue whether the beach renourishment now permitted for June, July, and August may go forward. The purpose of the restriction of construction to June, July, and August in Specific Condition Number Three of the permit was to confine construction to the months of minimum wave height. In southeast Florida, the summer months are climatologically the months of minimum average wave height. The amount of sand transported by the coastal littoral system, and consequently, the amount of optical turbidity due to suspension of particulate matter in the water column such as fine sand, is a function of wave height and longshore currents. The lesser the wave height and calmer the sea, the less sand is resuspended and the lower are the turbidity levels. During the months of June, July, and August, the waves propagate from the southeast and the corresponding longshore littoral direction is predominantly to the north. The remainder of the year, the littoral drift is primarily to the south. DER determined that project construction during the period of predominantly northerly littoral transport would better protect Red Reef Rock, a large rock outcropping located to the south of the project area. The Red Reef Rock area supports rich and diverse fish resources as fish are attracted to the rock for feeding and take advantage of the relief the rock outcroppings provide. The City of Boca Raton agreed to construct a groin composed of limestone boulders in order to afford additional protection to Red Reef Rock against the drift of sand to the south. The City is also limited by Specific Condition Number Ten of the permit, which remains in effect, and restricts disposal of material in the southernmost .15 mile portion of the beach to times when the prevailing longshore current is from south to north. Nonetheless, construction during May increases the possibility that some material suspended in the water column as the result of the renourishment will be transported over the Red Reef Rock area. Although project construction during the months of June, July, and August presents the optimum conditions from a water quality perspective, construction during that period conflicts with the height of the sea turtle nesting season. The City of Boca Raton has been monitoring sea turtle nesting activity on the Boca Raton public beaches from Spanish River Boulevard to Palmetto Park Road, a distance of 2.6 miles which encompasses the project area, for the past 11 years. Three species of sea turtles, logger head, green and leatherback turtles have been known to nest on the beaches of Boca Raton within and adjacent to the project area. All three species are protected under state and federal law. Loggerhead sea turtles, by far the most numerous nesters on Boca Raton's beaches, are classified as a threatened species by the U.S. Department of Commerce. Green sea turtles and leatherback sea turtles are classified as endangered species. Compared to the number of nests historically established by loggerhead turtles, green sea turtles are infrequent nesters on Boca Raton's beaches. Leatherback turtles are very rare nesters in this area. Southeast Florida is not a significant nesting habitat for leatherbacks. During the eleven-year monitoring period an average of only 2.4 leatherback sea turtles nested on the beach each year, the largest number nesting in a single year was 7; an average of 8 to 9 green sea turtle nests have been recorded annually in this area. By way of comparison, during the same period an average of 333 loggerhead sea turtle nested in this area. Sea turtle nesting in Boca Raton has historically occurred from April through September. The earliest nest of the year recorded by the City of Boca Raton occurred on April 2, 1987, and was a leatherback. The latest nest of the year occurred on September 13, 1983, and was a loggerhead. Leatherbacks nest early, and green turtles are late to nest. Loggerhead nests commonly begin in May, with the peak nesting period occurring in late June and early July. In light of the facts set out above concerning the likely timing of sea turtle nesting, which also being cognizant of DER's water quality concerns, the Service requested the City of Boca Raton to seek a modification of its DER permit to allow construction to begin on May 1, 1988. This would enable the City of Boca Raton to avoid construction during the peak of the sea turtle nesting season in late June, July, and August. The construction should take about 30 days. In addition to the permit modification request, the Service has recommended several other "reasonable and prudent measures" to avoid possible adverse effects to sea turtle nesting activity during the renourishment of the beach. These include a) tilling the beach to soften the new sand if it becomes compacted over a certain degree, b) relocation of nests is undertaken only by trained persons, c) lighting on the dredge is minimized to reduce any confusion it could cause to turtles attempting to locate the beach for nesting, and d) the addition of dune plants to the project area. The City of Boca Raton has agreed to implement these measures. The Boca Raton beach restoration project will enhance sea turtle nesting activity in the future. Currently, the beach in the project area is critically eroded, posing an immediate threat to successful sea turtle nesting. Nests are at risk of being inundated by sea water or washed away if not found and relocated by City of Boca Raton staff. The project will provide a long-term benefit to sea turtles by providing a wider dry beach area for safer nesting and better nest site selection. The City proved that wave heights, littoral drift, and other climatological conditions in southeast Florida do not vary dramatically, on the average, between the months of May and June. May is a transitional month, and there is net littoral movement south due to cold fronts and northeast winds in the area, along with swells caused by storms out in the Atlantic Ocean. While there is a potential for isolated events in May which could have an adverse impact on Red Reef Rock by causing a shift of newly dredged material south over the reef, the evidence presented by petitioners did not persuade the hearing officer that the risk of such events was unacceptably large when balanced against the value of advancing the construction into May to minimize conflict with the peak nesting season of loggerhead sea turtles. The petitioners' evidence did not quantify the likelihood of storm-related events with enough energy to adversely affect the Red Reef Rock area. The hearing officer is, therefore, more persuaded by Dr. Echternacht's testimony that long-term (i.e., average) data is more useful when assessing safety margins, and the available data gives reasonable assurance that renourishment may take place in May. Consequently, construction commencing during the month of May would not present any adverse water quality or marine resource effects. Petitioners have not persuaded the hearing officer that the subject permit modification would adversely affect water quality to such an extent as to be contrary to the public interest. The City has obtained a permit for a mixing zone which will accommodate all the turbidity which is likely to be caused by the beach renourishment. There is insufficient evidence that climatological event in May are likely to cause the turbidity to extend beyond the approved mixing zone.
Recommendation It is recommended that the Department of Environmental Regulation enter a final order granting the permit modification. DONE AND ENTERED in Tallahassee, Leon County, Florida, this 3rd day of May, 1988. WILLIAM R. DORSEY, JR. 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 3rd day of May, 1988. APPENDIX TO RECOMMENDED ORDER, CASE NO. 88-1590 The following are my rulings on the proposed findings of fact submitted by the petitioners pursuant to Section 120.59(2), Florida Statutes, (1985). Rulings on Petitioners' Proposed Findings of Fact Covered in finding of fact 2. Covered in finding of fact 5. 3-4. Covered in finding of fact 6. 5. Covered in finding of fact 7. 6-7. Covered in finding of fact 8. Rejected because while wave heights are higher in May, there is insufficient evidence that higher wave height would cause turbidity in violation of the mixing zone which has been permitted. Covered in finding of fact 8. 10-11. Rejected as unnecessary. 12-15. Covered in finding of fact 8. 16. To the extent appropriate, covered in finding of fact 9. 17-20. Covered in finding of fact 9. 21-22. Covered in finding of fact 10. 23-24. Rejected because the Hearing Officer accepts the testimony of Mr. Possardt that southeast Florida is not a significant nesting habitat for leatherbacks, and therefore rejects the argument that leatherbacks are entitled to greatest protection. The Boca Raton Beach is a significant habitat for loggerhead turtles, and it is more appropriate to assess the impact of the project based on the predominate species of turtles nesting on the beach, rather than the impact of the project on a species which only rarely nest on this beach and has predominate nesting areas elsewhere. Rulings on Respondent DER's Proposed Findings of Fact Covered in finding of fact 2 and 4. Covered in finding of fact 3. Rejected because the evidence adduced at the hearing did not support findings concerning three systems of hard bottom and rock outcroppings. 4-6. Covered in finding of fact 8. Covered in finding of fact 8 and 13. Covered in finding of fact 14. Rejected as cumulative. Rejected for lack of evidence. Covered in finding of fact 13 and 14. Covered in finding of fact 10-12 Covered in finding of fact 10-12. 14-20. Rejected as unnecessary because the only evidence submitted pertain to potential violations of water quality standards or adverse affect on habitat of endangered species. Rulings of Respondent Boca Raton's Findings of Fact 1. Covered in finding of fact 1. 2. Covered in finding of fact 2. 3. Covered in finding of fact 5 and 6. 4. Covered in finding of fact 7. 5. Covered in finding of fact 8. 6. Covered in finding of fact 9. 7. Covered in finding of fact 10. 8. Covered in finding of fact 11 and 12. 9. Covered in finding of fact 8. Covered in finding of fact 13. Rejected as argument. COPIES FURNISHED: Alexander Stone Judy Schrafft, President South Florida Director Coral Reef Society American Littoral Society 357 North Lake Way 75 Virginia Beach Drive Palm Beach, Florida 33480 Key Biscayne, Florida 33149 Alfred Malefatto, Esquire Karen Brodeen, Esquire David C. Ashburn, Esquire Department of Environmental Post Office Box 24615 Regulation West Palm Beach, Florida 33416 Twin Towers Office Building 2600 Blair Stone Road Alan J. Kan, Esquire Tallahassee, Florida 32399-2400 Penthouse Suite 11088 Biscayne Boulevard Jonathan Shepard, Esquire Miami, Florida 33181 5355 Town Center Road Suite 801 Dale Twachtmann, Secretary Boca Raton, Florida 33486 Department of Environmental Regulation Daniel H. Thompson, Esquire 2600 Blair Stone Road General Counsel Tallahassee, Florida 32399-2400 Department of Environmental Regulation 2600 Blair Stone Road Tallahassee, Florida 32399-2400
Findings Of Fact Harbor Course South is a one hundred and seventy two lot real estate development which is a portion of the Ocean Reef Club located at the extreme northern end of Key Largo, Monroe County, Florida. The Harbor Course South property was acquired in approximately 1964 along with over 1200 acres of adjoining property for approximately 1.5 million dollars. Driscoll Properties, Inc. ("Driscoll"), a Florida Corporation, is the developer of Harbor Course South. Driscoll Foundation, Inc., (the "Foundation") is a non-profit Florida corporation which owns a portion of the Harbor Course South property. (Driscoll and the Foundation are collectively referred to as the "Intervenors" or the "Permittees.") The Ocean Reef Club is a one thousand two hundred unit development encompassing approximately eight hundred acres including at least two eighteen hole golf courses, a marina and an air strip. Nine holes of golf are located in Harbor Course South. These nine holes were leased to the Ocean Reef Club in 1974-1975 pursuant to an agreement providing for creation of golf course lots and lake-front lots in Harbor Course South. The nine holes of the golf course located in Harbor Course South were in place by at least 1978 and have been in use since that time. In order to install those nine holes, some roads were cut through the property and the lakes were dredged. Thirty-eight of the one hundred and seventy-two lots in Harbor Course South were originally platted in 1978 or 1979. These thirty eight lots are referred to as Section 1 of Harbor Course South. All of lots in Section 1 have been sold to individual purchasers for an average price of $34,210.00 per lot. The thirty-eight lots in Section 1 were all sold prior to 1988. In approximately 1979, some roads were cleared and paved on the Harbor Course South property in order to provide access to the thirty-eight originally platted lots in Section 1. A number of the lots in Section 1 have been permitted for construction by Monroe County and houses have been constructed on several of them. No individual lot owner in Section 1 has been denied a permit for clearing at least some of his land for a homesite. Both the United States Fish and Wildlife Services ("U.S.F.W.S.") and the Florida Game and Fresh Water Fish Commission (the "Commission") have determined that the clearing and/or development of the lots in Section 1 will not require permits for the taking of endangered or threatened species or their nests. In 1985, the Intervenors, in conjunction with the Ocean Reef Club, sought a determination as to the extent of their vested development rights with respect to the Harbor Course South property by initiating a vested rights hearing before Monroe County. These proceedings were initiated under Chapters 380 and 120, Florida Statutes and resulted in a Joint Stipulation on February 23, 1988 recognizing that the Intervenors have vested rights to develop the Harbor Course South plats. (The Joint Stipulation is referred to as the "Vested Rights Determination.") The Vested Rights Determination recognized that the Intervenors and the Ocean Reef Club had incurred obligations and expenditures based upon the approval of the master plan for development of Ocean Reef in 1977 in accordance with the then-existing regulations of Monroe County. The expenses and improvements upon the property included the construction of roadways, water main extensions, medical facilities, and golf courses. As a result of these expenditures, the Vested Rights Determination established that the Intervenors were authorized to continue development under the master development plan for the Ocean Reef Club, notwithstanding the enactment of a comprehensive land use plan and development regulations by Monroe County on September 15, 1986. No appeal of the Vested Rights Determination was filed by the Florida Department of Community Affairs or any other party. The remaining one hundred thirty-four lots in Harbor Course South were subdivided into three plats in 1986. These plats have been designated Ocean Reef Plat Numbers 17, 18 and 19 (also referred to as Sections 2, 3 and 4 respectively of Harbor Course South.) The Intervenors were not required to obtain a permit from the U.S.F.W.S. or the Commission prior to subdividing and/or selling lots of the Harbor Course South property. Most of the infrastructure for development of Plats 17, 18 and 19 is in place. Paved roads were completed in 1987-1988. The electrical lines and sewer lines are in place and operational in all three plats. The water lines are in place and connected in Plat 17. The waterlines are also in place, but not connected, in Plats 18 and 19. The total area of Sections 2, 3 and 4 of Harbor Course South is 134.09 acres. The remaining one hundred thirty-four lots occupy approximately 53.66 acres of this total. The lots in the area are priced at an average of $127,000 each. The Intervenors have begun selling the lots in Plat 17 (Section 2 of Harbor Course South). This plat consists of twenty-five lots. No competent substantial evidence was offered to establish the exact number of lots sold or houses constructed in this area, but it appears that ten to twelve lots were sold between July 1, 1989 and December 13, 1989. At least one house has been constructed on this plat and three building permits are pending before Monroe County. Prior to selling the lots in Plat 17, the Intervenors reached an informal agreement with the U.S.F.W.S. and the Commission as discussed in more detail in Findings of Fact 33 below. In accordance with that agreement and because there was no indication of the presence of endangered or threatened species on these lots, it was determined that none of the lots sold in Plat 17 would require the issuance of a permit from the Commission before land clearing could take place. The sales of the lots in Plat 17 were not completed until after the issuance of a Proposed Permit by the Commission for the "incidental taking" of endangered and threatened species with respect to the entire Harbor Course Property. (This Proposed Permit is discussed in more detail in Findings of Fact 44.) After the Proposed Permit was issued and this challenge was filed, the titles to the lots sold in Plat 17 were transferred to the purchasers. As indicated above, some of these lot owners have proceeded with the development of their property without the need of a permit from the U.S.F.W.S. or the Commission. None of the lots in Plats 18 and 19 (Sections 3 and 4) have yet been offered for sale. The natural vegetation of North Key Largo, including the Harbor Course South property, consists largely of tropical hardwood hammock. The quality of the vegetation varies widely throughout the area. Development of the Ocean Reef Club has largely supplanted the hardwood hammock in that area. The golf course which is located on the Harbor Course South property was placed in the midst of the hammock. The golf course and the infrastructure for development of Harbor Course South have fragmented the hammock in Plats 17, 18 and 19. The hardwood hammock of North Key Largo is a unigue flora to North America, being extremely tropical in character. It is characterized by vegetation more commonly found on the tropical islands of the Carribean and is different from the tropical hammocks of mainland South Florida because of a difference in hydrology, i.e., the Florida Keys are substantially drier and have a lower water table. The hammock of North Key Largo has a very high species diversity with one hundred and five species of trees and shrubs and fifteen species of woody vines in the hammock vegetation. The ecology of a hardwood hammock is cyclical. Over the years, the hammock has demonstrated its ability to regenerate naturally. Thus, while much of North Key Largo was used as agriculture land in the late nineteenth and early part of the twentieth century, the hammock has recovered in those areas where it has been allowed to naturally regenerate. The species of plants in the hardwood hammock are well-adopted for colonizing. The trees are "good at getting their seeds into places where they will grow." Many of the species of hammock trees and shrubs have fruits that are attractive to birds and some animals such as raccoons. These animals, birds, and raccoons eat the fruit, do not digest the seeds, but pass them in their fecal material which helps spread the vegetation. Tree growth in a young hammock is initially rapidly vertical before spreading out to provide larger coverage. A mature hammock provides a "closed canopy" of branches which affords protection and transportation for many animals including woodrats and cotton mice. As the hammock matures, there is an accumulation of humis and leaf litter on the ground beneath the trees. This humis layer serves as a seed bed for new growth and accumulates over the years. The humis layer is an important factor in assessing the quality of a hammock as habitat for endangered species. It takes decades for a hammock to fully mature to the point that it provides habitat and food sources for woodrats and similar creatures. Because of the biological richness of the hardwood hammock, as well as to protect the off-shore coral reefs from the detrimental effects of run-off from development, the State of Florida, through the Conservation and Recreational Land Acquisition program, ("CARL") has designated much of area of North Key Largo at the top of the acquisition priority list. The area slated for acquisition under the CARL program extends approximately twelve miles from the point where U.S. Highway 1 enters Key Largo northeastward to the southern boundary of Harbor Course South. The State of Florida has already acquired large tracks of North Key Largo under the CARL program. These tracks include a large portion of the land on the east side of State Road 905 from Port Bougainville to the southern border of the Ocean Reef Club (Harbor Course South.) Moreover, the Foundation is currently negotiating with the State regarding the acquisition of approxiately twelve hundred acres immediately adjacent to Harbor Course South. The federal government has established the Crocodile Lake National Wildlife Refuge which embraces most of the land lying west of State Road 905 from Card Sound Road (near and west of the Ocean Reef Club) south to Lake Surprise, a distance of approximately twelve miles. In sum, a large portion of the property in North Key Largo outside the Ocean Reef Club and Harbor Course South does not have vested development rights. A vast majority of this property is, or will likely become in the near future, publicly owned for conservation purposes. Thus, large quantities of high quality tropical hardwood hammock habitat have been, or are in the process of being, acquired in the immediate vicinity of the Harbor Course South property. The hardwood hammocks of North Key Largo are inhabited by certain endangered and threatened species. The Commission has the authority to determine endangered species within the area of its jurisdiction under the Endangered Species Act of 1973, 35 U.S.C.A. 1531, et seq. The Key Largo woodrat (neotoma floridana smalli) and the Key Largo cotton mouse (peromystus gossypinus allapaticola) are animals which can be found in the secondary growth and mature tropical hardwood forests of North Key Largo. Both the woodrat and cotton mouse as well as the Schaus' swallowtail butterfly (heraclides aristodemus ponceana,) have been listed as endangered species in Rule 39-27.003, Florida Administrative Code. The hardwood hammock of North Key Largo also serves as a habitat for the Eastern Indigo snake (drymarchon corais couperi), which has been listed as a threatened species by the Commission pursuant to Rule 39-27.004, Florida Administrative Code. Rock piles, tree roots, mounds, piles of sticks, holes in the rock substrate, holes in the humis layer beneath the trees and similar hiding areas all serve as nests or "refugia" for the woodrat. A mature hammock provides an ideal habitat for the woodrat. Destruction of the habitat of the woodrat has been a key factor in the woodrat becoming an endangered species. The Key Largo cotton mouse occupies much of the same habitat as the woodrat. Although the density of the population has not been established, there is no dispute that some portions of the Harbor Course South property are populated with woodrats and cotton mice. The quality of the habitat varies significantly throughout the property. There is only limited evidence of the presence of the Schaus' swallowtail butterfly on the Harbor Course South property. There have been a few citings of the species in the vicinity of Harbor Course South, but it does not appear that this property is an important habitat for the Schaus' swallowtail butterfly. There is no specific evidence of the presence of the Eastern Indigo snake on the subject property. Before a lot owner in Harbor Course South can clear his homesite, the Monroe County Code requires the owner to secure a habitat analysis which must be prepared by an accredited biologist approved by the County. That analysis determines the quality of the hammock on the lot, which in turn determines the amount of vegetation which the County will allow the lot owner to clear. This requirement was in place for the first thirty eight lots that were originally platted in Section 1. Under the existing Monroe County Land Clearing Regulations, only twenty percent of a lot with high quality tropical hardwood hammock can be cleared; forty percent of a lot with medium quality hammock can be cleared and forty to eighty percent of a lot with low quality hammock can be cleared. As of the date of the hearing in this case, all lot owners in Harbor Course South who have applied for a building permit were allowed to clear at least a portion of the lot for construction of a homesite. It does not appear that any lot owner was permitted to clear more than forty percent of his lot. As indicated above, no permits from the Commission or the U.S.F.W.S. were necessary in order to clear the lots and commence building on the thirty- eight lots in Section 1. Likewise, the Commission determined that the habitat quality in the area of Plat 17 was sufficiently low that a permit would not be required for development on that Plat. However, the Intervenors were aware of the presence of endangered and threatened species in this area. Around the time that the Vested Rights Determination was obtained, the Intervenors entered into discussions with the U.S.F.W.S. and the Commission in an attempt to obtain an overall permit for Plat 17, 18 and 19 with respect to endangered and threatened species. During these negotiations, the Intervenors received permission from the U.S.F.W.S. and the Commission to proceed with development in Plat 17 even before a permit was issued. The Commission determined that the Intervenors could proceed with the development of Plat 17 without obtaining a permit because of the relatively low habitat value of most of the parcel and the apparent absence of any endangered species in this area. As part of the negotiations regarding this authorization, the Intervenors agreed to seek a permit with respect to the remaining one hundred and nine lots in the subdivision. The negotiations were prompted, at least in part, by an agreement between the U.S.F.W.S. and the Florida Keys Aqueduct Authority (which provides water to the area) that established certain requirements before water connections could be made to new residential property in North Key Largo. This agreement requires that, before water connections can be made to an area inhabited by endangered or threatened species of wildlife, a permit must be obtained by the U.S.F.W.S. During the negotiations, the U.S.F.W.S. indicated to the Intervenors its desire to address the conflict between the endangered species on North Key Largo and development interests in "one big conflict rather than having to handle it land owner by land owner." The Commission agreed with this approach feeling it could better protect the subject species through required mitigation by the developer which would probably not be possible or practical when dealing with individual lot owners. Although the Intervenors questioned the legality of the requirements imposed as a result of the agreement between the U.S.F.W.S. and the Florida Keys Aqueduct Authority, the Intervenors decided to try and work with both the federal and state agencies and attempt to meet their concerns rather than engage them in a legal battle over their authority to impose mitigation requirements on new developments. A permit from the U.S.F.W.S. or the Commission is not necessary for the Intervenors to sell the lots in Plats 17, 18 and 19. The Intervenors sought permits from the Commission and the U.S.F.W.S. in a good faith attempt to cooperate with the agencies responsible for enforcing the Endangered Species Act and to eliminate obstacles to the clearing and development of the lots by individual lot purchasers. The U.S.F.W.S. has developed specific rules and procedures for protecting the habitat of endangered species and issuing "incidental take" permits for activities that may impact on the species or their habitat. The Commission has not adopted any rules that specifically protect the habitat of endangered species other than a prohibition against molesting or harming their nests. Similarly, the Commission has no specific rules regarding "incidental take" permits. The Intervenors filed an application with the U.S.F.W.S. on March 13, 1989 seeking a permit for covering all of Plats 17, 18 and 19. Attached as exhibits to the application were copies of the pleadings from the proceedings whereby Intervenors received their Vested Rights Determination, a summary of a proposed revegetation project to be undertaken in connection with the permit; the Harbor Course Subdivision construction plans together with construction details; a report prepared by Dr. Earl Rich regarding North Key Largo endangered rodent preservation measures; a report by Dr. Jack Stout setting forth the results of woodrat and cotton mice trapping in the subject area; and an aerial photograph of the subject area. The application sought a "permit for the incidental taking of endangered species in connection with completion of development of a residential subdivision and related site improvements surrounding an existing golf course. The area to be cleared may include habitat for the Key Largo woodrat, cotton mice, or Schaus' swallowtail butterfly." A permit has not been issued by the U.S.F.W.S. with respect to Plat 17, 18 and 19. The Intervenors' application for a permit has been transmitted to the Commission. It is not clear how the application filed with U.S.F.W.S. came before the Commission for consideration. The Commission has no direct agreement with the Florida Keys Aqueduct Authority regarding water connections. The Commission's authority for asserting jurisdiction over the development is not based on any existing rules or statutes regarding "incidental take" permits. The U.S.F.W.S. has apparently agreed to defer to the Commission with respect to the issuance of a permit for the Harbor Course South development. The U.S.F.W.S. has been kept abreast of the negotiations and terms of the Proposed Permit and has suggested various changes during the negotiation process in an effort to coordinate the conditions of the two permits. By letter dated July 24, 1989, the Commission set forth conditions for the issuance of a permit to the Intervenors which would authorize them to take the nests and habitat of woodrats and cotton mice, to harm or molest Schaus' swallowtail butterflies, and to take Eastern Indigo snakes, "incidental to land clearing operations and building construction of single family and cluster homes" on Plat 17, 18 and 19. The permit does not authorize the killing of woodrats, cotton mice or Schaus' swallowtail butterflies. The Commission stated that the permit was being issued pursuant to Rules 39-27.002(1) and 39- 27.002(2), Florida Administrative Code. (The July 24, 1989 letter setting forth the conditions for the permit will be referred to as the "Proposed Permit.") The Proposed Permit states that the permit will inure to the benefit of the Intervenors and their "successors in title or their agents." In other words, purchasers of lots from the Intervenors would be covered by the Permit and no additional permit would be necessary to take the nests and habitat of woodrats and cotton mice, to harm or molest Schaus' swallowtail butterflies, or to take the Eastern Indigo snakes incidental to the development of their lots. The terms and conditions of the Proposed Permit were prepared after several meetings and discussions between Commission personnel, the Intervenors' expert biologist Dr. Stout and the developers themselves. The Proposed Permit requires both on-site mitigation and off-site mitigation. The on-site mitigation requires the permanent dedication in the form of a conservation eastment of 5.94 acres in Tract E of Harbor Course South, Section 3 ( Ocean Reef Plat 18) to provide perpetual protection for the habitat for the species listed in the Proposed Permit. The exact provisions of this conservation easement are not speficified in the Proposed Permit and were not established in this proceeding. The Permit also requires specific habitat enhancement of Tract E by planting torchwood seedlings as a means to attract Schaus' swallowtail butterflies in the area of an old service road on Tract E, revegetation in accordance with specific planting instructions of another road that bisects Tract E and the placement of ten piles of rocks and logs of at least four cubic yards each in the old roadway. A ten thousand dollar surety bond or letter of credit is required to ensure compliance with the planting and debris placement provisions within three years of the date of the issuance of the permit. The Intervenors had intended to subdivide Tract E into ten additional lots to be sold as homesites. While Petitioner contends that the development of lots in Tract E may have been prohibited because of the high quality hammock on some of these lots, the evidence established that most, if not all, of the lots in Tract E will be sold and developed as individual homesites if the area is not set aside as a conservation area pursuant to the terms of the Proposed Permit. The establishment of a conservation area in Tract E will help preserve a continuous habitat area for the endangered species. Tract E is adjacent to a large track of property that has been or is in the process of being acquired by the state for conservation purposes. By requiring the Intervenors to provide rubble and debris piles and revegetation on Tract E, the Proposed Permit will further enhance the quality of the habitat in this area. The Proposed Permit requires the existing dirt road which currently cuts through Tract E to be closed and revegetated. There is no requirement that the fill installed for the road bed be removed. While Petitioners contend that such a condition is necessary for the development of this tract into high quality habitat for the endangered species, the natural regeneration of the hammock will be enhanced by the revegetation plan and this area will ultimately develop into high quality habitat. Planting torchwood in the area of Tract E, which is close to the golf course and areas that will be developed, may actually harm the survival potential of the Schaus' swallowtail butterfly. The butterflies are extremely susceptible to chemical insecticides. Planting torchwood in areas where insecticides will be used may create an attractive nuisance to the butterflies. Therefore, the requirement for planting should be moved to an off-site area that is remote from the development to guard against this problem. The area of the old service road should be revegetated pursuant to a schedule similar to the one used for the other revegetation area. Off-site mitigation is to be provided through the enhancement of hammock succession on five, one acre segments of the right-of-way of Old State Road 905 or an alternative similar site approved by the Commission with an area of enhancement to equal five acres. The amount of off-site mitigation was baseed upon a calculation of the amount of road surface in Harbor Course South. The Proposed Permit requires the old road bed and asphalt to be removed and the road restored to original grade. The enhancement of the site is to be accomplished by planting tropical hardwood vegetation from a specified vegetation list, adherence to specific planting instructions governing phase of planting, survival rate and watering conditions, placement of twenty rock and debris piles, (each four cubic yards in volume), removal of exotic plant species semi-annually for a five year period and removal of weedy species of trees and shrubs in an area within a radius of three feet around each planted tree over a similar time period. Four lots in Plat 18 are to be set aside as an assurance against failure to complete the planting or failure to provide an alternative site. A surety bond or letter of credit in the amount of $50,000.00 is also required to ensure compliance with the planting requirements. Old State Road 905 is currently owned by the Florida Department of Transportation. There are plans to convey this right-of-way to Monroe County which in turn plans to abandon the road, remove the road bed and asphalt, and cooperate with the restoration. Thus, it appears that Monroe County may assume responsibility for removing the asphalt road along Old State Road 905. The Proposed Permit requires the Intervenor to ensure that this removal is accomplished. Old State Road 905 is utilized by some utility companies to service their utility lines. At this point, it is not clear whether the utility easements will preclude the revegetation required by the Proposed Permit from becoming effective. The Proposed Permit provides adequate procedures for selecting alternative sites in the event that Old State Road 905 can not be effectively used for a mitigation area. With respect to both the on-site and off-site mitigation, the revegatation requirements in the Proposed Permit are reasonably related to the Commission's goal of enhancing the long term survival of woodrats and cotton mice on North Key Largo. While the diversity of the flora in a natural hammock is greater than that called for in the proposed mitigation, the revegetation will accelerate the development of the mitigation areas into high quality habitat for the endangered species. While a hardwood hammock has a natural capability to regenerate on its own, the regeneration can be enhanced by planting trees in a scarified area. The revegetation required pursuant to the Proposed Permit will be placed mainly in corridors replacing old road ways. This placement will hasten the redevelopment of these areas into high quality habitat. The Intervenors are required to ensure a two year, seventy five percent survival rate for trees planted. Any trees that die are to be replaced by the species with the highest survival rate. The evidence established that the most effective way to enhance the revegetation process is to plant those species of trees that are slow to seed or that are relatively rare. It is not clear whether the planting schedule and sucession procedures attached to the Proposed Permit have taken this fact into consideration. While the diversity of species detailed in the attachments to the Proposed Permit could be reallocated between species to further enhance the revegetation process, the proposed schedules are adequate except for the requirement of planting torchwood on Tract E. Torchwood is an important habitat and food source for Schaus' swallowtail butterflies and should not be placed in an area where chemical insect control efforts are likely. As indicated above, the Proposed Permit requires a survival rate of 75% for the planted trees within two years of the initial planting. The Intervenors are also required to inspect the revegetation sites semi-annually for five years and to remove invasive exotic plants. In addition, Intervenors are required to remove weeding trees, shrubs and vines within a radius of 3 feet around each planted tree for a period of five years. Semiannual reports must be filed with the Commission for the first five years after planting to advise as to the presence of such species. There are no enforcement mechanisms in the Proposed Permit to ensure that the monotoring and removal of exotic species requirements will be completed. The bond requirements of the Proposed Permit only apply to the plantings and installation of debris piles. The requirement for removal of exotic species will help ensure that those exotic species cannot invade the mitigation sites and prevent or retard the natural hammock regeneration process. This requirement will enhance the development of a high quality hammock which will hopefully provide habitat for the endangered species. It is important that an enforcement mechanism be provided in the permit with respect to this requirement. The State Department of Natural Resources has a program for the removal of exotic plants from state lands. DNR is currently preparing a major management plan for North Key Largo and DNR employees are currently involved in removing exotic species from the right-of-way of Old State Road 905. The requirements of the Proposed Permit will augment the on-going efforts of DNR and free-up resources to focus on the removal of exotic species in neighboring areas. The Proposed Permit does not impose qualifications on the individuals who will be responsible for removing the exotic species. The permit should require the Intervenors to retain qualified people to identify the exotic species. The spacing, watering and survival rate aspects of the revegetation plan were based, in part, upon the experiences with revegetation at a previous mitigation site (the Budd Post site discussed below) and represent a reasonable effort for enhancing the revegetation of the hammock. While there is no requirement that the planted trees survive longer than two years after the initial planting, the 75% survival requirement during the first two years provides reasonable assurance that the revegetation will be done properly and with a high probability of success. General Condition 1 of the Proposed Permit indicates that the Commission will review the Permit periodically and "may initiate enforcement or revocation action for any violation of the Permit Conditions by the Permittee, its agents, its employees, or representatives." There is no provision for enforcement or revocation of the permit for violations of the permit conditions by purchasers of lots or other third parties who obtain title to the property from the Intervenors. This enforcement mechanism will become essentially obsolete if and when the Intervenors transfer their interests in the property. General Condition 2 of the Proposed Permit indicates that the Permit is valid "only for the specific processes and operations applied for and indicated in the approved drawings or exhibits." This provision is meaningless since there are no "specific processing operations applied for" and there have been no approved drawings or exhibits other than the planting schedules which are part of the revegetation aspect of the mitigation requirements. There are certain provisions of the Proposed Permit which are vague and/or ambiguous. Special Conditions 4(b) indicates that the requirements of Specific Condition 3(j) are applicable to the restoration of Tract E. Special Condition 3(j) requires the placement of twenty debris piles. However, Specific Condition 4(c) only requires a placement of ten such piles in Tract E. This ambiguity should be clarified. Special Condition 4(d) indicates that there are utility lines in the revegetation area which will have to be maintained. Under this provision, the applicant is allowed to maintain, using hand tools only, a clear path of up to eight feet wide over each utility line. It is not clear from the evidence presented how many utility lines are involved and whether a separate eight foot area can be cleared for each utility line. If several separate utility lines are involved, this provision could effectively prevent the regeneration of the area into high quality hammock habitat. Free ranging domestic pets, especially cats, are a significant threat to the endangered species. One of the conditions imposed by the Proposed Permit would prohibit free ranging pets within the subdivision pursuant to a subdivision covenant to run with the land. The specific wording of such a covenant has not been provided. The Proposed Permit does not provide for any enforcement mechanism with respect to this covenant. Some enforcement mechanism must be provided in order for this condition to provide any effective protection for the endangered species. The Proposed Permit requires the Intervenors to hold four lots from sale until the off-site mitigation requirements have been met. If the planting is not accomplished within a five year period, the Intervenors are required to include these four lots as part of the conservation easement in Tract E. The lots being withheld for sale have an average market value in excess of $120,000 per lot. Thus, this requirement places a major incentive on the Intervenors to comply with the terms of the Proposed Permit. However, it is not clear whether this enforcement mechanism can be applied to the provisions of the Proposed Permit regarding the removal of exotic species. The Proposed Permit does not allow the Intervenors to kill any member of the endangered species. The Proposed Permit does allow the "incidental taking" of the threatened species (Eastern Indigo snake). The term "incidental taking" is interpreted by the Comimssion to include the killing of a member of the threatened species which is incidental to the conduct of otherwise lawful activities. The Commission contends that it has the jurisdiction to issue such an "incidental take" permit for an endangered species under appropriate conditions and mitigation requirements. The Commission did not believe an incidental take permit was necessary with respect to the endangered species on this site because the Commission felt that the habitat quality was relatively low and the likelihood of encountering a member of the species at the site was also low. The evidence established that there is a possibility that some members of the endangered species, i.e., woodrats and cotton mice, will be killed during the development and building of the subdivision. While this possibility is speculative, the chances of such a killing can be minimized by incorporating further protections in the permit. The evidence did not indicate any likelihood that East Indigo snakes or Schaus' swallowtail butterflies will be killed incidental to land clearing and/or development of Harbor Course South. The U.S.F.W.S. requires a habitat conservation plan ("H.C.P.") before it will issue an incidental take permit. A habitat conservation plan committee was established by the Governor in 1985 to prepare an H.C.P. for the North Key Largo area. The goal of the Committee is to designate areas which would be suitable for development and areas which may be necessary for conservation. A Draft Habitat Conservation Plan has been prepared, but it has not yet been officially approved. Harbor Course South is outside the study area of the Draft Habitat Conservation Plan and therefore is not proposed as a conservation area. The framework and structure of the Proposed Permit reflects the Commission's desire to apply a comprehensive permitting approach to the Harbor Course South development rather than rely upon a lot-by-lot determination of jurisdiction with each individual lot purchaser at the time clearing or development activities are sought. The evidence established that there is insufficient indicia of woodrat or cotton mouse presence on a number of the lots in Harbor Course South. Thus, if a lot-by-lot approach was used, the Commission would not have the authority under its current rules to require a number of the individual lot owners to obtain a permit before land clearing. Without question, further fragmentation of the hammock will reduce the quality of the habitat for the endangered species. If a lot-by-lot permitting process is utilized, the owners of the lots that do not show any signs of the presence of woodrats or cotton mice would be able to clear to the maximum extent allowable under the Monroe County development ordinances. Such an approach would not halt the further fragmentation of hammock. By utilizing a comprehensive permit, the Commission can establish uniform standards for development and require stronger mitigative measures to offset the impact of development in the area on the endangered and threatened species. The approach is further justified in view of the Commission's determination that the Harbor Course South property is of only minimal importance as a habitat for the endangered and threatened species. See, Findings of Fact 80-81 below. In sum, land development and land clearing activities are likely to take place on the Harbor Course South property regardless of whether the Proposed Permit is issued. If the Commission utilizes a lot-by-lot determination of jurisdiction, a large portion of the lots on Harbor Course South would not be required to obtain a permit from the Commission because many of those lots do not have nests or any indication of the presence of the endangered species. Under these circumstances, the Commission would probably not be able to obtain comprehensive mitigation conditions and the habitat for the endangered species would be further fragmented with little or no mitigation. As noted above, the Commission has not adopted any rules setting forth its policies and procedures for issuing an overall blanket permit for the "incidental taking" of endangered species. Similarly, there are no formal guidelines adopted to establish when the Commission has jurisdiction over land- clearing activities. In determining whether to assert jurisdiction over a particular piece of property, the Commission looks for evidence of existing nests or habitat of an endangered species or the probability that a taking, killing or some other molestation will occur to a particular member of the species. In connection with the Proposed Permit, the Commission determined that it had the authority under Rule 39-27.002, Florida Administrative Code, to issue permits for clearing and development activities that molest the nests of endangered species. As discussed below, the Commission has issued only one prior permit for land clearing and development activities. That prior permit is was not timely challenged. No rules or standards have been promulgated by the Commission to set forth the mitigative requirements that can be imposed, if any, upon individual lot purchasers. An important factor in the Commission's decision to issue the Proposed Permit in this case was the Commission's determination that the overall quality of the Harbor Course South property as habitat for the endangered species was minimal. In determining that the Harbor Course South property was of minimal importance to the survival of the endangered species, the Commission took into consideration various reports on the sparse density of the population of the endangered species on the subject property. The Commission also took into account what it deemed to be inevitable future development as reflected in the Vested Rights Determination, the fact that the site was not designated for preservation in the Draft Habitat Conservation Plan, and the fact that the site was not part of the North Key Largo CARL acquisition project. Finally, the Commission considered that the site was already a highly fragmented tropical hardwood hammock as demonstrated by Landsat Thematic Mapper Classfied Satellite Imagery. The only previous instance in which the Commission has issued a permit to molest or harm the nests or habitat of endangered species pursuant to land clearing or development activities involved another residential sub-division in North Key Largo. In June of 1986, separate permits were issued by the U.S.F.W.S. and the Commission to the Nichols/Post Hendrix Corporation to destroy nests and habitat of the Key Largo woodrat and Key Largo cotton mouse. (The permit issued by the Commission in connection with this prior project will be referred to as the "Budd Post Permit.") The property covered by the Budd Post Permit is south of Harbor Course South. It lies approximately six miles south of the intersection of Old State Road 905 and Card Sound Road. That property consists of approximately ten acres of high quality hardwood hammock located within the project area of the North Key Largo Hammocks, CARL land acquisition program. Thus, the property was essentially surrounded by high quality tropical hardwood hammock. The Budd Post property is similar to the Harbor Course South property in that both areas run from County Road 905 east to the ocean and both tracts contain habitat suitable for use by endangered species. However, Harbor Course South is a lesser quality habitat than the Budd Post property because it is more highly fragmented and is bordered on the north by the highly developed Ocean Reef property. Overall, there was a significantly greater indication of the presence of the subject endangered species on the Budd Post Property than there is at Harbor Course South. The Budd Post Permit was the first of its kind issued by the Commission and was processed simultaneously and concurrently with the comparable federal permit from the U.S.F.W.S. As a condition to issuance of the Budd Post Permit, the Commission required the permittee to set aside a preservation area, build debris piles to encourage nesting of woodrats and cotton mice and plant vegetation off-site to mitigate the loss of hammock habitat. A condition of the Budd Post Permit required the permittee to trap and remove the endangered species during land clearing activities. A similar condition in the Proposed Permit would help reduce the likelihood of any killing of the endangered species. The results of the mitigation plan for the Budd Post Permit indicate that such a plan can serve to enhance the survivability of the endangered species by providing high quality habitat and accelerating the revegetation of scarified areas. A little more than two years after the mitigation plan for the Budd Post Permit was implemented, it appears that the efforts are achieving their intended results. Specifically, the plants that were planted as a result of the revegetation plan are flourishing and at least some of the debris piles have been colonized by woodrats. Thus, it appears a viable habitat has been created. There is no definitive method for determining the density of population of woodrats or cotton mice at a given site. In making its jurisdictional determination with respect to the Budd Post property, the Commission looked for the presence of stick nests, (which are widely presumed to be constructed by woodrats) as the primary jurisdictional indicator. Subsequent to the issuance of the Budd Post Permit, the Commission has recognized that stick nests are not the sole indicators of the presence of wood rats and the Commission now considers other factors as well. The U.S.F.W.S. requires a trapping study of woodrats and cotton mice as part of its permit application. The permittee for the Budd Post Permit provided the U.S.F.W.S. and the Commission with a "trapping report" prepared by Dr. Stout. The Intervenors also hired Dr. Jack Stout, who is a biologist and professor at the University of Central Florida, and a similar report was prepared for Harbor Course South. The same methodology was used to trap woodrats and cotton mice on both sites. Dr. Stout concluded that the Harbor Course South property had a low density population of woodrats and cotton mice. Dr. Earl Rich, a biologist and ecologist and a former professor at the University of Miami with extensive experience researching woodrat habitat on North Key Largo, also inspected the Harbor Course South property on behalf of the Intervenors. His inspection took place after the date of the Proposed Permit. He determined that the overall quality of the subject property as habitat for the endangered species was low because of the fragmented and uneven quality of the hammock. These qualities are largely attributed to the existing intrastructure and the golf course which winds throughout the subject property. Julie Hovis, a wild life biologist employed by the Commission, performed a site inspection report in connection with the application for the Proposed Permit. While not an expert on the endangered species, she was qualified to identify certain signs of the presence of the species. She found that there was some evidence that woodrats and cotton mice were present on the Harbor Course South property. She noted that the quality of the habitat varies greatly. Her inspection and conclusions were the basis for the Commission's assertion of jurisdiction over the subject site. Dr. Steven Humphrey and Dr. Numi Goodyear inspected the area on behalf of the Petitioners to determine the presence and/or density of the endangered species populations. While their studies find more evidence of the presence of wood rats and cotton mice on the subject property than the prior studies had indicated, they also conclude that the property is a mixed quality habitat for the endangered species. While there are some areas that appear to be high quality habitat, these experts recognize the fragmented character of the habitat and the effect of the golf course in disrupting the habitat and producing "islands of vegetation." The Goodyear and Humphrey studies confirm that the densities of the endangered species are lowest in areas where the hammock is highly fragmented. The Goodyear and Humphrey studies do not refute the Commission's conclusion that a significant number of the lots of Harbor Course South do not reflect sufficient indicia of the presence of the endangered species to allow the Commission to assert jurisdiction on all the property if a lot-by-lot permitting process was utilized. The Commission has concluded that the continuing development of Harbor Course South is inevitable. The Commission has also concluded that its authority over clearing of individual homesites is limited. In view of these conclusions, the Commission has attempted to enhance the survivability of the endangered species by imposing certain mitigation requirements on the Intervenors. The evidence has established that, assuming the development of Harbor Course South is inevitable, and the Commission lacks the authority to halt the development of Harbor Course South, the Commission's comprehensive approach to permitting will be more favorable to the survival potential of the endangered species than a lot-by-lot jurisdictional determination would be.
Recommendation Based upon the foregoing Findings of Fact and Conclusions of Law, it is RECOMMENDED that the Florida Game and Fresh Water Fish Commission enter a Final Order setting forth the terms and conditions for an Agreement with the Intervenors for a specific period of time as set forth in Paragraph 30 of Conclusions of Law, whereby permits will be issued for the incidental destruction and/or molestation of the nests and habitat of the subject endangered species in accordance with the terms and conditions of the Proposed Permit as modified in accordance with the provisions of Paragraph 32 of the Conclusions of Law above. DONE AND ORDERED in Tallahassee, Leon County, Florida, this 17th day of October, 1990. J. STEPHEN MENTON Hearing Officer Division of Administrative Hearings The DeSoto Building 1230 Apalachee Parkway Tallahassee, Florida 32399-1550 (904) 488-9675 Filed with the Clerk of the Division of Administrative Hearings this 18th day of October, 1990.
The Issue The issue is whether Petitioner is entitled to additional compensation for fishing nets that he sold to the State of Florida under the Net Buy-Back Program.
Findings Of Fact Petitioner is a commercial fishers who is an affected person under the Florida Net Ban, which is set forth in the Florida Constitution, Article X, Section 16. Section 370.0805(5), Florida Statutes, which became effective on July 1, 1995, establishes the Net Buy-Back Program. The program enables eligible persons previously engaged in the commercial fishing industry to sell fishing nets to the State of Florida. The Legislature appropriated $20 million to the Seafood Workers Economic Assistance Account (the Account) to fund the payments authorized in Section 370.0805, as well as agency expenses in administering the program. Section 370.0805(3)(b) directs Respondent to purchase nets "according to the availability of funds on a first-come, first-served basis determined by the date of receipt of each completed application." By Net Buy-Back Application signed on July 5, 1995, and filed with Respondent on the same day, Petitioner applied to sell nets to the State of Florida. His application form is completely filled out and shows two saltwater-product license numbers, one for an individual and one for a vessel. The application form calls for the applicant to list the "TOTAL NUMBER OF YARDS OF EACH NET TYPE THAT YOU INTEND TO SELL." The form lists five categories of nets: gill (49 meshes or less); gill (50 meshes or more); beach, purse, seine; trawl; and trammel. The former gill net is a shallow-water gill net. The latter gill net is a deepwater gill net. Petitioner listed on his application 800 yards of shallow-water gill nets, 4600 yards of deepwater gill nets, two trawls, and 600 yards of trammel nets. After checking a data base maintained by the Department of Environmental Protection, Respondent found only one of Petitioner's two listed saltwater-product licenses. Respondent thus processed Petitioner's application as though he had only one license. By letter dated August 8, 1995, Respondent advised Petitioner that he was eligible "to receive compensation for 8 nets" and set an appointment for him to turn in the nets on September 6, 1995. On September 6, 1995, Petitioner appeared at the appointed site with nets to sell to the State of Florida. He delivered 4800 yards of seine nets, for which he received a voucher for $27,998.40. Prior to paying the voucher, Respondent discovered that the Account might be exhausted before Respondent had paid for all of the nets that fishers might lawfully seek to sell to the State. Respondent thus dishonored Petitioner's voucher, as well as the vouchers held by numerous other fishers, while Respondent considered changes in its administration of the program. The purpose of the Net Buy-Back Program, as provided by Section 370.0805(5)(a), Florida Statutes, was to allow, "[a]ll commercial saltwater products licensees and persons holding a resident commercial fishing license" to apply to Respondent "to receive economic assistance to compensate them for nets rendered illegal or useless by the constitutional limitation on marine net fishing." The emphasis was on economic assistance. Section 370.0805(5)(a) authorizes Respondent to make payments only "in nonnegotiable amounts not intended to reflect the actual value of the nets." Section 370.0805(5)(a) assigns payment amounts of $3500 for beach, purse, or seine nets of at least 600 yards in length; $500 for trawls and shallow-water gill nets of at least 600 yards in length; and $1000 for trammel nets of at least 600 yards in length and deepwater gill nets of at least 600 yards in length. Section 370.0805(5)(a) states that, except for trawls, nets of less than 600 yards in length shall be "valued proportionately." Section 370.0805(5)(c) limits the number of nets that a commercial fishers could sell, based on his annual earnings from the sale of eligible saltwater products. The limits range from four nets, for licensees whose annual earnings average from $2500 to $4999 in earnings, to ten nets, for licensees whose annual earnings average more than $30,000. Respondent relied on another data base from the Department of Environmental Protection to determine the average yearly earnings of applicants. The Department of Environmental Protection maintains records of each licensee's trip tickets, which disclose earnings. The only other limit in the statute as to the type and number of nets to be purchased is that, under Section 370.0805(5)(d), "[n]o licensee may be paid for more than two. . . trawls." Respondent reviewed the applications that it received from the initial 951 fishers who filed applications. This was a large majority of the 1104 fishers who would eventually sell their nets to the State under the Net Buy-Back Program. The purpose of the review was to determine whether the funds in the Account would be sufficient to cover the nets that the State was to be purchasing. Respondent found from the applications that seine nets represented only about five percent of the nets that fishers intended to sell to the State. Relying on this information, Respondent calculated the potential encumbrance of $6.5 million on the Account, based on an average payment of $1000 per net. Applications contained few seine nets because commercial fishers initially resisted selling their best nets to the State of Florida. The Net Buy-Back Program provided for payment of only $3500 per seine net, even though many seine nets were worth $10,000. And commercial fishers were optimistic at first that their legal challenges to the constitutional amendment would succeed. Applying liberal eligibility criteria, such as calculating the number of nets that each applicant could sell based on the number of licenses that he held, Respondent raised its estimate of the potential encumbrance to $8.775 million. But in recalculating the potential encumbrance on the Account, Respondent still assumed that the average payment per net would be $1000. Respondent began receiving nets on August 3, 1995. Through the first three weeks of August, Respondent purchased seine nets in roughly the same five-percent mix that it had used in calculating the potential encumbrances on the Account. After this point, however, fishers started turning in much larger numbers of seine nets than they had listed in their applications. During this first phase of the program, Respondent paid fishers for whatever types of nets they presented at their net buy-back appointment. Respondent would pay a fishers entitled to sell eight nets for seine nets if he turned in seine nets, even though he had listed only gill nets on his application. This policy jeopardized the solvency of the Account because the payments to fishers turning in all seine nets were 3.5 times greater than the figures that Respondent had used in calculating the potential encumbrance on the Account. From the fishers's perspective, the program acquired an element of chance, as applicants with earlier appointment times-which did not necessarily correspond with earlier-filed applications-netted fine catches of economic assistance at the expense of their counterparts, upon whom destiny had bestowed later appointment times. By late August, the applicants, less sanguine about their litigation prospects (as the fishers suggest) and more inventive in recasting old gill nets as seine nets (as Respondent suggests), began turning in seine nets in large numbers, so that Respondent was purchasing nearly all seine nets. Eventually, the cumulative effect of this trend raised the total mix of seines purchased from five percent, during the first three weeks, to sixty percent. After a brief period of trying to stay the course, Respondent decided on September 6, 1995, that it had to take action or else the Account would be exhausted before the State had purchased all of the nets listed on the applications. Respondent immediately suspended further payments on issued vouchers and applied new criteria to persons holding unpaid vouchers, as well as to applicants who had not yet received vouchers. This action stopped payment on all vouchers issued from around August 28 through September 6. At the time that it stopped payment on outstanding vouchers, Respondent had approved the purchase of nets from about 750 fishers. About 450 of these applicants received their money prior to the suspension of payments, leaving about 300 applicants, including Petitioner, holding worthless vouchers. However, a large number of the 450 applicants who were actually paid for their nets prior to September 6 sold a relatively large percentage of gill nets rather than seine nets. As of September 6 (retroactive to August 28), Respondent began the second phase of the Net Buy-Back Program. In this phase, Respondent paid for seine nets, but only up to the greater of the number of seines shown on the application or the number of seines based on past use of seines. Respondent determined the latter figure from the trip tickets, which also contained information as to types of catch, from which Respondent could infer the type of net used. As in the first phase, Respondent continued to insist the fishers turn in seines if they were being paid for seines. The 300 fishers holding dishonored vouchers filed a class action suit. Petitioner's voucher for his first eight nets was covered in this legal action and is not the subject of this case. Petitioner received slightly more than $10,000 on his claim for about $28,000. In the meantime, Respondent discovered that Petitioner in fact held two licenses, as he had represented on his application. By letter dated October 5, 1995, Respondent advised Petitioner that it had reconsidered his application and determined that he had the right to sell 16 nets, not eight nets, but none could be a seine net. Respondent issued Petitioner a new voucher for these additional eight nets. This voucher is in the amount of $7996.80 for 4800 yards of deepwater gill net. On October 13, 1995, Petitioner turned in eight nets and received his money. Petitioner's application lists no seine nets. His application, as noted above, lists one and one-third shallow- water gill nets (i.e., 800 yards), eight deepwater gill nets, two trawls, and one trammel net. Petitioner claimed that he turned in seine nets. If turned in during the first or second phase of the program, Respondent would have treated these nets as seine nets. But it is Petitioner's unique fortune to have been intimately involved with all three phases of the Net Buy-Back Program. Evidently dissatisfied with the effects of the restrictions introduced by the second phase of the program, Respondent added a third phase by promulgating an emergency rule defining "seine nets," effective October 2, 1995. This third phase, which did not change Respondent's policy of paying for the greater number of seines as shown on the application or the trip tickets, restricted the kinds of nets that fishers could turn in as seine nets. Rule 38BER95-1 provides that, for the purpose of "the implementation of the Net Buy-Back Program" described in Section 370.0805(5): "Gill net" means a wall of netting suspended vertically in the water, with floats across the upper margin and weights along the bottom margin which captures fish by entangling them in the meshes, usually by the gills. Any net offered for the net buy- back program that consists of at least fifty- one percent (51 percent) gill net, shall be considered a gill net. "Seine" means a small-meshed net suspended vertically in the water, with floats along the top margin and weights along the bottom margin, which encloses and concentrates fish, and does not entangle them in the meshes. No net offered for the net buy-back program shall be considered a seine if the wings are composed of entangling mesh. * * * THIS RULE SHALL TAKE EFFECT IMMEDIATELY UPON BEING FILED WITH THE DEPARTMENT OF STATE. Effective Date: October 2, 1995 Under the emergency rule, Respondent's nets were not seines, but were gill nets because they were at least 51 percent, by area, gill net. At the time of the final hearing, Respondent estimates that the Account balance is about $300,000 with about 160 contested claims remaining to be resolved.
Recommendation It is RECOMMENDED that the Department of Labor and Employment Security enter a final order dismissing the petition for additional payment from the Account. ENTERED on October 3rd, 1996, in Tallahassee, Florida. ROBERT E. MEALE Administrative Law Judge Division of Administrative Hearings The DeSoto Building 1230 Apalachee Parkway Tallahassee, Florida 32399-1550 (904) 488-9675 SUNCOM 278-9675 Fax Filing (904) 921-6847 Filed with the Clerk of the Division of Administrative Hearings this October 3rd, 1996. COPIES FURNISHED: Secretary Douglas L. Jamerson Department of Labor and Employment Security 303 Hartman Building 2012 Capital Circle Southeast Tallahassee, Florida 32399-2152 Edward A. Dion General Counsel Department of Labor and Employment Security 303 Hartman Building 2012 Capital Circle Southeast Tallahassee, Florida 32399-2152 John Wayde Campbell 1103 67th Street Northwest Bradenton, Florida 34209 Louise T. Sadler Senior Attorney Department of Labor and Employment Security 2012 Capital Circle, Southeast Suite 307, Hartman Building Tallahassee, Florida 32399-2189
The Issue Whether Respondent's wholesale and retail dealer's licenses should be revoked or otherwise disciplined for two convictions of Possession of Undersized Crawfish Tails, as alleged.
Findings Of Fact I. MGB Corporation, a corporation organized under the laws of Florida, owns and operates a seafood dealership known as Gulfstream Seafood at 5300 Georgia Avenue West Palm Beach, Florida. It holds Retail Seafood Dealer's License No. RC-W3246 and wholesale Seafood Dealer's License No. WD2239 issued by DNR for the 1985-86 license year. (DNR Ex. 1,2) George M. Michael is the president and chief executive officer of MGB. In connection with MGB's application for issuance or renewal of its current seafood dealer's licenses, Mr. Michael executed a required affidavit from the individual responsible for the day-to-day management of the business. By the terms of the affidavit, he pledged himself "to the faithful observance of all . . . laws . . . regulating the . . . possession of fish, seafood, and other saltwater products (DNR Ex.2) On October 21, 1985, following a plea of no contest, the County Court of Palm Beach County, Florida, adjudicated MGB d/b/a Gulfstream Seafood guilty of two counts of Possession of Undersized Crawfish Tails, a violation of Section 370.14, Florida Statutes. MGB was fined $500, in addition to a $20 surcharge and a $25 fine for contempt of court. (DNR Ex.3; Tr.21-22) II. One of these counts alleged that on March 29, 1985, MGB d/b/a Gulfstream Seafood, unlawfully possessed crawfish tails which measured less than five and a half inches lengthwise from the point of separation along the center of the entire tail until the rearmost extremity is reached, contrary to Section 370.14(2), Florida Statutes. Facts Underlying this Violation. On March 29, 1985, Officer Francis Crowley accompanied by another officer of the Florida Marine Patrol entered the premises of Gulfstream Seafood and observed undersized crawfish on pallets in the production area. They were not refrigerated and had not yet been processed. Mr. Michael, who was present, tried to divert Officer Crowley's attention while another individual attempted to wheel the crawfish out the back door. The two officers separated the legal-sized crawfish from the undersized crawfish and weighed each category. There were 254 pounds of undersized crawfish, i.e., crawfish with tails measuring less than five and a half inches lengthwise from the point of separation along the center of the entire tail to the foremost extremity. The number of undersized crawfish involved is unknown. Officer Crowley issued a citation to Mr. Micheal and donated the undersized crawfish to a children's home in Fort Pierce. III. The other count of which MGB was found guilty alleged that on May 17, 1985, MGB again unlawfully possessed 3undersized crawfish in violation of Section 370.14(2), Florida Statutes. The circumstances surrounding this violation including the weight or number of undersized crawfish involved, have not been shown. IV. MGB has 165 employees, a payroll of $127,000 a month, and processes between 10,000 and 15,000 crawfish per month. A suspension of its seafood dealers' license for a month or more would adversely impact its operations. Customers would most likely obtain seafood from other dealers and it would be difficult for MGB to recoup the lost business.
Recommendation Based on the foregoing; it is RECOMMENDED: That the charges, and administrative complaint filed against MGB; be DISMISSED. DONE and ORDERED this 12th day of August, 1986, in Tallahassee, Florida. R. L. CALEEN, JR. Hearing Officer Division of Administrative Hearings The Oakland Building 2009 Apalachee Parkway Tallahassee, Florida 32301 (904)488-9675 Filed with the Clerk of the Division of Administrative Hearings this 12th day of August, 1986.
Findings Of Fact The following are the facts to which the parties have stipulated: Respondent is the holder of a pound net registration issued on November 30, 1983, by Dennis E. Holcomb, Director, Division of Fisheries, for the Executive Director of the Game and Fresh Water Fish Commission (Commission). The registration authorizes the Respondent to operate pound nets for Commercial purposes on certain areas of the St. Johns River, subject to law and Commission rules. On April 30, 1986, Petitioner pled guilty to illegal fishing with pound nets and was adjudged guilty and fined by the County Court of Putnam County, Florida. As a result of this Conviction, Respondent's pound net registration was temporarily revoked for a period of six (6) months dating from June 23, 1986 until December 23, 1986. On October 15, 1986, during the afore-mentioned revocation period, Respondent pled guilty to illegal fishing with unpermitted pound nets, and was adjudged guilty and fined by the County Court of Putnam County, Florida. Based on the Respondent's conviction of illegal fishing with pound nets during the revocation period, the Commission found just cause to permanently revoke Respondent's pound net registration and filed an Administrative Complaint on March 30, 1987 against Respondent to effectuate that revocation. Based on Respondent's unrebutted testimony which I found to be credible, the following relevant facts are found: That in addition to the fine imposed on the Respondent by the County Court of Putnam County, Florida on October 15, 1986, for illegal fishing, the Commission seized and Confiscated two (2) of Respondent's pound nets worth approximately $6,000.00. Respondent, subsequent to October 15, 1986, continues to fish pound nets as the designee of other parties holding pound net registrations, without incident and in compliance with the law and Commission rules. The Respondent is substantially dependent upon pound net fishing for his livelihood and has been prohibited from fishing his pound nets since June 23, 1986. Respondent's pound net registration was not reinstated at the end of the revocation period ending on December 23, 1986.
Recommendation Having considered the foregoing Findings of Fact and Conclusions of Law, the evidence of record and the conduct and demeanor of Use witness, it is, therefore, RECOMMENDED that the Commission enter a Final Order temporarily revoking Respondent's pound net registration for a period of twelve (12) months beginning December 23, 1986. Respectfully submitted and entered this 11th day of August, 1987, in Tallahassee, Florida. WILLIAM R. CAVE 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 11th day of August, 1987.
Findings Of Fact Respondent, Norman Padgett, holds a haul seine permit, issued by the Commission, which authorizes Respondent to operate a haul seine net on Lake Okeechobee. The permit is renewable annually and is one of ten such permits issued by the Commission. The Lake Okeechobee Haul Seine Permits authorize their holders to fish by haul seine and to harvest game fish in commercial quantities, activities not legal absent such a permit. To minimize conflicts between sport fishermen and commercial haul seine permittees on Lake Okeechobee, the Commission has, by rule, prohibited seining activities in certain areas. Among the areas closed by rule to haul seining is the area south of a line that connects the northernmost point of Kreamer Island to the northernmost point of Ritta Island. That line is approximately five miles long and can be readily determined since the northernmost point of either island is visible from the other island. Also closed by rule to haul seining are those areas shoreward of a line delineated by the Commission's commercial fishing boundary buoys. The boundary line is approximately one mile lakeward of emergent aquatic vegetation. The Commission, by rule, has prohibited the use of "short" haul seines as an aid to its enforcement against haul seining in closed areas. "Sport" nets are prohibited because of the ease with which they can be deployed and retrieved. During the time period pertinent to these proceedings, the Commission's rules prohibited use of haul seine nets of less than 350 yards in length. On June 18, 1984, a crew was conducting haul seining operations under the authority of Respondent's haul seine permit. The crew was operating in the closed area south of the line established by the northernmost points of Kreamer and Ritta Islands and was warned by a Commission employee that use of a haul seine in that area was prohibited. On June 19, 1984, a crew was again conducting haul seining operations under the authority of Respondent's haul seine permit in the closed area south of the line established by the northernmost points of Kreamer and Ritta Islands. The seining operations were being conducted from one-half to one mile within the closed area. On June 20, 1984, a crew was again conducting haul seining operations under the authority of Respondent's haul seine permit. On this occasion the crew was operating in a closed area shoreward of a line delineated by the Commission's commercial fishing boundary buoys. The haul seine net being used measured 277 yards in length. Respondent was not on board the fishing vessels during the foregoing events. However, consistent with the Commission's rule, the crews were in possession of his permit. At hearing Respondent offered no evidence of what, if any, efforts he took to supervise or maintain control of the haul seine crews. His testimony established, however, that he was aware the haul seine net was less than 350 yards in length. By letter dated March 28, 1985, the Commission informed Respondent of its intent to revoke his Lake Okeechobee Haul Seine Permit. Respondent timely requested a formal hearing. The case was forwarded to the Division of Administrative Hearings and assigned Case No. 85-1312. By letter dated July 23, 1985, the Commission informed Respondent of its intent to deny his application for renewal of his haul seine permit, predicated on their prior decision to revoke his permit. Respondent timely requested a formal hearing. The case was forwarded to the Division of Administrative Hearings, assigned Case No 85-2612, and consolidated with Case No. 85-1312.
The Issue Whether proposed rules promulgated by the Florida Marine Fisheries Commission are an invalid exercise of delegated legislative authority.
Findings Of Fact The Florida Marine Fisheries Commission (MFC) has proposed rules requiring use of bycatch reduction devices (BRD.) The proposed rules are applicable where trawling for shrimp is permitted in specified Florida waters within the Gulf of Mexico. The notice of proposed rulemaking was published in Volume 23, Number 30, Florida Administrative Weekly, July 25, 1997. The Petitioners have challenged the proposed rules, specifically the provisions prohibiting possession of an otter trawl (a type of trawling net) that is rigged for fishing aboard any vessel without having a required BRD installed. All parties have standing to participate in this proceeding. The federal government requires BRDs in the Florida waters not impacted by the proposed rules at issue in this proceeding. The federal rules are intended to protect red snapper in the Gulf and weakfish and Spanish mackerel in the Atlantic Ocean. The MFC rules are intended to offer broader protection than federal rules, and are intended to protect the Gulf ecosystem rather than specific species of organisms. Shrimp trawls operating in the Gulf of Mexico harvest approximately 2.4 pounds of non-shrimp species for every pound of shrimp harvested. The MFC goal is to reduce the level of bycatch harvested by 50 percent. The proposed rules do not cover the “Big Bend grass beds” where trawling for shrimp is already prohibited. The proposed rules do not cover Florida’s northeast coast where other BRD rules are in effect. The Petitioners challenge the same provision in three separate rules. Proposed Rule 46-31.010(4), Florida Administrative Code, provides: In the Northwest Region, no person harvesting shrimp as a food shrimp producer shall operate or fish any otter trawl, or possess any otter trawl that is rigged for fishing aboard any vessel, which otter trawl does not have a bycatch reduction device (BRD) installed therein meeting the requirements of Rule 46-31.045. (emphasis supplied) Proposed Rule 46-31.012(4), Florida Administrative Code, provides: In the Southwest Region, no person harvesting shrimp as a food shrimp producer shall operate or fish any otter trawl, or possess any otter trawl that is rigged for fishing aboard any vessel, which otter trawl does not have a bycatch reduction device (BRD) installed therein meeting the requirements of Rule 46-31.045. (emphasis supplied) Proposed Rule 46-31.013(2), Florida Administrative Code, provides: In all waters of the Southeast Region outside nearshore and inshore Florida waters, no person harvesting shrimp as a food shrimp producer shall operate or fish any otter trawl, or possess any otter trawl that is rigged for fishing aboard any vessel, which otter trawl does not have a bycatch reduction device (BRD) installed therein meeting the requirements of Rule 46-31.045. (emphasis supplied) On a shrimping boat, “otter trawl” nets are suspended from the ends of “outriggers” attached to the sides of the boat. When in use, the nets are dropped from the outriggers into the water. Once in the water, the nets are dragged along behind the boat, collecting shrimp and other marine species. The non-shrimp marine species collected are referred to as the “bycatch.” The phrase “rigged for fishing” means that the nets are shackled to the outriggers and are in a condition ready to fish, but are not yet in the water or being dragged along the bottom of the water. Nets attached to the outriggers of a shrimping boat and ready to be dropped into the water are rigged for fishing. Nets lying on the deck of the boat which are not attached to the outriggers are not rigged for fishing. It takes no more than a few minutes to attach the nets to the outriggers. The phrase being challenged in the proposed rules essentially prohibits a shrimp boat operator from suspending the nets above the water prior to dropping the nets into the water without having the BRD installed in the nets. Although there is no credible evidence indicating the reason shrimp boats leave the docks with nets in a position rigged for fishing, many apparently do so. There is no credible evidence suggesting any reason nets would be suspended from the outriggers other than in anticipation of initiation of shrimp harvest activity. There is no credible evidence that any impact would result from requiring that non-BRD equipped nets remain unrigged for fishing until outside of waters affected by the proposed rule. Use of the BRDs results in a substantial reduction of bycatch. There is no evidence that use of the BRDs results in any reduction in shrimp harvest. The evidence establishes that the reduction in bycatch will contribute towards the preservation of renewable marine fishery resources and will benefit the continuing health of the resources. There is no evidence that the proposed rules are unfair or inequitable to any persons including shrimp boat operators. The Petitioners assert that because the penalty for violations of the rules may eventually result in incarceration, the cited phrase creates a criminal presumption that a shrimp boat operator with non-BRD equipped nets is presumed to be fishing without a BRD. The evidence fails to support the assertion. There is no presumption being created by the proposed rule. The challenged rules are gear specifications for shrimp trawls, and are clearly within the realm of the MFC's rulemaking authority. The cited phrase does not prohibit the mere possession of a net without a BRD installed. The cited phrase prohibits suspension of a net from an outrigger without having a BRD installed in the net. There is no reason, other than in anticipation of immediately dropping the net into the water, that a trawl net must be suspended from an outrigger. The Petitioners assert that the rule would impact shrimp boat operators who are passing through Florida waters traveling to waters outside the areas impacted by the proposed rules. There is no evidence that the proposed rules would interfere with fishing operations. In the example of boat operators fishing outside Florida waters and using non-BRD equipped nets, compliance with the rule requires only that the nets remain unrigged for fishing while passing through Florida waters. The Petitioners assert that there are instances due to emergency, weather or otherwise, that may result in a shrimp boat operator working waters outside those covered by the proposed rules, raising non-BRD equipped nets and moving through into Florida jurisdictional waters. In such an event, the Petitioners assert that an operator could be subject to application of the rule even though the non-BRD equipped nets, still rigged for fishing, were not used in Florida waters. The Florida Marine Patrol will be responsible for enforcement of the proposed rules. Obviously, a Marine Patrol officer’s judgment will be required to determine the existence of an emergency and whether any official action is appropriate. A shrimp boat officer cited for violation of the proposed rules is entitled to challenge the application of the rule.
The Issue The Department of Professional Regulation charged Dr. Samy Hassan Helmy, D.V.M., with violation of Sections 474.215 and 474.214(1)(g), Florida Statutes, for failure to have a premises permit. The primary issue for factual determination is whether Citrus Fair Animal Hospital applied for licensure within thirty days subsequent to its opening. Both parties have submitted post-hearing Proposed Findings of Fact. A ruling has been made on each proposed finding of fact in the Appendix to this Recommended Order.
Findings Of Fact Dr. Helmy is, and has been at all times material herein, a licensed veterinarian in the State of Florida, having been issued license number 0028884 by the Florida Board of Veterinary Medicine. In January of 1985 the wife of Dr. Samy Hassan Helmy purchased real property in Inverness, Florida. Between January 1985 and April 1985 said facility was extensively remodeled to make it suitable as an animal hospital. Dr. Helmy frequently worked at this facility, supervising workmen and participating in the remodeling. On February 19, 1985 an investigator of the Department of Professional Regulation inspected Dr. Helmy's licensed facility in Wildwood, Florida. At that time, Dr. Helmy was not at the facility. Certain equipment required at an animal hospital was not found during this inspection. The inspector called and spoke with Dr. Helmy who was at the Inverness facility, hereinafter referred to as "Citrus Fair." Dr. Helmy advised the inspector that he had the equipment with him. Dr. Helmy told the inspector that he only treated animals at the Wildwood clinic. (See Transcript page 60, line 11-12.) After notice to their customers and the public, Dr. Helmy began to receive patients regularly at the Citrus Fair facility during the first part of April 1985. Dr. Helmy admitted that he had seen animals on an emergency basis at the facility prior to that date as opposed to transporting them to Wildwood; however, the Citrus Fair facility was not open to the public until the first part of April. A receipt for professional services dated April 9, 1985 was introduced into evidence as Respondent's exhibit #2. Although introduced by Respondent, this exhibit was part of the Petitioner's investigative file. An inspection was conducted of the Citrus Fair facility on April 12, 1985 by an employee of the Department of Professional Regulation. At the time of this inspection veterinary medicine was being practiced on the premises. An inspection of the Citrus Fair facility was conducted by an employee of the Department of Professional Regulation on April 19, 1985. At the time of said inspection, veterinary medicine was being practiced on the premises. The Citrus Fair facility is wholly owned by the wife of Dr. Helmy. Dr. Helmy is the professional veterinarian responsible for the Citrus Fair facility. On April 29, 1985, Dr. Helmy's application for licensure of the Citrus Fair facility was received by the Department of Professional Regulation. (See Petitioner's Exhibit #2)
Recommendation Based upon the foregoing findings of fact and conclusions of law, and having determined the Respondent did not violate any of the statutes as alleged, it is recommended that the administrative complaint be dismissed. DONE AND ORDERED this 19th day of February 1986 in Tallahassee, Leon County, Florida. _ STEPHEN F. DEAN, Hearing Officer Division of Administrative Hearings 2009 Apalachee Parkway Tallahassee, Florida 32399 (904) 488-9675 Filed with the Clerk of the Division of Administrative Hearings this 19th day of February 1986. COPIES FURNISHED: Mildred Gardner,Executive Director Board of Veterinary Medicine 130 North Monroe Street Tallahassee, FL 32301 Fred Roche,Secretary Department of Professional Regulation 130 North Monroe Street Tallahassee, FL 32301 Salvatore A. Carpino,General Counsel Department of Professional Regulation 130 North Monroe Street Tallahassee, FL 32301 Cecilia Bradley, Esquire Department of Professional Regulation 130 North Monroe Street Tallahassee, FL 32301 William E. Lackay, Esquire M. C. of Florida Building P. O. Box 279 Bushnell, FL 33513 APPENDIX Respondent's Findings of Fact Adopted. Adopted. Conclusion of Law. Adopted. Adopted. Adopted. Rejected as not relevant. Adopted. It appears Respondent erroneously labeled Conclusions of Law as Findings of Fact. Petitioner's Findings of Fact Adopted. Contrary to facts - rejected. Rejected to the extent the application was dated April 23, 1985. Adopted that application was received on April 29, 1985. Adopted. While true, this proposed finding lacks any reference to when this occurred which is the key issue and is therefore rejected. Rejected. No evidence was submitted showing that Citrus Fair was operated as a veterinary facility on February 18, 1985. Evidence to the contrary was received which is more credible. See TX-60, lines 11-12. Rejected as contrary to evidence on TX-61. The Respondent stated he carried the kits to both clinics, not that he used them at both clinics. Rejected. The proposed facts are not consistent with the testimony on TX 61 & 62 and the facts presented are not probative that veterinary medicine was practiced at the Citrus Fair facility. Rejected. The witness says nothing about going to Wildwood by appointment in TX-70. The statement by Respondent that "he was working between the two offices" is not inconsistent with the Respondent's testimony that he was remodeling the Citrus Fair facility. Adopted. Adopted. Rejected as cumulative of the fact that after April 9, 1985 veterinary medicine was practiced at Citrus Fair. Same as No. 12 above.
