The Issue The issue is whether proposed regulations for Brevard County manatee protection areas by the Florida Fish and Wildlife Conservation Commission (FWCC), which are amendments to Rule 68C- 22.006, Florida Administrative Code, noticed in the April 20, 2001, Florida Administrative Weekly (F.A.W.)("Proposed Rule"), with a Notice of Change published in the F.A.W. on June 15, 2001, are an invalid exercise of legislative authority.
Findings Of Fact Based upon observation of the witnesses and their demeanor while testifying, the documentary evidence received, and the entire record compiled herein, the following material and relevant facts are found. Effective July 1, 1999, Respondent, FWCC became primarily responsible for implementation of the Florida Manatee Sanctuary Act, Section 370.12(2), Florida Statutes (2000) instead of the Department of Environmental Protection, by operation of Section 45, Chapter 99-245, Laws of Florida. FWCC is the State agency responsible for promulgating rules pursuant to Section 370.12, Florida Statutes. Respondent noticed proposed rules, and is a mandatory party to a challenge thereto. Section 120.56(1)(e), Florida Statutes. STANDING OF THE PARTIES McGill, Pritchard, Dovark, Gentile, Akins, Mason, Jaren, Robertson, Standing Watch, Inc., Save the Manatee Club, Inc., Florida Wildlife Federation, Inc., and Sea Ray Boats, Inc.1, are substantially affected by one or more of the Proposed Rules in that they operate motorboats in one or more of the areas proposed for regulation, or in that they represent the interests of members who operate motorboats in one or more of the areas proposed for regulations, or who desire to protect manatees and manatee habitats on behalf of members who derive aesthetic or other benefits from manatees, and who observe or otherwise enjoy manatees in Brevard County and elsewhere. Intervenor, Florida Power and Light Company (FPL), is a Florida corporation that owns and operates the Cape Canaveral Power Plant located in Cocoa, Brevard County, Florida. FPL's operations are specifically addressed in the proposed rule in that the proposed rule creates a no-entry zone along an area bordering the FPL Cape Canaveral Power Plant property boundary including easements and right-of-way where electrical generation operating equipment and electrical distribution and transmission equipment are located. Intervenor, Cocoa Beach is a Florida Municipal Corporation located in Brevard County. The Cocoa Beach Sports Area located with the Banana River Lagoon has been designated since 1988 as an area for water-related recreational activities for the residents of the City of Cocoa Beach and for the general public. The Proposed Rule seeks to impose speed restrictions for boats operating within this area and, if promulgated, will directly regulate and restrict the boating, fishing and other water-related recreational activities of the public within the area. Intervenor, Titusville is a Florida Municipal Corporation located in Brevard County, whose elected body has determined that a substantial number of its residents are substantially affected in the Proposed Rule. The parties alleged facts supported their standing in individual petitions, and the parties stipulated to standing. Therefore, none of the Petitioners presented any evidence regarding their standing. Petitioners and Intervenors are substantially affected by one or more sections of the proposed rule in that they operate motorboats in one or more of the areas proposed for regulation, or they represent the interests of members who operate motorboats in one or more of the areas proposed for regulation or who desire to protect the manatees and manatee habitat on behalf of members who derive aesthetic or other benefits from manatees and who observe or otherwise enjoy manatees in Brevard County. ADOPTION PROCESS FOR THE 2001 RULE PROPOSAL On September 6, 2000, the Commission authorized staff to initiate amendments to the Brevard County rules at a public meeting in Deland, Florida. On October 6, 2000, the Commission published a Notice of Rule Development in the Florida Administrative Weekly and announced a rule development workshop. On October 26, 2000, the Commission staff conducted a rule development workshop in Melbourne, Brevard County, Florida. On January 24, 2001, the Commission directed staff to conduct a second rule development workshop in Brevard County, Florida. On February 16, 2000, the Commission published notice in the Florida Administrative Weekly of the rule development workshop scheduled for March 7, 2000. On March 7, 2000, the Commission staff conducted a second rule development workshop in Viera, Brevard County, Florida. On March 30, 2000, the Commission conducted a public meeting in Tallahassee, Florida, and authorized publication of a Notice of Proposed Rulemaking in the Florida Administrative Weekly. On April 20, 2001, the Commission published a Notice of Proposed Rulemaking in the Florida Administrative Weekly and advertised public hearings to be held on May 3 and May 23, 2001. On May 3, 2001, the Commission staff conducted a public hearing on the Proposed Rule in Melbourne, Brevard County, Florida. On May 23, 2001, the Commission staff conducted a public hearing on the Proposed Rule in Melbourne, Brevard County, Florida. On June 15, 2001, a Notice of Change was published in the Florida Administrative Weekly. There are no algorithms, formulae, protocols, matrices, math models, or metrics used by the Commission to combine the individual data sources into findings that idle-speed, slow-speed, or no-entry zones were required for any specific zone in question. Aerial surveys have been conducted by the Florida Marine Research Institute (FMRI) and others. One type of aerial survey technique is a statewide survey. These surveys are typically flown in the winter, after the passage of a cold front. Typical winter aggregation areas are included in these surveys. The synoptic surveys are used for monitoring winter aggregations of manatees. Population biologists working on manatee recovery view synoptic survey results as the best available information about the minimum estimated size of the manatee population in Florida at this time. The statewide synoptic survey data from the past several years is as follows: 1991 1,268 manatees 1991 1,465 manatees 1992 1,856 manatees 1995 1,443 manatees 1995 1,822 manatees 1996 2,274 manatees 1996 2,639 manatees 1997 2,229 manatees 1997 1,709 manatees 1998 2,022 manatees 1999 2,034 manatees 1999 2,354 manatees 2000 1,629 manatees 2000 2,222 manatees 2001 3,276 manatees During the most recent statewide synoptic survey, portions of Brevard County were observed in five counts made during January 5, 6, and 7, 2001. Of the 591 manatees observed in Brevard County on January 6, 2001, 457 manatees were adjacent to Florida Power and Light Company's thermal discharge, 38 manatees were in Sebastian River, 16 manatees were in Berkley Canal System, and 8 manatees were along the east Banana River shoreline on the southeastern extension of Merritt Island. In addition to statewide surveys, targeted aerial surveys in specific areas are used to establish manatee distribution and relative manatee abundance. These types of surveys are used by the FWCC in assessing manatee use of an area and then establishing manatee protection regulations. The most recent, comprehensive FMRI aerial survey in Brevard County consisted of 45 flights between September 1997 and September 1999. A standardized flight path designed to cover most probable manatee habitats was flown over Brevard County at least once per month during the two-year period at an altitude of approximately 500 feet (except for June 1999, where excessive smoke covered the area); the only area of the county not covered at all was restricted airspace associated with the Kennedy Space Center Complex. The highest number of manatees counted during this survey was 790 manatees in March 1999. General Description of Brevard County. Located in east central Florida, Brevard County is approximately 72 miles north-south and approximately 20 miles east-west. The west boundary of the county is the St. Johns River; the east boundary is the Atlantic Ocean. The Indian River Lagoon in Brevard County extends north of the Kennedy Space Center, at the north end of the county, to Sebastian Inlet, at the south end of the county. Brevard County consists of two major landforms and two major surface waters. From east to west, the geographical features are the Atlantic Ocean, a barrier island running the length of the county, the Indian River Lagoon, and the mainland. Northern Brevard County contains two other major geographical features. The barrier widens to form the Canaveral Peninsula on the east and Merritt Island on the west. Merritt Island is bordered by the Indian River on the west; the Banana River on the east; and the Mosquito Lagoon on the north. At the southern end of Merritt Island, the Banana River joins the Indian River. Besides Sebastian Inlet at the southern boundary of the county, the only navigable connection between the Indian River Lagoon and the Atlantic Ocean is at Port Canaveral. Port Canaveral cuts across the Canaveral Peninsula; along the west shoreline, the Canaveral Locks permit vessels to pass from the Port into the Banana River. The Mosquito Lagoon, Indian River and Banana River are located in a transitional zone between the temperate and tropical zones and form one of the most diverse estuaries in North America. The Indian River Lagoon varies from 0.5 to 5 miles in width and has an average depth of one meter (39.4 inches). The Indian River Lagoon system is not subject to significant periodic lunar tides. The water depths are depicted as mean lower low water, while the shorelines are represented in terms of approximate mean high water. In the lagoon system in Brevard County, the relative water levels rise and fall as influenced by wind, rainfall, storms, and tides. Expert witnesses with local knowledge of the waters acknowledged the variation in water level or relative depth and testified that the water level fluctuates in the Indian River Lagoon by more than three feet and fluctuates by two or two and one-half feet or greater annually. The Indian River Lagoon contains extensive sea grass beds, which are the preferred food for manatees. A bathymetric survey commissioned by the St. Johns River Water Management District determined the acreage of submerged land within the lagoon that can be potentially vegetated with submerged aquatic vegetation at a depth of six feet below mean sea level. Brevard County is the hub of the Atlantic Coast manatee population with a large year-round and a large migratory transient manatee population present throughout the year. THE MANATEE The West Indian manatee (Trichechus manatus) is one of endangered marine mammals in coastal waters of the United States. The West Indian manatee is presently classified as an "endangered species" by the federal Endangered Species Act and has protected status under the Marine Mammal Protection Act. The West Indian Manatee is one of the four living species of the mammalian Order Sirenia, the other three are the West African manatee, the Amazonian manatee and the dugong; the fifth species, Stellar's sea cow, was hunted into extinction. In the southeastern United States, manatees are limited primarily to Florida and Georgia and this group forms a separate subspecies called the Florida manatee (T. manatus latirostris). The Florida manatee (hereinafter "manatee") is a migratory species with a large range of movement along the Atlantic and Gulf Coasts of the United States. During the winter, cold temperatures keep the population concentrated in peninsular Florida, but during the late spring and summer they expand their range and are seen infrequently as far north as Rhode Island, and as far west as Texas. Manatees demonstrate "site fidelity" with some individual mammals adjusting their behavior to take advantage of changes in the availability of resources. Manatees often return to the same winter thermal refuges and the same summer habitats year after year. Manatees prefer water temperatures above 68 degrees F and when ambient water temperatures drop below 68 degrees, they seek warm water refuges, such as spring-fed rivers and power plans discharge outs. Florida Power and Light Company and Reliant Energy Power Plants and the Sebastian River are the primary warm water refuges sought by manatees in Brevard County. For feeding, resting, cavorting, mating and calving, manatees prefer shallow sea grass beds in coastal and riverline habitats with ready access to deep channels, particularly near the mouths of creeks, embayments and lagoons. Manatees sometimes prefer vegetation growing along the banks of waterways, instead of submerged or floating aquatic vegetation. Manatees seek and find sources of fresh water for drinking. In brackish or estuarine environment, they locate fresh water sources, either natural or artificial. They have been observed drinking fresh water at marinas, from air conditioning condensate discharge, from pockets of fresh water floating on the surface of the saltier water, from storm water outfalls and from springs. Typically, six-to-eight hours per day are spent on feeding, usually at one-hour intervals. Intermittently, between two and 12 hours per day are spent resting or sleeping either at the surface of the water or on the bottom. Time not devoted to feeding or sleeping is spent in traveling, socializing or exploring during both day and nighttime hours. The basic social unit consists of a female manatee and her dependent calf. Manatees, apart from winter aggregations at warm water resources and transient mating herds, are semi-social or mildly social mammals. Manatees usually prefer to swim below the surface at one to three meters (3.28 to 9.84 feet) depth, surfacing every few minutes to breathe. They typically have a swimming cruising speed between four and ten KM/HR (2-6 MPH), but can swim in short bursts at up to 25 KM/HR (15 MPH). Manatees have been seen in shallow waters with their backs and heads out of the water and on occasion have been observed fully or partially out of the water to feed or escape pursuing male manatees. Female manatees reach sexual maturity by age five years and males at the age of three to four years. Mating occurs when estrous females are successfully approached by dynamic epherimal mating herds of between five and 20 males (lasting up to four weeks). Female manatees will swim to very shallow water when pursued by mating herds of males as a preventive measure from mating. Manatees have a low reproductive rate and a long life expectancy. Manatee's gestation period is 11 to 14 months with usual birthing of one calf. Dependent calves remain near their mother's side from one to two years, swimming parallel to its mother, directly behind her flipper. Life expectancy for a manatee is in excess of 50 years. A significant decrease in adult survivorship due to, among other things, watercraft collisions could contribute to a long-term population decline. The manatee population in Florida has shown yearly increases resulting in more manatees now than there were in 1976 in the areas of Brevard County that are subject to the Proposed Rules. MANATEE PROTECTION PLANS The United States Fish and Wildlife Service developed an initial recovery plan for West Indian manatees in 1980, primarily for manatees in Florida. The plan was revised in 1989 and 1996. A third revision to the Recovery Plan was noticed for public comment in November 2000, and in July 2001. The recovery plans hereinabove recognized the major human-related cause of manatee mortality is collisions with watercraft. The existing and draft recovery plans state: Because watercraft operators cannot reliably detect and avoid hitting manatees, federal and state managers have sought to limit watercraft speed in areas manatees are most likely to occur to afford boaters and manatees time to avoid collisions. Avoidance technology research is ongoing for deterrent devices designed to "avoid collisions"; however, no device or combination of devices has gained acceptance and approval by the Marine Biological Scientific Community. The Florida Legislature has designated the entire State a refuge and sanctuary for the manatee--the Florida State marine mammal. Section 370.12(2)(b), Florida Statutes. HISTORY OF MANATEE PROTECTION IN BREVARD COUNTY The Florida Legislature initially authorized the adoption of manatee protection rules for Brevard County effective July 1, 1978, when it required the (former) Florida Department of Natural Resources to adopt rules regulating the speed and operation of motorboats between November 15 and March 31, 1978, in those portions of the Indian River within 3/4 mile of the then Orlando Utilities Commission (now Reliant) and Florida Power and Light Company power plant effluents. These rules became effective on March 19, 1997 (former Rule 16N-22.06, Florida Administrative Code ("Brevard County Manatee Protection Rules" or "BCMPR"). In 1989, a strategy to improve manatee protection in 13 key counties was approved by the Governor and Cabinet. The strategy called for development of manatee protection plans, for boat facility siting criteria, for priority land acquisition of critical manatee use areas, and improved aquatic preserve management for sea grass protection. Guidelines for implementation included new or expanded speed zones, refuges or sanctuaries for the regulation of boat speeds in critical manatee areas. Financial assistance was given Brevard County for its manatee protection plan in 1993. After creation of the FWCC, effective July 1, 1999, the BCMPR and other manatee protection rules were transferred from Florida Department of Environmental Protection (FDEP) to the FWCC, and the Secretary of State renumbered the prior rules to Chapter 68C-22, Florida Administrative Code. In 1994, FDEP amended BCMPR to establish manatee protection zones in the Canaveral Barge Canal and portions of adjacent areas of the Indian and Banana Rivers; to expand the existing "slow speed" zone in Sykes Creek (north of "S Curve") to include the channel; to establish a maximum 25 MPH zone in the Sykes Creek channel between Sykes Creek Parkway and the "S Curve"; and to renumber and correct map inconsistencies. This site- specific rule-making action was taken in response to proposed additional threats to manatees resulting from development of Abby Marina (now Harbortown Marina), pending completion of Brevard County comprehensive countywide manatee protection plan. In 1998, FDEP amended the BCMPR to establish seasonal "motorboats prohibited" and "no-entry" zones at the then Orlando Utilities Commission's (now Reliant) power plant and a seasonal "no-entry" zone at Florida Power and Light Company's power plant. THE PROPOSED MANATEE PROTECTION RULE AMENDMENTS FOR BREVARD COUNTY 1906 Section II - Proposed Rules THE FULL TEXT OF THE PROPOSED RULES IS: (Substantial rewording of Rule 68C-22.006 follows. See Florida Administrative Code for present text.) 68C-22.006 Brevard County Zones. The Commission hereby designates the waters within Brevard County, as described below, as areas where manatee sightings are frequent and where it can be assumed that manatees inhabit on a regular, periodic or continuous basis. The Commission has further determined that a likelihood of threat to manatees exists in these waters as a result of manatees and motorboats using the same areas. The primary purpose of this rule is to protect manatees from harmful collisions with motorboats and from harassment by regulating the speed and operation of motorboats within these designated areas. A secondary purpose is to protect manatee habitat. In balancing the rights of fishers, boaters, and water skiers to use these waterways for recreational and commercial purposes (as applicable under 370.12(2)(j), F.S.) with the need to provide manatee protection, the Commission has examined the need for unregulated areas or higher speed travel corridors through regulated areas. Such areas or corridors are provided in those locations where the Commission determined, on the basis of all available information, (1) there is a need for the area or corridor and (2) the area or corridor will not result in serious threats to manatees or their habitat. Unregulated areas or higher speed corridors are not provided in locations where both of the above findings were not made. The following year-round and seasonal zones are established, which shall include all associated and navigable tributaries, lakes, creeks, coves, bends, backwaters, canals, and boat basins unless otherwise designated or excluded. As used in this rule, ICW means the Intracoastal Waterway. Access to the NO ENTRY and MOTORBOATS PROHIBITED zones designated in paragraphs (2)(a) and (b) will be provided in accordance with procedures set forth in subsection (4), hereunder, and applicable provisions of Rule 68C-22.003. NO ENTRY (November 15 – March 31) Indian River, Reliant Corporation Delespine Power Plant Area: All waters within the discharge canal of the Reliant Corporation Delespine power plant, and; All waters southerly of a line extending eastward from and following the same bearing as the southernmost seawall of the power plant discharge canal, with said line bearing approximately 70º, westerly of a line 250 feet east of and parallel to the western shoreline of the Indian River, and northerly of the jetty on the north side of the power plant intake canal. Indian River, FPL Frontenac Power Plant Area: All waters in the vicinity of the Florida Power and Light (FPL) Frontenac power plant southerly of a line connecting the northern guy wires of the power poles immediately north of the FPL Unit 2 discharge area from the western shoreline of the Indian River to the third power pole east of the western shoreline (approximately 1,650 feet east of the shoreline), and westerly of a line running from said third power pole to the easternmost point (approximate latitude 28º 28' 07" North, approximate longitude 80º 45' 19" West) of the jetty on the north side of the FPL intake canal. MOTORBOATS PROHIBITED (All Year, except as noted) Indian River, Reliant Corporation Delespine Power Plant Area: All waters in the vicinity of the Reliant Corporation Delespine power plant southerly of a line bearing 90º from a point (approximate latitude 28º 29' 41" North, approximate longitude 80º 46' 35" West) on the western shoreline of the Indian River 95 feet north of the northernmost seawall of the power plant discharge canal, westerly of a line 250 feet east of and parallel to the western shoreline of the Indian River, and northerly of a line extending eastward from and following the same bearing as the southernmost seawall of the power plant discharge canal, with said line bearing approximately 70º. This zone is in effect from November 15 through March 31. C-54 Canal: All waters of the C-54 Canal (South Florida Water Management District Canal 54) east of the spillway (approximate latitude 27º 49' 50" North, approximate longitude 80º 32' 24" West) and west of a line drawn perpendicular to the northern shoreline of the C-54 Canal at a point (approximate latitude 27º 49' 55" North, approximate longitude 80º 32' 00" West) on the northern shoreline 2,500 feet east of the spillway. IDLE SPEED (All Year, except as noted) Indian River, Power Plant Area: All waters west of the western boundary of the ICW channel, south of a line bearing 90° from a point (approximate latitude 28º 30' 13" North, approximate longitude 80º 46' 48" West) on the western shoreline of the Indian River approximately three-fourths of a mile north of the Delespine power plant discharge canal, and north of a line bearing 90° from a point (approximate latitude 28º 27' 27" North, approximate longitude 80º 45' 43" West) on the western shoreline of the Indian River approximately three-fourths of a mile south of the Frontenac power plant discharge canal, except as otherwise designated under (2)(a) and (b)1. This zone is in effect from November 15 through March 31. Banana River, Cape Canaveral Area: All waters north of a line bearing 270° from the southwesternmost point (approximate latitude 28º 23' 29" North, approximate longitude 80º 37' 10" West) of Long Point in Cape Canaveral to a point (approximate latitude 28º 23' 29" North, approximate longitude 80º 37' 49" West) in the Banana River approximately 3,500 feet west of Long Point, and east of a line bearing 331° from said point in the Banana River to a point (approximate latitude 28º 24' 16" North, approximate longitude 80º 38' 19" West) on the State Road 528 Causeway (west of State Road 401). Section II - Proposed Rules 1907 Banana River, Manatee Cove Area: All waters of Manatee Cove (on the east side of the Banana River, just south of State Road 520) east of a line at the mouth of the cove running between a point (approximate latitude 28º 21' 21" North, approximate longitude 80º 36' 52" West) on the northern shoreline and a point (approximate latitude 28º 21' 09" North, approximate longitude 80º 36' 51" West) on the southern shoreline. Turkey Creek: All waters of Turkey Creek north and east (downstream) of Melbourne- Tillman Drainage District structure MS-1 and south and west of a line at the mouth of Turkey Creek that runs from the southeasternmost point (approximate latitude 28º 02' 21" North, approximate longitude 80º 34' 48" West) of Castaway Point to the northeasternmost point (approximate latitude 28º 02' 14" North, approximate longitude 80º 34' 43" West) of Palm Bay Point. Sebastian Inlet Area: All waters of the cove on the northern side of Sebastian Inlet (commonly known as Campbell Cove) northwest of a line running between the two rock jetties at the entrance to the cove. Sebastian River Area: All waters of the North Prong of Sebastian River, and; All waters of the North Fork Sebastian River (also known as Sebastian Creek) and the C-54 Canal west of a north-south line from a point (approximate latitude 27º 50' 08" North, approximate longitude 80º 31' 02" West) on the northern shoreline of the North Fork Sebastian River at the intersection of the river and the North Prong and east of a line drawn perpendicular to the northern shoreline of the C-54 Canal at a point (approximate latitude 27º 49' 55" North, approximate longitude 80º 32' 00" West) on the northern shoreline 2,500 feet east of the spillway. SLOW SPEED (All Year) Mosquito Lagoon: All waters west of the ICW channel, south of the Volusia County/Brevard County line, and north of ICW channel marker “43,” and; All waters of Mosquito Lagoon (including the ICW channel) south of ICW channel marker “43,” southwest of a line commencing at ICW channel marker “43” and then running to ICW channel marker “45” and then on a bearing of 132° for a distance of 1,000 feet to the line’s terminus at a point in Mosquito Lagoon (approximate latitude 28º 44' 35" North, approximate longitude 80º 44' 35" West), and north of a line running from said point in Mosquito Lagoon on a bearing of 221° to the western shoreline of Mosquito Lagoon. Indian River, Turnbull Basin Area: All waters south and east of a line commencing at a point (approximate latitude 28º 44' 36" North, approximate longitude 80º 46' 19" West) on the eastern shoreline of Turnbull Basin (about one mile north of Haulover Canal) and then bearing 193° to a point 1,500 feet northwest of the ICW channel, then running in a southwesterly direction 1,500 feet northwest of and parallel with the ICW channel to a point (approximate latitude 28º 41' 22" North, approximate longitude 80º 49' 05" West) 1,500 feet northwest of ICW channel marker “12,” and then running in a southerly direction 1,500 feet west of and parallel with the ICW channel to the Florida East Coast Railroad Bridge, including all waters west of the ICW channel and south of an east-west line 1,500 feet north of the point where the Florida East Coast Railroad Bridge crosses over the ICW, but excluding the ICW channel as designated under (2)(e)2. Indian River, Titusville Area: All waters south of the Florida East Coast Railroad Bridge, east of the ICW channel, and north of an east-west line 1,200 feet south of the point where the Florida East Coast Railroad Bridge crosses over the ICW, and; All waters west of the ICW channel south of the Florida East Coast Railroad Bridge and north of the State Road 402 Bridge and Causeway. Indian River, State Road 402 (Max Brewer Causeway) to State Road 405 (NASA Parkway): All waters within 2,000 feet of the general contour of the western shoreline of the Indian River, excluding the ICW channel where the channel is less than 2,000 feet from the western shore; All waters within one mile of the general contour of the eastern shoreline of the Indian River south and east of a point (approximate latitude 28º 36' 04" North, approximate longitude 80º 44' 44" West) on the western shoreline of Peacock’s Pocket (northwest of Banana Creek), and; All waters south of an east-west line 3,400 feet north of the point where the State Road 405 Bridge crosses over the ICW, excluding the ICW channel as designated under (2)(e)3. Indian River, State Road 405 (NASA Parkway) to State Road 528 (Bennett Causeway): All waters north of an east-west line 3,000 feet south of the point where the State Road 405 Bridge crosses over the ICW, excluding the ICW channel as designated under (2)(e)3.; All waters west of the ICW channel and north of the overhead power transmission line that crosses the western shoreline of the Indian River approximately 1,200 feet north of State Road 528, excepting those areas otherwise designated for seasonal regulation under (2)(a), (b)1., and (c)1. when said seasonal zones are in effect; All waters south of said overhead power transmission line and west of a north-south line running through the second power pole east of the western shoreline; All waters within one-half mile of the eastern shoreline of the Indian River north of a point (approximate latitude 28º 25' 47" North, approximate longitude 80º 43' 24" West) on the eastern shoreline of the Indian River 1,500 feet south of the canal on the southern side of Meadow Lark Lane, including all waters of Rinkers Canal, and; All waters east of the ICW channel and south of the overhead power transmission line that crosses the eastern shoreline of the Indian River approximately 3,900 feet north of State Road 528. Indian River, State Road 528 (Bennett Causeway) to State Road 518 (Eau Gallie Causeway): All waters within 1,000 feet of the general contour of the western shoreline of the Indian River; All waters south of State Road 528 and within 1908 Section II - Proposed Rules 500 feet of the State Road 528 Causeway, within 500 feet of the State Road 520 Causeway, within 500 feet of the State Road 404 Causeway, and north of State Road 518 and within 500 feet of the State Road 518 Causeway; All waters within 1,000 feet of the general contour of the eastern shoreline of the Indian River between State Road 528 and State Road 520; All waters east of the ICW channel from State Road 520 to an east-west line 300 feet south of the southernmost point (approximate latitude 28º 19' 22" North, approximate longitude 80º 42' 00" West) of the spoil island east of ICW channel marker “80,” and; All waters within 500 feet of the general contour of the eastern shoreline of the Indian River south of the aforementioned east-west line and north of State Road 404 (Pineda Causeway). Indian River, State Road 518 (Eau Gallie Causeway) to Cape Malabar: All waters within 1,000 feet of the general contour of the eastern shoreline of the Indian River; All waters south of State Road 518 and within 500 feet of the State Road 518 Causeway and within 500 feet of the State Road 192 Causeway; All waters within 1,000 feet of the general contour of the western shoreline of the Indian River south of State Road 518 and north of the easternmost point (approximate latitude 28º 02' 24" North, approximate longitude 80º 34' 48" West) of Castaway Point (including all waters of the Eau Gallie River and Crane Creek), and; All waters south of said easternmost point of Castaway Point, north of Cape Malabar, and west of a line commencing at a point (approximate latitude 28º 02' 29" North, approximate longitude 80º 34' 38" West) in the Indian River 1,000 feet northeast of said easternmost point of Castaway point, then bearing 130° to the westernmost point (approximate latitude 28º 02' 15" North, approximate longitude 80º 34' 19" West) of the spoil site west of ICW channel marker “14,” then bearing 153° to the westernmost point (approximate latitude 28º 01' 32" North, approximate longitude 80º 33' 55" West) of the spoil site southwest of ICW channel marker “15,” then bearing 138° to the line’s terminus at a point (approximate latitude 28º 01' 12" North, approximate longitude 80º 33' 35" West) in the Indian River approximately 2,400 feet northeast of Cape Malabar. Indian River, Cape Malabar to Grant: All waters within 1,000 feet of the general contour of the eastern shoreline of the Indian River south of Cape Malabar and north of a point (approximate latitude 27º 55' 59" North, approximate longitude 80º 30' 30" West) on the eastern shoreline of the Indian River (north of Mullet Creek); All waters south of Cape Malabar, north of the spoil island between ICW channel markers “25” and “27,” and west of a line commencing at a point approximate latitude 28º 01' 12" North, approximate longitude 80º 33' 35" West) in the Indian River approximately 2,400 feet northeast of Cape Malabar, then bearing 157° to the easternmost point (approximate latitude 28º 00' 26" North, approximate longitude 80º 33' 13" West) of the spoil site between ICW channel markers “16” and “17,” then bearing 152° to the easternmost point (approximate latitude 27º 59' 21" North, approximate longitude 80º 32' 35" West) of the spoil island west of ICW channel marker “22,” then bearing 166° to the line’s terminus at the easternmost point (approximate latitude 27º 57' 50" North, approximate longitude 80º 32' 10" West) of the spoil island between ICW channel markers “25” and “27;” All waters within 1,000 feet of the general contour of the western shoreline of the Indian River south of said spoil island between ICW channel markers “25” and “27,” and north of ICW channel marker “35,” and; All waters west of the ICW channel between ICW channel markers "35" and “38.” Indian River, Grant to the Indian River County Line: All waters west of the ICW channel between ICW channel marker "38" and the Brevard County/Indian River County line, including those waters east of the centerline of the U.S. 1 Bridge over the Sebastian River, and: All waters within 1,500 feet of the general contour of the eastern shoreline of the Indian River, south of a point (approximate latitude 27º 55' 59" North, approximate longitude 80º 30' 30" West) on the eastern shoreline of the Indian River (north of Mullet Creek) and north of an east-west line running through ICW channel marker “59” (approximate latitude 27º 51' 38" North, approximate longitude 80º 28' 57" West), including those waters within 1,500 feet west of the westernmost edge of the Mullet Creek Islands, within 1,500 feet west of the westernmost edge of the islands south of Mathers Cove, within 1,500 feet west of the westernmost edge of Long Point, and within 1,500 feet west of the westernmost extensions of Campbell Pocket south to said east-west line running through ICW channel marker “59,” and; All waters of the Indian River and Sebastian Inlet east of the ICW channel, south of said east-west line running through ICW channel marker “59,” north of the Brevard County/Indian River County line, and west of a line 200 feet southwest of and parallel with the centerline of the State Road A1A Bridge, except as otherwise designated under (2)(c)5. and excluding the marked Sebastian Inlet channel. Sebastian River Area: All waters of the Sebastian River (including waters also known as San Sebastian Bay), the South Fork San Sebastian River (also known as St. Sebastian River, Sebastian River and Sebastian Creek), and the North Fork Sebastian River (also known as Sebastian Creek) within Brevard County west of the centerline of the U.S. 1 Bridge and east of a north-south line from a point (approximate latitude 27º 50' 08" North, approximate longitude 80º 31' 02" West) on the northern shoreline of the North Fork Sebastian River at the intersection of the river and the North Prong of Sebastian River. Canaveral Barge Canal: All waters of the Canaveral Barge Canal east of the general contour of the eastern shoreline of the Indian River and west of the general contour of the western shoreline of the Banana River. Sykes Creek and Kiwanis Basin: All waters of Sykes Creek and Kiwanis Basin south of the Canaveral Barge Canal and north of the centerline of State Road 520. Section II - Proposed Rules 1909 Newfound Harbor: All waters south of State Road 520 and within 1,000 feet of the State Road 520 Bridge and Causeway; All waters within 1,000 feet of the general contour of the western shoreline of Newfound Harbor north of the runway for the Merritt Island Airport (approximately one mile south of State Road 520), and; All waters within 1,000 feet of the general contour of the eastern shoreline of Newfound Harbor and an extension of said shoreline to a point 1,000 feet south of Buck Point. Banana River, North of State Road 528: All waters within 1,500 feet of the general contour of the western shoreline of the Banana River south of a point (approximate latitude 28º 26' 10" North, approximate longitude 80º 39' 35" West) on the shoreline near Kars Park on the boundary of the federal No Motor zone; All waters south of an east-west line running through the westernmost point (approximate latitude 28º 24' 42" North, approximate longitude 80º 38' 34" West) of the first spoil island north of the Canaveral Locks (commonly known as Ski Island), including those waters in Port Canaveral west of State Road 401, and; All waters east and south of a line commencing at the northernmost point (approximate latitude 28º 24' 44" North, approximate longitude 80º 38' 32" West) of Ski Island, then running to the southernmost point (approximate latitude 28º 24' 55" North, approximate longitude 80º 38' 31" West) of the second spoil island north of the Canaveral Locks, then following the eastern shoreline of said spoil island to its northernmost point, then bearing 6° to a point (approximate latitude 28º 25' 09" North, approximate longitude 80º 38' 29" West) in the Banana River underneath the overhead power transmission line south of the third spoil island north of Canaveral Locks, then following said transmission line (which is the boundary of the federal No Motor zone) in an easterly direction to the line’s terminus at a point (approximate latitude 28º 25' 16" North, approximate longitude 80º 36' 13" West) on the eastern shoreline of the Banana River. Banana River, State Road 528 to State Road 520: All waters south of State Road 528 and north of an east-west line 1,000 feet south of the point where the State Road 528 Bridge crosses over the main Banana River channel, except as otherwise designated under (2)(c)2.; All waters west of a line running from a point (approximate latitude 28º 24' 16" North, approximate longitude 80º 39' 30" West) on the State Road 528 Causeway east of the western State Road 528 Relief Bridge to a point (approximate latitude 28º 21' 26" North, approximate longitude 80º 39' 32" West) on the State Road 520 Causeway approximately 1,200 feet west of the water storage tanks, and; All waters south of a line bearing 270° from the southwesternmost point (approximate latitude 28º 23' 29" North, approximate longitude 80º 37' 10" West) of Long Point in Cape Canaveral to a point (approximate latitude 28º 23' 29" North, approximate longitude 80º 37' 49" West) in the Banana River approximately 3,500 feet west of Long Point, and east of a line bearing 174° from said point in the Banana River to a point (approximate latitude 28º 21' 28" North, approximate longitude 80º 37' 35" West) on the State Road 520 Causeway approximately 1,000 feet west of Cape Canaveral Hospital Complex. Banana River, Cocoa Beach Area: All waters south of State Road 520 and within 1,000 feet of the State Road 520 Causeway, excluding the main Banana River channel; All waters within 1,000 feet of the general contour of the western shoreline of the Banana River, south of State Road 520 and north of Buck Point and an extension of said shoreline to a point 1,000 feet south of Buck Point, excluding the main Banana River channel where the channel is less than 1,000 feet from the western shoreline, and; All waters east of a line commencing at a point (approximate latitude 28º 21' 25" North, approximate longitude 80º 38' 30" West) on the State Road 520 Causeway (approximately 2,000 feet east of the State Road 520 Bridge over the main Banana River channel), then bearing 190° to a point (approximate latitude 28º 19' 15" North, approximate longitude 80º 38' 55" West) in the Banana River approximately 1,900 feet west of the northwesternmost point of the Cocoa Beach Municipal Park, then bearing 270° to a point (approximate latitude 28º 18' 38" North, approximate longitude 80º 38' 55" West) in the Banana River approximately 1,700 feet west of the southwesternmost point of the Cocoa Beach Municipal Park, then bearing 171° for approximately 3,000 feet to a point (approximate latitude 28º 18' 07" North, approximate longitude 80º 38' 50" West) in the Banana River east of channel marker “15,” then bearing 124° to a point (approximate latitude 28º 16' 52" North, approximate longitude 80º 36' 45" West) in the Banana River 1,000 feet west of the eastern shoreline of the Banana River, then heading in a southerly direction 1,000 west of and parallel with the eastern shoreline of the Banana River to the line’s terminus at a point (approximate latitude 28º 15' 51" North, approximate longitude 80º 36' 38" West) in the Banana River near the northern boundary of Patrick Air Force Base. Banana River, South of Cocoa Beach to State Road 404 (Pineda Causeway): All waters south of an east-west line running through the southernmost point (approximate latitude 28º 16' 19" North, approximate longitude 80º 39' 25" West) of the more southerly of the two islands east of Macaw Way (on Merritt Island) and west of a line bearing 162° from said southernmost point to State Road 404; All waters south and east of the overhead power transmission line in the Banana River adjacent to Patrick Air Force Base, and; All waters north of the centerline of State Road 404 and within 2,000 feet of the State Road 404 Bridges and Causeway, excluding the main Banana River channel as designated under (2)(e)5. Banana River, South of State Road 404 (Pineda Causeway): All waters south of the centerline of State Road 404, including those waters east of a line bearing 270° from the southernmost point (approximate latitude 28º 08' 32" North, approximate longitude 80º 36' 15" West) of Merritt Island 1910 Section II - Proposed Rules (commonly known as Dragon Point) to the Eau Gallie Causeway, excluding the main Banana River channel as designated under (2)(e)5. 25 MPH (All Year) Mosquito Lagoon: All waters in the ICW channel south of the Volusia County/Brevard County line and north of ICW channel marker “43” (north of Haulover Canal). Indian River, Turnbull Basin and Titusville Area: All waters in the ICW channel southwest of ICW channel marker “1” (southwest of Haulover Canal) and north of an east-west line 1,200 feet south of the point where the Florida East Coast Railroad Bridge crosses over the ICW. Indian River, State Road 405 (NASA Parkway) Area: All waters in the ICW channel south of an east-west line 3,400 feet north of the point where the State Road 405 Bridge crosses over the ICW and north of an east-west line 3,000 feet south of the point where the State Road 405 Bridge crosses over the ICW. South Indian River Area: All waters in the ICW channel south of ICW channel marker “59” and north of the Brevard County/Indian River County line. South Banana River Area: All waters in the main Banana River channel south of a point in the channel 2,000 feet north of the State Road 404 Bridge, and north of a point (approximate latitude 28º 09' 15" North, approximate longitude 80º 36' 32" West) in the channel on the northern boundary of the local Idle Speed zone approximately 1,900 feet north of the Mathers Bridge. Commercial Fishing and Professional Fishing Guide Permits: The following provisions pertain to the issuance of permits to allow individuals engaged in commercial fishing and professional fishing guide activities to operate their vessels in specified areas at speeds greater than the speed limits established under subsection (2) above. Procedures related to the application for and the review and issuance of these permits are as set forth in 68C-22.003, Florida Administrative Code. Permits shall be limited as follows: Permits shall only be available for the zones or portions of zones described under (2)(d)1. through (2)(d)9., and (2)(d)13. through (2)(d)18. Permits shall not apply on weekends or on the holidays identified in s. 110.117, F.S. Permit applications may be obtained at the Commission’s Law Enforcement office at 1-A Max Brewer Memorial Parkway in Titusville or by contacting the Commission at Mail Station OES-BPS, 620 South Meridian Street, Tallahassee, Florida 32399 (850-922-4330). Access to the NO ENTRY and MOTORBOATS PROHIBITED zones is allowed for Reliant Corporation employees or their authorized agents (for the zones designated under (2)(a)1. and (b)1.) and for Florida Power and Light Company employees or their authorized agents (for the zone designated under (2)(a)2.) provided that entry into the zones is necessary to conduct activities associated with power plant maintenance, emergency operations or environmental monitoring. The Commission must receive notification of the activity prior to its commencement. In the event of an emergency activity, the Commission shall be notified no more than one week after the activity has been commenced. All vessels used in the operation or associated with the activity shall be operated at no greater than Idle Speed while within the zones and must have an observer on board to look for manatees. The zones described in 68C-22.006(2) are depicted on the following maps, labeled “Brevard County Manatee Protection Zones.” The maps are intended as depictions of the above-described zones. In the event of conflict between the maps and descriptions, the descriptions shall prevail. DATA SOURCES CONSIDERED BY FWCC IN PROMULGATING THE PROPOSED RULE FWCC's staff who were primarily responsible for the development of the recommended revisions to the BCMPR to the FWCC included: Scott Calleson, who holds a Bachelor of Science degree in Marine Science and a Masters of Science degree with emphasis on Environmental Planning and Natural Resource Management, and has worked with manatee protection rules since 1992; David Arnold, who holds both a Bachelor of Science degree in Biology and a Master of Science degree in Biological Oceanography, and who supervised the Department of Environmental Protection's marine turtle protection program prior to becoming Chief of the Bureau of Protected Species Management in 1995; and Dr. Charles Deutsch, who has both a Bachelor of Science and a Doctorate degree in Biology with specialization in biology of marine mammals and behavior, animal behavior and behavioral ecology, and worked for the United States Geological Survey (USGS) in a number of analyses of manatee radio tracking along the Atlantic Coast. The verbal, narrative and graphical presentations of the experts were relied upon in making recommendations to the FWCC for the proposed rule revisions. FWCC's staff gave good faith consideration to the experts' opinions, publications, articles, data analysis, and reasonable inferences and predictions. MANATEE MORTALITY DATA FWCC relied upon manatee mortality data in evaluating manatee inhabitation (Brevard County Mortality Information and Brevard County Misc. Information), including FMRI manatee salvage database for Brevard County from January 1974 to December 2000 (including carcass recovery location and cause of death). AERIAL SURVEY DATA In evaluating manatee inhabitation, FWCC relied upon manatee aerial survey data in existing manatee inhabitations. Included in this process were: information on aerial surveys performed for Kennedy Space Center by Dynamic Corporation; Geographic Information System information for FMRI's 1997-1999 Brevard County aerial survey along with data in "Seasonal Manatee Distribution and Relative Abundance in Brevard County, Florida, 1997-1999"; Geographic Information System data from earlier Brevard County aerial surveys; and aerial surveys conducted by the Florida Marine Research Institute and others. Aerial Surveys Aerial surveys have been conducted by the Florida Marine Research Institute and others using various techniques. One type of aerial survey technique is a statewide survey. These surveys are typically flown in the winter, after the passage of a cold front. Typical winter aggregation areas are included in these surveys. The synoptic surveys are used for monitoring winter aggregations of manatees. Population biologists working on manatee recovery view synoptic survey results as the best available information about the minimum estimated size of the manatee population in Florida at this time. The statewide synoptic survey data from the past several years is as stated in Finding of Fact 23 herein above. In addition to statewide surveys, targeted aerial surveys in specific areas are used to establish manatee distribution and relative manatee abundance. The commission in assessing manatee use of an area and then establishing manatee protection regulations uses these types of surveys. SYNOPTIC AERIAL SURVEYS Considered by FWCC was the statewide synoptic survey for the period 1991 to 2001. These surveys are used for monitoring winter aggregation of manatees and provide a minimum estimate of the number of manatees observed. Population biologists view synoptic survey results as the best available information source to estimate the minimum size of the manatee population in Florida at the present time. The statewide synoptic survey data for the years 1991-2001 are detailed in paragraph 22 herein above. The Berkeley Canal system location, where manatees were observed on January 6, 2001, has four connecting canals to the eastern shoreline of the Banana River; the northernmost connection is just south of the Pineda Causeway and the southernmost connecting canal is located about three and three-fourths miles to the south between Carter's Cut and the Mathers Bridge. The West Banana River shoreline locations where manatees were observed on January 6, 2001, is the Banana River Marina. MANATEE DISTRIBUTION AND RELATIVE ABUNDANCE Targeted aerial surveys in specific areas are used to establish manatee distribution and relative manatee abundance. They are used in assessing manatee use of an area and then in establishing manatee protection regulations in those areas. Forty-five flights between September 1997 and September 1999 are the most comprehensive and recent FMRI aerial surveys in Brevard County. Aerial surveys possess an inherent bias because the location of animals can only be seen during daylight hours and do not account for nighttime locations. FWCC's aerial survey data were presented in various forms: raw data entry sheets completed by the surveyors; a composite, GSI plot of the data points for Brevard County; small- format GIS plots of data points that depicted manatees seen by month; and small-format GIS plots of data points that depicted manatees seen during each flight, along a flight path. Before the 1997-1999 Bervard survey, relative abundance and distribution surveys for portions of Brevard County were conducted in late-1985 through early-1987. The 1985-87 Banana River surveys included only the area between Launch Complex 39B and Eau Gallie, but included portions of Canaveral Barge Canal, Sykes Creek and Newfound Harbor. Flights were flown over the Cocoa Beach area during morning hours for a nine-month period (March 3, 1990- November 27, 1990), and showed more than one manatee during each flight, with one exception on March 3, 1990. SATELLITE TELEMETRY DATA AND VHF RADIO TELEMETRY DATA The FWCC relied upon manatee telemetry data in evaluating manatee inhabitation for Brevard County. Included in the satellite and VHF radio telemetry data relative to inhabitation was a GIS database obtained from the "United States Geological Survey (USGS) Biological Resources Division, Florida Carribean Science Center, Sirenia Project, Gainesville, Florida," and reports authored by Dr. Charles Deutsch who analyzed the USGS data. The USGS Sirenia Project data analyzed by Dr. Deutsch were collected from May 1986 to May 1998, and included both VHF radio and telemetry and satellite telemetry data for the 78 manatees that were tagged for varying amounts of time during that period along the lower East Coast of the United States, excluding data for manatees that were born and raised in captivity. This data was considered by Dr. Deutsch as the best telemetry data available. Of the full USGS Sirenia Project data evaluated by Dr. Deutsch, 61 manatees were tracked at some time during the study period in Brevard County, including 16 manatees that were only tracked using VHF radio tracking and not satellite telemetry. The maximum number of tagged manatees observed in Brevard County during the study period was 12 manatees at one time. Dr. Deutsch opined that about one or two percent of the documented East Coast manatee sub-population was tracked each year. The radio telemetry data subsets from the Sirenia Project covered a ten-year period from May 1986, and included over 6,000 manatee observations for 54 individual tagged manatees. Of those 6,000 observation points, three-quarters (almost 5,000) were actual visual sighting of manatees made by persons on shore or in vessels. Of those visual sightings, approximately ten percent were made by non-government employees. The satellite telemetry data evaluated by Dr. Deutsch included data for 45-tagged manatees that was collected from April 1987 to May 1998, with over 34,000 location records of Class 1, 2, or 3 accuracy. Of the 61-tagged manatees that were observed in Brevard County during the 12-year study period, the median tracking period was 135 days, with some animals tracked for several years while others were tracked for shorter periods of time. Of the 61 manatees tracked in Brevard County, approximately one-half were fitted with radio or satellite telemetry transmitters (tags) while in Brevard County, the other half were tagged in different areas of northeast Florida, in southeast Georgia, or in southeast Florida. A majority of the animals tagged outside of Brevard County were observed in Brevard County, and Dr. Deutsch opined that this data demonstrated Brevard County to be the hub of manatee activity along the Atlantic Coast. MIGRATORY RANGE OF TAGGED MANATEES The size of the migratory ranges of tracked manatees varied with considerable variation of movement by individual manatees in Brevard County. Some manatees would spend eight months of the year near Canaveral Sewer Plant (Banana River) and spend each winter near Port Everglades (Ft. Lauderdale). Many tagged manatees displayed strong site-fidelity, returning to the same seasonal locations yearly while others did not. Telemetry data points are not precisely a depiction of the actual and true location of the manatee at the time of data transmission from the tag to the satellite. Services Argos, the company that administers the hardware, assigned 68 percent of the data points within 150 meters of the true location in class three locations. In 1994, USGS performed accuracy experiments in Brevard County of satellite telemetry and found location class 3 data points to be within 225 meters of the true location, and 95 percent within 500 meters of the true location. In addition to Dr. Deutsch's reports, FWCC considered various telemetry papers and publications pertaining to Brevard County: "Tagged Manatee Use of the Cocoa Beach/Thousand Island Area;" "Winter Movements and Use of Warm-water Refugia by Radio- tagged West Indian Manatees Along the Atlantic Coast of the United States;" and "Easton, Tagged Manatee Movement through the Canaveral Barge Canal, Brevard County Florida" (February 14, 1997). MANATEE SIGHTING DATA FWCC relied upon manatee sighting data in its evaluation of manatee inhabitation. Included in the sighting data was the Brevard County 2001 Rule Development and Trip Notes of February 6- 7, 2001; Sea Ray Boats, Inc. Water Test Re-Run Manatee Sighting Records for 2000-2001; Canaveral Barge Canal Boater Activity and Compliance Study; Sharon Tyson's Sykes Creek Observation Records; and cold-seasons sighting logs for the C-54 canal structure. STUDIES AND REPORTS PERTAINING TO MANATEE DISTRIBUTION, RELATIVE ABUNDANCE, HABITAT, BEHAVIOR, OR OTHER MANATEE INFORMATION. FWCC considered and relied upon the Brevard County Manatee Protection Plan that included an inventory and analysis section about manatees, analysis of manatee mortality data, manatee legislation and protection, law enforcement, habitat issues, existing boat facilities, Brevard County boating activity patterns, and an inventory of present manatee education programs. The existing Federal Manatee Recovery Plan, to which members of the Bureau of Protected Species and Florida Marine Research Institute contributed, was relied upon. SCAR CATALOG DATA FWCC considered and relied upon scar catalog data in evaluating manatee protection needs with Brevard County Misc. Information as the source provider. EXPERT OPINIONS FWCC relied upon expert opinions in evaluating manatee inhabitation. A staff meeting with manatee experts, as part of the process, included, but was not limited to, meetings with Jane Provancha and Sharon Tyson in December 2000, meetings and discussions with Dr. Charles Deutsch between November 2000 and May 2001, and various discussions with members of the federal Recovery Plan Team. OTHER AVAILABLE SITE-SPECIFIC INFORMATION FWCC considered site-specific information that was available, principally drafts of the Brevard County Manatee Protection Plan. FWCC also considered site-specific information about water skiing areas and prospective additional travel times in various waters proposed for new, or changed, regulations. DATA ANALYSIS Threat Analysis Rule 68C-22.001(3), Florida Administrative Code, contemplates a qualitative assessment and exercise of discretion by taking into consideration a balancing of manatee protection needs, including an assessment of relative threats to manatees, with the right of boaters, fishers and water skiers. In assessing where threats to manatees may exist from motorboats, the manatee death database provides information on confirmed interactions, such as locations where manatee carcasses have been recovered. Manatee deaths, carcass recovery and confirmed interactions locations are maintained in FMRI's database. From January 1974 to December 2000, 728 manatees died in Brevard County and 184 of those deaths were because of interactions with watercrafts. Watercraft related deaths account for 23.5 percent of all manatee deaths recorded in Brevard County between 1974 and 2000. Approximately 19 percent of all watercraft related deaths of manatees in Florida have occurred in Brevard County. FWCC has determined that manatee death from watercraft interaction is due to blunt trauma more than 50 percent of the time. Deaths from propeller cuts account for less than 50 percent. Often injury instead of immediate death from motorboat strikes is the case. Many manatees have scars from previous sub- lethal motorboat strikes, and manatees have been observed with more than 30 different strike patterns. Where the cause of death is classified as watercraft related, carcass recovery may or may not be where the collision occurred depending upon the acuteness of the injury at the time of collision. Acuteness of the injury, wind, current, tide, and decomposition all affect the location of the carcass at the time of salvage. Additionally, operation of motorboats can disrupt essential manatee behaviors such as warm water sheltering, feeding, sleeping, mating, and nursing. This harassment can lead to cold-related illnesses and increase mortality risk by driving manatees from warm water refuges. The increase in the Atlantic Coast manatee population and the increase of the number of boat registrations result in an increase in the threat of harmful collisions between boats and manatees. Geographic Scope of Threat Analysis Section 370.12(2)(m), Florida Statutes, does not specifically describe the geographic scope of the FWCC's evaluation of "other portions of state waters" for manatee sightings and assumed inhabitation on a periodic or continuous basis. Subsection 370.12(2)(g), Florida Statutes, suggests that the evaluation of manatee sightings is appropriate for large portions of navigable waterways, such as the Indian River between St. Lucie Inlet and Jupiter Inlet. A "waterway" is generally defined as "a navigable body of water." (Webster's Ninth New Collegiate Dictionary, p. 1333.) Rule 68C-22.001(3)(a)2.f., Florida Administrative Code, contemplates a qualitative assessment of the "likelihood of threat" to manatees. The only reference is to the "characteristics of the waterway in question." The rule does not mandate the geographic scope of a "threat evaluation." The FWCC analyzed various data on different scales depending upon the nature of the inquiry - the evaluation of sighting "frequency" generally considered a large geographical area such as a section of a river. Conversely, the regulatory alternatives to protect manatees were evaluated at a smaller or finer scale. The Commission also considered segments of waterways divided by causeways or natural barriers. The Commission considered research that divided Brevard County (north of Eau Gallie) into 12 zones for purposes of analysis. In the Brevard County Manatee Protection Plan, the waterways were analyzed in terms of seven "planning zones," to include review of physical characteristics such as bathymetry and sedimentological conditions, shoreline conditions, and water quality; Manatee Habitat Features, including sea grass, mangrove/salt marsh, freshwater sources, warm water refugia, calving and resting areas, feeding areas, travel corridors, and habitat protection; Manatee Data including manatee abundance and distribution and manatee mortality; boat facilities; boating activity patterns; waterspouts areas; and manatee zones. The Commission's consideration of waterway characteristics and manatee behavior during the Brevard County rule-making process, including the geographic scope of manatee inhabitation and threat from watercraft, was reasonable and consistent with the approach taken by other resource management agencies and researchers as contemplated by the statutory purpose. Proximity and Degree of Known Boating Activities FWCC evaluated available boating activity information in assessing threat. Staff considered the general analysis of boating activity and detailed analysis of boating activity in specific portions of Brevard County as provided in the County's MPP; included therein were maps that show locations of the County's 72 marinas and 65 boat ramps, of which 27 are public ramps. Also considered was the study of Brevard County-Wide Boating Activity by Dr. J. Morris, of the Morris of Florida Institute of Technology. Dr. Morris' inquiry resulted in the following specific finding. First, Brevard County residents are the primary ones who launch at boat ramps, followed by residents of Orange, Osecola, Seminole, Indian River and Volusia counties. Second, the Inter Costal Waterways experiences increases in transient traffic during late fall and winter months, including out-of-state boats. Third, Class One boats (16 to 25 feet) are the most observed type, followed by Class A (less than 16 feet) vessels. Fourth, most boating activity occurs during weekends. Fifth, the greatest concentrations of boats were in specific areas such as NASA causeway (SR 405, Indian River), East Canaveral Barge Canal, SR 520 and the Banana River (the Merritt Island Causeway), the Pineda Causeway (SR 404, Banana River), the Melbourne Causeway (Indian River), near Grant Island Farm, the Sebastian River and the Sebastian Inlet. Dr. Morris concluded that the boating public preferred to cruise the waters of the lagoons with the marked channels and use Indian and Banana Rivers as highways for recreational boating purposes. The United States Fish and Wildlife Service (USFWS) closed a portion of the northern Banana River within the Merritt Island National Wildlife Refuge to public boat entry, limiting public entry to wading or by non-motorized vessels. The closed area has one of the largest concentrations of manatees in the United States, and recently has been the most important springtime habitat for the east coast manatee population. As a result of the March 1990 closing to motorized boats, an average increase of manatee use observed during the summer months in the area increased by 60 percent. The increased use is attributed to improved habitat quality aided by the lack of human disturbance and reduced propeller scarring of sea grass. In December of 1994, Dr. Morris submitted a report, "An Investigation of Compliance to Boat Speed Regulations in Manatee Protection Zones in Brevard County, Florida." This report contained an analysis from on-water and aerial observations in both "slow speed" and "idle speed" zones in various areas of Brevard County for a one-year period of April 1993 to April 1994. At Mosquito Lagoon, of 1,214 boats observed, speeds were clocked for 98 percent of the boats and 11 percent of those exceeded the posted Inter Costal Waterways 30 MPH speed limit, all of which were recreational boats. At the Indian River site between Grant and Sebastian, 2,511 boats were observed, speeds were clocked for 97 percent of the boats and 16 percent of those exceeded the posted ICW 30 MPH speed limit. In posted "slow speed" zones outside the ICW channel, 25 percent of boats observed underway were deemed non- compliant with the speed zone limitation. Of those non-compliant Class A powerboats, the violators were typically personal watercrafts ("Jet Ski" type vessels.) A detailed boater activity study was made of the Canaveral Barge Canal and Sykes Creek Area. The study found, in part, that: highest boating use occurred during holidays, except during bad weather; most use occurred on weekends; and in Canaveral Barge Canal and Sykes Creek 63 percent of the vessels were Class 1 boats and 74.3 percent of the vessels were Class 2 or Class 3 boats. INCREASED LEVEL OF BOATING ACTIVITY IN BREVARD COUNTY In general, the level of boating activity in Brevard County continues to increase with the increasing population, launching facilities, and boat registrations in Brevard County and nearby counties, including Orange and Seminole counties. In 2000, 34,316 vessels were registered in Brevard County. In the preceding year there were 31,842 vessels registered. In 1995, 28,147 boats were registered and in 1987, 23,352 boats were registered in Brevard County. In 2000, Florida registered 840,684 recreational vessels, an increase over the 695,722 vessels registered in 1994. Boating accidents increased with the increased registration of vessels with Brevard County ranking 10th out of the state's 67 counties with the number of boating accidents. Brevard County, since mid-1990's, has registered an increased number of "flats skiffs" which are shallow draft, low profile motorboats capable of speeds up to 50-60 MPH while operating in shallow (about 1 foot) water and often used for sight-fishing in shallow sea grass flats. SEASONAL AND/OR YEAR-ROUND PATTERNS OF MANATEE USE AND THE NUMBER OF MANATEES KNOWN OR ASSUMED TO OCCUR IN, OR SEASONALLY USE THE AREA FWCC staff evaluated whether seasonal restrictions could or would be effective. Staff concluded that the only seasonal regulation of motorboats justifiable by the data was at the power plant discharges in the Indian River. At those locations, extreme concentrations of manatees are regular during the cold season. Year-round manatee protections were proposed for this area, but they would have to be more restrictive during the winter months. During the coldest periods of winter, following a strong cold front, manatees have been observed in large concentrations in: the power plant discharges at Florida Power and Light Company's Indian River plant and at the adjacent Reliant Energy Plant and the Sebastian River Canal. The congregation of manatees at thermal refuges on cold winter days was not for the duration of the winter season. They have been known to leave the thermal refuge for a part of a day, a day, or for many days at a time. Sharon Tyson, observer, performed a detailed Brevard County Manatee Photo-Identification Project during late 1999 and early 2000 at the Brevard County power plants, and documented a number of manatees in the FPL discharge zone between December 24, 1999, and March 4, 2000. During that period the number of manatees in the zone varied greatly, through late-December to mid-January (from 7 to 57 manatees). On January 16, 2000, no manatees were present. On January 17, 2000, 10 manatees were present. On January 23, 2000, 29 manatees were counted. Two weeks later, February 6, 2000, 111 manatees were present. Similar sightings made at the C-54 Canal Structure (near Sebastian Creek), during the same time-period, found as few as 11 manatees to as many as 90 manatees. Apart from the extreme concentration of manatees during extremely cold periods, manatees are distributed through the county waterways during each season of the year. The 1997-1999 Brevard County Aerial Survey GIS Plots gave a clear representation of year-round manatee distribution patterns varying greatly. MANATEE MORTALITY TRENDS WITHIN THE AREA Only in rare cases is the approximate or actual location of a manatee and motorboat collision known. The FWCC considered and relied upon a review of the general trend of watercraft-related (and other) mortality County-wide to assess a generalized increased mortality trend. In doing so as part of the rule-making process, FWCC reviewed total manatee mortality for Brevard County for the period for which records existed from 1974 to 2000. That data base source indicated increasing watercraft mortality in recent years. FWCC evaluated manatee salvage data for January-March 2001 and preliminary information for April-May 2001. Staff employee, Scott Calleson's working file mortality information was reviewed and considered as was Dr. Ackerman's "Mortality Rates White Paper," which concluded that human-caused manatee mortality levels were at an unsustainable rate in the Atlantic, Brevard County, Tampa Bay, and Southwest Florida Regions. The Florida Inland Navigation District provided documentation that was considered in the FWCC rule making that included a regional evaluation of "Watercraft Related Manatee Deaths in the Nine Critical Counties of FIND" from 1990-1999. Of these nine critical east coast counties, Brevard County had the highest mortality trend. During the last two-to-three years, there has not been a clear trend of increased manatee mortality in Brevard County, but the number of watercraft-related mortalities is capable of being reduced, in part, through improved regulations. Historical manatee mortality data for Brevard County from 1977 through 2000 demonstrates a clearly increasing trend in watercraft-related manatee mortality. For each five-year increment, water-related manatee mortality has increased as follows: from 1977-1979 there were an average of 1.9 water-related mortalities/year; 1980-1985 there were 4.6 mortalities/year; 1986-1990 there were 7 mortalities/year; 1991-1995 there were 8.8 mortalities/year; and 1996-2000 there were 11.8 mortalities/year. EXISTENCE OF FEATURES WITHIN THE AREA THAT ARE ESSENTIAL TO THE SURVIVAL OF, OR KNOWN TO ATTRACT, MANATEES SUCH AS SEAGRASSES, FAVORABLE WATER DEPTHS, AND FRESH OR WARM WATER SOURCES Dr. Deutsch stated that his telemetry analysis indicated that the most important habitat correlation for Brevard County manatees was with sea grass, and in particular, often with outer edge of sea grass beds. Manatees prefer feeding on submerged, emergent and floating vegetation, generally in that order. Manatees extensively use Brevard County sea grass beds for feeding. Sea grass coverage is depicted on the Florida Department of Environmental Protection's Boater's Guide to Brevard County, which has no date, but was prepared by the DEP. Sea grass coverage in 1989 is depicted in the 2000 maps prepared by the STMC, using the Atlas of Marine Resources, Versions 1.2 and 1.3b. The most recent St. Johns River Water Management District sea grass coverage data for the Indian River Lagoon indicates a strong correlation between sea grass coverage in waters with an average depth of 66.93 inches (1.7 meters) or less. As of 1992, of the estimated 46.190 acres of sea grass in Brevard County, nine percent of the sea grass suffered light scarring from boat activity; 4.2 percent of the sea grass suffered moderate scarring; and 13.4 percent of the sea grass suffered severe scarring. Areas with boat scarring of sea grass included a number of areas that are included within proposed "slow speed" zones: the eastern portion of Turnbill Basin; the eastern shoreline of the Indian River between the NASA railroad bridge and Rinkers Canal; the Banana River around Manatee Cove and south of the City Golf Course; the northwest part of Newfound Harbor; and the western shoreline of the Banana River, between Newfound Harbor and Pineda Causeway. The location of the proposed manatee protection zones corresponds well to the location of sea grass beds, deeper waters and channels adjacent to sea grass beds or established migratory routes, and fresh warm water sources. FAVORABLE WATER DEPTHS Dr. Deutsch stated that his telemetry analysis indicated that bathymetry is an important habitat correlate for Brevard County. Generally, tagged manatees were observed in the area from a two-meter (6.65 feet) depth contour to the shoreline. FWCC consideration of "favorable water depths" took into account the fact that water levels fluctuate in the Indian River Lagoon. However, unlike many coastal areas of Florida, the Indian River Lagoon does not experience significant daily tidal fluctuation. On an annual basis, however, the water level fluctuates about 2.5 to 3 feet in response to environmental conditions. It was determined to be impractical to amend manatee protection rules (and to move regulatory signs implementing the rules) in response to changing water levels. Manatees usually swim between one to three meters (3.28 to 9.84 feet) below the surface, surfacing every few minutes to breathe, and typically feed at just below the surface to a depth of three meters. Manatee experts, including persons with extensive experience observing manatee behavior in Brevard County, all testified that manatees used areas where the water level at the time was less than three feet for mating, feeding, fleeing a pack of male manatees, and resting. The FWCC used a bathymetric survey prepared on behalf of the St. Johns River Water Management District for purposes of establishing preferred sea grass habitats during the rule-making and considered the bathymetry in conjunction with other data to predict areas where manatees are likely to inhabit. The St. Johns District advised the FWCC staff that the 1.7-meter depth on its bathymetric survey was the rough depth limit for sea grass, and provided the FWCC staff with a GIS file on the bathymetric survey at 0.3-meter depth intervals for most areas, although the approximate sea grass contour was shown as 1.5 to 1.7 meters. Surveys are tied to a horizontal datum and a vertical datum. A survey depicts the three-dimensional lagoon basin, part of the spheroid planet Earth, on a two-dimensional map. The hydrographic survey data used by the FWCC in the rule-making was based upon a survey tied to a horizontal datum - North American Datum (NAD) 83/90; and a vertical datum - North American Vertical Datum of 1988 (NAVD-88). The horizontal and vertical accuracy of the survey differs. Positional accuracy of horizontal (e.g. shorelines) points is within 1 to 5 meters (3.28 to 16.4 feet). Vertical accuracy of depth data points averages within .03 feet. The hydrographic survey states that it is not to be used for navigation - - "The use of NAVD-88 for the bathymetric survey gives the impression of deeper water than is actually present within the lagoon since the "0" contour of NAVD-88 is located on dry land approximately 1 foot above the ordinary water line." Manatee distribution from aerial surveys and 1992 bathymetry data was graphically depicted by the STMC and confirms manatee use of areas proposed for regulation in the proposed rules. FRESH WATER SOURCES FWCC considered and relied upon major fresh water sources that have been historically used by manatees such as: Turnbull Creek; Titusville Marina/POTW; Addison Canal; the two Indian River power plants; two wells along the eastern shoreline of the Indian River approximately two miles south of Rinkers Canal; the intersection of Bacardi and Dakar Drive in Sykes Creek; the Cape Canaveral POTW (sewer plant); the Banana River Marina; the outfall into the Indian River from the east shore of Merritt Island westerly of the south end of Newfound Harbor; the Indian River Isles; the Eau Gallie River; Crane Creek; Turkey Creek; and the Sebastian River. Also considered were less significant sources of fresh water found at many marina basins, at the Sear Ray Boats, Inc. facilities and in residential canals. WARM WATER SOURCES FWCC considered major warm water sources in the two Indian River power plants and the Sebastian River Canal. Minor sources of warm water include deeper water and areas with artesian springs such as: Port Canaveral; a basin off Wynar Street in Sykes Creek; the Banana River Marina; and the Berkeley Canals. CHARACTERISTICS OF THE WATERWAY IN QUESTION IN RELATION TO KNOWN BOATING ACTIVITY PATTERNS FWCC considered, as its basic source document, Morris' Final Report for Brevard County Boating Activity Study. Boating activity patterns in Brevard County are dependent upon weather, economic conditions, and other factors. Larger motorboats (including tug/barge combinations) are constrained in movement to deeper water--in some areas, primarily within marked or maintained navigation channels including the Canaveral Locks, Canaveral Barge Canal, ICW, and Banana River main channel. In the Indian River, south of the NASA railroad bridge, the deeper area outside of the marked channel widens to between half-a-mile to a mile with depths ranging from seven to 12 feet MLLW, all the way to Rock Point, just north of Grant. For most of the length of the County, larger boats have sufficient water depth to travel adjacent to the ICW channel. Waters outside the main channel in the Banana River are relatively shallow. The Canaveral Barge Canal is dredged to maintain a depth of approximately 15 feet. Barges and escorting tugs navigate through the Canaveral Locks and into the ICW. Some barges proceed northward from the Canaveral Locks into the Banana River channel to make deliveries to the Space Center, according to the Lockmaster, Mr. Querry. Sea Ray Boats, Inc.'s, design and production facilities located along the Canaveral Barge Canal use the Canal to access testing areas to the west in the Indian River ICW, to the east in the Banana River channel, and in the Atlantic Ocean. Limited retests are permitted in an area adjacent to the Canaveral Barge Canal facilities. Recreational motorboats and personal watercrafts can be operated outside of marked channels. Some of these recreational motorboats can navigate "on plane" and up to 60 MPH in water about one-foot deep. Motorboat users engage in a variety of activities having differing operational patterns. Fishers might prefer to travel at relatively high speed enroute to preferred fishing areas, and then operate with a push pole, trolling motor or adrift, in order to hunt certain species of fish. If no fish are located, then high-speed operation to another spot is used, repeating the pattern of locating fish by sight. Water-skiers usually operate at high speed in a relatively small area, usually protected from the wind, and often located near an island or park. BOAT-MANATEE INTERACTIONS FWCC considered that manatees display varying reactions to motorboats. Higher speed motorboat operation in relatively shallow water presents a greater threat to manatees than operation at slow speed or idle speed or than operation in relatively deeper waters, since manatees have fewer opportunities to avoid the collision. Manatees can swim or rest at the surface or underwater and must come to the surface to breathe air every two to three minutes for smaller, active manatees and up to 20 minutes for large, resting manatees. Their general cruising speed is two to six miles per hour, but they can travel at short bursts up to 15 MPH. Boats operated at "slow speed" vary in miles-per-hour over the bottom within a range of about seven to eight miles-per- hour. At "slow speed," the manatee and vessel operator have more time to avoid collision, or the manatee can avoid serious blunt trauma injury from collisions with most vessels. The ability of manatees to avoid being hit by motorboats has diminished in Brevard County as a result of an increase in the manatee population, increase of motorboats, increase in boating access points, and development and use of faster boats that operate in less-predicable (non-linear) patterns in relatively shallow waters where manatees often feed on submerged vegetation. TESTIMONY REGARDING MOTORBOAT-MANATEE INTERACTION Officer Dennis Harrah, qualified as expert in boating safety, marine law enforcement, and local knowledge of the waterways of Brevard County, testified that "slow speed" zones provide greater reaction time for the vessel operator to avoid collision than unrestricted speed areas and than the "25 MPH maximum speed" areas. He further testified that "idle speed" zones provide greater reaction time for vessel operators to avoid collision than "slow speed" areas. Dr. John Reynolds, qualified as expert in marine mammal conservation and policy, manatee biology and behavioral ecology of marine mammals, opined, based on frequent observation of motorboat-manatee interactions, review of videotapes of such interactions, and review of studies on the subject, that there is an increased threat to manatees associated with boats that operate in planing speeds as opposed to slow speeds. His opinion is based, in part, on "common sense" that objects moving faster have greater momentum and therefore greater magnitude of impact, and on the reduced reaction time of both vessel operators and manatees to avoid collision. Dr. Reynolds was not aware of any evidence to suggest that the majority of watercraft strikes to manatees are from vessels operating at "slow speed," and it is his belief that "a good percentage of manatee mortality was from fast-moving vessels." Ms. Spellman, qualified as expert in marine biology and in manatee rescue and salvage, testified that she had observed considerable variability in manatees' reactions to kayaks, canoes and windsurfers, including manatees approaching the vessel, manatees not reacting at all, and manatees swimming away. She has observed manatee reactions to small motorboats as highly variant, depending upon the animal, including: swimming under a slow-moving motorboat, moving just as a motorboat approaches at idle speed, or diving and leaving the area as soon as a motorboat got anywhere near. Ms. Spellman testified, based upon her presence in the waters of the Canaveral Barge Canal or in the Port east of the Locks, that she has been in the water with manatees on five occasions when a barge/tug combination came by and in all cases the manatees reacted to the barge well in advance of the barge coming near her and the manatee, and that in each instance the manatee swam to within 15 to 20 feet of the shoreline. Of the thousands of times that she has seen manatees, she estimated that 95 percent of the time the manatees had scars from boat propellers or skegs. Dr. Powell testified, based upon over 30 years of observation of boat-manatee interactions, that the typical reaction is a flight or startle response, often to dive to deeper water. The diving response may take the manatee under the boat, away from the boat, or across the path of the boat. Based on his observations, including manatees reacting to motorboats moving at "idle-speed," "slow-speed" and at "faster-speeds," Dr. Powell opined that the manatees' reactions resulted from acoustical cues, visual cues, and perhaps pressure cues. Captain Singley, tugboat operator in Brevard County for over 30 years, observed a group of manatees react to a fast moving planing hull; some animals broke the surface, others scattered to the right or left, and others dove to the bottom. Mr. Walden, Sea Ray's Boat, Inc.'s, performance and water test specialist, testified that he had observed manatees in the Barge Canal, and sometimes the manatees would react to the motorboat. The majority of time when the boat was operating at planing speed or faster the manatee would dive and go deeper, and would began evasive action, upon hearing and noticing the motorboat a couple of hundred feet away. Dr. Gerstein testified that fast moving boats can hit manatees and that he was not aware of any physical evidence, eye- witness account, or law enforcement report of a slow-moving boat hitting a manatee. STUDIES ABOUT MOTORBOAT-MANATEE INTERACTION KNOWN BOAT STRIKES FWCC considered that watercraft collisions with manatees are rarely reported to authorities, and, as a result, it is difficult to directly assess the circumstances of such collisions, such as boat size, type and speed at the time of collision. A summary entitled "Watercraft-related Manatee Deaths Where the Responsible Vessel is Known," indicates that barges, displacement hull vessels, and planing hull vessels are known to have been in fatal collisions with manatees. In those planing- hull incidents where the vessels and estimated speed are known, the speed of the vessel ranged from getting-up-on-plane (45-foot boat with twin 425 HP outboard motors) to 35 MPH (18-foot boat with 150 outboard motor). Two other incidents were a 46-foot boat with twin inboard motors operating at 18 knots and a 20- foot boat with 200 HP outboard operating at 20 MPH. The only indication that a slow-moving planing-hull vessel struck a manatee is a report from an individual who was operating at estimated five MPH in a flat hull vessel and reported to have "felt a bump on aft hull, saw two animals (manatees) swam off." PROTECTION OF MANATEE-SEA GRASS HABITAT FWCC considered protection of sea grass habitat a secondary purpose in the Proposed Rule for areas subject to Section 370.12(2)(m), Florida Statutes. The Florida Guide To Recreational Boating notes that: Sea grass beds have been severely scarred (torn up) by boats operated in extremely shallow water. This is due, in part, to the "flats fishing craze" and the rising popularity of vessels designed to operate in shallow water. The Guide recommends that operators set the boat's drive unit at the highest possible setting and that the operator "proceed at idle speed when moving through shallow grass beds." Dr. Reynolds testified that "idle speed" or "slow speed" shoreline buffer zones provide greater sea grass protection (and manatee conservation) than higher motorboat speeds. The Executive Director of the Indian River Guides Association testified that the group is promoting "pole and troll" areas within the Merritt Island National Wildlife refuge portions of the Indian River Lagoon. He stated that many people from Orlando and elsewhere bring their boats by trailers to Brevard County, or move to Brevard County, and operate their boats so as to tear up seagrass beds. FWCC correctly concluded that "slow speed" and "idle speed" zones provide a greater measure of protection to shallow seagrass beds than do higher speeds for motorboats. DATA SOURCES CONSIDERED BY FWCC IN PROMULGATING THE PROPOSED RULE Differing Opinions About Manatee Protection Areas FWCC's Opinion The FWCC, based on the following, took the position that the proposed rules are more likely to protect manatees from motorboat impacts than the existing rules, and that the proposed rules take advantage of the available science of manatee biology and conservation, using the same basic approach used in manatee conservation by officials in Australia to protect dugongs (another Sirenian) from motorboats. The FWCC postulates that "idle speed" and "slow speed" zones provide greater protection to manatees than do higher motorboat speeds. "Maximum 25 MPH" speed zones in deeper water areas provide greater manatee protection than do unregulated waters. Most motorboats observed operating in unregulated areas (outside "slow speed" or "idle speed" zones) in Brevard County, during Dr. Morris' boating compliance study, were operating at or below 25 MPH. The FWCC correctly concludes that "maximum 25 MPH" speed was reasonable in light of research into the minimum planing speed of most recreational motorboat models, the observations of typical motorboat speed and operation in unregulated waters of Brevard County. The FWCC considered 1997 DEP-solicited information from motorboat manufacturers to determine minimum planing speeds and maximum planing speeds, and draft on- and off-plane for various sizes and types of motorboats. Considered also by the FWCC was boating test literature to determine that most boat models could reach planing speed at or slightly below 25 MPH. The FWCC considered information that was submitted showing that many production boats reached planing speed between 20-25 MPH. For example, Scout Boats' 11 models planed between 20- 25 MPH, and Shamrock's 13 models planed between 20-25 MPH. The Florida Marine Research Institute's 1992 information on this topic found a range of minimum planing speed between 14 and 24 MPH. Motorboats operating at speeds higher than 25 MPH are many. Ranger Boats offered several models with maximum speed in the "upper 60's" to "low 70's"; Scout Boats' models had top speeds of 35-60 MPH; Shamrock's models ran at the top end between 36-41 MPH; Donzi Boats operate at speeds in the 70 MPH range; and Bayliner's Capri 1700LS had a top speed of 46 MPH, as did Stingray's 180RS. Since the FWCC's creation, speed zone rules adopted for Lee County included maximum 25 MPH zones. Rule 68C-22.005, Florida Administrative Code for Brevard County has regulated motorboats with a "maximum 25 MPH" speed in channels. Commission staff applied their professional judgment in developing recommendations on manatee protection areas, and presented those recommendations to the FWCC, who considered staff recommendation, in context with public comment, to determine what manatee protections were warranted. PETITIONERS' OPINIONS The various Petitioners advocate manatee protection zones that, in many cases, are similar to the FWCC's proposed rules, including "slow speed" shoreline buffer zones and "maximum 25 MPH channels." Petitioners' challenge to many of the protection zones alleges that FWCC's basic regulatory mechanisms are flawed. FEDERAL LAWSUIT-SETTLEMENT AGREEMENT On or about January 13, 2000, STMC and other related environmental groups filed a lawsuit in the Federal District Court against Alan Egbert as Executive Director of the FWCC. The suit alleged, inter alia, that the FWCC is in violation of the Endangered Species Act by permitting the unauthorized taking of manatees in the State of Florida. During the pendency of the litigation, FWCC engaged in a series of mediations resulting in a settlement agreement approved by FWCC and executed by the parties in April 2001. The agreement contained a series of maps with draft manatee (speed) zones for Brevard County. Petitioners alleged that "the genesis of the Proposed Rule is this settlement agreement reached in the Egbert case, and there is a definite connection between the language of the Proposed Rule being challenged and the settlement agreement." Petitioners' speculative conclusion regarding this suit was tendered without one iota of evidence. Mr. Calleson, FWCC's staff employee, acknowledged that portions of existing speed zones and proposed speed zones in maps resulting from the federal mediation process contained a "lot of similarities" with speed zones in maps of the proposed rule. Mr. Calleson acknowledged that the FWCC did not direct staff to conduct negotiated rule-making on the proposed rule, and staff participation in the federal mediation process was not a negotiated rule-making process pursuant to Section 120.54(2), Florida Statutes, which provides, in pertinent part: (d)1. An agency may use negotiated rulemaking in developing and adopting rules. The agency should consider the use of negotiated rulemaking when complex rules are being drafted or strong opposition to the rules is anticipated. The agency should consider, but is not limited to considering, whether a balanced committee of interested persons who will negotiate in good faith can be assembled, whether the agency is willing to support the work of the negotiating committee, and whether the agency can use the group consensus as the basis for its proposed rule. Negotiated rulemaking uses a committee of designated representatives to draft a mutually acceptable proposed rule. * * * 3. The agency's decision to use negotiated rulemaking, its selection of the representative groups, and approval or denial of an application to participate in the negotiated rulemaking process are not agency action. Nothing in this subparagraph is intended to affect the rights of an affected person to challenge a proposed rule developed under this paragraph in accordance with s. 120.56(2). THOMAS MCGILL PETITIONERS Most of the McGill Petitioners support the adoption of rules that are consistent with the Citizens for Florida Waterway, Inc. (CFW), proposal submitted on December 29, 2000. The CFW proposal endorsed the use of "slow speed" zones, the use of "maximum 25 MPH zones," existing power plants "idle speed" and "motorboat prohibited" zones, and the use of shoreline buffers. The CFW proposal differed from the proposed rules primarily in scope of the proposed zones, rather than the nature of the proposed zones. The CFW proposal recommended numerous 25 MPH channels (in marked channels) through protected areas: from the Canaveral Locks through the Canaveral Barge Canal to the Indian River (except for three slow-speed boating safety zones); in North Sykes Creek; in the Banana River north of State Road 528 and between Bicentennial Park to the State Road 520 Relief Bridge. STANDING WATCH, INC. Stowell Robertson, one co-Petitioner of Standing Watch, Inc., is Executive Director of the Indian River Guides Association, Inc. (Guides). Mr. Robertson wrote the Guides' Recommendations, but his personal recommendation differed in two respects: in the North Indian River between NASA railroad bridge and the State Road 405 bridge, he would establish a "slow speed" zone from the western shoreline out to 500 feet (instead of 300); and he would impose a maximum 25 MPH speed in the Canaveral Barge Canal instead of 20 MPH. The Guides recommended that motorboat speed and operation be limited as follow: Mosquito Lagoon-make no changes to existing rule Turnbull Basin, North Indian River Create two "slow speed" zones in Turnbull - one in the Mimms Scottsmoor Canal, another from Jones Road boat ramp to Little Flounder Creek from the shore to 100 feet into the Basin; Set a new "slow speed" zone on the north side of the NASA railroad causeway and bridge out to 250 feet; Set a maximum 25 MPH in the ICW from Haulover Canal to the NASA railroad bridge; Take no further action [to change regulations]. Indian River, NASA railroad bridge to S.R. 402 Place "slow speed" zones on the south side of the NASA railroad bridge and causeway out to 250 feet; Reduce the [existing] west shoreline "slow speed" zone so that the western boundary is 350 feet from the ICW between markers R2 and G1; Set a maximum 25 MPH in the ICW; Take no further action [to change regulations] Indian River, State Road 406 to State Road 402 (1) and (2) Replace eastern "slow speed" zone with reduced "slow speed" zone extending from Peacock's Pocket to the existing "slow speed zone north of the State Road 405 Causeway, extending from shore to 250 feet west of the sand bar/drop off or three feet of water; Reduce the size of the "slow speed" zone north of State Road 405 Causeway to 300 feet; Reduce the size of the existing western shoreline "slow speed" zone to 500 feet from shoreline; Take no further action [to change regulations]. Indian River, State Road 405 to State Road 528 Bridge Close the warm water refuge sites at the power plants to manatees, not to boats; Deliver fuel to the power plants by land; Reduce the existing "slow speed" zone on the western shoreline to 1,000 feet from the shore; Take no further action [to change regulations]. Canaveral Barge (and Banana River to Locks) Maximum 20 MPH channel from Indian River to entrance to Canaveral Locks with "slow speed" zones at 100 feet either side of State Road 3 bridge, Sea Ray docks, Harbor Square Marina; Take no further action (to change regulations). Banana River (1) (2) All waters of Banana River, including channels, not otherwise regulated at "slow speed" should have 25 MPH limit; Reduce all existing "slow speed" zones along east and west shorelines, causeways, and bridges to 500 feet of shore; Retain existing "slow speed" zones in the two channels into "Long Point"[north and south ends of Canaveral Sewer Plant area]; Take no further actions [to change regulations]. Newfound Harbor (1) (2) All waters of Newfound Harbor, including channels, not otherwise regulated at "slow speed" should have a 25 PMH daytime limit and 20 MPH nighttime limit; Establish a "slow speed" zone along western shoreline from State Road 520 south to Two Islands; Establish a "slow speed" zone along eastern shoreline from State Road 520 south to the inside point north of Buck Point; The east and west "slow speed" zones be 500 feet from shorelines, and 200 feet[along northern shore] from S.R. 520; Take no further action. Sykes Creek North State Road 520 Set speed limit in marked channel at 20 MPH; All residential canals should be "slow speed"; Take no further action. Indian River State Road 528 to State Road 520 Establish 500 foot "slow speed" zones along western and eastern shorelines and 200 feet from causeways and bridges; Take no further action. Indian River State Road 520 to State Road 404 Establish 500 foot "slow speed" zones along western and eastern shorelines and 200 feet from causeway bridges; Take no further action. Indian River State Road 404 to State Road 518 Establish 500 foot "slow speed" zones along western and eastern shorelines and 200 feet from causeways and bridges; Take no further action. Indian River State Road 518 to State Road 192 Establish 500 foot "slow speed" zones along western and eastern shorelines and 200 feet from causeways and bridges; Establish Eau Gallie River "slow speed" zone with 20 MPH speed limit in marked channel daytime only, "slow speed" at night; Take no further action. Indian River (1) Establish 500 foot "slow speed" zones along western and eastern shorelines and 200 feet from causeways and bridges; (2)-(5) Crane Creek, Turkey Creek, St. Sebastian River, C-54 canal should be "slow speed"; Take no further action. Mr. James Kalvin, Standing Watch co-Petitioner and also President of Standing Watch, Inc., testified at deposition that neither he, nor the corporation, had any objection to the existing Brevard County manatee protection rules. SPECIFIC PROPOSED ZONES CHALLENGED The Petitioners' Challenge All Petitioners challenged the validity of Proposed Rule 68C-22.006, as "an invalid exercise of delegated legislative authority" as that phrase is defined in Section 120.52(8), Florida Statutes. MCGILL PETITIONERS The McGill Petitioners challenged the proposed rule amendment for Brevard County manatee protection areas, Proposed Rule 68C-22.006 (2)(d)2, 5, 6, 7, 8, 11, 12, 13, 14, 15, 16, 17, and 18, as an invalid exercise of delegated legislative authority. They allege that additional slow speed zones in Brevard County are invalid because the FWCC exceeded the authority granted in Section 370.12(2), Florida Statutes. McGill Petitioners based their allegations on the FWCC's lack of definable principles or data and an erroneously assumed cause-effect relationship for boat-manatee collisions, failure by the FWCC to consider the hearing limitations and capabilities of manatees in their environment, and a failure by the FWCC to employ standards and definitions for critical terms in its rule promulgation. At the final hearing, McGill Petitioners agreed that they do not object to that portion of Proposed Rule 68C- 22.006(2)(d)15 that reduces the width of the slow-speed zone in the Banana River between State Road 528 and State Road 520 causeways. Petitioners do, in fact, object to removal of the 25 MPH exemption for residential channels. The McGill Petitioners' position as set forth in their Prehearing Stipulation states: The Florida Fish and Wildlife Commission has exercised unbridled discretion and acted beyond the authority delegated in 370.12(2)(m), Florida Statutes, and has developed the proposed rule in an arbitrary and capricious manner. The proposed rule exceeds the delegated legislative authority because it is not based on scientifically definable principles or data. By failing to understand the root cause of watercraft mortality such as the manatee's inability to hear slow moving vessels, the Commission cannot deem their actions "necessary" to justify imposing speed restrictions as required by Section 370.12(2)(m), Florida Statutes. The Commission continues to impose speed motorboat restrictions even after finding that such restrictions are ineffective at preventing manatee mortality. The Commission relies on a flawed mortality database, a poor understanding of the limitations and applicability of satellite telemetry data, and lack of standards and definitions for critical terms. [emphasis added] The McGill Petitioners' Amended Petition alleged in paragraph 6: The Commission has not employed the best available science or even reasonable science. . . . aerial survey and telemetry data were misapplied. . . . in that areas that did not reflect frequent usage . . . were designated . . . slow speed zones. Also, the use of inaccurate telemetry tracking information was used as the basis for justifying areas where aerial survey data showed no manatee activity. . . . In support of their alleged inaccuracy of the satellite telemetry data, Petitioners presented the testimony of Mr. Dvorak and his Power-point Presentation of Aerial Survey Mortality, Telemetry and Bathymetry Assessment, and other technical papers. Mr. Dvorak did not include in his presentation/analysis survey data available on the Atlas or Marine Resources and did not include all telemetry data available from the United States Geological Survey, which was included in Dr. Deutsch's analysis presented for Respondent, FWCC. The Amended McGill Petition, paragraphs 10 and 12, stated: The McGill Petitioners advised the FWCC that creation of new "slow speed" zones was based upon incorrect assumption "that such slow speed zones alleviate collisions between vessels and manatee" and they suggested that "slow moving vessels are responsible for the majority of documented manatee collisions." McGill Petitioners' evidence proffered to demonstrate that "slow moving vessels are responsible for the majority of documented manatee collisions," consisted of inclusive studies and undocumented theories to demonstrate that slow speed zones do not alleviate collisions between vessels and manatees. FWCC considered an abundance of the best evidence of known or suspected collisions between vessels and manatees that demonstrated that "fast moving motorboats" are a known major source of manatee- vessel collisions. The McGill Petitioners further stated in paragraph 11 that: The rule does not consider the acoustic realities of the manatee's hearing limitations and its environment. McGill Petitioners presented the testimony of Dr. Edmund Gerstein regarding his measurements of the manatees' ability to hear noises. Dr. Gerstein concluded from his research that manatees have difficulty hearing and locating low-frequency sounds (below 400Hz), and they have difficulty detecting sounds of any frequency when it is not sufficiently louder than the ambient noise level. The testimony of Dr. Joseph Blue was given in support of the McGill Petitioners' position that low-frequency sounds are quickly attenuated in shallow water because of the Lloyd Mirror effect. Upon this foundation, Dr. Blue testified that since sound is shadowed ahead of the barge(s), the tugs that push the fuel oil barges between Prot Canaveral and the power plants on the Indian River emit low-frequency sound that is shadowed in the forward direction by the barge(s) and it would be undetectable to animals. Thus, the McGill Petitioners' witnesses concluded that there are acoustic consequences associated with slowing down boats. According to Dr. Gerstein, requiring motor boats to travel a slow speed deprives manatees of acoustic information they can use to detect, localize, and avoid boats. It is this "science of acoustics" Petitioners alleged that the FWCC gave no weight in promulgating the proposed rule. The FWCC considered the issues raised by acoustic studies. The FWCC's Executive Director was advised on the subject by the Manatee Technical Advisory Committee (MATC) whose recommendation resulted from a workshop on acoustic research and technology with presentations of the work of Drs. Gerstein and Blue. No reliable scientific sources, professional literature, expert opinions, and direct observations of manatee reactions to motorboats, supports the proposition of Drs. Gerstein and Blue that manatees cannot hear slow-moving motorboats. The FWCC rejected the studies of Drs. Gerstein and Blue. McGill Petitioners' alleged in paragraphs 3, 4, 13, and 14, of their Amended Petition that the FWCC did not provide a reasonable opportunity for and ignored much of the public's input. In their Prehearing Stipulation, the McGill Petitioners' acknowledgement of public hearings held by FWCC and the opportunity for pubic input during those hearings. There is an abundance of evidence in the record that demonstrates that the FWCC staff held non-mandatory pre-rule development meetings with interested persons, including some of the McGill Petitioners. The Staff held two rule development workshops in Brevard County. Staff held a public hearing specifically on the Proposed Rules in Brevard County. Staff considered the rule adoption at many hours of public hearings on three different dates and locations. Staff mailed special notices regarding the Proposed Rules to all identified waterfront property owners of whom many are the McGill Petitioners, and Staff mailed a series of survey documents to identified boaters and businesses in conjunction with the preparation of a statement of estimated regulatory cost. (CSERC) In paragraphs 7 and 9 of their Amended Petition, the McGill Petitioners alleged that the FWCC entered into a Negotiated Rule-Making Process with litigants to the exclusion of a balanced committee in violation of 120.54(2)(d)1., Florida Statutes. Section 120.54(2)(a), Florida Statutes, authorizes an agency to engage in development of a "preliminary text" or "preliminary draft" of proposed rules prior to the publication of a notice of rule development. Preliminary maps of amendments to the BCMPR were similar to maps being discussed as part of the federal mediation. This fact alone is not a basis to conclude violation of the above-cited statutes. A second rule development workshop was noticed to discuss a preliminary copy of the Staff's "zone configuration" being considered. Subsequent to the second workshop, the FWCC authorized publication of Notice of Proposed Rule-making that incorporated changes to the preliminary draft maps that were discussed at the workshop. The McGill Petitioners, during the hearing, agreed that they do not object to that portion of Proposed Rule 68C-22.006(2)(d)15 that reduces the width of the slow-speed zone in the Banana River between State Road 528 and State Road 520 causeways. Petitioners do, in fact, object to removal of the 25 MPH exemption for residential channels. Petitioners offered no testimony in support of this allegation, choosing rather to adopt the evidence and position proffered by Standing Watch, Inc., herein below addressed. In paragraphs 5 and 15 of their Amended Petition, the McGill Petitioners alleged that the Commission did not properly address the consideration of lower cost regulatory alternatives. The "lower cost regulatory alternatives" submitted by McGill, Pritchard and Dvorak were considered and were discussed in the draft SERC. The draft SERC gave reasons for the rejection of each of the proposed "lower cost regulator alternatives," primarily because none would substantially accomplish the objectives of the law being implemented. The SERC was finalized, as required by Sections 120.541(1)(a) and (c); and 120.56(2)(b), Florida Statutes, before filing for adoption with the Secretary of State. In paragraph 17 of their Amended Petition, the McGill Petitioners alleged that the FWCC failed to employ metrics or standards that could be used to validate the effectiveness of both proposed and existing rules, in rule promulgation, and that without the use of metrics, the FWCC had no way to determine and verify that speed zones they propose are necessary to protect harmful collisions with motorboats. The McGill Petitioners proffered no evidence of specific "metrics or standards" that would validate the effectiveness of the existing and or the proposed rule they contend the FWCC could have or should have used in the Proposed Rule development. The FWCC relied upon the best available and reliable information in its rule-making, including opinions of experts. To the information available to it, the FWCC applied its professional judgment, gave consideration to public comments/concerns provided during public meetings, and considered the estimated regulatory costs and other applicable rule-making requirements. In paragraph 18 of their Amended Petition, the McGill Petitioners alleged that the FWCC repeatedly ignored requests to sub classify watercraft-related mortalities in order to properly identify appropriate corrective action. The FWCC considered all available data regarding manatee injury and death resulting from the speed of motor boats and rejected Petitioner's contention that boat size, large boats such as tugs and barges, were more dangerous to manatees than smaller and faster motorboats. Sea Ray Boat, Inc. Petitioner, Sea Ray Boats, Inc., challenged only Proposed Rule 68C-22.006(2)(d)(11) that modifies the existing manatee protection speed zones in the Canaveral Barge Canal (that is 200 feet wide with a 125-foot navigation channel maintained at a depth of 12.5 feet) such that the entire Canal will now be designated a "slow speed" zone. Sea Ray does not argue that the FWCC did not consider all available information or that FWCC's consideration of the information was not complete. Sea Ray's position is, were one to consider the information presented to the FWCC, as balanced against the federal lawsuit filed by Save the Manatee Club, Inc., the challenged Proposed Rule is the result of the latter not the former and, therefore, is an invalid delegation of legislative authority. Sea Ray alleges that the FWCC did not analyze nor address the adequacy of the existing rule and speed zones in effect in the Canaveral Barge Canal. Sea Ray alleged that the FWCC did not consider the alternative (with weekend boating increases over weekdays) whether the risk to manatees would be reduced by "restricting slow speed zones in the channel to weekend and holidays." Sea Ray alleged that the FWCC failed to apply "properly" the mandatory balancing test of the impact of the proposed rule on the rights of commercial and recreational boaters. Section 370.12(2)(j), Florida Statutes. Sea Ray argues that the FWCC's consideration of information in formulating the Proposed Rule was devoid of "ascertainable quantitative criteria, standards or analytical processes," that Sea Ray maintains is required by Section 370.12, Florida Statutes. Standing Watch, Inc. Standing Watch, Inc.'s, Second Amended Petition challenged and alleged that the proposed speed in proposed Rule 68C-22.006(2)(e) 1-5 is not based upon "competent, substantial evidence" and does not comport with Section 370.12(2), Florida Statutes. Paragraphs 38 and 39 alleged that the proposed speeds in the Proposed Rule 68C-22.006(2)(c) 1-6 and (2)(d) 1-18 are not based upon "competent, substantial evidence" and do not comport with Section 370.12(2), Florida Statutes. Standing Watch, in essence, challenges all "idle," "slow" and "25 MPH" maximum speed zones proposed. Standing Watch argues that the FWCC failed to "quantify" by rule or working definition such terms such as "frequent" and "seasonal" and failed to define the term "periodic." Therefore, without working definitions the FWCC had no "threshold" from which to determine whether manatees were "frequently sighted," and the proposed rule is, accordingly, invalid in its entirety. Thus, it is alleged that the FWCC made no independent findings based upon the data reviewed that manatees were "frequently sighted" in any specific area of Brevard County. Standing Watch alleged, "The genesis of the Proposed Rule is this settlement agreement reached in the Egbert case, and there is a definite connection between the language of the Proposed Rule being challenged and the settlement agreement." Mr. Calleson acknowledged that portions of existing speed zones and proposed speed zones in maps resulting from the federal mediation process contained a "lot of similarities" with the speed zones in maps of the Proposed Rule. The FWCC declined to direct staff to conduct negotiated rule-making on the Proposed Rule. Accordingly, staff's participation in the federal mediation process was not a negotiated rule-making process pursuant to Section 120.54(2), Florida Statutes. Continuing their argument, Standing Watch alleged that the FWCC without algorithms, formulae, protocols, matrices, mathematical models, or metrics made no separate determination for each zone and/or area (of the proposed rule) and had no factual basis for the identification of separate speed zones, rendering all determinations made by the Commission as arbitrary and capricious. Based upon the foregone foundation, Standing Watch challenged Proposed Rule 68C-22.006 in its entirety as arbitrary and capricious. City of Cocoa Beach Watersports Area Cocoa Beach intervened to challenge that portion of Proposed Rule 68C-22.006(2)(d)16, that "reduces allowable speeds in the area known as Banana River, Cocoa Beach Waterspouts Area." In support of its challenge, Cocoa Beach adopted the Proposed Final Order submitted on behalf of Petitioners, Standing Watch, Inc., Jim, Kavin, Thomas Mason, Dougals P. Jaren and Stowell Robertson. Additionally, Cocoa Beach relied upon "facts" particularly applicable to the Cocoa Beach (Waterspouts Area). Cocoa Beach alleged that prior to the Proposed Rule and subsequent to 1988 the FWCC had no evidence of manatee deaths attributed to watercrafts having occurred in the Watersports Area; that two years prior to the proposed rule only one or two manatees were sighted in that area; that the sea grass preferred by manatees is not found in the area, and that the Watersports Area does not have the depth [bathymetry] preferred by manatees. Petitioners contend that a "sub-classification" would corroborate Mr. James Wood's view "a majority of watercraft collisions are caused by large, slow-moving vessels, not by small, recreational motorboats." Mr. Wood's analysis was inconclusive as to the characteristics of watercraft that caused manatee injury. The reliable and available evidence, including documentation on known or suspected boat strikes, scar catalog data, and affidavits of persons who perform manatee necropsies, does not support the view held by Mr. Wood. To the contrary, evidence and testimony of experts herein presented, established that small, fast moving motorboats kill and injure manatees and their habitat. The sub-classification of watercraft-related mortalities is not required for rule adoption. The proposition set forth by McGill Petitioners, and adopted by other Petitioners, that larger vessels and barge/tugs were responsible for Brevard County manatee mortalities was raised in an earlier rule challenge filed by McGill, and was rejected, as it is herein rejected. DOAH Case No. 99-5366, page 18 (officially recognized); Final Order, McGill v. Fish and Wildlife Conservation Commission, 23 F.A.L.R. (DOAH 2000). All data, 1997-1999 Brevard County relative abundance and distribution aerial survey, 2000 synoptic aerial survey, telemetry analyses, other data considered, and professional literature indicated that Brevard County is an important year- round habitat for manatees.
The Issue Whether the petition for administrative determination of the invalidity of a proposed rule was filed within the time Section 120.54(4)(b), Florida Statutes (1987), prescribes for instituting challenges to proposed administrative rules?
Conclusions The time limit Section 120.54(4)(b), Florida Statutes (1987) sets for filing petitions which seek determinations of invalidity under Section 120.54, Florida Statutes (1987), before proposed rules ever take effect, is jurisdictional Department of Health and Rehabilitative Services vs. Alice P., 367 So.2d 1045 (Fla. 1st DCA 1979); Organized Fishermen of Florida vs. Marine Fisheries Com'n, No. 88-3821R (DOAH; Sept. 14, 1988); City of Gainesville vs. Florida Public Service Com'n., 3 FALR 2448-A (DOAH 1981). Contra, Florida Medical Center vs. Department of Health and Rehabilitative Services, No. 88- 3970R and consolidated cases, Nos. 88-4018R and 88-4019R (DOAH; Nov. 1, 1988). If a petition challenging a proposed rule is not filed within 21 days of the notice initiating rulemaking which Section 120.54(13)(b), Florida Statutes (1987) requires agencies to publish, those seeking invalidation are relegated to rule challenge proceedings under Section 120.56, Florida Statutes (1987), unless they are parties to the rulemaking, and take timely stems to secure judicial review of the agency action adopting the rule. See City of Key West vs. Askew, 324 So.2d 655 (Fla. 1st DCA). Substantially affected parties who fail to file a Section 120.54 challenge in time are not without an administrative forum in which to litigate both whether the substance of a rule is authorized by statute and whether the manner of its adoption was lawful. Since the petition alleges no constitutional infirmity in the rule, nothing petitioners have pleaded here would be foreclosed from consideration in a Section 120.56 proceeding. See Department of Environmental Regulation vs. Leon County, 344 So.2d 297 (Fla. 1st DCA 1977). On appeal from an order invalidating an existing rule which had been challenged pursuant to Section 120.56, Florida Statutes (1987), the court in Department of Administration vs. Herring, 530 So.2d 962 (Fla. 1st DCA 1988), while rejecting the hearing officer's conclusions, considered the propriety of the procedures employed in rulemaking. Challenges to existing rules on grounds of inadequacy of economic impact statements are other instances in which rulemaking procedures have been tested in Section 120.56 proceedings. See Department of Health and Rehabilitative Services vs. Delray Hospital Corp., 373 So.2d 75 (Fla. 1st DCA 1979). Even where an agency makes no claim that it has followed any of the procedures required for rulemaking, challengers must ordinarily file under Section 120.56, Florida Statutes (1987). See State, Department of Administration vs. Stevens, 344 So.2d 290 (Fla. 1st DCA 1977). The petition in the present case may be read as alleging that DER published notice of proposing a mitigation rule in June of 1987, although the Florida administrative Weekly reflects publication on May 1, 1987. But it is clear from the petition that more than a year elapsed, after publication, before the present petition (or the earlier petition dismissed July 21, 1988) was filed. This makes the petition untimely under Section 120.54, Florida Statutes (1987) It is, accordingly, ORDERED: The petition for administrative determination of the invalidity of a proposed rule is dismissed, without prejudice to the filing of a petition pursuant to Section 120.56, Florida Statutes (1987). DONE and ENTERED this 15th November, 1988, in Tallahassee, Florida. ROBERT T. BENTON, II Hearing Officer Division of Administrative Hearings The Oakland Building 2900 Apalachee Parkway Tallahassee, FL 32399-1550 (904) 488-9675 Filed with the Clerk of the Division of Administrative Hearings this 15th day of November, 1988. COPIES FURNISHED: Peter B. Belmont, Esquire 511 31st Avenue North St. Petersburg, FL 33704 David A. Crowley, Esquire Department of Environmental Regulation 2600 Blair Stone Road Tallahassee, FL 32399 Janet E. Bowman, Esquire P.O. Box 1876 Tallahassee, FL 32302 James S. Alves, Esquire Thomas T. M. DeRose, Esquire P.O. Box 6526 420 First Florida Bank Building Tallahassee, FL 32314 Lawrence E. Sellers, Jr., Esquire P.O. Drawer 810 Tallahassee, FL 32302 Cindy L. Bartin, Esquire P. O. Box 271 Tallahassee, FL 32302
The Issue The issue presented is whether the Department of Environmental Protection's proposed Rule 62N-22.005, Florida Administrative Code, constitutes an invalid exercise of delegated legislative authority.
The Issue The issue is whether an application by Petitioner, Hancock Bridge Marina, LLC (Petitioner or Hancock), for an Environmental Resource Permit (ERP) and sovereign submerged lands lease to expand an existing docking facility on Hancock Creek near the Caloosahatchee River in unincorporated Lee County (County), Florida, should be approved.
Findings Of Fact Based on the evidence presented by the parties, the following findings of fact are made: Background Hancock is a limited liability corporation with two shareholders: Donald Epler and Stefen Heinke. After conducting a feasibility study, on April 26, 2004, Hancock purchased a 5.51-acre parcel of property in the County with the expectation of constructing and operating a 400-slip marina and a 5,000- square-foot building housing a restaurant, ship's store, and other sundry items needed for operation. (Hancock has subsequently revised its plan by reducing the number of slips requested from 400 to 352.) The cost of the property was around $2.5 million. The property is located in an unincorporated part of the County on the north side of the Caloosahatchee River (River), a Class III water, south of Hancock Bridge Parkway, east of the City of Cape Coral, and west of U.S. Highway 41 and the City of North Fort Myers. The property currently contains a 30-wet slip marina with 13 finger piers and a 4-slip T-dock. The remainder of the parcel is essentially vacant. The parcel borders a River tributary named Hancock Creek, which is a man- altered tidal creek branching off of the River in a northwestern direction, and the North Key Canal, which extends east from Hancock Creek for approximately one-half mile. Access to the River, which is no more than a hundred yards or so south of the parcel, is by traversing North Key Canal and Hancock Creek. The Department is the state agency with the authority under Part IV of Chapter 373, Florida Statutes, to issue an ERP. In addition, the Department has authority from the Board of Trustees of the Internal Improvement Trust Fund to review and take final agency action on requests to authorize activities in sovereign submerged lands. See § 253.002(1), Fla. Stat. The Commission is the agency with constitutional regulatory authority over "wild animal life and fresh water aquatic life and shall also exercise regulatory and executive powers of the state with respect to marine life." See Art. IV, § 9, Fla. Const. The Commission's authority for the regulation of manatees is derived from the Florida Manatee Sanctuary Act, which is codified in Section 379.2431, Florida Statutes. Under Sections 373.428 and 380.23, Florida Statutes, it also has authority to review ERP applications for federal consistency purposes pursuant to the federally approved Florida Coastal Management Program. On September 12, 2005, Petitioner filed an application for an ERP (a regulatory approval) and a lease to use sovereign submerged lands (a proprietary approval) with the Department's South District Office in Fort Myers, Florida. (For unknown reasons, the application was resubmitted to the Department on August 14, 2006.) The two requests are linked, and the Department cannot approve one without approving the other. See Fla. Admin. Code R. 62-343.075(2). The application seeks authority to expand in two phases the existing 30-slip facility. The first phase would generally authorize the construction of a 198-slip upland dry storage facility and reconfiguration of the existing docks. In phase 2, Hancock would add 154 dry slips and construct a 5,000-square-foot marina building. Because the docks are constructed on and over sovereign submerged lands, a proprietary authorization is necessary. Before making a decision on the application, the Department forwarded a copy to the Commission for its recommendation. After receiving the Commission's comments, which consist of 89 pages, including transmittal letters, on December 10, 2007, the Department issued its Notice of Intent to deny the ERP and proprietary authorization on the grounds the project area is sited in an area of very high level of manatee use and the project will increase local boat traffic, resulting in significant adverse effects on the manatee, which is listed by the state and federal governments as an endangered species. A more detailed description of the reasons for denial is found in the Notice of Intent. See Petitioner's Exhibit 6, pages 4 through 9; Department's Exhibit 1.b., pages 4 through 9. The Department acknowledges that its decision was based wholly upon the Commission's determination that the project, as proposed, would have an adverse impact on manatees. The DRI and Estoppel In its Petition, Hancock contends that the Department is "estopped to deny a permit for Phase 1 of the marina in light of its acquiescence to the approval of DRI 2-8990-99." By way of background, in 1990, Hancock's predecessor in interest (Waterway Group, Inc.) applied with the County for a DRI which included, among other things, 400 dry boat spaces on the property. DRI 2-8990-99 was approved by the County on July 8, 1991, and has been amended three times. See Petitioner's Exhibit 3. The original terms of approval contained several conditions that specifically addressed manatee protection. One separated the project into two phases of 200 spaces, the first of which was authorized without additional studies, while the second was subject to additional study and review by the Florida Department of Natural Resources (DNR). When the DRI was approved, the State's manatee protection program was under the jurisdiction of the DNR. That agency reviewed the DRI and recommended manatee protection conditions. The conditions in the final approval were consistent with the program's recommendation. On June 29, 2004, the County adopted a resolution approving a MPP for the County. See Petitioner's Exhibit 4. It was not adopted as an ordinance, and individual notice was not provided to interested property owners, including Hancock's principals. After adoption, the County incorporated the MPP into its Comprehensive Plan. The MPP is a planning document that provides a comprehensive review of manatee and boating data on a county-wide basis. It is developed, reviewed, and approved by local, state, and federal governments and is used for guidance when considering appropriate levels of slip densities within a county. The County is one of thirteen counties directed to adopt a MPP. On October 20, 2004, Hancock filed with the County an application to amend its DRI. The application included requests to extend the DRI approval a third time and to revise the site plan. The site plan changes included a reduction in the total number of dry spaces from 400 to 352. On June 20, 2005, the County approved the DRI amendment. The Development Order included a finding of fact that the marina was exempt from the requirements of the MPP because Section 8.4 of the MPP "exempts existing projects with valid permits and Chapter 380 vested status for the construction of slips (wet or dry) that have not been constructed at the time the MPP was adopted by the Board of County Commissioners." See Petitioner's Exhibit 3, Third Development Order Amendment for Hancock Bridge Marina, page 4, paragraph H. Hancock then filed the instant application on September 12, 2005. To date, Hancock has expended $1,731,000.00 in its permitting efforts, including the DRI extension and ERP application. There is no evidence that during the DRI process, the Department or Commission made any representations to Hancock about its ability to obtain an ERP or sovereign submerged lands authorization. Also, neither agency was consulted during that period of time, presumably because the DRI and ERP processes are separate and independent of one another. Permitting Criteria Section 373.414, Florida Statutes, contains the standards and criteria governing the approval of an ERP. Subsection (1) requires that the applicant provide reasonable assurance that the regulated activity is "not contrary to the public interest." In determining whether this test is met, paragraph (1)(a) requires that the Department consider and balance the following criteria: Whether the activity will adversely affect the public health, safety, or welfare or the property of others; Whether the activity will adversely affect the conservation of fish and wildlife, including endangered or threatened species, or their habitats; Whether the activity will adversely affect navigation or the flow of water or cause harmful erosion or shoaling; Whether the activity will adversely affect the fishing or recreational values or marine productivity in the vicinity of the activity; Whether the activity will be of a temporary or permanent nature. Whether the activity will adversely affect or will enhance significant historical and archaeological resources under the provisions of s. 267.061; and The current condition and relative value of functions being performed by areas affected by the proposed activity. These same factors are found in Florida Administrative Code Rule 40E-4.302, an ERP rule adopted by the South Florida Water Management District. This rule has been adopted by reference by the Department to be used when it considers ERP applications within the geographical jurisdiction of that water management district. See Fla. Admin. Code R. 62-330.200(4). An additional requirement in the rule is that an applicant give reasonable assurance that the project will not cause unacceptable cumulative impacts. See Fla. Admin. Code R. 40E- 4.302(1)(b). Besides the foregoing requirements, additional conditions for the issuance of an ERP are found in Florida Administrative Code Rule 40E-4.301, also adopted by reference by the Department. Relevant here are requirements that the applicant give reasonable assurances that the proposed activity (a) will not adversely impact the value of functions provided to fish and wildlife and listed species by wetlands and other surface waters, and (b) will not cause adverse secondary impacts to the water resources. See Fla. Admin. Code R. 40E-4.301(1)(d) and (f). Section 373.414(1)(b), Florida Statutes, provides that if an applicant is unable to meet the above criteria, the Department shall consider measures proposed by or acceptable to the applicant to mitigate adverse effects that may be caused by the regulated activity. In this case, mitigation measures have been proposed by Hancock and are discussed below. Finally, Section 373.4132, Florida Statutes, requires that the Department evaluate applications for dry storage facilities for ten or more vessels in the same manner as any other ERP application, including that the applicant demonstrate that the facility will not be harmful to the water resources, provides reasonable assurance that the secondary impacts from the facility will not cause adverse impacts to the functions of the wetlands and surface waters, and meets the public interest test in Section 373.414(1)(a), Florida Statutes. There are no rules or statutes which require that the Department consider the status of, or otherwise take into account, a DRI in evaluating an application for an ERP or proprietary authorization. Impacts on Manatees After reviewing the application for an ERP, the Department determined that the project, as proposed, should be denied because of direct, secondary, and cumulative effects it would have on manatees. The Department further determined that the applicant had not met the applicable requirements under Florida Administrative Code Rule Chapter 18-21 for authorization to use sovereign submerged lands. In making these determinations, the Department considered not only potential deaths of manatees, but also potential impacts such as harassment, disturbance, and sub-lethal boat strikes. The latter strikes may cause permanent injury and can affect reproduction and behavior. The State is a refuge and sanctuary for the manatee. See § 379.2431(2), Fla. Stat. The manatee is a marine mammal that can live as long as sixty years. It is unable to tolerate prolonged exposure to temperatures below around sixty-one degrees, which makes it susceptible to cold-related stress and death. Consequently, the manatees typically seek warm water when temperatures drop below sixty-eight degrees, migrating seasonally over extensive geographic areas. Hancock's marina is located just off the River. The River is one of the most studied and significant habitats for manatees on the west coast of Florida. The County's water bodies, including the River, provide manatees with submerged aquatic vegetation for foraging, fresh water sources, and several warm-water sites to use as refuges during colder weather. Hancock Creek, which is used to access the River from the marina, is an area used by manatees because it provides fresh water and a quiet environment. Manatees also use the River as a major travel corridor between the Florida Power and Light Company (FPL) power plant on the Orange River, a tributary of the River located around eight miles upstream from the project site, and the estuaries found downstream where foraging resources are abundant. Hundreds of manatees go up and down the River throughout the year, and those traveling to and from the warm water around the FPL plant must travel past Hancock Creek. Manatee deaths have occurred within a five mile radius of the project site. Also, the number of manatee watercraft- related deaths in the River has steadily increased over the years. According to a 1998 study of boating activity in the County, vessels use the River more as a travel corridor to the bays and estuaries outside of the River than as a destination itself, and that on weekends there is almost constant traffic with vessels leaving or entering the mouth of the River every thirty-five seconds. The majority of the boats leaving the project site are expected to travel downstream through the mouth of the River, an area with substantial vessel congestion. This travel pattern, in conjunction with the typical travel patterns of manatees, indicates that there is a great potential for boat/manatee overlap in the River, increasing the likelihood of impacts to manatees. Besides manatee deaths, there are sub-lethal effects of increased boat traffic in the area. Increased traffic in important manatee areas may create disturbances which will alter behaviors such as feeding, suckling, or resting, or it may separate mothers from their calves. Also, vessel traffic may cause them to leave preferred habitats. Finally, as noted above, vessel collisions with manatees produce non-lethal injuries as well, causing pain and extreme scarring, which can alter natural behaviors and affect reproduction. The single biggest known cause of death to manatees is impacts from boats. The project would increase the risk of watercraft collisions with manatees in this region. As the level of boat traffic increases, the probability of boat and manatee collisions is also likely to increase. Because the project is located along the travel corridor between the largest wintering aggregation of manatees on Florida's west coast and their local foraging habitat, the expected secondary impacts from increased vessel traffic associated with the project is expected to reduce the value of the functions of the River as a travel corridor. Therefore, the secondary impacts of vessel traffic from the expansion of the marina are expected to result in adverse impacts to manatees. In 1990, the DNR reviewed the proposed DRI for this site under the state manatee program. It found that during the preceding thirteen years (1976-February 1990), thirty-six manatees had died from water-related injuries in the County. Within a five-mile radius of the site, four manatees had died from watercraft-related injuries. DNR concluded that since the manatee protection speed zones for the River had just been established, they were expected to offset the impact of the additional 198 slips. From March 1990 until September 2006, however, twenty-five additional manatees have died from watercraft-related injuries within a five-mile radius of the site. Therefore, the number of deaths had increased without the additional 198 slips. The logical inference is that if the new slips are allowed, boat traffic and the associated adverse impacts on manatees will likewise increase. The fact that dry slips will be used does not change the Department and Commission's evaluation of the project. A boat has the same risk to a manatee whether stored in a wet or dry facility. Marine industry groups suggest that an average usage rate is between ten and fifteen percent at any time, and that usage is likely to increase on the weekends. Thus, as density increases so does the risk. In addition to its own analysis, the Commission reviewed the County MPP, which indicated that nine additional slips at this location would be acceptable, for a total of thirty-nine. This number was calculated by using a slip density of three slips for every one hundred feet of shoreline owned. (The actual linear feet of shoreline owned by Hancock is unclear. The Commission concedes that Hancock "may own a total of 1,214 linear feet of shoreline.") A MPP typically allows for higher boat densities in areas that pose less risk to manatees and lower boat densities in higher risk locations. Had the MPP not been considered, the number of allowable slips would remain at thirty since the MPP provides for a countywide strategy instead of a case-by-case review. To date, the Commission has never recommended approval of a marina application in the County that would authorize more docks than the MPP would authorize. The Commission initially makes an independent assessment of the application without regard to the MPP. In this case, based upon mortality data, aerial surveys, telemetry data, rescue data, and boat studies, the Commission determined that no further slips are appropriate. Therefore, even if the County's MPP is based upon outdated data and analysis, as Hancock contends, approval of the application would not be warranted. Petitioner's expert posited that the proposed project would only result in one manatee death over the next twenty years, which would amount to no more than a de minimus impact on the overall population. Assuming this to be true, manatees are nonetheless an endangered species, and there is no minimal amount of death that is considered acceptable. The witness also opined that Hancock is entitled to an unlimited number of slips under the MPP due to flawed data and analysis underpinning that document. In formulating his recommendations, however, Hancock's expert relied on mathematical models and statistics while ignoring the principles of manatee behavior and biology. Finally, the expert agreed that the greater the number of boats in the water, the greater the likelihood that a manatee could be accidentally crushed. On the issue of impacts to manatees, the testimony of the Commission witnesses is deemed to be the most credible and persuasive. The more persuasive evidence supports a finding that the marina will be located in an area adjacent to the River, that large numbers of manatees use the River, and that the project is expected to increase boat traffic. This in turn will lead to a higher incidence of boating-related manatee casualties in the area. Therefore, the proposed activity adversely affects the conservation of wildlife and marine productivity in the vicinity of the project; it adversely affects the marine productivity in the area; it is permanent in nature; and it diminishes the current condition and relative value of functions performed by areas affected by the activity. On balance, then, the project is contrary to the public interest. Based on the evidence presented, Hancock has not provided reasonable assurance that the project will not cause adverse secondary impacts to water resources, as required by Florida Administrative Code Rule 40E-4.301(1)(f). Similarly, based on the evidence presented, Hancock has not provided reasonable assurance that the project will not result in unacceptable cumulative impacts upon wetlands and other surface waters, as required by Florida Administrative Code Rule 40E-4.302(1)(b). By failing to provide reasonable assurances that the facility will not be harmful to water resources, that the secondary impacts from the facility will not cause adverse impacts to the functions of wetlands and surface waters, and that the project meets the public interest test, Hancock has failed to satisfy the requirements of Section 373.4132, Florida Statutes. Mitigation If an applicant cannot meet the requirements of Section 373.414(1)(a), Florida Statutes, the Department "shall consider measures proposed by or acceptable to the applicant to mitigate adverse effects that may be caused by the regulated activity." As noted in Finding of Fact 27, supra, the Department is willing to approve an additional nine slips that would be allowed under the County MPP, for a total of thirty- nine. According to Hancock, this number is not acceptable because more slips are needed to make the project financially feasible. Although a copy of the application is not a part of this record, the testimony suggests that in its application, Hancock proposed certain measures to mitigate the impacts on manatees. In a letter to the Department dated November 8, 2007, however, the Commission stated that "[i]f the Applicant propose[s] changes to the project to minimize fish and wildlife resource impacts that are consistent with the Lee County MPP, such a project would be consistent with Chapter 370.12(2), F.S." (The Legislature has subsequently consolidated this statute into Section 379.2431, Florida Statutes.) Despite this lack of clarity in the record, sometime during the application process, and presumably before the Notice of Intent was issued, the Commission staff discussed with Hancock whether the following mitigation measures would offset or adequately reduce the impacts: placing a size restriction on boats docking at its facility; providing boater education; installing speed zone marking and making it a requirement for all boats at the marina to be equipped with a speed zone map or a Global Positioning Satellite unit with speed zone mapping; implementing a volunteer watch program to enforce speed limits; making a cash donation to study manatee population dynamics; and installing sonar avoidance technology on vessels. The Commission established that these measures, even if implemented, would not offset the impacts from 198 slips expected with phase 1 of the project. For example, the research associated with sonar technology is not yet completed, and devices are not available for boaters. Also, given the location of the project, even with additional law enforcement and boater education, the impacts would not be offset due to the level of traffic already existing on the River at that site, and the importance of the area to manatees. The middle of the River is a high-speed corridor (with a twenty-five miles per hour speed limit) and even with one hundred percent compliance in that zone, a small boat can still hit and kill a manatee. The Proprietary Authorization Because denial of the ERP is being recommended, the proprietary authorization must likewise be denied. See Fla. Admin. Code R. 62-373.075(2). Even so, for the purpose of addressing all issues in this Recommended Order, a discussion of the application for proprietary authorization is set forth below. Florida Administrative Code Rule Chapter 18-21 contains the rules that implement the administrative and management responsibilities of the Department in authorizing activities in sovereignty submerged lands. Florida Administrative Code Rule 18-21.004 establishes the specific standards and criteria to be applied by the Department in determining whether Hancock should be allowed to use sovereign submerged lands. Paragraph (1)(a) provides that "[f]or approval, all activities on sovereignty lands must be not contrary to the public interest." The public interest is defined as "demonstrable environmental, social, and economic benefits which would accrue to the public at large as a result of a proposed action, and which would clearly exceed all demonstrable environmental, social, and economic costs of the proposed action." See Fla. Admin. Code R. 18-21.003(43). The more persuasive evidence supports a finding that, on balance, the project is contrary to the public interest based upon the standards in the rules. Florida Administrative Code Rule 18-21.004(2)(a) provides that "[a]ll sovereignty lands shall be considered single use lands and shall be managed primarily for the maintenance of essentially natural conditions, propagation of fish and wildlife, and traditional recreational uses such as fishing, boating, and swimming. Compatible secondary purposes and uses which will not detract from or interfere with the primary purpose may be allowed." The evidence does not show that Hancock's proposed marina expansion constitutes a secondary use not interfering with the propagation of wildlife. Therefore, the project is not consistent with this rule. Florida Administrative Code Rule 18-21.004(2)(b) provides that "unless there is no reasonable alternative and adequate mitigation is proposed," activities which result in significant adverse impacts to sovereignty lands and associated resources shall not be approved. As previously found, the mitigation measures proposed by Hancock are not adequate. Paragraph (2)(i) of the rule further provides that activities in submerged lands "shall be designed to minimize or eliminate adverse impacts on fish and wildlife habitat, and other natural or cultural resources. Special attention and consideration shall be given to endangered and threatened species habitat." Because Hancock failed to prove that the project would not result in unmitigated adverse impacts to manatees, it fails to meet this criterion. Paragraphs (7)(d) and (e) of the rule are general conditions for authorization and provide that activities "shall be constructed and used to avoid or minimize adverse impacts to sovereignty submerged lands and resources" and "shall not adversely affect any species which is endangered, threatened, or of special concern." Here the more persuasive evidence shows that neither condition has been met.
Recommendation Based on the foregoing Findings of Fact and Conclusions of Law, it is RECOMMENDED that the Department of Environmental Protection enter a final order denying Petitioner's application for an ERP and authorization to use sovereign submerged lands to expand an existing marina on Hancock Creek in Lee County, Florida. DONE AND ENTERED this 15th day of May, 2009, in Tallahassee, Leon County, Florida. S DONALD R. ALEXANDER Administrative Law Judge Division of Administrative Hearings The DeSoto Building 1230 Apalachee Parkway Tallahassee, Florida 32399-3060 (850) 488-9675 Fax Filing (850) 921-6847 www.doah.state.fl.us Filed with the Clerk of the Division of Administrative Hearings this 15th day of May, 2009.
The Issue Petitioner has challenged a series of emergency rules promulgated by the Respondent to address the discovery of Mediterranean fruit flies (medflies) in parts of central Florida. Specifically, Petitioner contends that 5BER 97-3, 5BER 97-4, 5BER 97-6, and 5BER 97-7 are invalid to the extent that they make any geographical area subject to emergency rule for more than 90 days. The issue for determination, therefore, is whether the emergency rules are invalid as claimed.
Findings Of Fact Petitioner Rick Martinez resides and operates an organic farming business in Tampa, Hillsborough County, Florida. As stipulated, Mr. Martinez is substantially affected by the emergency rules at issue. The Mediterranean fruit fly (medfly) is considered one of the world's most serious pests affecting fruits and vegetables. It has a host range of over 260 different fruits and vegetables, 80 of which are grown in the state of Florida. It is an exotic pest of grave concern to commercial agricultural interests as well as to home gardeners. In the adult stage, the female medfly deposits or lays eggs in ripe fruit. The eggs develop into larva or maggots that feed on pulp of the interior portion of fruit, causing damage and secondary pathogens to enter the fruit and causing the fruit to rot and fall from the tree. The medfly reproduces very rapidly. It can complete a life-cycle in as little as 18 days under optimum conditions; in Florida and in recent months, it completed its life-cycle in approximately 23-25 days. As a winged insect the medfly can move several miles from its point of introduction in search of a host to deposit eggs or in search of a food source. Over a lifetime, the female can lay hundreds or thousands of eggs. The medfly enters an area via the traveling public or on commercial fruits and vegetables. Host plants or fruits can include plants or fruits that are not grown in Florida. The Florida Department of Agriculture and Consumer Services (FDACS) maintains a detection program, including 13,000 traps to detect the presence of the medfly. Under certain circumstances for every medfly detected, there can be hundreds of others in the area. Because of the biology of the medfly, mere control is difficult to achieve. Eradication, or complete elimination of the pest from a particular area, is the goal when the medfly is detected. To further this goal, Florida cooperates with the U.S. Department of Agriculture and other states. On or about May 28 or 29, 1997, a medfly was discovered in the Seminole Heights area of Hillsborough County. Very quickly other medflies were discovered in Hillsborough County, with the epicenter determined to be in the Brandon area. Soon other detections occurred in Manatee, Sarasota, Orange, and Polk Counties. This was determined to be the most severe infestation of medflies in Florida in several decades. On May 30, 1997, Commissioner of Agriculture, Bob Crawford, issued a proclamation announcing an immediate danger to the public health, safety, or welfare in the state of Florida on account of the infestation by the Mediterranean fruit fly. The proclamation cited authority and powers conferred by Article IV, Section 4, Florida Constitution and Sections 120.54(4) and 570.07(21), Florida Statutes. The proclamation called for immediate eradication procedures including aerial and ground pesticide applications in infested areas. FDACS also promulgated and filed an emergency rule, 5BER 97-2, Florida Administrative Code, "Mediterranean Fruit Fly Rule and Quarantine." The rule provided definitions, designated a quarantine area and treatment area, identified regulated articles and host plants, and provided for entry of authorized representatives to inspect, confiscate suspect fruit, or apply treatment on property on which the medfly is known or suspected to exist. The rule also declared the medfly a pest and nuisance pursuant to Section 581.031(6), Florida Statutes, and described the rule's purpose: . . . to provide detailed direction for conducting a regulatory and eradication program to prevent spread of the Mediterranean fruit fly, Ceratitis capitata, within the State. This rule is promulgated to provide a quarantine on areas regulated due to the presence of the Mediterranean fruit fly, and to specify conditions under which regulated articles may be certified as free of Mediterranean fruit fly when moved from the quarantined area. This rule also provides for the treatment and eradication of the Mediterranean fruit fly within the State of Florida. (5BER 97-2(2), Florida Administrative Code) The quarantine area within 5BER 97-2 is an area of Hillsborough County described with specificity with references to road boundaries. The treatment area was defined as "[a]ny location including urban and residential areas within a nine- square-mile area around an [sic] Mediterranean fruit fly detection. " Quarantine areas are generally 81 square miles; treatment areas are 9 square miles and may be wholly outside of a quarantine area. In the words of FDACS Director of the Division of Plant Industry, Richard Gaskalla, "[t]his was a very active infestation. For the first 90 days of the program, it was a very fluid and dynamic situation. Each day brought a new challenge, a new area to place traps in or regulate fruit in. So it was giving us quite a challenge." (transcript, 48-49) As new medflies were discovered subsequent to the end of May 1997, FDACS expanded the treatment and quarantine areas. Additional emergency rules on the infestation were filed: 5BER 97-3, on June 20, 1997; 5BER 97-4, on July 3, 1997; 5BER 97-6, on July 28, 1997; and 5BER 97-7, on August 11, 1997. With the exception of the specifically described quarantine area in section (4), each emergency rule is substantially the same. 5BER 97-3 repeats the quarantine area described in 5BER 97-2 and adds a specific portion of Polk County. 5BER 97-4 repeats the quarantine area described in 5BER 97-3 and adds a specific portion of Manatee County. 5BER 97-6 and 5BER 97-7 include a much larger quarantine area to include portions of Hillsborough, Polk, Manatee, Orange, and Sarasota Counties. There are portions of Hillsborough County which are found in the quarantine area described in all five emergency rules. Other geographical areas overlap in two or more of the five rules. The "treatment area" remains described in each of the five emergency rules as the nine-square-mile area around a medfly detection. As more medflies were found, this area obviously expanded. Eventually the treatment area became almost as large as the quarantine area in Hillsborough County. FDACS developed its series of emergency rules to address the medfly eradication program as it evolved. The agency consulted a science advisory panel that was put together to review the eradication program, and the agency received public comment and suggestions from public meetings. As new detections were made, the emergency rules were promulgated to cover the areas which the agency considered important for its regulation and control (quarantine). Richard Gaskalla did not consider each new emergency rule to be a renewal but rather a response to the unpredictable expansion of the medfly within existing areas. As soon as FDACS adopted the first emergency rule, it began work on a permanent rule and scheduled a rule development workshop in June to receive public comment. Citizens in Hillsborough County requested another workshop which was held approximately two weeks prior to the hearing in this case. A permanent rule has not been adopted, but the pre-adoption process continued as of the hearing in this case. As of the time of hearing, the last medfly detected in Hillsborough County was mid-July. Medflies were discovered after this in other counties covered by the emergency rules. Eradication is generally not considered complete until traps have been empty for two life cycles after the last treatment. Depending on the length of the life cycle, eradication could be complete from 60 to 100 days after the last fly find.
Findings Of Fact It is stipulated that Marine Industries Association of South Florida, Inc. (Petitioner), has standing to bring this rule challenge. It is also stipulated that Save The Manatee Club, Inc. (Intervenor), has standing to intervene in this rule challenge. The Department of Environmental Protection (Respondent) has the responsibility of implementing the Florida Manatee Sanctuary Act, Section 370.12(2), Florida Statutes, which involves interpreting the terms thereof. Respondent's responsibility includes promulgating rules to regulate motorboat speeds and their operation incident to the protection of manatees, pursuant to the Act. 4. Respondent's Rules 16N-22.001(2), 16N-22.002(20) and (21), Florida Administrative Code, set forth criteria for determining the state waters in which motorboat speed would be regulated for the protection of manatees. Also, Respondent's Rules 16N-22.010(1)(e) and (g), Florida Administrative Code, establish a seasonal slow speed zone on weekends for a certain area in the Intracoastal Waterway within Broward County and a year-round slow speed and buffer zone in a certain area in the Atlantic Intracoastal Waterway within Broward County for the protection of manatees. The manatee is an endangered marine mammal residing in the southern United States, principally in Florida, and has been declared by the State of Florida as its state marine mammal. Only 900 manatees are considered to be on the east coast of Florida. Respondent uses all available information on the presence of manatees, which includes actual visual sightings as well as any other method to identify their presence. Respondent refers to this information as "sightings." Respondent's information gathering procedure is consistent with established and accepted procedures for the gathering of information on manatees. Aerial surveys are part of the information relied upon by Respondent for its determinations regarding manatees. It is possible, and not uncommon, that aerial surveys may include sightings of the same mammal on different days. Whether a manatee is sighted frequently involves more than just numbers. It also includes a reasonable expectation that manatees will be seen. Aerial survey data is a minimum count to ascertain where the manatees are, not to determine how many exist or their population. Sixty-one aerial surveys were conducted in the waters of Broward County, excluding the Hillsboro Inlet, by Respondent and Broward County for Respondent. During the aerial surveys from 1988 to 1993, sixty-seven to sixty- nine sightings were made in the northern Intracoastal Waterway (NICW) in Broward County. Also, the aerial survey data showed sightings in seven out of twelve, five out of fifteen, and eleven out of eighteen flights. Manatees occasionally travel in the ocean. The aerial surveys included passes over the Atlantic Ocean. The NICW has lowlight transmission and high turbidity. Manatees travel two to five feet below the surface of the water. Because of water clarity, surface conditions and the fact that manatees must be at or very near the surface to be spotted, manatees are difficult to see in the NICW. The aerial surveys revealed an average of one sighting per flight. Lack of sightings in the aerial surveys reflect survey conditions as much as the absence of manatees. Manatees regularly move in and out of the Hillsboro Inlet zone. Manatees use the NICW in Broward County often and are frequently sighted there. When determining whether manatees inhabit an area, all data bases available should be used. The Intracoastal Waterway (ICW) is used by manatees for travel through Broward County. Aerial surveys of the NICW are performed at a lesser density than those performed of the power plants which are warm water refuges. Regular travel corridors constitute essential habitat. The NICW is a major travel corridor for manatees. They migrate through the NICW. Migration means purposeful movement from one point to another, as well as seasonal movement of species in mass. Manatees use the waters of the NICW and the power plants when moving back and forth between Port Everglades and Riviera Beach, and this exchange is documented. More than 200 manatees use both the Port Everglades and the Riviera Beach Power Plants (both warm water discharge areas) as warm water refuges, making repeated trips back and forth in single seasons. Thirty-Eight to forty-seven percent of manatees on the east coast use the Port Everglades area. Manatees inhabit areas where they are found. As to the waters of the ICW, they inhabit it on a regular basis. Moreover, manatees inhabit the NICW virtually continuously in winter and regularly or periodically in the off-winter months. Manatees inhabit Broward County year round, continuously in the winter months and regularly in the off-winter months. Although to a lesser degree, Respondent considers radio telemetry data in its determinations regarding manatees. Radio telemetry is a data gathering technique which is not experimental, but is less revealing when used with manatees. Telemetry data is hard to acquire in the NICW because manatees' behavior of resting and traveling deploys the tag being used in a way which is not available to the satellite. As a result, every tagged manatee is not seen on every satellite pass. Data from telemetry studies show that manatees predominantly travel the ICW, and extremely infrequently in the ocean, and have a regular exchange between the Port Everglades and Riviera Beach plants. Tagged manatees, when located visually, are found in association with others. The behavior of radio-tagged manatees is representative of the population of manatees as a whole. Manatees travel in groups in the NICW. A congregation of mammals means more than one mammal together, without assigning a reason for the congregation. Manatees congregate in areas where they are sighted in groups of two to three or more. All of the available information taken together indicates that manatees congregate in the NICW, using it on a regular and frequent basis. Respondent considers the entire NICW, including the Hillsboro Inlet zone, as a single unit when interpreting manatee sightings because of the types of manatee behavior observed and the character of the NICW. Respondent also considers anecdotal data in its determinations regarding manatees. Anecdotal data is useful for confirmation of, but not for providing new insights about manatees and their behavior. Anecdotal sighting data are consistent with and confirm what is known by Respondent from other sources about manatees. Motorboats kill, maim and disturb manatees. Manatees have scars on their bodies, which are caused by collisions with watercraft. Virtually all manatees have propeller scars and approximately 900 are documented in what is known as the Scar Catalogue. Scar patterns on manatees indicate numerous collisions, some nine to ten times. The Scar Catalogue also indicates that manatees move back and forth between the Port Everglades and Riviera Beach plants. Since 1974, when Respondent started compiling manatee mortality data, of the manatees recovered for which the cause of death could be determined, 522 were attributed to watercraft collision. Of the 522 watercraft collision deaths, twenty-seven manatees were recovered in Broward County, which represents over one-half of the total manatee deaths in Broward County for which the cause of death could be determined. However, the recovery data fails, and is unable, to show where within the ICW or NICW the manatees were struck. After a collision, manatees will seek out a quiet area. It is not unusual and is expected that injured manatees in Broward County will seek refuge at the Port Everglades. Boat traffic poses a threat to manatees. Increased or higher boat traffic poses an elevated or even greater risk to manatees. Broward County waters are utilized by large numbers of boaters. In addition to Broward boaters whose boat registrations have increased eighteen percent between 1986 and 1991, boaters from Dade and Palm Beach Counties and in winter from out-of-state use Broward waters. Boating traffic in Broward County and the NICW is heavier on weekends than on weekdays. There is no change in the traffic for Broward County in the winter months from November through March. More boating occurs during the day than at night on the NICW. A survey of boaters in Broward County relied upon by Respondent indicated that over fifty percent of boaters leave between 8:00 a.m. and noon and return between 2:00 p.m. and 6:00 p.m.; that eighty-four percent of those surveyed were in favor of speed limits to protect manatees; and that fifty-nine percent of those surveyed were in favor of slow speed for the whole county on weekends and holidays from November to March. Comparatively, Respondent's slow speed rule is substantially less stringent than that which was found acceptable by those surveyed and not as stringent as recommended by the federal Fish and Wildlife Service. Several local governments in the NICW adopted resolutions calling for more stringent regulations than Respondent's rule. In an effort to lessen the interference with boaters while also providing an area of protection for manatees in the NICW, the 25 mph speed limit with the fifty-foot buffer zone was adopted. A slow speed zone in the NICW will enhance boating safety. At slow speed, only boats with propeller-on-shaft and a rudder will exhibit an unsafe condition referred to as wobbling. However, virtually no typical recreation boat which is under thirty feet is configured that way.
Findings Of Fact Petitioners, Larry C. and Jan D. Giunipero, reside at 2345 Tour Eiffel Drive, Tallahassee, Florida. On February 29, 1984, they obtained a building permit from Franklin County to construct a single-family dwelling on their lot in Alligator Point, Franklin County, Florida. The Giuniperos engaged the services of a professional engineer to design their beach house. In so doing, the engineer designed the structure so as to comply with the Federal Emergency Management Association (FEMA) guidelines, which are minimum building requirements established by the Federal Insurance Administration to qualify for federal flood insurance. These guidelines have been adopted by the Franklin County Planning and Zoning Department, and insure that the structure can withstand winds of 110 miles per hour. Even before the Guiniperos obtained their permit, respondent, Department of Natural Resources (DNR), was in the process of adopting new Rule 16B-26.14, Florida Administrative Code, which would establish a coastal construction line for Franklin County. Under the proposed rule, a coastal construction control line on Alligator Point would be established, and any excavation or construction activities thereafter on property seaward of the control line would require a permit from DNR, and have to be in conformity with all structural requirements set forth in Rule 168-33.07, Florida Administrative Code. Because the Guiniperos' lot lies on the seaward side of the control line, they were obviously affected by the rule. The rule adoption process was quite lengthy and well publicized. It began in October, 1983 when a public workshop was held in Apalachicola and aerial displays of the control line were placed in the courthouse. Further public hearings were held in Tallahassee in February, March and April, 1984. These hearings were the subject of numerous notices and advertisements in the Florida Administrative Weekly, Tallahassee Democrat, Apalachicola Times, Panama City News Herald, and Franklin County News. Clearly, the agency met all legal requirements in advertising the rule. However, for some reason, neither the Giuniperos or their professional engineer were aware of the pending rule change. Similarly, the Franklin County planner failed to advise them of the imminent rule change even though aerial displays of the proposed line were in the courthouse when the permit was issued. Rule 168-26.14, Florida Administrative Code, was adopted by the Florida Cabinet on April 5, 1984, and eventually became effective on April 30, 1984. As of that date, any construction or excavation work seaward of the control line required DNR to issue a permit unless a dwelling was already "under construction" in which case the project was grandfathered in. The parties agree that petitioners do not fall in this category since the dwelling was not "under construction" within the meaning of DNR rules. A few days before the rule became effective, a DNR engineer met with the Franklin County planner to review all building permits issued since September, 1983 for construction on the seaward side of the control line. The engineer did this so that he could inspect all building sites after the line became effective and determine which, if any, were "under construction" and therefore exempt from DNR permitting requirements. Because of the volume of permits issued to persons seeking to beat the April 30 deadline, and his unfamiliarity with alligator Point, the planner was unable to give the DNR engineer the precise location of petitioners' lot. On or about May 1, 1984, the engineer visited the general locale of petitioners' lot. There was no activity on petitioners' lot, and no permit posted on the site. Accordingly, he assumed a recently completed beach house some 300 feet east of petitioners' lot was actually the Giuniperos' house. Since it was already completed, he merely filed a report the following day indicating that "if the location referenced above is accurate, the structure appeared to be completed at that time." On July 6, 1984, petitioners proceeded to install twenty-three 8" by 8" pilings on their lot at a cost of $1,760. DNR discovered this construction activity a few days later and notified petitioners by telephone that such activity was illegal without a permit. A formal cease and desist order was sent on July 11, 1984, and no activity has taken place since that time. An application for a permit remains in abeyance pending the outcome of this proceeding. The structural requirements of DNR are more stringent than those previously required by Franklin County and FEMA. Indeed, the FEMA guidelines are not a part of a coastal construction regulatory program but are merely minimum standards to meet federal flood insurance criteria. Therefore, while the Guiniperos' proposed dwelling is designed to withstand a windload of 110 miles per hour DNR requires a structure to meet a windload of 140 miles per hour. DNR also recommends that larger and more expensive pilings be used, and that the structure be designed to adequately resist a 100 year return interval storm event. Because the DNR requirements are more stringent, petitioners estimate they will incur total costs of $8,890 just to pull out the old pilings and install larger ones. 1/ Additional costs may be incurred to redesign and build the structure to withstand a wind velocity of 140 miles per hour. By rule, DNR does not grant a waiver of its permit requirements except where a building is already constructed and an applicant desires to make "minor additions" to existing nonconforming structures. The Giuniperos do not qualify for such a waiver.
Recommendation Based on the foregoing findings of fact and conclusions of law, it is RECOMMENDED that petitioners' request for a waiver from the permitting requirements of Rule 16B-33.07 be DENIED. DONE and ORDERED this 11th day of March, 1985, in Tallahassee, Florida. Hearings Hearings DONALD R. ALEXANDER Hearing Officer Division of Administrative The Oakland Building 2009 Apalachee Parkway Tallahassee, Florida 32301 (904) 488-9675 Filed with the Clerk of the Division of Administrative this 11th day of March, 1985.
Findings Of Fact On September 15, 1976, Manatee Energy Company submitted to the Department of Environmental Regulation, through the Manatee County Pollution Control Department, an application to construct an air pollution source in connection with a crude splitter to be built at Port Manatee, Manatee County, Florida. On October 15, 1976 the Department of Environmental Regulation requested additional information from the Manatee Energy Company concerning its application. The primary response of the Manatee Energy Company to this request for additional information was hand carried to the Department of Environmental Regulation on November 3, 1976, at which time a meeting was held between representatives of the Department of Environmental Regulation and the Manatee Energy Company to discuss whether the additional information satisfactorily responded to the request. On November 9, 1976, representatives of the Manatee Energy Company met with representatives of the Manatee County Pollution Control Department to discuss the additional information and the status of the application. The Department of Environmental Regulation considered the application complete and, in fact, all requested additional information was received by the Department of Environmental Regulation no later than November 22, 1976. By letter dated December 14, 1976, to the Department of Environmental Regulation, the Manatee County Pollution Control Department recommended approval of the permit sought by the Manatee Energy Company. On February 17, 1977, the Department of Environmental Regulation issued a Notice Of Intent To Issue Its Final Agency Order approving the permit application for construction of the air pollution source sought by the Manatee Energy Company. This Notice Of Intent contained the statement that the final agency order approving the application would be adopted and issued by the district manager unless an appropriate petition for hearing was filed on or before February 20, 1977, pursuant to the provisions of Section 120.57, Florida Statutes. On February 17, 1977, the Manatee Chapter of the Izaak Walton League filed a Petition And Request For Public Hearing And Other Relief. At the time the petition was filed on February 17, 1977, neither the Manatee Chapter of the Izaak Walton League nor its parent organization, the Izaak Walton League of America was a corporation not for profit organized and operating under the laws of the state of Florida. However, at the time the petition was filed on February 17, 1977, the parent organization, the Izaak Walton League of America was a corporation not for profit organized in a state other than Florida. The Manatee Chapter of the Izaak Walton League has never filed a corporate charter or articles of incorporation with the Florida Secretary of State under that corporate name. Further, the Izaak Walton League of America has never filed a corporate charter or articles of incorporation with the Florida Secretary of State under that corporate name. On May 18, 1977, the Manatee Chapter of the Izaak Walton League of America, Inc. filed its articles of incorporation, as a corporation not for profit, with the Florida Secretary of State. The Manatee Chapter of the Izaak Walton League is chartered by the Izaak Walton League of America. The Manatee Chapter is a sub unit of the national organization. Members of the Manatee Chapter do not join the Manatee Chapter, but rather, join the national organization, the Izaak Walton League of America, and then affiliate themselves with the local chapter. According to the president of the Manatee Chapter of the Izaak Walton League their charter from the national organization requires that before the local chapter takes any legal action it must inform the national organization for their approval. In this case, the Manatee Chapter of the Izaak Walton League did inform the national organization, the Izaak Walton League of America, and received their approval, before filing the petition which initiated this proceeding. At no time pertinent to this cause had the Manatee Chapter of the Izaak Walton League, or the national organization, the Izaak Walton League of America, filed with the Florida Secretary of State a duly authenticated copy of its charter or articles of incorporation, together with the requisite fee and received from the Secretary of State a permit to carry on in Florida the objects and purposes of its incorporation as required by Section 617.11, Florida Statutes. As of the date of this hearing, July 21, 1977, the Department of Environmental Regulation has neither approved nor denied the application for permit by the Manatee Energy Company. The Notice Of Intent To Issue by the Department of Environmental Regulation and the filing of the Petition And Request For Public Hearing And Other Relief by Petitioner, Manatee Chapter of the Izaak Walton League, occurred 87 days after the receipt by the Department of Environmental Regulation of the timely requested additional information in connection with the application.
Recommendation Therefore, it is hereby RECOMMENDED: That the application for a permit to construct an air pollution source by the Manatee Energy Company which is the subject of this proceeding be granted and issued forthwith with the provision that an operating permit will not issue until such time as the Port Manatee Port Authority has taken the necessary corrective steps to eliminate the present violation of the ambient air quality standard with regard to particulates. ENTERED this 10th day of January, 1978, in Tallahassee, Florida. CHRIS H. BENTLEY Hearing Officer Division of Administrative Hearings The DeSoto Building 1230 Apalachee Parkway Tallahassee, Florida 32399-1550 (904) 488-9675 COPIES FURNISHED: Judith S. Kavanaugh, Esquire 543 Tenth Street, West Bradenton, Florida 33505 Terry Cole, Esquire Department of Environmental Regulation 2562 Executive Center Circle, East Montgomery Building Tallahassee, Florida 32301 Roger D. Schwenke, Esquire Post Office Box 3239 Tampa, Florida 33601
The Issue Whether Charles River Laboratories, Inc.'s (CRL) applications for permits for its primate facilities on Raccoon Key, Key Lois, and Summerland Key should be granted and, the conditions, if any, that should be attached to the permits.
Findings Of Fact THE PARTIES Charles River Laboratories (CRL) is a corporation that breeds rhesus monkeys on two offshore islands in the Florida Keys (Key Lois and Raccoon Key) and has a land base on Summerland Key.1 The Florida Game and Fresh Water Fish Commission is the agency of the State of Florida authorized to exercise the executive and regulatory powers of the State with respect to wildlife and fresh water aquatic species. Article IV, Section 9 of the Florida Constitution provides that authority as follows: There shall be a game and fresh water fish commission, composed of five members appointed by the governor subject to confirmation by the senate for staggered terms of five years. The commission shall exercise the regulatory and executive powers of the state with respect to wild animal life and fresh water aquatic life, except that all license fees for taking wild animal life and fresh water aquatic life and penalties for violating regulations of the commission shall be prescribed by specific statute. The legislature may enact laws in aid of the commission, not inconsistent with this section. The commission's exercise of executive powers in the area of planning, budgeting, personnel management, and purchasing shall be as provided by law. Revenue derived from such license fees shall be appropriated to the commission by the legislature for the purpose of management, protection and conservation of wild animal life and fresh water aquatic life. Curtis Kruer resides on Big Pine Key and maintains an office on Summerland Key. Mr. Kruer lives within a thirty minute boat ride of Raccoon Key and Key Lois. Mr. Kruer is a recreational fisherman and a licensed fishing guide and boat captain. He earns a portion of his livelihood as a fishing guide and has, in the past, chartered trips to the shallow waters surrounding Key Lois and Raccoon Key. In recent years, he has stopped fishing these areas because of what he perceives to be diminished fish population caused by degraded water quality and less seagrass extent and quality. Mr. Kruer considers his ability to use the waters in the vicinity of Raccoon Key and Key Lois to have been diminished as a result of what he perceives to be a threat to his safety and the safety of his clients posed by the free ranging monkeys on these two islands. Mr. Kruer has standing to challenge whether the subject permits protect the public safety. CRL’S POSSESSION OF WILDLIFE CRL established its monkey colony on Key Lois in 1973. It thereafter established its colony on Raccoon Key in 1976. CRL obtained its first license to possess wildlife from the Florida Game and Fresh Water Fish Commission (Commission) in 1973, and has received annual licenses ever since. These annual permits have been issued pursuant to the provisions of Section 372.921, Florida Statutes. Raccoon Key, Key Lois, and Summerland Key are within the Florida Keys Area of Critical State Concern. Key Lois, formerly known as Loggerhead Key, is located within the Florida Keys Marine Sanctuary approximately two miles south of Cudjoe Key in Hawk’s Channel, which is in the Atlantic Ocean. Raccoon Key is located in the Great White Heron National Wildlife Refuge approximately three miles north of Cudjoe Key in the Gulf of Mexico. The waters surrounding Raccoon Key and Key Lois are relatively shallow. There is a great deal of boating activity in the vicinity of both islands. CRL does not have an accurate count of the number of monkeys on either Key Lois or Raccoon Key and it does not maintain an accurate inventory of its monkeys. CRL’s best estimate at the time of the formal hearing was that there were approximately 200 free ranging monkeys on Key Lois and approximately 1,000 free ranging monkeys on Raccoon Key. The facility on Summerland Key is utilized for shipping and receiving, and no monkeys are permanently housed at that facility. CRL tattoos its adult monkeys, but it does not tattoo or otherwise mark its subadult monkeys. It is difficult to establish ownership of a monkey that has escaped and has been recaptured if the monkey has not been tattooed or otherwise marked. The Commission has reasonably determined that CRL should be required to keep an accurate inventory of the monkeys it possesses and that it should be required to mark for identification by tattoo, computer chip, or otherwise its monkeys that are one year old or older. An accurate inventory will assist CRL in knowing when a monkey is missing. Marking its monkeys will enable CRL to identify an escaped monkey after it has been caught. The free range monkeys on Raccoon Key and Key Lois are primarily used for breeding and are generally older monkeys that have lived in a free range society all of their lives. These free range monkeys have formed active social groups. CRL sells monkeys for use in medical research for numerous diseases and conditions affecting humans, such as osteoporosis, diabetes, Alzheimer’s disease, and AIDS. CRL’s monkeys have been isolated from human contact and are free from disease, including the Herpes B Virus. CRL’s monkeys are a valuable resource for medical research. CRL located its monkey colonies on Key Lois and Raccoon Key with the expectation that the location of the monkeys on these offshore islands would help keep the monkeys free from disease. CRL is licensed by the United States Department of Agriculture (USDA)as a dealer under the Animal Welfare Act, 7 U.S.C. 2131, et seq. CRL is prohibited by its registration under the Animal Welfare Act to sell its animals as pets or to any entity that has not been licensed either as a dealer or as a research facility pursuant to the Animal Welfare Act by the USDA.2 PRIOR CONSENT AGREEMENTS To settle a dispute with the Florida Department of Environmental Protection’s predecessor agency (the Florida Department of Environmental Regulation) CRL committed to eliminate free-ranging animals from Key Lois by the year 2003 and from Raccoon Key by the year 2008. CRL has begun to eliminate free range animals from both islands pursuant to that agreement. To settle a dispute with the Trustees of the Internal Improvement Fund filed in the Circuit Court of the Sixteenth Judicial Circuit in and For Monroe County (Case 86-190-CA-13), CRL agreed to cease its operations on Key Lois and convey title to the State of Florida no later than December 31, 2012. It also agreed to cease its operations on Raccoon Key and quitclaim its ownership of Raccoon Key no later than December 31, 2024, to the United States for inclusion in the National Wildlife System. THE APPLICATION CRL is the applicant for the permit that is the subject of these proceedings. Paul Schilling, D.V.M., has been the director of CRL’s monkey breeding activities in the Florida Keys since 1983. The permit that immediately preceded the permits at issue in this proceeding was issued by the Commission with an effective date of issuance as June 29, 1994. The date of expiration was July 4, 1995. On June 8, 1995, the Commission mailed to CRL a written renewal notice. The Commission’s policy is to accept as timely renewal applications for up to thirty days following the stated expiration date of the former permit. Under that policy, CRL timely filed the applications for the subject permits (one for Key Lois, one for Raccoon Key, and one for Summerland Key). The initial renewal application was filed after July 4, 1995, but within the thirty day grace period. Because the applications were submitted without the signature of a representative of CRL, the applications were returned to CRL for Dr. Schilling’s signature. Consistent with its practice, the Commission accepted the applications after they were signed and resubmitted as applications for renewal of the existing permits even though the completed applications were not received until July 24, 1995. The Commission’s action in treating the applications as renewals is not explicitly authorized by rule, but it is consistent with the Commission’s established policy. Under Commission policy, while a license renewal is being processed, the facility is still under license and the renewed permit is issued retroactive to the expiration date of the previous permit so that there is no gap in licensure. Under Commission policy, CRL remains a licensed facility pending the outcome of this administrative proceeding. CRL’s application states on its face that the “Company breeds Rhesus monkeys, Macaca mullata for sale to commercial laboratories.” This activity is described as being “COMMERCIAL ACTIVITY.” CRL captures most of the younger animals for sale or placement in captive breeding facilities. The application for Raccoon Key required the applicant to provide the “exact number by species” of wildlife to be possessed”. In response thereto, CRL provided the following: “Approximately 2,000 Rhesus Monkeys (Macaca mullata) animals are free range and group housed on an island off the Florida Keys (Raccoon Key).” The amount of the application fee was $25.00, the amount charged for eleven or more animals. The application for Key Lois also required the applicant to provide the “exact number by species” of wildlife to be possessed.” In response thereto, CRL provided the following: “Approximately 1,500 Rhesus Monkeys (Macaca mullata) animals are free range and group housed on an island off the Florida Keys (Key Lois).” The amount of the application fee was also $25.00, the amount charged for eleven or more animals. The application for Summerland Key was for “Holding of 0 - 8 Rhesus under clinical care." The Commission accepted and processed CRL’s application consistent with its established policies. THE APPLICABLE STATUTES Section 372.021, Florida Statutes, provides as follows: The Game and Fresh Water Fish Commission may exercise the powers, duties and authority granted by s. 9, Art. IV of the Constitution of Florida by the adoption of rules, regulations, and orders in accordance with chapter 120. Section 372.921, Florida Statutes, provides, in pertinent part, as follows: In order to provide humane treatment and sanitary surroundings for wild animals kept in captivity, no person, firm, corporation, or association shall have or be in possession or, in captivity for the purpose of public display with or without charge of for public sale any wildlife, specifically birds, mammals, and reptiles, whether indigenous to Florida or not, without having first secured a permit from the Game and Fresh Water Fish Commission authorizing such person, firm, or corporation to have in its possession in captivity the species and number of wildlife specified within such permit; however, this section does not apply to any wildlife not protected by law and the regulations of the Game and Fresh Water Fish Commission. Section 372.922, Florida Statutes, provides, in pertinent part, as follows: It is unlawful for any person or persons to possess any wildlife as defined in this act, whether indigenous to Florida or not, until she or he has obtained a permit as provided by this section from the Game and Fresh Water Fish Commission. * * * (4) Any person, firm, corporation or association exhibiting or selling wildlife and being duly permitted as provided by s. 372.921 shall be exempt from the requirement to obtain a permit under the provisions of this section. CRL’s sale of monkeys to commercial laboratories is a “public sale” within the meaning of Section 372.921, Florida Statutes. CRL’s monkey breeding operation in the Florida Keys requires a permit from the Commission pursuant to Section 372.921, Florida Statutes. THE APPLICABLE RULES Chapter 39-6, Florida Administrative Code, has been duly adopted by the Commission and is intended to implement Sections 372.921 and 372.922, Florida Statutes. The title to this chapter, “Wildlife as Personal Pets.” While this title is misleading, CRL knew that its operations were regulated by these rules of the Commission. Rule 39.6.0011, Florida Administrative Code, pertains to the possession of wildlife in captivity and provides, in pertinent part, as follows: Except as otherwise provided by this Title, no person shall possess any native or non-native wildlife in captivity except as authorized by permit issued in accordance with ss. 372.921 or 372.922, F.S., and as provided in this chapter. The provisions of this chapter shall not apply to entities operating solely as research facilities which are registered and regulated as such in accordance with Animal Welfare Act (7 U.S.C. 2131 et seq.) and regulations promulgated thereunder. Rule 39-6.002(1)(b)9, Florida Administrative Code, classifies macaques (genus Macaca) as Class II wildlife, which are wildlife “considered to present a real or potential threat to human safety." See, Section 372.922(2)(b), Florida Statutes. Under Rule 39-6.0023, Florida Administrative Code, Class II wildlife are required to be caged or, if unconfined, are required to be maintained under rigid supervision and control, so as to prevent injuries to members of the public. Rule 39-5.004(5), Florida Administrative Code, provides the following criteria pertinent to this proceeding:: The severity of the conduct; The danger to the public created or occasioned by the conduct; The existence of prior violations of ch. 372, F.S., or the rules of the commission; The length of time a licensee or permittee has been licensed or permitted; The effect of denial, suspension, revocation or non-renewal upon the applicant, licensee, or permittee’s existing livelihood; Attempts by the applicant, licensee or permittee to correct or prevent violations, or the refusal or failure of the applicant, licensee, or permittee to take reasonable measures to correct or prevent violations; Related violations by an applicant, licensee or permittee in another jurisdiction; The deterrent effect of denial, suspension, revocation or non-renewal; Any other mitigating or aggravating factors. The provisions of Rule 39-5.004(5), Florida Administrative, are the duly adopted rules of the Commission providing permitting criteria and those provisions were applied by the Commission in processing the subject permits. THE CHALLENGED PERMITS AND ADDENDUM On March 29, 1996, the Commission issued its “Notice of Intent to Issue Renewal of a Permit to Possess Wildlife for Exhibition or Public Sale with Addendum” that provided, in pertinent part, as follows: This is a notice of intent to renew the permit to authorize Charles River Laboratories, Inc. (CRL), to possess for breeding and sale, sub-human primates on Key Lois and Raccoon Key in Monroe County, Florida, in accordance with Section 372.921, Florida Statutes, and Rule 39-6, Florida Administrative Code, consistent with the following Addendum to enhance public security and prevent escapes of primates: GENERAL FINDINGS The water surrounding Key Lois and Key Raccoon (sic) and the remote location of the islands were once believed to constitute an adequate barrier to prevent escape of primates from the islands and to prevent interference with the primate population by unauthorized persons. However, primates have escaped (or have been removed without CRL’s authorization) from the islands, and the islands are not secure from those who may seek to trespass or enter upon them. Accordingly, the Commission finds that water alone is no longer an adequate barrier to prevent escape of the resident primates and to prevent entrance upon the islands by unauthorized persons. Therefore, affirmative security measures are required for public safety. CRL is subject to a Petition for Appeal of Development Order in the case of The Department of Community Affairs v. Charles River Laboratories, Inc., et al., Case No. 96-1405DRI, FLAWAC APP-96-003 (Florida Land and Water Adjudicatory Authority Commission), which asserts that the continued use of Raccoon Key and Key Lois as a primate facility will adversely impact the quality of nearshore waters, mangroves, seagrass beds and other marine resources; and therefore, the facility is inconsistent with the Principles for Guiding Development for the Florida Keys Area of Critical State Concern. The Board of Trustees of the Internal Improvement Trust Fund of the State of Florida has filed a Motion to Enforce a Consent Final Judgment in the case of Charles River Laboratories, Inc. v. Trustees for the Internal Improvement Trust Fund. Case No. 86-190-CA-13. The Commission shall fully coordinate and cooperate with the Department of Community Affairs and the Department of Environmental Protection in their efforts to resolve the above-cited actions. ADDENDUM Special Permit Conditions as to Key Lois only: CRL shall eliminate all free-ranging primates from Key Lois no later than December 31, 1996. Special Permit Conditions as to Raccoon Key only: CRL shall eliminate not less than thirty-three percent (33%) of free-ranging primates from Raccoon Key by December 31, 1996, shall eliminate not less than sixty-six percent (66%) of the total free-ranging primates from Raccoon Key by December 31, 1997, and eliminate all remaining free- ranging primates from Raccoon Key by December 31, 1998. Special Permit conditions as to security on Key Lois and Raccoon Key: CRL shall institute random water security patrols of the islands during non- work hours; CRL shall provide cellular telephones to all personnel working the islands to insure more rapid reporting and responses to escapes or thefts; CRL shall install chains and locks to all temporary and permanent caging; CRL shall provide remote sensing alarms, or in the alternative, provide day- time security personnel on site on both Keys during periods when CRL personnel are not present; CRL shall immediately tattoo or permanently mark all adult and subadult primates as they are captured and caged, so that ownership can be positively identified in the case of escape or theft. CRL shall comply with all sanitation, water disposal and waste disposal requirements provided by local, state or federal law. CRL shall reimburse the Commission in the amount of $1000 per primate, payable to the Florida Game and Fresh Water Fish Commission, as reimbursement for the Commission’s costs associated with the investigation or recapture of primates which have escaped or which have been removed without CRL’s authorization from the CRL facility. All primate escapes or thefts from the CRL facility must be reported to the Tallahassee Office, (904)488-6253, of the Commission immediately. CRL shall at all times maintain a complete and accurate inventory of all primates on Key Lois and Raccoon Key and shall submit such inventory records to the Commission (a) within thirty (30) days of the date of issuance of this permit, (b) at the Commission’s request, upon an escape or unauthorized removal of a primate from the facility, and (c) no later than thirty (30) days prior to the expiration of this permit. The inventory shall include the total number of primates held in field cages on each island, the total number of free-ranging primates on each island and numbers of primates brought to the CRL facility as of January 1, 1996. This permit may be subject to revocation, suspension, or non-renewal in accordance with Rule 39-5.004, F.A.C. Nothing herein shall authorize CRL to construct or maintain any structure or facility that would be in violation of the Monroe County Comprehensive Land Use Plan, the Monroe County Code and the Principles for Guiding Development in the Florida Keys Area of Critical State Concern or in violation of any final order, judgment, or settlement agreement thereto in the case of Department of Community Affairs vs. Charles River Laboratories, et al., DOAH Case No. 96- 1405DRI, FLAWAC APP-96-003 (Florida Land and Water Adjudicatory Commission). This permit will be effective twenty- one (21) days from the date of receipt of this notice by the applicant or within twenty-one (21) days from the date of publication of this notice, whichever is later. This addendum to permit will expire concurrent with the expiration of the Permit to Possess Wildlife for Exhibition or Public Sale, unless otherwise authorized by the Executive Director. THE 1990 CORRESPONDENCE On September 21, 1990, Robert M. Brantly, the Commission’s Executive Director, wrote to Dr. Schilling a letter that contained the following discussion on the issue of safety: F.A.C. 39-6.003(1)(a), requires, “A fence sufficient to deter entry by the public shall be present around the premises wherein Class I or Class II animals are housed or exercise outdoors.: There are no perimeter fences around Key Lois or Raccoon Key, and Rhesus macaques are classified as Class II animals. In the past, we have considered the water surrounding your facilities as a barrier to escape and public access. During the August 24th inspection, we found that water alone does not meet the intent of the regulation requiring a security fence. Past security breeches documented on that inspection included: The holding compound was broken into on Raccoon Key. The intruders released numerous primates. It is also possible that a theft of some primates occurred. This incident occurred four years ago. The holding compound was broken into again about two or three years ago. A macaque escaped twice (same animal) about five years ago. Employees recaptured the animal on Little Crane Key. A generator was stolen from one of the islands. You did not report the escapes to us as required in you agreement with the Commission, nor were we made aware of the security problems. To prevent future security breeches, you must construct a fence capable of deterring entry by the public and preventing the escape of the macaques from the islands. As an alternative to a monkey- proof fence, you may confine the primates in enclosures that meet minimum pen specifications; however, you must still construct a fence that will deter entry by the public. In October 1990, there was a meeting between Col. Brantly and Dr. Schilling and Mr. Routa, the attorney for CRL. On November 5, 1990, Col. Brantly wrote to Dr. Schilling a letter that contained the following: Having met with you and Mr. Routa on October 23, 1990, we now determine that the Laboratory [CRL] may continue to operate under its current captive animal permit without the perimeter fence required by Rule 39-6.0023, Florida Administrative Code. This rule requirement was not applied to the Laboratory because the water barrier around the keys was believed to provide adequate security to prevent monkeys from escaping and unauthorized persons from entering the facility. However, if a primate escapes or if unauthorized entry by the public were to occur, the water barrier would no longer be considered adequate security and appropriate action under Rule 39-6.002, F.A.C., would be taken. We ask that the Charles River Laboratory report, immediately and in writing, all incidents of escape of any monkeys from the islands or unauthorized public entry of the facilities. We further require, in accordance with Rule 39-9.002, F.A.C., that the Laboratory apply for a permit to capture any monkey which has escaped the islands. (Emphasis added.) The facts reflected by Col. Brantly’s two letters were accurate. ESCAPES SUBSEQUENT TO 1990 There have been several escapes of monkeys from Key Lois or Raccoon Key since the Commission’s 1990 letters. In addition, there have been unauthorized intrusions on these islands since 1990. On or about August 4, 1993, a CRL monkey (tattoo #81- 688) escaped from Raccoon Key to Little Crane Island which is approximately one-half mile from Raccoon Key. Little Crane Island is part of the Great White Heron Wildlife Refuge. The staff of the wildlife refuge shot and killed the monkey after attempts to tranquilize it failed. In 1994, a monkey was sighted on Big Torch Key and a monkey was also sighted on Little Torch Key. Both of these keys are approximately one-half mile from Raccoon Key. The monkey on Little Torch Key was a CRL monkey (tattoo #F-513), and was recaptured by CRL staff. The ownership of the monkey sighted on Big Torch Key was not established. In 1995, a CRL monkey escaped to Cudjoe Key, which is approximately two miles from Raccoon Key. This one-year old male was captured and returned to CRL. A second CRL monkey was sighted on Cudjoe Key in 1995. The Commission’s investigation revealed that this monkey had been taken from Key Lois by intruders and subsequently released. Another CRL monkey was stranded on a channel marker off Big Torch Key and recaptured by CRL. Rhesus monkeys are capable of wading or swimming from Raccoon Key and Key Lois to nearby islands. Most of the islands in the vicinity of Raccoon Key and Key Lois are capable of sustaining monkeys. Several of these nearby islands are residential areas. There is a lack of security for the CRL facilities on Raccoon Key and on Key Lois. There is no security personnel on either Raccoon Key or Key Lois after normal working hours. The additional security measures required by special permit condition 3 and its subparts are reasonable whether the CRL animals remain free range or are caged. POTENTIAL DANGER TO THE PUBLIC Rhesus monkeys have been known to attack humans if cornered or sufficiently provoked. Free range monkeys grow to approximately 30 pounds and are capable of inflicting serious injury on a human. Because they present a potential to humans, rhesus monkeys are appropriately classified as Class II wildlife by the Commission. There has not been an injury to a member of the public since CRL began its operations in 1973. This absence of injury is primarily attributed to the fact that the CRL monkeys are shy of humans because of the environment in which they were raised. Instead of attacking humans, it is more likely that an escaped monkey would run from humans. Although there is no perimeter fencing around either Raccoon Key or Key Lois, it is not appropriate to recommend such fencing as a means of preventing escapes because Rhesus monkeys can escape from fencing. The potential danger to the public posed by these free ranging animals can be eliminated only by removing all free ranging animals from both islands. The Commission has appropriately determined that CRL should be required to eliminate the free range populations from both islands. With adequate time, CRL can safely and humanely remove all free-ranging monkeys from Key Lois and Raccoon Key and continue its breeding operations with its monkeys being caged. If CRL elects to continue its operations by using cages on Key Lois and Raccoon Key, it would have to obtain all pertinent permits, including building permits from Monroe County, in order to construct the necessary cages to house the former free ranging monkeys. ENDANGERED SPECIES Silver rice rats are listed by the U.S. Fish and Wildlife Service and by the Commission as an endangered species. Raccoon Key provides a valuable habitat for this endangered species. The free-ranging monkey population has enhanced Raccoon Key as a habitat for silver rice rats because of the monkey chow and the fresh water that are made available. The additional caging that will be necessary for CRL to construct to eliminate the free-range population should be located in areas that will not destroy the silver rice rat habitat. Although Raccoon Key is within the National Key Deer Refuge, there was no evidence that Key Deer have historically used Raccoon Key. Key Deer would be more likely to use Raccoon Key if the monkeys were not present. Monkeys have destroyed habitat used by nesting birds and the mangrove terrapin. In determining that the free range monkeys should be eliminated, the Commission has considered the impacts of the free ranging monkeys on Raccoon Key and Key Lois on these species. Since the Commission’s responsibilities extend to these species, it was appropriate for the Commission to consider these impacts. HURRICANE VULNERABILITY Key Lois and Raccoon Key are vulnerable to hurricanes. These islands and all structures thereon would likely be inundated if a major hurricane were to strike them. While free- ranging monkeys would have a good chance of surviving a hurricane, any caged monkeys on Key Lois and Raccoon Key would likely drown when the storm surge inundates the cages.
Recommendation Based on the foregoing findings of fact and conclusions of law, it is RECOMMENDED that the Commission enter a final order that renews the subject permits with the special conditions recommended herein. DONE AND ENTERED this 23rd day of January, 1997, in Tallahassee, Florida. CLAUDE B. ARRINGTON Administrative Law Judge Division of Administrative Hearings The DeSoto Building 1230 Apalachee Parkway Tallahassee, Florida 32399-3060 (904) 488-9675 SUNCOM 278-9675 Fax Filing (904) 921-6847 Filed with the Clerk of the Division of Administrative Hearings this 23rd day of January, 1997.
Findings Of Fact Citizens for Responsible Boating, Inc., the Petitioner, is a not-for- profit corporation organized under the laws of Florida. Its approximately 500 members own, sell and use boats and boat related products on the waters regulated by the State. Their purposes are to promote boating and water sports and to protect the boating public's right to access and use of Florida waters. The Department of Environmental Protection ("DEP") is the state agency with primary responsibility for rulemaking to regulate boat speeds incident to protection of manatees, pursuant to Subsection 370.12(2), Florida Statutes. After a series of public hearings on earlier versions of the rule, the Secretary of DEP approved the rules on August 11, 1993, to be effective on September 9, 1993. Subsection 370.12(2), Florida Statutes, the Florida Manatee Sanctuary Act, was enacted to give DEP the authority to regulate: (f). . . the operation and speed of motorboat traffic, only where manatee sightings are frequent and it can be generally assumed, based on available scientific information, that they inhabit these areas on a regular or continuous basis . . . . The challenged rules enacted pursuant to the Act have the effect of limiting boat speeds in western Volusia County in the Hontoon Dead River, and the parallel St. Johns River, roughly from a point just south of the Beresford Peninsula at Marker 63 extending south to Marker 81; and in eastern Volusia County on the Indian River from the North Bridge in New Smyrna Beach through Ponce Inlet to Rock House Creek, and on the Indian River in Edgewater and Oak Hill from Marker 65 to Marker 9A. The waterways are designated year round slow speed zones. Slow speed zones are, according to the definitions in Rule 16N- 22.002, designated areas . . . "within which it has been established that manatees are known to congregate." Eastern Volusia County (Halifax and Indian River) In the slow speed zone north of New Smyrna Beach, Michael Godfrey, Sr., a boat dealer from Edgewater who formerly water-skied in the area, reported seeing probably 6 manatees over 27 years. His average speed on the water was 45 miles per hour in boats, and in excess of 38 miles per hour on water-skis. The only manatees he is able to see are the ones which have come to the surface of the water to feed. High speed corridors are included in most of the Volusia County waterways. Exemptions from the speed limits are available for boat dealers with service departments, but no application has been made based on Mr. Godfrey's unexplained conclusion that it is not economically feasible. What was a 15 minute demonstration ride for boats from his Edgewater dealership through the Ponce Inlet prior to the enactment of speed restrictions, now takes 45 minutes. Water-skiing is impossible in the slow speed zone, and because he is a professional skier, Mr. Godfrey has to use a freshwater lake in Volusia County to ski at speeds exceeding 35 miles per hour. The nearest available freshwater lake is 35 miles from Edgewater. For nonprofessionals, water-skiing is still available in a 35 mile per hour designated water sports area near a power plant. That area is particularly congested on weekends. The water temperature is usually below 68 degrees in December, January and February. Surface temperatures go as low as 58 degrees. The rule also applies to jet skis and other types of personal watercraft, skies which average 300 pounds in weight, and extend approximately three inches into the water and have no propellers. These watercraft are not equipped with speedometers. Some barges on the St. Johns River extend six feet into the water and have not had the speed at which they operate affected by the rule. The speed allowed for boats depends, in part, on the type of hull. Mr. Godfrey knows how to determine if a boat is operating on a plane, not causing a wake, and coming off plane. A United States Coast Guard licensed ocean master, Edward J. Stupack, Jr., operated commercial fishing, diving and tour boats in Volusia County to see shuttle launches and to tour Tomoka State Park. The speed limits have caused him to eliminate Tomoka State Park tours, because trips that took four hours now take a full day. Shuttle launch tours which previously took 1 1/2 hours to the shuttle, now take 3 to 4 1/2 hours to the shuttle site. Registration for the Greater Daytona Strike and Fish Tournament has fallen from 250 boats to less than 200 in the past two years. At slower speeds, more carbon collects in boat engines, and more maintenance is required. In addition, exhaust fumes and heat make boat rides less comfortable at slow speeds. In eleven years of boating in eastern Volusia County, Mr. Stupack has seen two manatees both hugging the shoreline, one going out Ponce Inlet to sea and another around Rock House Creek. There is undisputed expert testimony in this case, however, that manatees do not always, or as a general rule, travel along the shoreline. Mr. Stupack has not applied for an exemption from the rules because he does not believe his small, part-time business has enough clout. In the 50 miles of Intercoastal Waterway from Flagler to Brevard County, eight of the total ten and a half miles regulated were regulated idle speed areas for boating safety prior to the manatee protection speed limits. The manatee slow speed zone resulted in the addition of two and a half miles of regulated area. There are two designated recreational areas along the 50 miles. DEP relied, in part, on the 1988 report of the Marine Manual Commission to support regulation in Eastern Volusia County. Western Volusia County (St. Johns River) Richard E. Rawlins, the owner and operator of a fish camp in Deland with a 150 boat slip and 59 unit campground, operates guided fishing tours exclusively in the St. Johns River Basin from Lake George at Putnam County to Lake Monroe in Seminole County. Prior to the adoption of the rule, idle zones existed around bridges and marinas on the St. Johns. Mr. Rawlins operated guided fishing tours at speeds of 40 to 45 miles per hour. The camp is close to bankruptcy having gone from 8 to 3 employees, from 80 to 85 percent to 10 percent wet storage occupancy and 30 to 35 percent dry storage occupancy. Having received three tickets and many warnings for exceeding the speed limit, Mr. Rawlins has reduced, by approximately half, his own recreational boating and fishing. Pulling persons on innertubes has also been eliminated by slow speeds, which he estimates equates to 5 to 7 miles per hour, as compared to innertubing at 40 miles per hour prior to the rule. Although, innertubing at 40 miles per hour was probably unsafe. Mr. Rawlins 20 foot boat with a 200 horsepower engine gets up on a plane at approximately 28 miles per hour and maintains a plane at 25 miles per hour. Prior to the rule, water-skiing on the St. Johns occurred primarily between Markers 38 and 20 at Cross Creek. The area now has a 30 mile per hour speed limit above Marker 32 and 25 miles below it. From the fish camp to the lower basin of the Hontoon Dead River takes over four hours, as compared to 45 to 50 minutes by boat prior to the adoption of the rule. The camp's operation of bass fishing tournaments has been eliminated by the inability to cover greater distances in shorter periods of time. In 32 years of St. Johns River boating and fishing, Mr. Rawlins estimates having seen manatees on one of every 18 to 20 trips, although the waters of the St. Johns River and its tributaries are relatively dark. He recalls one boat related manatee killing near his camp two and a half years ago, and a couple more at the Hontoon Dead River at about the same time. Recently, he has seen manatees outside of the Blue Springs area near Marker 20. Prior to that, he had not seen manatees in the area for 60 to 70 days. Although it varies, generally in December, January and February, the guide sees up to 70 manatees congregating in Blue Springs. When water temperature drops below 68 degrees in the rest of the river basin, the manatees move to Blue Springs because of its constant water temperature of 72 degrees. Mr. Rawlins does not need a speedometer to determine whether his boat is settled in the water. Because different boats settle differently depending on the type of hull, Mr. Rawlins believes Marine Patrol enforcement is not uniform. The speed limits in the areas north of the camp in the Norris Dead River to Lake Woodruff are at least 25 miles per hour, except for areas of idle zones established for marinas and for public safety, but not under the manatee protection rules. Access to southern fishing areas through the Hontoon Dead River have been adversely affected by the rule. Mr. Rawlins has not filed any written application for an exemption from the rule. He claims to have applied and been turned down by telephone. One boat manufacturer in Volusia County has received an exemption to test its boats at higher speeds. William B. Flowers, Sr., is a fishing guide who lives near the Lake Beresford Peninsula, and operates a 14 foot boat powered by a 48-horsepower motor at slower speeds than 300 foot long barges pushed by tugboats with two five foot propellers. It now takes approximately 4 hours to reach the areas of the Wekiva, River which he could reach in 35 minutes prior to the adoption of the rule. He will not apply for an exemption from the rule based on concern for his neighbors who would still have to adhere to the slow speeds. Lake Beresford is too crowded with fishermen to also accommodate water-skiers. Lake Woodruff and Lake Dexter are in a Federal Wildlife Refuge infested with alligators. On the St. Johns River, three miles of idle speed zone is imposed for boating safety and an additional nine-tenths of a mile for manatee protection, seven miles around Blue Springs and south of it, and another four and a quarter miles going into the southern Norris Dead River. The best estimate is that two thousand manatees live in Florida waters. Up to 76 manatees spend some time during the winter months in Blue Springs, particularly when water temperatures elsewhere drop to 20 degrees Centigrade or 68 degrees Fahrenheit. As water temperature approaches 50 degrees, manatees stop feeding and must get to warmer water to survive. Except for times of the most severe cold fronts, manatees in Blue Springs venture out into the St. Johns River system on a daily basis. In general, they venture out 12 kilometers from the springs, but have been known to go to Jacksonville. Mr. Flowers sees manatees around the springs from December to early March, and a few in Lake Beresford when there is grass left in the lake. The Regulations Rule 16N-22.003(6) authorizes exemptions for commercial fishermen and professional fishing guides and adopts, by reference, a written application form. Exemptions may not be granted for speeds in excess of 20 miles per hour nor in "motorboat prohibited" and "no entry" zones. There have been no denials of exemption applications from Volusia County. One exemption has been granted in Volusia County, other applications are pending. DEP relied, in part, on the Bengston study of manatees in the St. Johns River, which shows manatees move from one area to another depending on the availability of grasses for feeding. DEP also relies on the federal Endangered Species Recovery Plan for Manatees, which lists as its first priority reducing boating speeds in order to reduce boating-related accidental manatee deaths. A killing of a manatee by personal watercraft has been reported in Puerto Rico. There are no documented cases of manatees being killed by airboats. The rules apply to personal watercraft and airboats. Although, there was undisputed expert testimony that exemptions are available for airboats in some slow zones. In the last 15 to 20 years, an average of two manatees a year have been killed in Volusia County. There was no evidence of the types of watercraft causing the fatal injuries. Average boating speeds in Broward, Palm Beach and Pinellas Counties are 26 to 28 miles per hour, and lower in the rest of Florida. The majority of smaller recreational boats plane safely at speeds of 25 miles per hour or less. Because of its size and depth of the hull, DEP acknowledges that a barge going 5 miles per hour may pose more danger to manatees than smaller vessels traveling faster. The meaning of slow speed, as taught to Marine Patrol officers, is that a vessel is fully settled and level in the water and the wake does not endanger other vessels operating on the water or tied up along the shore. If an officer approaches a boat which settles into the water after reducing its speed, then the boat has not been operating at a slow speed. The view from a moving boat is a poor vantage point to determine the presence of manatees. Manatees are only able to move at speeds up to 15 miles per hour for short distances. To allow vessels to plane at approximately 20 miles per hour, 25 miles per hour zones have been adopted due to the absence of lower effective boat speeds between slow and 25 miles per hour, at which a boat could plane. The regulations also include 30 and 35 mile per hour speed zones. At 30 miles per hour, virtually all vessels, except the largest cigarette boats, can plane. At 35 miles per hour, innertubing, parasailing and water-skiing are possible if the water is deep and wide enough, except for barefoot and professional water- skiing. Although many boats are not equipped with speedometers, relatively accurate and inexpensive ones are available to determine speeds in excess of 10 miles per hour. Personal watercraft and jet skis cannot be equipped with speedometers. Other methods for determining speed are frequently used by boaters. Some of the higher speed zones in Volusia County decrease to 25 miles per hour at night, although moving boaters are unlikely to see manatees and manatees are unlikely to see boats. Manatees are able to see only two or three feet ahead, depending on water clarity, but there was unrefuted expert testimony that they are more aware of surroundings in daylight and better able to sense where to move to avoid boats.
