Findings Of Fact Upon consideration of the oral and documentary evidence adduced at the hearing, as well as those facts stipulated to by the parties, the following relevant facts are found: Petitioner, Southeastern Fisheries Association, Inc., is a not-for- profit incorporated association of commercial fishermen, fish processors, fish dealers, fish brokers, seafood restaurants and retailers, employing approximately 14,000 employees, and including 450 corporate and individual members. The executive offices of Southeastern Fisheries Association, Inc. are located at 312 East Georgia Street, Tallahassee, Florida 32301-1791. The members of Southeastern Fisheries Association, Inc., either catch, process, transport or sell Spanish mackerel and Spanish mackerel constitutes a major part of their business and livelihood. Petitioner, Organized Fishermen of Florida, Inc., is a not-for-profit incorporated association of 2,000 commercial fishermen, fish processors, fish dealers, fish brokers, seafood restaurants and retailers, with its headquarters at P. O. Box 740, Melbourne, Florida 32901. Petitioner, Harry H. Bell & Sons, Inc., is a fish processor and sales company employing about 210 employees, located at 756-28th Street South, St. Petersburg, Florida 33712. A large percentage of the fish processed by Harry H. Bell & Sons, Inc., are Spanish mackerel. Petitioner, Bayside Shellfish, Inc., is a fish processor and fish seller, located at P.O. Box 176, Apalachicola, Florida 32320. This petitioner also obtains a substantial amount of its business through the processing and sale of Spanish mackerel. Petitioner, Inlet Fisheries, Inc., is a corporation with its headquarters at P. O. Box 3604, Ft. Pierce, Florida 33450, which unloads and ships fish, and, in particular, Spanish mackerel. Petitioner, J. O. Guthrie, Inc., is a fish processor located at P.O. Box 895, Ruskin, Florida 33570. This petitioner processes fish, including Spanish mackerel, which makes up a high percentage of its fish processing. Petitioner, C. & W. Fish Co., Inc., is a company which unloads and ships fresh fish, located at P.O. Box 1356, Port Salerno, Florida 33492. This petitioner earns its living from the loading and shipping of fresh fish including Spanish mackerel. Petitioner, City Fish Company, Inc., also unloads and ships fish and is located at 3880 Gulf View Avenue, Marathon, Florida 33050. Intervenor, Florida Conservation Association, located at 402 West College Avenue, Tallahassee, Florida 32301, is an affiliate of the Coastal Conservation Association, a non-profit corporation incorporated under the laws of Texas. Effective November 28, 1985, the Marine Fisheries Commission (MFC) adopted rules relating to the commercial harvesting of Spanish mackerel on the East Coast of Florida. As pertinent to this proceeding, those rules prohibited the harvesting of Spanish mackerel by power-assisted gill netting in Dade and Palm Beach Counties, and imposed a 3 and one half-inch mesh size minimum for the monofilament portion of gill nets used to take Spanish mackerel from the remainder of the East Coast of Florida until March 15, 1990. After that date, the entire net was to have a minimum mesh size of 3 and one half inch stretched mesh. These net size requirements were applicable to all gill nets used on the East Coast to harvest Spanish mackerel during the period from November 15th to March 15th. The existing rule allows the harvest of Spanish mackerel as an incidental by-catch of other lawfully targeted species, so long as the combined weight does not exceed 15 percent of the total weight of the lawfully harvested species. The challenged proposed amendments to the MFC's Spanish mackerel rules continue the Palm Beach and Dade Counties gill net closures; establish gill net minimum sizes for three different regions of Florida; closes the weekend harvesting of Spanish mackerel by use of any nets; establishes set seasons for operators of vessels greater than 40 feet in length using power- assisted gill nets, said seasons subject to being shortened if the total regional commercial catch is projected to reach a specified poundage; and imposes a limit on the number of Spanish mackerel which recreational fishermen may possess per day. More specifically, the challenged proposed rules impose the following net size requirements on the harvesting of Spanish mackerel for the three regions of Florida. For the East Coast, defined as those state waters north of the Dade-Monroe County line, the period of the 3 and one half inch mesh size for the monofilament portion of gill nets is shortened to October 1, 1988, with the required minimum size being increased to 3 5/8- inches thereafter until October 1, 1990, whereupon all portions of gill nets are to be 3 5/5 inches stretched mesh. For the Southwest Coast, defined as state waters between the Taylor-Dixie County line and the Dade-Monroe County line, the minimum monofilament portion mesh size is 3 3/8 inches until October 1, 1988, increasing to 3 5/8 thereafter until October 1, 1990, whereupon the entire net is to have a minimum mesh size of 3 5/8 inches stretched mesh. The corresponding requirement for the Northwest Coast, defined as state waters west of the Taylor-Dixie County line, is 3 inches until October 1, 1988, increasing to 3 5/8 inches thereafter. Except for the 15 percent by-catch allowance provided in the existing rule, harvesting Spanish mackerel by use of any net is prohibited in all three regions on weekends, defined as commencing at sunset on Friday and ending at sunset on the following Sunday. Identical commercial fishing seasons for the use of power-assisted gill net gear by vessels greater than 40 feet in length are set for all three regions of Florida. That season opens on December 15 of each year and closes on November 1 of the following year. For other forms of commercial harvesting of Spanish mackerel, the season is year-round, or defined as from December 15 through December 14 of the following year. However, the proposed rule, Rule 46- 23.004, provides a mechanism for shortening the seasons in each region for all forms of commercial fishing (except for the various by-catch allowances) when the total harvest for each region reaches a specified number of pounds. For the larger vessels using power-assisted gill nets, the seasons for the East Coast, Southwest Coast and Northwest Coast close prior to November 1st if the total regional commercial harvest is projected to reach, respectively, 1,670,400 pounds, 1,350,900 pounds and 354,600 pounds. For commercial fishermen using other types of gear, the year-round season will close when the total regional commercial harvest in the season reaches, before December 14, 1,856,000 pounds (East Coast), 1,501,000 pounds (Southwest Coast) and 394,000 pounds (Northwest Coast). In addition to the 15 percent by-catch allowance previously mentioned, the proposed rule also excepts from the required season closures Spanish mackerel harvested as an incidental by-catch of other lawfully targeted species so long as the total weight of mackerel does not exceed 500 pounds, as well as those harvested with a net size greater than 4 inches stretched mesh used to lawfully harvest another target species. When the specified poundages which trigger the closing of the seasons are projected to be reached, the proposed rule provides for the giving of notice by the Executive Director of the Department of Natural Resources in the manner provided in Section 120.52(15)(d), Florida Statutes. Proposed Rule 46-23.005 sets forth a bag limit for recreational fishermen which applies during all times of the year. That limit is four Spanish mackerel per person per day. Because of evidence indicating that the abundance of Spanish mackerel in Florida is declining, the MFC began considering that fishery as a subject of possible regulation in March of 1984. Stock assessments were performed and updated, federal studies and mackerel fishery management plans were considered, various workshops and meetings were held, and numerous management option papers and alternatives were considered. Many of the witnesses in the instant rule- challenge proceeding appeared before, testified or otherwise provided input to the MFC during the rule promulgation process. In considering the proposed regulations, the MFC had before it evidence that commercial and recreational landings of Spanish mackerel had substantially decreased since the 1970's and that seasonal and areal compression had occurred in this fishery. While it could not be concluded with certainty whether the resource was experiencing recruitment overfishing or growth overfishing, the MFC determined that the resource was being overfished to the extent that a reduction in effort and an increase in the size of the fish caught was necessary to protect, conserve and recover the resource. While single year or seasonal commercial and recreational landing statistics may not be entirely accurate due to under-reporting, they are reliable indicators of trends and can be utilized to indicate abundance. Likewise, declining commercial landing statistics can be indicative of a decline in the effort directed toward harvesting and/or market conditions. In approximately 1977, there were over 120 large roller rig boats in the Spanish mackerel fishery. At the present time, there are approximately 41 large roller rig vessels utilized to commercially harvest Spanish mackerel. The size of fish desired in the market has changed somewhat, with a declining demand for the smaller fish. While the price of Spanish mackerel per pound has remained relatively stable over the past ten or more years, its price in relationship to other species of fish and shellfish has declined. The above factors, as well as the voluntary use of larger mesh size nets and the recent closure of Palm Beach and Dade Counties, may provide some rationale for the decline in commercial landing statistics since the 1970's. However, given the evidence concerning a decline in recreational landings, seasonal and areal compressions, and the increased capacity of large power-assisted gill netting vessels, it was not unreasonable for the MFC to conclude that the decline in commercial landings is indicative of a decline in abundance resulting from overfishing. The conceptual goal of the proposed rules is to return the Spanish mackerel fishery to the condition in which it was in the early 1970's. In order to accomplish this goal, the MFC determined to effect an approximate 45 percent reduction in efforts devoted to harvesting and to effect an increase in the size of the fish harvested for commercial purposes. The minimum gear size proposed is directed toward the desired fish size, and the reduction in effort goal is to be accomplished through continued closures of certain areas, weekend closures, and the establishment of commercial seasons, commercial season catch limits and recreational bag limits. Gill mesh nets are highly selective for a specific size of fish. A 1/8 inch difference in gill net mesh size makes a significant amount of difference in the size of the fish caught. The large nets utilized for Spanish mackerel harvesting can cost up to $20,000.00, with the monofilament portion of the net costing between $3,000.00 and $4,000.00. Due to destruction by sharks and normal wear and tear, the life expectancy of the monofilament portion of a gill net is between 1/2 to 3 seasons. The initial minimum mesh sizes proposed in the challenged rules for the monofilament portion of gill nets are reflective of the sizes currently being utilized in the industry in each of the three regions specified in the rule. No conclusive scientific data exists on a statewide basis as to the size of fish that will be captured using a 3 5/8 inch gill net mesh size. The MFC does intend to gather more data concerning gill net mesh size selectivity, and that is one of the reasons the proposed rule delays imposition of the 3 5/8 inch requirement until October of 1988. The evidence does demonstrate that Spanish mackerel in the Northwest Coast region or Panhandle area tend to be longer and thinner with less yield per fish than those found in the East Coast or Southwest Coast areas. There is insufficient evidence to conclude, however, that the Gulf Spanish mackerel stock and the Atlantic Spanish mackerel stock constitute two separate populations. Due to the seasonal migration of the Spanish mackerel in a southerly and northerly direction along the East Coast of Florida, it is impossible to determine the precise impact on effort reduction of the closure of Palm Beach and Dade Counties. The MFC heard evidence from commercial fishermen that the impact from closing those areas could result in a reduction in catch of at least 30 percent. The MFC's calculation of a lower percentage was not unreasonable given the large capacity of the power-assisted gill net industry and the potential for harvesting Spanish mackerel while en route to or from these closed counties. The proposed season catch limits for commercial fishermen are intended to provide a backup to the other effort reduction measures in the proposed rules. It is intended that if the commercial seasons for larger power-assisted rigs, the weekend closures, the increased net sizes, and the areal closures do not significantly reduce the actual landings of Spanish mackerel in Florida, then the season for all commercial fishing can be shortened to effectuate such a result. The quota for each region constitutes a fixed cap on commercial landings per season. Consequently, if abundance does increase, there is no automatic mechanism in the proposed rule for increasing season catch limits. This, of course, will result in the unreliability of landing statistics alone as an indicator of stock abundance. Because the proposed rule contains no restrictions upon the number of recreational fishermen who may enter the fishery, no season for recreational fishing and no limit upon the number of fish caught, as opposed to possessed, by recreational fishermen, the rule could cause some reallocation of the Spanish mackerel fishery from the commercial sector to the recreational sector. In recent years, the commercial sector has maintained at least a 75 percent share of the Spanish mackerel resource. Within the commercial sector, there is no domestic substitute for Spanish mackerel.
The Issue Whether the Department of Environmental Protection should issue a Consolidated Environmental Resource Permit and Sovereign Submerged Lands Authorization to Deep Lagoon Boat Club, Ltd., for the upgrade of its existing commercial marina in Deep Lagoon, an arm of the Caloosahatchee River?
Findings Of Fact The Caloosahatchee River Located in Lee County and considered a part of Charlotte Harbor, the Caloosahatchee River (the "River") is among the Class III surface waters of the state, so classified on the basis of the designated uses "Recreation, Propagation and Maintenance of a Healthy, Well-Balanced Population of Fish and Wildlife." Fla. Admin. Code R. 62-302.400(1). The River runs from Lake Okeechobee in a southwesterly direction past the City of Ft. Myers into San Carlos Bay. The bay, adjoining the Gulf of Mexico, is directly south of Matlacha Pass. It sits in the midst of, and is formed by, Sanibel Island, Pine Island, and the land masses on the north side of the Caloosahatchee (the site of City of Cape Coral) and the south side that culminates in Shell Point, at the mouth of the River. Beginning 120 years ago or so, the River underwent a series of major man-made alterations. Together with a statement of the current status of the River, they are summarized briefly in a publication of a recent special study of manatees and the River by the Florida Fish and Wildlife Conservation Commission's Florida Marine Research Institute (the "Special Study"). (Highly pertinent to this case, the Special Study is referred to elsewhere in this order.) This is its summary of the alterations to the River: Prior to the late 19th century, the Caloosahatchee River was a meandering waterway that ran from west Lake Flirt to San Carlos Bay . . . In 1881, Hamilton Disston began dredging a canal to connect the river's headwaters with Lake Okeechobee (citation omitted). This procedure caused severe flooding downstream, especially during the hurricane season. To mitigate the flooding effects, various spillways, locks and dams were constructed, including the locks at Moore Haven and Ortona. In 1947, the Central and Southern Florida (CS&F) project was authorized to manage the flood-control system and water supply issues of the Caloosahatchee River basin. The CS&F project involved widening and straightening the river and constructing the Olga Lock and Dam (now known as the . . . Franklin Lock and Dam). The river today is 65 miles long with a 25- foot-deep channel. Petitioners' Exhibit 20, A Special Study of Manatees in Mullock Creek and the Caloosahatchee River Eastward to the Edison Bridge, Florida Fish and Wildlife Conservation Commission, Florida Marine Research Institute, November 2002. Despite these alterations, the River is listed among the waters of the state designated as Outstanding Florida Waters. Fla. Admin. Code R. 62-302.700(9)(b)2. As such, it is entitled to special protection by virtue of DEP's pronouncement that "[I]t shall be the Department policy to afford the highest protection to Outstanding Florida Waters". Fla. Admin. Code R. 62- 302.700(1). The Franklin Lock is located on the Caloosahatchee about 25 miles upstream from San Carlos Bay. The lock permits fresh water to flow downstream toward the bay, of course, but it keeps the salt in brackish waters in the River south of the lock from penetrating upstream. In other words, the lock is a salinity barrier. The estuarine extension of the River, therefore, is defined by the lock. Little more than four miles downstream from the lock, the Orange River feeds into the Caloosahatchee. Upstream on the Orange, not far from its mouth, is the site of a Florida Power and Light Company ("FP&L") power plant. Until very recently, the power plant discharged into the Orange River effluent roughly seven degrees Celsius warmer than its ambient waters. (Waters discharged now are not as warm but still significantly warmer than the River's ambient water.) The warmed waters flow into the Caloosahatchee. These river system waters warmed by power plant effluent are sought by manatees as refuge from colder water in the River, the bay and the gulf. "Controlled releases or pulses of fresh water from Lake Okeechobee, upstream runoff, and prolonged periods of drought can severely, though temporarily, alter the salinity gradient [downstream of Franklin lock]." Id. at p. 20. It is believed that the variations in salinity affect seagrass biomass more than actual salinity levels. The salinity ranges cause turbidity and decrease in water clarity in the Caloosahatchee. They darken the water color and result in the submerged aquatic vegetation being variable and patchy instead of plentiful as it would be were the River not affected by rapid and extreme salinity changes. The River is crossed by a number of bridges: the Interstate 75 Bridges, Edison Bridge (part of U.S. Highway 41), the Midpoint Bridge, and the Cape Coral Bridge. The average depth of the water at river's edge is three feet. The center, including the channel, ranges from 6 to 25 feet in depth. Relatively shallow, the length and breadth of the River is traveled by manatees who use it as a critical link in habitat in southwest Florida. Manatee Habitat Linkage The presence of manatees in the River and their use of it for habitat is also summarized in the Special Study: The Caloosahatchee River between the Edison Bridge and Shell Point links habitats used by manatees including warm-water refugia, feeding areas, and resting areas. Because of drastic changes in salinity . . . coupled with high turbidity from development and vessel traffic, the distribution of submerged aquatic vegetation (marine and freshwater) in the study areas is variable and patchy. Manatees travel between stable feeding areas found upstream (freshwater) and downstream (estuarine), although they presumably feed opportunistically while passing through the area. Selected areas in the Cape Coral and Ft. Myers canals likely afford manatees with fresh water through stormwater runoff and drainage, resting habitats, and possible nursery areas. In winter, manatees may also use a few of these canals as temporary warm- water sites. Id. Among the places along the River where manatees congregate is Deep Lagoon. Deep Lagoon Deep Lagoon is a natural, relatively short, largely mangrove-lined arm of the Caloosahatchee on its southern shore just east of Palmetto Point. The lagoon is to the west and south of the downtown area of the City of Ft. Myers, less than a mile south of the southern terminus of the Cape Coral Bridge, and approximately 12 miles downstream from the FP&L power plant. Roughly four miles upstream from Shell Point where the River opens to the bay, the mouth of the lagoon opens west. Just inside the lagoon's mouth, it widens into an area known as the Cove. The lagoon turns 90 degrees to the south and extends in a southerly direction toward McGregor Boulevard. The upper reaches of the lagoon, or its headwaters, very close to McGregor Boulevard, are known as Cow Slough. Like the Caloosahatchee, Deep Lagoon is one of the Class III waters of the state. Unlike the River, the lagoon is not listed among the Outstanding Florida Waters. Wildlife in the area around Deep Lagoon include great blue herons, night herons, osprey and other hawks, and, of course, the manatee. In fact, Deep Lagoon is considered by the Bureau of Species Management in the Florida Fish and Wildlife Conservation Commission (the "FWC") to be a "minor aggregation area" (Tr. 792) for manatees. The lagoon provides some warm waters attractive to the manatee, and manatees consume fresh water discharged into the lagoon from the Iona Drainage District ditch. (See paragraph 17, below.) The waters in and near the lagoon are frequently used by citizens for fishing. Fly fishing for snook, redfish, snapper, sea trout, and sheepshead is particularly popular in and about the lagoon. The lagoon is also the site of the Boat Club's Deep Lagoon Marina. The Deep Lagoon Marina The Deep Lagoon Marina (the "Marina") consists of 24 acres less than one-half mile from the River, north of Cow Slough, and south of the Iona Drainage District ditch. The Iona Drainage District ditch, the result of the first dredging in the Deep Lagoon area, is separated from the Marina by a relatively thin strip of mangrove fringe. It is a source of fresh water runoff from predominately fresh water wetland and upland areas. It appears in a 1944 aerial photograph that pre-dates dredging for the marina or of the lagoon otherwise. An aerial photograph taken in 1958, 14 years later, shows development of the Deep Lagoon marina property, as well as completion of a north canal separated from the Iona Drainage Canal by the mangrove fringe. Sometime between 1958 and 1966, two additional canals were dredged as part of the Marina. The marina consists of 15.4 acres of uplands, largely the result of the dredge and fill activity that created the marina's three man-made canals: the "north canal"; the "main canal" that includes a basin (the "main basin") at its eastern end; and the "south canal." At their eastern ends, the three canals terminate a short distance from MacGregor Boulevard. On their opposite ends to the west, the canals open to the lagoon. Except for the Iona Drainage District ditch that discharges into the north canal, the canal water system has little circulation. Within the dead-end system the canals comprise, the water sloshes back and forth. The dead-end nature of the canals has led to violations of water quality standards as found in paragraphs 4 and 5 of Sheridan, et al. v. Deep Lagoon Marina, et al., Case No. 88-4759 (DOAH June 10, 1989): As a result of poor water circulation within the system, sediments have built up in the canal bottoms and in the basin. Although different historical incidents, such as ship building, the burning of a large building on the east-west peninsula and the receipt of agricultural and highway drainage into the northern canal may have caused some of the build-up, marina activities and the use of the canals for marina purposes have contributed significantly to the problem. Water quality samplings within the canals and basin indicate that State Water Quality standards are currently being violated for dissolved oxygen, oils and greases, total and fecal coliform, copper, lead, mercury and tributylin. Sediments in the canals and basins are contaminated by lead, copper, cadmium, chromium and mercury. The canals and basin are currently devoid of seagrasses, oyster beds and benthic organisms. Id. at pp. 4 and 5. The north peninsula (referred to in other DOAH orders as the "east-west peninsula") is the longer of the two peninsulas on the marina property. It lies between the north canal and main canal. The south peninsula lies northeast of the south canal, southwest of the main basin, and south of the main canal. Two steel buildings used for dry boat storage, a building used for boat repair and related marina uses are located on the south peninsula. The marina property located east of the marina's two peninsulas that fronts MacGregor Boulevard is occupied by a boat dealership and the Boat Club's sales trailer. To the north of the marina is the Town and River subdivision. The subdivision has an extensive canal system. Like the marina's canals, the Town and River Canal System is also the result of historic dredge and fill activity. As the Town and River subdivision expanded in the 1970's, the use of the marina increased. A boat storage building appears on the north peninsula in a 1970 aerial photograph. Extensive outdoor dry boat storage on the north peninsula began in the late 1970's. Dry boat storage expanded in the 1980's. An examination of aerial photography taken in 1990, 1993, 1999, 2000, and 2001, reveals 1990 to be "the period of time that the facility appeared to be at full operating capacity." (Tr. 787). As early as March 23, 1980, a travel lift facility appears in aerial photographs at the west end of the north peninsula. The boat lift appears in the same spot on the western end of the northern peninsula, west of the longitude at which the Iona Drainage District canal opens onto the North Canal, in a series of aerial photographs taken over the next two decades. The area surrounding the marina is fully developed, including the residential areas and boat basins to the north and south. Opposite the marina and along much of the western border of the lagoon, there is a vacant tract of wetlands. Purchased by Lee County as conservation lands, it will not be developed. It is the Department's position that Deep Lagoon Marina can operate as a marina without a permit. But a permit is required if its owners seek to upgrade the marina by activity that trips permit requirements such as construction or dredging of channels. The Boat Club became involved in permitting processes soon after it purchased the marina. Purchase by the Boat Club The Boat Club purchased the marina in 1997, with a closing on the purchase in September of that year. At the time of the purchase, it was the Boat Club's intent to redevelop the entire marina property and upgrade its facilities under the authority of development orders and permits obtained by the former owners. These included a Development of Regional Impact Development Order (the "DRI DO") issued in 1987; a surface water management permit (the "MSSW permit") from the South Florida Water Management District issued in 1988; and a dredge and fill permit from the former Department of Environmental Regulation issued in 1989, and extended through a major modification in 1995. A Litigious History These permits have a litigious history, particularly the dredge and fill permit and its conditions. Modifications to the permit resulted in additional permit processes, including administrative hearings. The history of the dredge and fill permit litigation, including litigation related to the Boat Club's application for an environmental resource permit to construct a surface water management system (the "SWMS permit") at the marina site is summarized in a final order of the Department of Environmental Protection rendered March 6, 2000 ("Sheridan III"): Applicant [Deep Lagoon Boat Club, Ltd., or, as referred to in this order, the Boat Club] is the owner and operator of Deep Lagoon Marina (the "Marina"), presently consisting of 61 wet slips, 200 dry slips and other marina-related buildings. * * * In 1989, the Department of Environmental Regulation ("DER") entered a final order issuing a dredge and fill permit to a predecessor in title of Applicant authorizing a major renovation and expansion of the Marina, including additional boat slips and other related activities. See Sheridan v. Deep Lagoon, 11 F.A.L.R. 4710 (Fla. DER 1989). The final order in the original Sheridan case was appealed and the portion thereof issuing the dredge and fill permit was subsequently affirmed by the appellate courts Sheridan v. Deep Lagoon, 576 So. 2d 771 (Fla. 1st DCA 1991). A permit was ultimately issued by the Department in October of 1995 (the "Original Permit") after the conclusion of the appellate proceeding. The Original Permit was modified by the Department in November of 1995 and again in April of 1997. This 1989 DER final order in the original Sheridan case adopted the hearing officer's findings that the waters of the Marina canals violated water quality standards for dissolved oxygen, oils and grease, total and fecal coliform, copper, lead, and mercury. Sheridan, supra, at 11 FALR 4727. These persistent water quality violations in the marina canals in the 1980's were the impetus for specific conditions set forth in the Original Permit issued by the Department in 1995 to ensure a net improvement" to water quality. Specific Condition 5K of the Original Permit, as revised in 1997, requires that a "stormwater treatment system providing treatment meeting the specifications of Florida Administrative Code 40E-4 for all discharges into the basins from the project site shall be permitted and phased in prior to use of the parking lot and the new boat slips." . . . In order to meet these requirements of Specific Condition 5K of the Original Permit, Applicant filed an application with the Department in December of 1997 for an environmental resource permit to construct a surface water management system at the Marina site. The Department executed a Notice of Intent to Issue Applicant's requested permit for the surface water management system (the "SWMS" permit) in November of 1998. In March of 1998, Applicant also gave the Department written notice that it intended to "maintenance dredge" the internal canals at the Marina site. The Department's South District Office then issued a letter determining that Applicant's proposal to maintenance dredge the Marina's internal canals was exempt from environmental resource permitting requirements. Upon receipt of this letter from the Department, Applicant's contractor proceeded with the "maintenance dredging" of the three canals. Petitioner and Intervenor then filed petitions challenging the Department's notice of intent to issue the SWMS permit and the Department's maintenance dredging exemption determination. These petitions were forwarded to DOAH and were consolidated for final hearing in Sheridan v. Deep Lagoon Boat Club, DOAH Case Nos. 98-3901 and 98-5409 ("Sheridan II"). A recommended order was entered in Sheridan [II] in November of 1999 by a DOAH administrative law judge ("ALJ"). The Department subsequently entered a final order in January of 2000 in the Sheridan [II] consolidated cases. See Sheridan v. Deep Lagoon Boat Club, OGC Case Nos. 98-1184 and 98[-]3047 (Fla. DEP, January 28, 2000) In its final order in Sheridan [II], the Department adopted the ALJ's conclusion that Applicant failed to establish at the final hearing that the already completed dredging of the three Marina canals complied with two of the statutory requirements for entitlement to "maintenance dredging" exemption. The Sheridan II final order also adopted the ALJ's conclusion that Applicant failed to provide reasonable assurance that the secondary impacts of the operation of the proposed SWMS would not violate water quality standards and would not adversely impact the West Indian manatee. The Sheridan [II] final order of the Department thus disapproved the prior determination of Department staff that Applicant was entitled to a permit exemption for maintenance dredging of the Marina Canals [although the matter was moot since the Boat Club had, in fact, conducted the dredging while the proceeding was pending] and denied Applicant's SWMS environmental resource permit application. While Sheridan [II] was pending, DEP issued a notice of intent in March of 1999 to further modify the specific conditions of the 1995 Original Permit. These modifications would allow Applicant to construct and operate a boat travel lift at a new location within the Marina and to install flushing culverts in lieu of the previous requirement of a flushing channel between the north and middle Marina canals. [The modification for the boat lift would allow the construction and operation of a boat lift at the eastern end of the north canal.] These 1999 modifications to the Original Permit were timely challenged by Petitioner and the matter was referred to DOAH, resulting in the formal administrative proceeding now on review in this Department Final Order. Sheridan vs. Deep Lagoon Boat Club, Ltd., et al., OGC Case No. 99-0619, DOAH Case No. 99-2234, (DEP March 6, 2000). As stated in the quote above, following its purchase of the marina, the Boat Club conducted contamination and maintenance dredging of the marina's canals. This dredging had been preliminarily authorized by DEP, but DEP's preliminary action was challenged. The result of the litigation was that the permit for the dredging was disapproved, a result too late for the opponents of the process because the dredging had been undertaken and completed while the litigation wended its way through state agencies and the court. In the meantime, the boats stored on the north peninsula were removed to make way for the dredged materials. When the dredging was completed, dry boat storage resumed on the north peninsula. During the Sheridan II proceedings, the Final Order in Sheridan III was rendered. It accepted the recommendation of the administrative law judge that, with four changes, the modifications that would allow the boat travel lift at the eastern end of the north canal and the flushing culverts be granted. The recommendation was predicated on findings related to and conclusions that any adverse impacts on water quality would be negligible and that impacts to the manatee would be minimal or that projections of significant impacts were speculative. These findings and conclusions were adopted and accepted by DEP in the Sheridan III Final Order. While the administrative process in Sheridan III proceeded toward its culmination with the issuance of a final order in March of 2000, Sheridan II was under appeal in the Second District Court of Appeal. Almost a year after the Sheridan III Final Order, the Court rendered an opinion in Sheridan II. Rehearing in the Sheridan II appellate proceeding was denied on April 6, 2001. The Court affirmed DEP's adoption of the conclusion that the Boat Club failed to provide reasonable assurance that the secondary impacts of the operation of the proposed SWMS would not violate water quality standards and would not adversely impact the West Indian Manatee. While the appellate litigation in Sheridan II was pending, the 1989 dredge and fill permit expired. In order to upgrade the Marina, therefore, the Boat Club was required to re-apply to DEP for an Environmental Resource Permit, a type of permit that succeeded the type of permit (the dredge and fill permit) issued by DEP in 1989. This most recent Environmental Resource Permit application is the subject of this proceeding. The ERP Subject to this Proceeding The Boat Club application for the new Environmental Resource Permit ("ERP") was received on August 24, 2001. The following January 22, 2003, approximately one year and five months after the filing of the ERP application, DEP issued a "Consolidated Environmental Resource Permit and Sovereign Submerged Lands Authorization" (the "Permit/Authorization"). The Permit/Authorization governs the Boat Club's proposed dredge and fill activity, its proposed stormwater and surface water management plan and authorization of sovereign submerged land use. The permitted activity is described in DEP Permit/Authorization No. 36-0128502-008 as follows: The project is to upgrade an existing 445 slip commercial marina. Upon completion, the marina will accommodate 485 slips (129 wet slips and 356 dry slips) 40 of which shall be occupied by sailboats or left unoccupied. This shall include the construction of 1,693 lf (2,257 sq. ft.) vertical retaining wall in the north canal landward of mean high water (MHW) and existing mangroves. The construction of a travel lift affecting approximately 600 sq. ft. and approximately 37,369 sq. ft. of docking structure (3,529 sq. ft. of fixed docking structure and 33,840 sq. ft. of floating docking structure). The construction of two 48" grated culverts to enhance flushing, as well as, the removal of two travel lifts and approximately 10,443 sq. ft. docking structure. Further, the activity is to construct a surface water management system to serve 15.4 acres (total upland area) of the entire 24.0-acre commercial marina site. Construction of the surface water management system will include three separate and independent stormwater collection systems with associated pretreatment areas and underground vault (Infiltrator) systems for stormwater storage/treatment prior to discharge through concrete weir outfall control structures into adjacent Class III waters. Petitioners' Exhibit 15, page 3 of 20. The Parties Petitioners The three petitioners all reside in proximity to Deep Lagoon. Brenda Sheridan resides to the northeast of the marina. Her lot, owned since 1976, is on the shores of the Caloosahatchee River at Deep Lagoon. She and her husband are avid practitioners of fly fishing. In addition to fishing, Ms. Sheridan boats in Deep Lagoon, including in the north canal, where she enjoys observing wildlife, particularly manatees. A member of the Save the Manatee Club for more than 20 years, she has observed manatees in Deep Lagoon "[f]or many years" (Tr. 963) and continues to see them "all the time." Id. With the exception of calving, she has seen them "doing just about everything" (Tr. 964), including drinking fresh water off the surface of Deep Lagoon. She has participated in posting manatees signs "starting at the channel coming in from the river into Deep Lagoon . . . through the cove." (Tr. 973). She has assisted state personnel in the recovery of a manatee carcass, and has reported what she has believed to be speeding boats the many times she has seen them. She believes that the proposed permit will adversely affect her activities of fishing and observing wildlife and fervently hopes to be able to continue to "enjoy wildlife and unpolluted waters for the rest of my life and also for my grandchildren." (Tr. 979). Kevin Derheimer and Kathryn Kleist reside on Deep Lagoon Lane in Ft. Myers adjacent to the Iona Drainage Ditch immediately north of the north canal. Members of the Audubon Society, they selected the property where they built their home because it had been owned by Ms. Kleist's family, and because they "had observed wildlife, manatees, and birds from this piece of property and [so] decided to build a home there because of the proximity to wildlife" (Tr. 856), as well as its proximity to wetlands that could not be developed. They boat, kayak and fish on Deep Lagoon, and observe the abundant wildlife there especially manatees. Ms. Kleist has seen up to seven manatees at one time together in Deep Lagoon. Her observations have taken place over the last five years. She describes herself and her husband as avid observers of manatees who keep their binoculars at the ready any time they think they might have spotted a manatee in the lagoon. Ms. Kleist has a number of concerns about the proposed permit, particularly its effect on the north canal and the areas of the lagoon used by manatees observed by her over her years of residence in the area. Of major concern to her is the increase in boat traffic. Consistent with Mr. Ruff's testimony quoted in paragraph 178 below, Ms. Kleist testified that the proposal will make the marina "much larger" (Tr. 941) than it has been in her five years living in the area. (Tr. 940). When asked whether she observed the speed zones that apply to Deep Lagoon, Ms. Kleist candidly replied: Probably not all the time. Just like I don't with my car. But we attempt to pay attention to speed zones. It's not intentionally, but if you're asking me to 100 percent of the time, have I never speeded in my boat, I would say no. (Tr. 959). Respondents Respondent DEP is the state agency authorized to issue environmental resource permits for projects affecting the waters of the state under Chapter 373, Florida Statutes. It is delegated authority to issue proprietary authorizations to use sovereign submerged lands by Florida Administrative Code Rule 18- 21.0051. Deep Lagoon Boat Club, Ltd., is the owner and operator of Deep Lagoon Marina, a 24-acre marina, claimed in its proposed recommended order (adopted by DEP) to consist presently "of 50 wet slips and approximately 350 dry slips (171 boats stored inside two storage buildings and the remainder stored outside of the buildings on racks or block)." Deep Lagoon Boat Ltd.'s Proposed Recommended Order, p. 6-7. A principal of the Boat Club is Edward J. Ruff, a developer of marinas in southwest Florida. The business is a family concern as was evidenced by the presence of many members of the Ruff family at the final hearing. Mr. Ruff has had success in developing several marinas in southwest Florida. An advocate of the Clean Marina Program, Mr. Ruff attributes the success to his pursuit of development of marinas that meet Clean Marina criteria. The Boat Club has applied for Clean Marina status for the Deep Lagoon Marina, but was turned down for lack of compliance with one criterion. It does not yet have a surface water management system that has been finally approved by DEP. The Boat Club hopes that approval of the surface water management system under review will clear the way for it to be able to "fly the flag" (Tr. 312) that demonstrates its achievement of Clean Marina status. Petitioners' Challenge Petitioners raised 10 bases in their petition for denial of the Consolidated Permit/Authorization. One, found in paragraph 32.H., of the petition, concerning the application of Florida Administrative Code Rule 18-21.0045, has been waived. See p. 55 of Petitioners' Proposed Recommended Order. The remaining nine alleged in paragraph 32 of the petition are as follows: Whether Deep Lagoon Club has provided reasonable assurances of compliance with the applicable water quality standards as required by Section 373.414(1), Fla. Stat., including Florida's anti-degradation policy in Rules 62-4.242(1)9a) and Rule 62- 302.300(7), Florida's minimum standards in Rule 62-302.500, and Florida's Class III standards Rule 62.302.560. * * * Whether Deep Lagoon Club has provided reasonable assurances of compliance with the public interest criteria of Section 373.414(1)(a), Fla. Stat., . . . Whether Deep Lagoon club has provided reasonable assurances of compliance with the elimination and avoidance criteria of Section 373.414(1)(b), Fla. Stat. and SFWMD Basis of Review Section 4. Whether Deep Lagoon Club is collaterally estopped from being granted an ERP for its proposed stormwater management system due to the DEP's denial of the same proposed stormwater management system and its secondary impact on Manatees. . . . Whether Deep Lagoon Club failed to provide reasonable assurance concerning the direct impacts and secondary impacts of its proposed activities on the endangered Manatee. (Section 373.414(1)(a), Fla. Stat.; Rule 40E-4.301(1)(d)-(f); Basis of Review Section 4.2.7(a); [citation omitted]; Section 370.12(2)(m), Fla. Stat.; Fla. Admin. Code Chapter 68C-22 . . .; . . . Whether Deep Lagoon Club failed to provide reasonable assurance concerning the past, present and foreseeable cumulative impacts, especially including cumulative impacts on the endangered Manatee. . . . Whether Deep Lagoon Club has provided reasonable assurances its sovereign submerged lands application complies with the public interest criteria of Rule 18-21.004, including secondary impacts on the endangered Manatee . . . * * * Whether Deep Lagoon Club has provided reasonable assurances that its proposed activities are consistent with Florida's Coastal Zone Management Program . . . Whether Deep Lagoon Club has provided reasonable assurances of compliance with applicable standards, rules and ordinances in light of its past violations such as failing to register for sovereign land lease, dredging the marina basin without authorization, and dredging the marina basin to depths and widths greater than Florida's exempt statute authorized . . . Petition for Hearing, pp. 11-15. These bases can be grouped under three headings: the proposed stormwater management system and water quality; the impact of the Consolidated Permit/Authorization on the Endangered Manatee, and (3) other issues related to these two such as collateral estoppel and past violations. Fundamental to resolution of these issues are issues that relate to the number of boat slips at the Boat Club marina and the number of power boats the marina can accommodate. These numbers vary depending on whether marina usage is considered in terms of physical capacity, actual usage or legal limits. Physical capacity, as found above, exceeds 600 slips. Actual usage has varied over the years. The lawful number of slips depends on local development orders and permit requirements. If a permit is to be obtained from the state, then the lawful number of boat slips and power boats may be restricted, just as is proposed in the permit at issue in this case. Lawful Number of Boat Slips and Power Boats Of the 485 boat slips (129 wet slips and 356 dry slips) allowed at the marina under the Consolidated Permit/Authorization, 40 may not be used for power boats. The 40 may be used for sail boats; otherwise, they must remain unoccupied. This leaves a maximum of 445 slips at the marina that may be used for power boats. Over the years, the number of boat slips at the marina and the number to have been authorized by the various sought- after permits have varied. For example, on June 26, 1998, a Manatee Impact Review Report issued by the Bureau of Protected Species Management, then in the DEP's Division of Marine Resources, showed the marina to have 228 existing slips: 61 wet and 167 dry. The report shows that the marina had an additional 446 slips (113 wet and 333 dry) that were "[p]reviously permitted but not constructed". DEP Ex. 41, page 2 of 7. According to the report, together the existing and authorized, not-yet-constructed slips totaled 674 (174 wet and 500 dry). In the Sheridan II administrative proceeding, the administrative law judge found as follows: 26. In 1988, DEP issued a DAF ["dredge and fill" permit] to Applicant's predecessor in title for additional wet slips (as modified, the Original Permit). Due partly to the likelihood of the replacement of some older, smaller slips with larger slips, there is some uncertainty as to the precise number of wet slips that Applicant would be able to construct under the Original Permit. However, Applicant would be able to construct approximately 89-113 new wet slips . . . so as to raise its marina capacity to 150 -174 wet slips. Applicant also plans to construct 227 dry slips, so as to raise its marina capacity to 427 dry slips, and add 115,000 square feet of buildings, including a restaurant. Deep Lagoon Ex. 9D, 22 FALR 3286. The Applicant and the Department took exception to Finding of Fact No. 26 while the recommended order was under consideration by DEP. The finding was modified in DEP's Final Order so as to reduce the number of new wet slips authorized to 89 so that the total number of wet slips numbered 150. The new dry slips to be added through the permit process under review were left at 227 by the DEP Final Order so that the marina's total capacity for dry slips, if the permit were granted, remained as the ALJ had found, at 427. See Id., at 22 FALR 3264. In the Sheridan II administrative hearing, Mr. Uhle, counsel for the Boat Club, made the following statement: "D.R.I. actually authorized more wet slips and more dry slips. But that's if the amendment is approved, that's what will be authorized." Deep Lagoon Ex. 43, p. 30. In fact, a DRI Amendment (presumably the one to which Mr. Uhle referred) was approved subsequent to the administrative hearing in Sheridan II. The Deep Lagoon Development of Regional Impact Development ("DRI") Order had been adopted on March 23, 1987. At the behest of the Boat Club by the filing of a Notice of Proposed Change on August 10, 1998, the DRI Development Order was amended for a second time. The amendment was adopted on June 7, 1999, a month or so after the administrative hearing in Sheridan II. The "Second Development Order Amendment for Deep Lagoon Marina, A Development of Regional Impact" (the "Current DRI Order") employs a "strike-through and underline format" (Boat Club Exhibit 8, Attachment 18, p. 2 of 17), that reveals both the amendment requested by the Boat Club and the DRI Development Order as it existed prior to the second amendment. The Current DRI Order authorizes "150 permanent wet slips; of which 30 will be reserved only for temporary moorings; 115,000 square feet of dry storage (427 slips)" (Id.) The Current DRI Order thus sets the number of boat slips at the marina as 150 wet slips and 427 dry slips. The Current DRI Order is consistent with the conclusion of DEP in its Final Order in Sheridan II: the legal capacity of the marina, were the permit applied for there to be granted, would be 150 wet slips and 427 dry slips for a total of 577 slips, wet and dry. This capacity was not achieved through permitting, however, because DEP accepted the recommendation of the administrative law judge that the permits applied for in Sheridan II be denied. The denials were based, at least in part, because DEP "declined to reject the ALJ's mixed statements of law and fact concluding that increased boating capacity and other Marina expansion activities authorized in the Original Permit constituted adverse secondary impacts of the proposed SWMS to water quality and to manatees and their habitat." Deep Lagoon Ex. 9D, 22 FALR at 3277. Water Quality and Surface Water Management The Boat Club proposes to construct a stormwater management system for the entire 15.4 acres of uplands at the marina site. Such a system is badly needed if the marina is to operate with environmental integrity. For the most part, any surface water that is generated presently on the south peninsula hits the pavement or the buildings and then runs off into the canals. On the north, runoff sheet flows across the non- vegetated areas and discharges directly into the canal systems. "A person proposing to construct or alter a stormwater management system . . . shall apply to the governing board or the department for a permit authorizing such construction or alteration." Section 373.413(2). Existing ambient water quality in Deep Lagoon does not meet water quality standards. Data collected in May of 2002, "showed exceedances . . . of total coliform . . . of dissolved oxygen and . . . of copper, cadmium and zinc." (Tr. 560). "If the applicant is unable to meet water quality standards because existing ambient water quality does not meet standards, the . . . department shall consider mitigation measures proposed by . . . the applicant that cause net improvement of the water quality in the receiving body of water for those parameters which do not meet standards." Section 373.414(1)(b)(3). Construction of the surface water management system will include three separate and independent stormwater collection systems, associated dry pretreatment areas, and an underground vault/infiltrator system for storage and treatment of stormwater prior to discharge through concrete weir outfall control structures into the adjacent Class III waters. The system proposed in this proceeding retains the components of the design that failed to win approval in Sheridan II, and it enhances them with additional measures designed to provide net improvement in water quality in the receiving body of water. Under the proposed system, any water flowing from a rain event is routed into above-ground pretreatment areas, an enhancement to the original system. Once the water in these detention systems reaches a certain level, it flows into drainage structures. The structures transport the water below ground into a series of pipes connected to underground infiltrator storage treatment areas. The underground infiltrator drainage structures, constructed over crushed stone, were not designed specifically as a retention system. Nonetheless, they have the ability to remove water through ex-filtration into the ground. Chambers will be placed throughout the marina property, including under buildings and parking surfaces, and under some pathways. Their primary function is to detain waters and, through a settling process, treat it. The number of infiltrators provided in the proposed system is increased over the prior system, another enhancement. After detention in the underground system, the water is discharged through three outfalls, one for each of three independent drainage areas. The proposed dry pretreatment areas increase total stormwater storage capacity over the prior system by roughly 18,000 cubic feet, a 30-40 percent increase of storage over the prior design. With the prior system, there could have been discharge from parking areas into the canals during storms. The proposed system is designed so that all the runoff from the uplands is captured by the system. The proposed Marina Management Plan (the "Plan"), another enhancement, will add extra safeguards to eliminate some pollutants. The Plan provides a maintenance program to be carried out by a designated Environment Compliance Officer. Maintenance includes regular inspection of the chambers, themselves, inspections of the outfall structures, and an annual reporting to DEP as to the status of the storage/treatment system. The surface water management system also incorporates three "closed loop" recycling systems, one for each of the two designated boat wash-down areas and a third, located in the maintenance and service area, added as an enhancement to the prior system. The three recycling systems each consist of a concrete containment area with a drain. The water flows into the drain and is pumped up into a closed loop treatment system. There the water is pumped through a purifying device, separating contaminants and byproducts. The clean water is then reused for future wash downs. In the prior system, overflow, during an extreme storm event, for example, would flow into the surface water management system. Under the proposed plan, overflow from the recycling systems discharges directly into the municipal sewage system that will serve the site, another enhancement over the previous system. The proposed permit requires the closed loop recycling systems to be inspected by a Florida-registered professional engineer on an annual basis. The water discharged from the discharge structure will meet Class III standards. The system also complies with design requirements for discharge into Outstanding Florida Waters. The surface water management design incorporates best management practices to eliminate erosion or water quality problems during construction of the project. If done in compliance with permit requirements, construction and operation of the proposed stormwater management system will be in compliance with the Southwest Florida Water Management District's Basis for Review. These requirements together with the Marina Management Plan will improve the quality of the water leaving the site. There will be a net improvement in water quality for all parameters in the marina's receiving waters that currently do not meet standards. The treated water leaving the site will not cause parameters currently within standards to violate those standards. The contamination and maintenance dredging project performed by the Boat Club in 1999, appears to have improved water quality based on a comparison between 1997 pre-dredging water quality data, and the 2002 post-dredging water quality. Jack Wu, a professional engineer and DEP's expert in "coastal engineering, hydrographic impacts of submerged lands and environmental resource permit projects" (Tr. 750), performed a technical review of the marina canals and the proposed projected in accordance with the Basis of Review. He considered the structural design, size, and configuration of the proposed docking system, the flushing and mixing study, tidal data, and water quality data. Mr. Wu's testimony establishes that the proposed flushing culverts will increase circulation and eventually reduce the flushing time of the canals. Jack Myers, DEP's stormwater system design expert testified that the proposed surface water management system would not cause adverse secondary impacts to water resources of the District according to his assessment. Mr. Myers' assessment of the secondary impacts, however, did not include impacts to manatees. The Endangered Manatee Manatees are listed as an endangered species under the federal Endangered Species Act of 1973 (ESA)(16 U.S.C. 1531, et seq.), and under Florida law (Florida Administrative Code Rule 68A-27.003(1)(a)(31). In view of their status as endangered and as a Florida wildlife resource, manatees have undergone extensive study by many including the Florida Marine Research Institute in the Florida Fish and Wildlife Conservation Commission. Among these studies is the Special Study, conducted as the result of a settlement of litigation and released in November of 2002. Paragraphs 91-129 are derived from the Special Study, a copy of which appears in the record as Petitioners' Exhibit 20. The Florida Manatee The Florida manatee (Trichechus manatus latirostirs) is one of two subspecies of the West Indian manatee (T. manatus). Florida manatees inhabit the southeastern United States, primarily occupying the marine, estuarine, coastal, and freshwater inland waters of Florida. Manatees are herbivorous marine mammals. Manatees are not typically gregarious although mothers and calves travel in pairs and, on occasion, manatees travel in mating herds. Otherwise, for the most part, they are solitary although they may aggregate in areas with resources essential to the well-being of the population. These resources include warm water, fresh water, quiet resting areas, and areas with aquatic vegetation (marine and freshwater). Like most large mammals, manatees have a potentially long life-span, mature slowly, are slow to reproduce, and have a high parental investment in their offspring. Threats to the manatee population have their origin both in nature and in the activities of human beings. Potentially catastrophic, naturally occurring threats to manatees include hurricanes, red tide events and disease, and exposure to cold temperatures. To combat cold temperature exposure, manatees rely on a network of warm-water sites in eastern and southwestern Florida, as refuge during the cold season. Tampa Bay is a prime site of warm water refuge because of the number of power plants in the area. The only power plant that produces a manatee aggregation site between Tampa Bay and eastern Florida is the FP&L power plant up river from Deep Lagoon. Continued high counts of manatees at sites near power plants in southwestern Florida highlight the manatees' dependence on this network. Manatees feed on a variety of marine, freshwater, and terrestrial plants. Common forage species include shoal grass, manatee grass, turtle grass, tape grass, and widgeon grass. Manatees are reported to feed on seagrass plants both above and below the sediment. It has been theorized that manatees use fresh water for regulation of body temperature. They obtain fresh water from the plants they consume and are able to maintain their body water balance in salt water systems without drinking fresh water. Nonetheless, manatees are attracted to fresh water sources, especially in areas of high or fluctuating salinity like the Caloosahatchee. In estuarine waters such as Deep Lagoon, where fresh water floats on the top of saltier water, manatees have been observed with their mouths open at the surface drinking fresh water. Warm-water refuges play an important role in defining manatee movements between Shell Point and the Edison Bridge. The warm water refuge at the FPL power plant is classified in the Special Study as a Primary warm-water site. A secondary warm- water site along the River is at the Franklin Lock and Dam. Another secondary warm-water site in the area is in the canals of the Matlacha Isles at the northern end of Matlacha Pass. An old quarry pit in Ten-Mile Canal, Mullock Creek, is another site near Deep Lagoon where manatees aggregate because of warm water. In 2001, FP&L re-powered its plant from oil to natural gas. This reduced its warm water effluent. To compensate for the reduction and to provide manatee habitat, FP&L installed "donkey boilers" in January of 2002. The discharge in January of 2002, was more than one degree Celsius cooler than it had been in January of 2000, but the average January temperature of the FP&L discharge remained more than two degrees Celsius warmer than the water at the Franklin Lock. The single greatest cause of manatees' human-related mortality (referred to in the Special Study as "anthropogenic") is collisions with watercrafts. With regard to "anthropogenic" threats to manatees, the study, in part, reported the following: From 1976-2001, watercraft collisions accounted for approximately 25% of all manatee deaths and are the single greatest cause of human-related mortality (FWC unpublished data). In 2001 there were over 943,000 registered vessels in Florida (citation omitted). Given that about 97% of registrations are for recreational watercraft (citation omitted), it can be expected that there will be a continued increase in recreational vessels plying the waterways of Florida due to an increase in the human population. In addition to the expected increase in boat numbers over the next 25 years, other factors may act synergistically to increase the risk of fatal collision between manatees and watercraft. Relatively new modifications to the design of vessel hulls and engines allow boats to travel at higher speeds in shallower waters (citation omitted), thus threatening manatees and scarring seagrass beds. Boater compliance with existing slow speed zones is inconsistent (citation omitted). Sub-lethal effects of increased vessel traffic on manatees and a growing human population in the nearshore waters create more risk to manatees. Most adult manatee carcasses bear scars from previous boat strikes, and the healed, skeletal fractures of some indicate that they had survived previous traumatic impacts (citation omitted). Of over 1000 living individuals in the manatee photo-identification database (citation omitted), 97% had scar patterns from multiple boat strikes (citation omitted). It should be noted that the photo- identification database contains only animals with scars or other identifiable features. Non-lethal injuries may reduce the breeding success of wounded females and may permanently remove some animals from the breeding population (citation omitted). Vessel traffic and recreational activities that disturb manatees may cause them to leave preferred habitats and may alter biologically important behaviors such as feeding, suckling, or resting (citation omitted). Other threats from human activities include entanglement in fishing gear or debris; entrapment or crushing in water-control structures, locks and pipes; exposure to contaminants; and incidental ingestion of debris (citation omitted). Indirect effects from increased vessel traffic include increased water turbidity from wake action and decline of seagrass beds due to scarring by propellers (citation omitted). Petitioners' Exhibit 20, pp. 3-4. Essential Habitat for the Manatee Essential habitat for manatees, referred to in the Special Study as "places" (see id., p. 17), are areas frequented by manatees for extended time periods. These manatee places contain key habitat for manatee feeding, resting, and thermoregulation. In addition to the warm water aggregation places, the FWC's field staff has verified other places in the Caloosahatchee River area important to manatees. These secondary sites are important because they either contain fresh water or seagrass beds, aid in manatee thermoregulation, or are areas of minimal disturbance. Manatees are frequently seen in these important secondary sites during rapid cooling spells that do not greatly drop the ambient water temperature. Id. These important secondary sites are: Eight Lakes (deep canal lakes with warm water and sediments in SW Cape Coral); Chiquita Canal (freshwater source with access to Eight Lakes area); Bimini Basin (may be used for resting); Shell Point Village Lagoon (may have fresh water); Punta Rassa (seagrass beds-feeding aggregation); Beautiful Island (possible feeding site); Downtown Fort Myers Basins (presumably for fresh water discharged from hoses); Deep Lagoon (fresh water, resting, or warm water); Iona Cove (feeding); and Billy Creek (sediments retain heat). Deep Lagoon has been denominated a "minor aggregation site." Manatee Corridors Manatee "corridors" are areas visited regularly by manatees for brief times as they travel from place to place. The FWC has used telemetry data of manatees to model manatee corridors and manatee places. The Caloosahatchee River is a major manatee travel corridor because of the warm water discharged by the FP&L plant. The FP&L refuge attracts one of the largest wintering aggregations of manatees in Florida, with as many as 469 manatees having been counted in Lee County during the winter. In January 2001, as many as 434 manatees were counted in one day at the FP&L refuge. Manatees in the Caloosahatchee River generally travel not far from the shoreline, but they have also been observed to travel in the River's channels. Manatees also cross the Caloosahatchee River between Deep Lagoon and the Redfish Point area where the river narrows to 1,000 meters, and at Shell Point where the river narrows to 710 meters. Redfish Point lies across the river from Deep Lagoon. Manatees frequently travel between Redfish Point and Deep Lagoon, thereby crossing the main boat channel of the river. The FWC has identified this narrow part of the river between Redfish Point and Deep Lagoon as both a manatee travel "corridor" and as a heavy boat vessel travel corridor. Manatee crossings of the river also occur at Shell Point where the River narrows to 710 feet. Shell Point is the mouth of the river area where the river flows into San Carlos Bay. The FWC has identified the Shell Point area as a manatee travel corridor, and as the most heavily used boat vessel travel corridor. The 1998 Gorzelany report recorded an average of five boats per minute passing the Shell Point area. Just to the west of Shell Point, the boat channel in eastern San Carlos Bay is known as the "Miserable Mile." The Shell Point and Miserable Mile area likely represent the highest risk areas for watercraft collisions with manatees. Manatee Population The exact number of Florida manatees is unknown. Manatees are difficult to count because they are often in areas of poor water quality, and their behavior, such as resting on the bottom of a deep canal, can make them difficult to see. Aerial surveys and ground counts (statewide synoptic survey) have been conducted by the state in most years since 1991. There are four regional sub-populations of the Florida Manatee, these being in the Northwest Region, the Upper St. Johns River Region, the Atlantic Region, and the Southwest Region. The great bulk of the Florida population lives in the Atlantic and Southwest Regions. The sub-populations of the Manatees in those two regions account for substantially more than 80 percent of the total Florida manatee population with roughly half of the two in each region. The Southwest Region of the West Indian Manatee consists of the coastal counties from Pasco County south along the Gulf of Mexico to Whitewater Bay in Monroe County (including Lee County), and the inland counties of DeSoto, Glades, and Hendry Counties. The Southwest Region population of the Florida manatee constitutes approximately 42 percent of the total Florida manatee population. The adult survival rates in the Southwest Region are substantially lower than the survival rates in all of the other manatee regions in the state. The average age at death of manatees in the Southwest Region is significantly lower than in other regions of the state and statewide. Of the four Florida sub-populations, there is less data available for the Southwest population. "[A] priority [has been] placed on catching up to gather the necessary amount of data to better evaluate [the] status of the southwestern population." (Tr. 516-517). Nonetheless, both FWC and the U.S. Fish and Wildlife Service (FWS) have developed manatee population models, that are both sound and comprehensive. The two agree about the status of the Southwest Region population of the Florida manatee and its immediate future as explained at hearing by Dr. Bruce Ackerman, an expert in marine mammal biology, manatee population modeling, and manatee aerial surveys: "The two models were written to answer somewhat different questions, but an area that they agree on is that the southwest population is likely to be declining now, whether a little or a lot, is not so clear, but likely to be declining at this time and in the near future." (Tr. 923). The FWC's Florida Manatee Recovery Plan contains three benchmark criteria for each of the four manatee regions: average annual adult survival rate of 94 percent, average annual reproduction (at least 40 percent of adult females with calves during the winter), and the average annual rate of population growth is equal to or greater than zero. The Southwest Region manatee population is currently failing to meet the Florida Manatee Recovery Plan goal criteria. Even in the absence of any water-craft related mortalities (incidental takes), the growth rate of the Southwest Region manatee population over the next 20 years is expected to be negative. In the Southwest Region, there is no excess manatee population growth and no net productivity which can be allocated to incidental takes. In the absence of any water-crafted related manatee moralities in the Southwest Region, the probability of recovery of the Southwest Region manatee population in the next 100 years is 63 percent. If current Southwest Region watercraft-related manatee mortality trend continues, there is a zero percent chance of the recovery of the Southwest Region manatee population. Natural Threats to Manatees Manatee populations are threatened by natural causes as well as causes whose origin is human activity. The fatal and non-fatal natural threats to manatees include cold temperatures, hurricanes, red tide (Karenia brevis) events, and disease. Manatee carcasses with evidence of cold- stress show reduced gastrointestinal tract activity, a condition that can reduce an animal's buoyance. Juveniles and sub-adults are the most vulnerable to cold-stress death. Manatees on Florida's west coast are frequently exposed to brevetoxin, a potent neurotoxin, during red tide events. Manatees are exposed to brevetoxin through inhalation and ingestion. There were 75 manatee fatalities in the Southwest Region due to red tide recently. Watercraft-Related Mortality Types of Fatal Injuries The Florida Marine Research Institute conducted an analysis of watercraft-related mortality of manatees in Florida covering the period 1979 to 1991. Its abstract sums up the analysis as follows: From 1974 to 1991, the annual number of manatee (Trichechus manatus latirostris) deaths increased. The most frequent cause of death from human activity is collision with watercraft. Scars and wounds from propellers are common. A total of 1,376 sets of fatal or healed wounds was measured on 628 dead manatees recovered from 1979 through 1991. Collisions with watercraft caused 406 of these deaths. Of the 406 deaths, propeller cuts caused 158 (39%); impact injuries (no propeller cuts) caused 224 (55%); propeller cuts and impact injuries, either of which would have been fatal, caused 16 (4%); and unidentified specifics of the collisions caused 8 (2%). Fatal cuts were usually larger (longer) than healed wounds. Many animals survived several boat collisions; one manatee had 22 separate patterns of propeller cuts. The mean length [formula omitted] of the longest fatal cut from a propeller indicated that death was most often caused by a direct-drive watercraft. In contrast, fatal-impact injuries may have resulted from fast-moving watercraft of many sizes and types. Impact injuries killed more manatees than propeller cuts and increased in proportion with time. Impact often resulted in massive internal injuries with only minor surface abrasions. Only 2% of the propeller strikes were to the head, but 98% were to the dorsum. In addition, nearly 90% of the scar patterns were along the head-to-tail axis, indicating manatees were moving in response to an oncoming boat when struck. Changes in watercraft design may increase the frequency of operation of boats in shallow water. This increases the probability of collisions with manatees. Petitioners' Exhibit 26, pp. 259-260. The location of scars and wounds from propellers ranged from the head to the tail of manatees: Head (2%), Thorax (26%), Mid dorsal (body)(17%), Abdomen (36%), Tail (19%). Watercraft collision with manatees are common. Even U.S. Coast Guard and the FWC marine patrol boats have struck manatees. Mortality Data While the FWC's manatee mortality data are deemed to be reliable, the FWC does not document all watercraft-related manatee fatalities. It is, of course, not possible to know how many manatee carcasses escape observation and are not recovered. Even estimation of such numbers has difficulties. But scientifically, it is generally accepted that there is an undercount of manatee carcasses. It is known, for example, that in cases of manatee perinatal (dependent calf) deaths, carcasses are frequently not recovered. No recoveries in such cases are due to a number of factors: the small size of the carcass, rapid decomposition, and presence of scavengers. The manatee deaths listed by the FWC as having an undetermined cause of death could be watercraft-related deaths. A perinatal death, moreover, could be the direct result of a watercraft-related death of the mother. Watercraft-related manatee injuries are not limited to power boats. They may also be caused by sailboats. A significant number of sailboats have shaft driven inboard motors with a rudder that functions as a skeg (a projection that is the after part of the keel or an extension upon which the rudderpost is mounted). Collisions between skegs and manatees cause sub- lethal and lethal injuries to manatees. Statewide Mortality Rate The most frequent cause of manatee death that is avoidable is watercraft collision. Statewide, the watercraft- related mortality of manatees is 24.5 percent for the time period January 1974, to December 2002, the highest single cause of manatee deaths. Lee County Mortality Rate Among counties, Lee County has the second highest level of watercraft-related deaths in Florida, with 163 reported between January 1974, and December 2002. From 1975 through 1993, the annual watercraft-related manatee deaths in Lee County were less than 10 per year. During the nine years from 1994 to 2002, there were 109 watercraft-related manatee deaths in Lee County, an average of 12.1 per year. In 1999, the watercraft-related deaths were 10 in Lee County. There were 13 in 2000, 23 in 2001, and 13 in 2002. The first six months of 2003, through June 10, have seen six watercraft-related deaths of manatees in Lee County. The 23 manatees to have died from watercraft-related injuries in Lee County in 2001, accounted for 45 percent of the total number of manatee deaths in Lee county for the year. Caloosahatchee River Mortality Rate For the ten years from 1976 to 1986, the number of watercraft-related manatee deaths in the Caloosahatchee River was 15, with an average annual number of such deaths being 1.5 per year. For the five years from 1988 to 1993 (no data available for 1989), the number of watercraft-related manatee deaths in the Caloosahatchee River was 13, with the average annual number of such deaths being 1.8 per year. For the seven years from 1994 to 2000, the number of watercraft-related manatee deaths in the Caloosahatchee River was 30, with the average annual number of such deaths being 4.3 per year, a substantial increase over the earlier annual numbers. From 1989 through 2001, the annual number of watercraft-related manatee deaths for the Caloosahatchee River increased by 15.1 percent per year. This rate of increase is higher than the rate of increase of such deaths in the Southwest Region manatee population (9.2%), and almost triple the rate of increase of such manatee deaths statewide (5.5%). The rate of increase of watercraft-related manatee deaths over the past 13 years in the Caloosahatchee River, moreover, is higher than: (a) the manatee death rates of all categories for the Caloosahatchee River, (b) of all watercraft- related manatee deaths in southwest Florida, and (c) of all watercraft-related manatee deaths statewide. There are a number of caveats to be considered when considering manatee death data. For example, "[I]t cannot be conclusively known where manatees are actually struck by boats." Petitioners' Exhibit 21, p. 9. A "Summary and Analysis of Manatee-related Data in Lee County, 2002" prepared by Mary Duncan of the FWC (Petitioners' Exhibit 21), elaborates: The mortality database reports carcass recovery locations, which is not necessarily where animals were struck by watercraft, or where they died. For watercraft-related manatee deaths, the precise location of where animals are struck usually cannot be verified unless reported by a witness of the incident. Carcasses may move with currents and tides, but also some injuries may not cause immediate death. Injured animals have been know to swim many miles before dying. Since there is a warm water refuge in the Orange River, at tributary off the Caloosahatchee River, it is possible that some injured animals may attempt to reach this area since it represents a safe place. Cases where death occurred several days to weeks after the trauma are considered "chronic". Some of the recent watercraft-related deaths recovered in the Orange River have been identified as chronic. Efforts are underway to make this determination on historical necropsy reports. It is possible that some animals included in the Caloosahatchee River dataset may have actually been struck outside the river system. While this analysis may provide additional information and insights, it should be recognized that most cases do not have evidence of chronic injuries-but the carcass location of those cases cannot [be] assumed to represent the impact site. Petitioners' Exhibit 21, pp. 9-10. Because of these caveats, Ms. Duncan's analysis posits, "[i]t is difficult to draw conclusions on relative risks to manatees from vessels with death data alone." Her report reaches these conclusions, There appears to be an intersection of high boat use and high manatee use at the . . . mouth of the Caloosahatchee River and San Carlos Bay, commonly called the Miserable Mile area (reference omitted). This area represents the highest risk area for boat/manatee collisions. Boating studies indicate that vessel traffic is higher during the spring and summer, with the Miserable Mile area of San Carlos Bay being the highest use area. Miserable Mile is also identified as the highest vessel traffic area in Lee County in a 1998 boating study by Mote Marine Laboratory. Manatee aerial survey data confirm higher manatee use in Miserable Mile area and other parts of Lee County outside of the Caloosahatchee River system during the spring and summer. This is also confirmed by a higher number of watercraft deaths in these areas during the same time of year. Id., at 11. Ms. Duncan's report summarizes its conclusions drawn from the analysis of manatee-related data in Lee County: Existing population models now being developed typically assume that the level of threat will remain the same, since it is difficult to factor in projected threat increases. However, it is likely that threats are increasing and will continue to increase, such as increasing boat traffic and reduced foraging resources from increased coastal development. Such factors are likely to influence reproductive success and mortality rates. On a statewide basis, the continued high level of manatee deaths raise concern about the ability of the population to grow or at least remain stable. (Citation omitted.) Lee County currently ranks second in watercraft-related deaths and second in all categories of deaths statewide, suggesting that this county's waters provide a crucial habitat for manatees. Previous offsetting measures recommended during the permit review process do not appear to have offset the impacts of increasing boat traffic. Speed zones alone do not offset all adverse impacts to manatees from increased boat traffic. Long term comprehensive planning documents, such as a boat facility siting plans and manatee protection plans, are also needed to place marinas where they are least likely to increase risks to manatees. These types of conservation measures are needed to reduce the number of human-related manatee deaths, which will reduce overall manatee mortality. Id., at 13. Speed Zones and Boating Restrictions In 1989, manatee speed zones were implemented in Lee County. The steady increase in the annual number of watercraft- related manatee deaths in the Caloosahatchee River since then, and the dramatic increase in the annual rate of watercraft- related deaths in the River during the recent seven-year time period from 1994 to 2000 demonstrate, as is generally accepted and as concluded by Ms. Duncan, that speed zones alone do not offset adverse impacts to manatees from increases in boat traffic. This increase has occurred despite many features of boating restrictions in the area. Primary features of the Lee County speed zone, for example, are a one-quarter mile slowspeed shoreline buffer on either side of the intercoastal waterway channel from the mouth of the River to the U.S. 41 Bridge, and slow speed outside most of the intercoastal waterway channel from the Edison Bridge to the railroad trestle. The State-mandated manatee protection speed zones administered by FWC's Bureau of Protected Species Management under Florida Administrative Code Rule 68C-22.005, impose a year- round one-quarter mile slow speed zone for the entire shoreline of the Caloosahatchee River to the Edison bridges. East of the Edison bridges there is a slow speed zone outside of the marked channel all year, and a 25 mph maximum speed in the channel. East of the railroad trestle near Beautiful Island to east of the I-75 bridge crossing, in the area that includes the FP&L power plant, there is an idle speed zone imposed outside the channel all year, and an idle speed zone in the channel from November 15 through March 31. There is also an idle speed zone in the Orange River all year. Lee County's regulations, pursuant to its Ordinance No. 02-14, adopted on March 26, 2002, restrict boat speed within 500 feet offshore from all beaches, and within 500 feet from any water-oriented structures, such as docks, to idle speed. The FWC rules at Florida Administrative Code Rule 68C- 22.002(7), define "slow speed" as "the speed at which a vessel proceeds when it is fully off plane and completely settled into the water." The definition also states, "This required level of protection for the safety of vessels and vessel operators is also intended to provide adequate protection for manatees and is therefore adopted because of its familiarity to vessel operators." The State defines a slow speed zone as "an area where vessels may not be operated at greater than Slow Speed." Fla. Admin. Code R. 68C-22.002(8). The County's Ordinance 02-14 describes "idle speed" as: the lowest speed at which a vessel can operate and maintain steering control. The actual speed will depend upon the design of the vessel and on the vessels load, wind direction and speed, and the sea conditions. Generally, it will be between 1 and 3 miles per hour for outboard and inboard/outboard vessels, between 2 and 5 miles per hour for fixed shaft/rudder vessels. Boat Club Ex. 20 at Section Three. This definition is substantially the same as the State's definition. Marine signs in Deep Lagoon include two idle speed County ordinance signs. One is at the entrance to the central and south canals; another is at the entrance channel into Deep Lagoon and the River, inside the one-quarter mile State manatee speed zone. The second sign lets boaters know they are entering the County idle speed zone from the slow speed zone. There is also a slow speed sign for the boaters leaving the Deep Lagoon channel. It lets them know they are leaving the idle speed zone and entering the State's slow speed zone. The State, Lee County Sheriff, and Lee County municipalities participate in enforcing the State speed zones in the Caloosahatchee River. The Lee County Sheriff and the municipalities, through a memorandum of understanding, enforce the Lee County Ordinance if there is not a more restrictive ordinance in the municipality. On July 11, 2002, the Lee County Sheriff enacted a "zero tolerance" policy. It directs its marine unit to no longer issue warnings. Every stop for violation of a speed restriction is ticketed. The cost of the tickets ranges from $50 to $75. It is too soon, however, to tell what effect the policy is having on protection of manatees. Funding for Lee County marine patrol officers has increased recently. In February 2003, local law enforcement entities created a Manatee Task Force in order to better coordinate manatee protection efforts within Lee County. Once or twice per month, the U.S. Fish and Wildlife Service selects an area in Lee County for a heavy patrol known as a "wolf pack." (Tr. 426). The wolf pack consists of "three to four boats and eight or more officers". (Tr. 427). It concentrates in one area. Lee County also maintains displays of the county's Boater Guide at all local boat ramps showing the State and County speed zones, with a more detailed inset of the area where the boat ramp is located. Another education effort consisted of the mailing of a Boater's Guide that detailed manatee protection zones to about 40,000 registered boaters. Nonetheless, there are channels exempt from speed zones. All manatee travel corridors and places, moreover, are not subject to speed limitations. For example, the corridor that crosses the River from Redfish Point to the mouth of Deep Lagoon is not entirely subject to speed limitations. Commercial vehicles, moreover, can apply for exemption from manatee speed zones and can be exempted if compliance would be "burdensome." (Tr. 443). Compliance with manatee speed zones by boaters, as Ms. Kleist, an advocate of manatee protection, confessed in her case, is far from exemplary. A review of vessel activity in the Special Study led to this summary: Boaters in the Caloosahatchee River behave similarly to others throughout the state (citation omitted). Vessel traffic is highest on spring weekend afternoons. Yachts, ski boats, and open fishermen are the three most common vessel types found between the Edison Bridge and Miserable Mile while Mullock Creek is dominated by open fisherman. In these areas, the most common vessel sizes range from 16-39 feet. Highest traffic densities occur at Shell Point, where the Caloosahatchee River and San Carlos Bay converge. Mullock Creek had comparatively low levels of boat traffic. Many of the boats along the lower Caloosahatchee River originate in the Cape Coral canal system and travel toward the Gulf of Mexico. The highly variable, site- specific nature of boaters' behavior and vessel compliance requires scientists and managers to treat each site individually. Compliance with speed zones ranged from 12- 77% in the Caloosahatchee with an overall compliance of 57.3%. Although the number of vessels using Mullock Creek was relatively low, compliance was 26% accompanied by a high level of blatant non-compliance. Compliance rates may not be as important as the total number of blatant violators. While Shell Point has higher compliance, it also has heavy boat traffic that yields a greater total number of blatant violators that could pose a threat to manatees than areas with lower compliance. Petitioner's Exhibit 20, at 15. The number and size of registered boats is substantially increasing. For management of the manatee, it is important to determine where and how watercraft collisions occur. Studies to date have not yet reached these determinations. Watercraft-Related Sub-Lethal Injuries Between 60 percent and 90 percent of all Florida manatees have propeller scars. Propeller scars on manatees are so common that the FWC uses propeller scars to identify manatees. Of the over 1,000 living manatees in FWC's photo-identification data base of manatees with scars or other identifiable features, 97 percent had scar patterns from more than one watercraft collision. Most adult manatee carcasses bear scars from previous boat strikes, and the healed skeletal fractures of some of these carcasses indicate they had survived previously traumatic impacts. An example of such scar patterns is manatee MSW9321. Its carcass "floating in the Caloosahatchee River just inside the mouth of Deep Lagoon" (Petitioners' Exhibit 26), was recovered by the Department of Natural Resources in May of 1993, with the assistance of Mrs. Sheridan. The manatee had ten fresh propeller wounds along its back and across its fluke, five of which penetrated its body cavity, and multiple healed and healing scars in the dorsum. There were 31 prior scars from propeller cuts. The FWC's study of 628 manatees carcasses recovered from 1979 to 1991, found that manatee carcasses with no propeller scars were rare. Many manatees have multiple sets of propeller scars from different collisions. Non-fatal propeller cuts can become contaminated wounds which can cause prolonged illness and death. Non-fatal watercraft-related injuries can damage a manatee's ability to swim. They may reduce the breeding success of wounded females, and remove some animals from the breeding population. In sum, as was found nearly four years ago by Administrative Law Judge Meale in paragraph 14 of the recommended order in Sheridan II: The rate of manatee deaths from collisions with watercraft has increased with the popularity of motorboating. Boat registrations in Lee County rose from 13,000 in 1974 to 36,000 in 1997. The potential from mitigation offered by the enactment of speed zones has been undermined by the fact that nearly half of the boaters fail to comply with the speed limits. (Petitioners' Exhibit 8, p. 9 [this exhibit contains only the odd-numbered pages of the recommended order; official recognition is taken of the order in its entirety]). As further found in the Sheridan II recommended order: "Manatee mortality from watercraft is extremely high in the immediate vicinity of Deep Lagoon, and the mortality rate has increased in recent years." Id. Manatees in Deep Lagoon Groups of manatees frequently use Deep Lagoon. The state, under the auspices of FWC and its predecessors, has made numerous aerial flight observations of manatees of Deep Lagoon. Between January 17, 1984, and December 19, 1985, there were 48 such flights. Between July 24, 1988, and November 15, 1995, 23 aerial observations were flown. Groups of manatees were observed in Deep Lagoon near the mouth of the north canal, in all portions of the north canal, and in the Cow Slough headwaters of Deep Lagoon. Manatees radio-tagged by the state have also been documented in Deep Lagoon. On May 28, 1998, photographs were taken of groups of manatees in Deep Lagoon near the mouth of the marina's north canal and in the north canal. In late May 2003, photographs were taken of manatees in the Iona Drainage District canal near the mouth of the north canal. The Boat Club has also taken video tapes on numerous times of numerous manatees (from one manatee to groups of as many as five manatees) in the north canal. Each of the three Petitioners testified that on numerous occasions they have observed numerous manatees, including manatee mating herds in Deep Lagoon, the north canal, and the Iona canal. A manatee pair was also seen one day in the Iona Canal which appeared to be a new born manatee. Manatees have been observed several times in Deep Lagoon with small calves. From April 1974, to August 2002, within Deep Lagoon itself, 13 manatee carcasses have been recovered by the state. Four of the manatee deaths were determined to be watercraft- related deaths. Five of these manatee deaths were due to natural causes other than cold stress. For three, the cause of death was notdeterminable due to decomposition. One of the deaths was perinatal. In the Caloosahatchee River just outside the mouth of Deep Lagoon, during this period of time, the FWC recovered six manatee carcasses. Three of the deaths were watercraft-related. One was perinatal. The cause of one of the deaths was undeterminable due to decomposition. Another of the deaths was verified but the carcass was not recovered, thus the cause of death of was not determined. The Opinions of Experts None of the Petitioners' manatee experts expressed the opinion that the proposed permit would have an adverse effect on the manatee. Dr. Ackerman, for example, had never seen the application and had no opinion about whether it should be granted or not. See Tr. 933. But two of Petitioners' experts expressed opinions either that the addition of watercraft into any river system that constitutes manatee habitat poses a risk of collisions between boats and manatees or that adding boats to the Caloosahatchee River system poses a threat to the manatee unless there is some other accommodation for manatee protection. Sara Lynn McDonald, a marine biologist with FWC's Florida Marine Institute and an expert in marine mammal biology, wrote the majority of the report for the Special Study. When asked her opinion concerning whether an increase in boat traffic on the Caloosahatchee would increase the possibility of water crafts colliding with manatees, she answered, "Yes, I believe that in any system an increase in vessel traffic would increase risk of harmful collisions with motor boats." (Tr. 898). Ms. McDonald was asked on cross-examination whether she believed that speed zones are an effective measure to prevent collisions between manatees and water craft, she answered, "I think they can be." (Tr. 913). Dr. Bruce Ackerman, an expert in marine mammal biology, manatee population modeling, and manatee aerial surveys, was also called by Petitioners. Dr. Ackerman testified that the between 1974 and 1991, boat registrations in Florida trended upward and so did manatee fatalities from water craft collisions. Both trends have continued since 1991. His opinion was that "all other things being equal, adding more boats into [the Caloosahatchee River] system would increase the risk to manatees." (Tr. 923). On cross-examination, Dr. Ackerman went so far as to agree that speed zones show promise for the protection of manatees. Education, required by the state now of new boaters, in his opinion "helps somewhat." (Tr. 930). Mr. Pitchford, like Ms. McDonald and Dr. Ackerman, is an employee of FWC's Florida Marine Institute. He manages the State's Marine Mammal Pathobiology Lab where manatee necropsies for cause of death is determined. He offered testimony about the causes of deaths of manatees and related issues, but did not express an opinion at hearing, just as Petitioners' other two manatee experts, on whether the Boat Club's application should be granted or not. In contrast to the three experts who testified at the behest of Petitioners, two experts called by the Boat Club opined that there would be no adverse impact to manatees if the Boat Club's application were granted in the form preliminarily approved by the Department. Tom Logan, an expert in wildlife biology, whose specialty is in "endangered species management" (Tr. 484), opined that the project will not have an adverse affect on the manatee or its habitat. Mr. Logan offered this opinion on the basis of information he had examined and because, "the level of use that will be there with the proposed marina in place relative to what has been there in the past . . . will not result in anything increased or additive in the way of activity in the water that manatees are using . . . ." (Tr. 491). In other words, there will be no increase in power boats or other watercraft (sailboats with skegs, for example) in the Caloosahatchee River as the result of the proposed permit and therefore, granting the permit would have no adverse impact on manatees. Furthermore, Mr. Logan testified that manatee management protection programs combining speed zones, enforcement of speed limitations and education, can assist in the protection of manatees particularly in marina areas where manatees tend to congregate or visit. The speed zones in Lee County (in place of a considerable number of years), coupled with a "zero tolerance" enforcement policy in place since July of 2002, appeared to him to be working. (Tr. 491). Ms. Mary Duncan, a state Environmental Specialist III and FWC's Bureau of Protected Species Management's coordinator of its mortality database, was accepted as an expert in "potential impacts to manatees from development." (Tr. 777). At the time of hearing, she had conducted permit reviews for the bureau for 11 1/2 years, the time in which the bureau has been a part of the Department of Natural Resources, the Department of Environmental Regulation, the Department of Environmental Protection and the Florida Fish and Wildlife Conservation Commission. She has a "Bachelor's in biology with a minor in chemistry" (Tr. 775), and prior to the hearing in this case had testified four times in judicial or administrative proceedings on potential impact of manatees from development. Ms. Duncan has been involved with Deep Lagoon Marina permitting since "about 1994." (Tr. 777). In 1998, for example, she prepared a Manatee Impact Review Report for the Deep Lagoon Marina permit modification that involved the stormwater permit application and "the allowance of liveaboards, the relocation of the travel lift ramp to the north canal, and a redesign of the proposed cross connection between the north canal and the main basin." DEP Ex. 41. Her review described the project as in "an area of relatively high manatee use in Lee County, based on aerial survey and mortality data . . . [where the power plant] effluent attracts one of the largest wintering aggregations of manatees in Florida." Id. Her report further noted: Despite some existing manatee protection measures such as speed zones, watercraft- related manatee mortality trend is continuing to increase within the Caloosahatchee River. It is unknown whether the continuing deaths are a result of inadequate speed zones, inadequate posting of speed zones, inadequate enforcement of speed zones, and/or the cumulative impact from years of adding boats to the system. It is probable that many or all of these factors are involved. Id. In the historical information section of the report, Ms. Duncan showed the project to have 228 existing slips (61 wet, 167 dry) with previously permitted but not constructed slip at 446 (113 wet and 333 dry) for a total of 674 slips (174 wet, 500 dry). In a section entitled "Cumulative Impacts," the report found: This project is expected to add a significant number of boats to this system, significantly increase the level of boat traffic, and change boat traffic patterns in the study area. The vessels from this project are expected to produce significant adverse impacts to manatees that use the Deep Lagoon in the immediate vicinity of the project as well as in the boater's sphere of influence of the project. Secondary adverse impacts include lethal and sublethal watercraft- related injuries, disturbance contributing to stress, and alteration of natural behaviors. Id. Numbers of recommendations were made in the report as conditions for approval including that "boat launching from the uplands be prohibited along the shoreline of the North Canal" (id., page 5 of 7), and that "[a]fter construction of the dry storage barns, storage of boats on trailer or open dry storage racks shall be prohibited." Id., page 6 of 7. On March 1, 1999, Ms. Duncan authored a memorandum through which the Bureau of Species Protection Management suggested that the following language be used as condition of the Boat Club's proposed permit, Launching and retrieval in the north canal shall be restricted to vessels requiring boat repair. The applicant shall maintain a daily log of vessels launched and retrieved from the north canal travel lift. The applicant shall also maintain a log of incoming and outgoing boat repairs, which shall correlate with the travel lift log. DEP Ex. 43. A letter authored by Ms. Duncan dated November 18, 2003, was sent to Mr. Calvin Alvarez in the Southwest District Office of DEP. Signed by Brian Barnett, Interim Director of the FWC's Office of Environmental Services, it represents the Commission's comments and recommendations regarding the Boat Club's application under review in this proceeding. The letter contains a number of recommendations for conditions of the proposed permit, all of which were, in fact, made conditions of the permit as approved. In addition to standard construction conditions, development of a marina manatee education program, and installation of grates over certain pipes to prevent manatee drowning, the recommendations included the following: Of the 485 slips proposed for this marina, the number of powerboats allowed at this facility shall be limited to 445. The remaining slips (40) must be either occupied by sailboats or left unoccupied. Future requests for additional powerboats will be considered if the secondary and cumulative impacts associated with this increase are not expected to adversely affect the West Indian manatee. Storage of boats on trailers or open land racks shall be prohibited. Use of the travel lift in the north canal for boats less than 40 feet in length is prohibited except in emergencies (approaching hurricane etc.). Limitation on the use of this lift shall not exceed a 28-day rolling average of ten vessels a week for those vessels, except in emergencies (approaching hurricane etc.). Launching and retrieval of boats in the north canal shall be restricted to vessels requiring boat repair. The applicant shall maintain a daily log of vessels launched and retrieved from the north canal travel lift. The applicant shall also maintain a log of incoming and outgoing boat repairs, which shall correlate with the travel lift log. DEP Ex. 33, page 3. So long as the recommendations in the letter are conditions of the proposed permit, Ms. Duncan offered the opinion that the proposed permit "imposes minimal adverse impacts to manatees, and if any impacts do occur, they have been offset by" the permit conditions. (Tr. 784). Ms. Duncan's opinion was based on review of the project, "the historical background of the facility, manatee data, the requirements of the ERP rule, and [her] general knowledge of Lee County and manatee use in Lee County." Id. The 1990 Aerial: Proof of Maximum Historical Use Of particular import to Ms. Duncan's review was the historical background of the facility. Ms. Duncan reviewed a document provided to her by Hans Wilson and Associates, the Boat Club's environmental consultant and marine engineer. The document, enlarged as DEP Ex. 37, "has two coverages. It is an aerial photograph in 1990 of the facility. Overlaid on that is a CAD drawing done by Hans Wilson to outline what they determined to be existing boats that were uncovered in open storage on the facility in 1990." (Tr. 786-787). Ms. Duncan used the document to determine "actually how many boats were located coming out of this facility." (Tr. 787). She determined that there were 217 "Uncovered Dry Slips" (DEP Ex. 33) at the marina in 1990. Together with 61 authorized wet slips and 167 authorized "Covered Dry Slips" (id.), she reached a total of 445 slips at the marina as the historical maximum, 40 slips less than the 485 that were proposed in the Boat Club's current ERP application. Hence, FWC recommended that the number of power boat slips be restricted to 445 slips. Ms. Duncan chose the 1990 aerial for the basis of her recommendation because unlike the other aerials she looked at from 1993, 1999, 2000 and 2001, "[t]he 1990 aerial was the period of time that the facility appeared to be at full operating capacity in the sense that this was the aerial that showed the most boats and open storage on the uplands." (Tr. 787). Furthermore, she chose the 1990 aerial because "it represents the existing use of the facility before they started clearing it to prepare for building boat barns later in the 1990's." (Id.) Use of the 1990 aerial as the proof of maximum usage of the marina enabled Ms. Duncan to conclude, like Mr. Logan, that restricting the number of power boats slips at the marina to 445 would not introduce any new boats into the system. Usage at Other Times However fair to the Boat Club the choice of the 1990 aerial as to historical background of usage at the marina might be, it is not free of problems. First, the 1990 aerial is more than a decade old. In the interim, the marina was not shown by a number of aerials to have achieved the usage that appears to have peaked in 1990. The actual usage at the marina, in fact, has varied over time greatly and has been less (at times, much less), than what it was in 1990. Recent usage at the marina, in fact, has been far less than it was in 1990. At the 1999 administrative hearing before Administrative Law Judge Meale, Mr. Ruff, in answer to a question from the Administrative Law Judge, offered that the covered dry space and uncovered dry space totaled only about 200 slips rather than the 356 dry slips proposed in the Boat Club's current application: The ALJ: Okay. Can we deal with first what's in the ground or on the water, regardless of what's been authorized? If you need to confer with other witnesses, that would be fine. Mr. Uhle: Mr. Ruff is the person who knows how many dry spaces there are. The figure 61 wet slips I believe is correct. The ALJ: For present conditions? Mr. Uhle: For present conditions. Ms. Holmes: And that's permitted and in use. Mr. Uhle: Those are existing. The ALJ: Existing, right. * * * The ALJ: How about dry spaces. Mr. Ruff: Okay. The existing dry space, there is approximately in the two buildings and on the ground and outside racks, about 200. When we bought the property [in 1997], there were about 400 because we used the entire north peninsula for dead storage. We've eliminated that, effectively, so we've probably eliminated 150 boats from the property since we bought it. And they were there for a long time. Petitioner's Exhibit 9 (emphasis supplied). Mr. Ruff's testimony supported the administrative law judge's finding that "Deep Lagoon Marina presently consists of 61 wet slips, 200 dry slips, and other marina-related buildings." Sheridan, et al., v. Deep Lagoon Boat Club, Ltd., et al., DOAH Case No. 98-3901, Recommended Order (November 24, 1999), paragraph 6, and supported the finding that adding 227 dry slips so as to raise its dry slip capacity to 427 dry slips would "adversely impact the value of functions provided to manatees by the affected surface waters." Furthermore, the Sheridan II Recommended Order found: Manatee mortality has increased as boat traffic has increased. Substantial number of boaters have ignored speed limits. Quality manatee habitat in this critical area along the Caloosahatchee River is not plentiful. Id., paragraph 137. In light of these facts, the recommended order reached the conclusion, "[a]pplicant has failed to provide reasonable assurance that the secondary impacts of the proposed system will not adversely impact the abundance and diversity of wildlife and listed species, of which manatees are one, and the habitat of wildlife and listed species." Id., paragraph 138. In its final order in Sheridan II, DEP disapproved the maintenance and dredging exemption issue to the Boat Club, denied the Boat Club's request for a determination of entitlement to a maintenance and dredging exemption for dredging in the marina canals, and denied the Boat Club's application for an ERP to construct a SWMS on uplands at the Marina site. In the course of the final order, DEP "declined to reject the ALJ's mixed statements of law and fact concluding that increased boating activity and other Marina expansion activities authorized in the Original Permit constituted adverse secondary impacts of the proposed SWMS to water quality and to manatees and their habitat." Petitioners' Exhibit 8, DEP Final Order, OGC Case Nos. 98-1184 and 98-3047 and DOAH Case Nos. 98-3901 and 98-5409, p. 42 (January 28, 2000). Actual usage at the marina of 61 wet slips and 200 dry slips was confirmed again in Sheridan III both in the recommended order issued in January of 2000, and the final order by DEP. Ms. Duncan's testimony was forthright; her demeanor earnest. There is nothing to suggest that her opinion was anything other than honest and sincerely held. If one were to suspect that Ms. Duncan had a bias, it would be, in light of her position with the state and the recommendations she has made in the past, toward manatee protection. Her opinion, therefore, that the proposed permit does not adversely affect manatees should be given substantial weight. Ms. Duncan's opinion, however, is rejected. It is rejected because, just as Mr. Logan's, it is based on a faulty assumption: that approval of the permit will not introduce into the Caloosahatchee River system more boats that threaten the endangered manatee. The approval of the permit will allow more slips (485) and power boats (440) than have been actually at the marina since 1999 when Mr. Ruff testified before Administrative Law Judge Meale (261, 200 dry slips and 61 wet slips). The approval will allow more boat slips and power boats than the Boat Club claims in its proposed recommended order exist there now (400, 50 wet and 350 dry). Furthermore, it may be inferred that the upgrade, particularly if Clean Marina status is achieved and is publicized, will make it likely that the marina will be more attractive to boaters and will operate at full capacity. Full capacity is 184 more power boats above the capacity that served as the baseline in Sheridan II, and 224 more boat slips than the Sheridan II baseline. Furthermore, and most persuasively, the Department decided in Sheridan II that allowing a similar number of boats to operate in the Caloosahatchee River system constitutes adverse secondary impacts to the manatee and its habitat. There is nothing in this record that is shown to have occurred in the past three years that would justify overriding the Department's conclusion. Sovereignty Submerged Lands Lease The applicant has provided all information necessary to qualify for a proprietary authorization for a lease of sovereign submerged lands. But the Boat Club has failed to demonstrate that the lease will not be contrary to the public interest. See paragraph 204, below. Claim of Boat Club Violations Petitioners claim that the Boat Club has violated permit conditions or environmental law in the past in a number of different ways. There was no proof, however, of these violations. There was not even proof that the Department has ever issued a notice of violation to the Boat Club. Applicable Law In General At hearing, DEP produced a notebook with a cover page inside the book entitled "ALJ's Copy of Statutes and Rules." Official recognition was taken of the contents with no objection from any of the parties. Included in the notebook is an "Operation Agreement Concerning Regulation Under Part IV, Chapter 373, F.S., . . . Between South Florida Water Management District and Department of Environmental Regulation." Pursuant to the agreement, DEP reviews and takes final action on all applications for permits under Section IV of Chapter 373, Florida Statutes, for docking facilities and adjacent docking and boating-related development which includes "parking areas for the docking facility, dry storage facilities, boat sale and supply facilities, maintenance and repair facilities, associated seafood loading and processing facilities, restaurants, harbor master and marina administration facilities." Section II, A. 1(i), pp. 3 and 4 of the Operating Agreement. Section 373.413 provides that "the governing board [of the water management district] or the department may require such permits and impose such reasonable conditions as are necessary to assure that the construction . . . of any stormwater management system . . . will comply with the provisions of (Part IV of Chapter 373] and applicable rules . . . and will not be harmful to the water resources of the district." Section 373.414, entitled "Additional criteria for activities in surface waters and wetlands," provides: As part of an applicant's demonstration that an activity regulated under this part will not be harmful to the water resources or will not be inconsistent with the overall objectives of the district, the governing board or the department shall require the applicant to provide reasonable assurance that state water quality standards applicable to water as defined in s. 403.031(13) will not be violated and reasonable assurance that such activity in, on, or over surface waters or wetlands . . . . is not contrary to the public interest. * * * In determining whether an activity, which is in, on, or over surface waters . . . and . . . is not contrary to the public interest . . . the department shall consider and balance the following criteria: Whether the activity will adversely affect the public health, safety, or welfare or 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. See also Fla. Admin. Code R. 62-4.242; Fla. Admin. Code R. 40E- 4.302; and SFWMD Basis of Review, Section 4.2.3. Florida Administrative Code Rule 62-302.300 states the Department's anti-degradation permitting policy for surface water quality. Section (15) of the rule provides that pollution that causes or contributes to new violations of water quality standards or to continuation of existing violations is harmful to the waters of this State and shall not be allowed. Section (17) of the rule provides that the Department shall permit new discharge if it will not reduce the quality of the receiving waters below their classification and if the degradation is necessary under federal standards and circumstances clearly in the public interest and meets other requirements. Of particular pertinence to this case, the subsection goes on to state, "[p]rojects permitted under Part IV of Chapter 373, F.S., shall be considered in compliance with this subsection if those projects comply with the requirements of subsection 373.414(1), F.S." Those requirements, of course, include the statement with regard to "net improvement in water quality" in Section 373.414(1)(b)3. In Florida Administrative Code Rule 62-330.100, DEP has adopted by reference certain ERP rules of SFWMD for its use in conjunction with its existing rules when regulating surface water management systems, including activities on, in, or over wetlands or other surface waters under Part IV of Chapter 373. The Basis of Review for Environmental Resource Permit Applications within the South Florida Water Management District August 1995 ("BOR") is also contained in the notebook of "ALJ's Copy of Statutes and Rules" produced at hearing as applicable law. Among the BOR's Environmental Criteria to be "implemented in a manner which achieves . . . a project permitting goal, of no net loss in . . . surface water functions" (Section 4.0, BOR) is Section 4.2.1. It requires the exploration of design modification to reduce or eliminate adverse impacts to surface water functions. The evidence establishes that the proposed surface water management system will enhance surface water functions by providing a net improvement of the water quality of marina's receiving waters. Section 4.2.2 of the BOR requires that the applicant "provide reasonable assurances that the regulated activity will not impact the values of wetland and other surface water functions so as to cause adverse impacts to: (a) the abundance and diversity of fish, wildlife and listed species; and (b) the habitat of fish, wildlife and listed species." The Boat Club has failed to provide assurances that the upgrade to the marina will not cause adverse impacts to manatees and their habitat. The opinions of the experts presented by the Boat Club that there will be no adverse impacts are based on the faulty assumption that the upgrade will not add more boats into the Caloosahatchee River system. The boating restrictions imposed by the federal, state and local governments, moreover, have not been shown in this proceeding to mitigate adverse impacts to the manatee and its habitat that will be produced by the introduction of additional boats, power and otherwise, into the River system. The Public Interest Test Deep Lagoon has been found in previous recommended orders and DEP final orders not to be among Florida's Outstanding Waters, even though it is an arm of the Caloosahatchee River and the River is so listed. The parties do not contend otherwise. They have structured their arguments along the line that the proposed permit must be shown to be "not contrary to the public interest." Section 373.414(1). Of the seven criteria of Section 373.414(1), which must be considered and balanced in determining whether the project is contrary to the public interest, it has been shown that there is no adverse impact with regard to criteria 1., 3., 4., and 6. In fact, for example, as the Boat Club points out with regard to criterion 1., "[e]xcept for mosquito control, the testimony and evidence demonstrated that this proposed project will have a positive impact on each and every one of [the] concerns" (Respondent, Deep Lagoon Boat Club Ltd.'s Proposed Recommended Order, p. 53) listed in Section 4.2.3.1 of the BOR for assessment of hazard to public health, safety with respect environmental issues. This leaves criteria 2., 5., and 7. Implementation of the proposed surface water management system will have a positive affect on the conservation of fish and wildlife but the upgrade otherwise will not. The project is of a permanent nature, a matter the Boat Club concedes. (Respondent Deep Lagoon Boat Club Ltd.'s Proposed Recommended Order, p. 55). The surface water management system will improve water quality in the area. The remainder of the upgrade will diminish the value to manatees and of the manatee habitat of the areas affected. Reasonable Assurances Section 4.2.4 of the BOR requires that an applicant provide "reasonable assurance that the regulated activity will not violate water quality standards in areas where water quality standards apply." Water quality standards will not be violated as a result of the proposed project. Reasonable assurances have been provided both in the short term with best management practices during construction, and in the long term with the Marina Management Plan governing the operation of the marina for the life of the facility. The Boat Club offered reasonable assurance that future water quality will be in compliance by detailed maintenance and reporting procedures for the surface water management system and the closed loop systems, and monitoring of water quality and sediments. Sections 4.2.4.2 and 4.2.4.3 of the BOR require long term water quality considerations. Reasonable assurances were offered that the project will not cause water quality violations. Flushing has been improved by making the canals more shallow, and will be further improved by the culverts that will connect the north and main canals. The fueling facilities are conditioned upon a detailed operations and procedures commitment in the area of spill response, minimizing the effects of any spills, as required by Section 4.2.4.3(f). The marina will have publicly available pump-out facilities for boat heads at a nominal cost to minimize improper disposal, as required by Section 4.2.4.3(g), and will not have live-aboards. The disposal of solid waste, such as garbage and fish cleaning debris, has been addressed to prevent disposal into wetlands or other surface waters, as required by Section 4.2.4.3(h). The pollutant leaching characteristics of pilings has been addressed as required by Section 4.2.4.3(i), by the replacement of the existing, treated wood docks with PVC and concrete structures. Anti-fouling paints on hulls have been addressed by requiring all wash-downs to take place in the closed loop contained areas that overflow in storms to the sewer system. Additionally, any boat scrapings are contained and disposed of by a contaminant disposal contractor, and the marina uses only low-copper bottom paints. The permit conditions, as well as the plans, address the short-term water quality impacts of the proposed system, as required by Section 4.2.4.1 of the BOR. The project plans attached to the permit include provisions for erosion and siltation barriers, and similar devices during construction. The permit conditions also require temporary erosion control barriers to remain in place and be inspected daily during all phases of construction until soils stabilize and vegetation has been established. All practices are required to be in accordance with the guidance and specifications described in Chapter Six of the Florida Land Development Manual: A Guide to Sound Land and Water Management (Department of Environmental Regulation 1988), unless a project-specific erosion and sediment control plan is approved as part of the permit. Additionally, all access for construction activities, including placement of floating docks into the water, must occur via the existing boat ramps, travel lift and fork lift areas of the marina. At no time are mangroves affected unless specifically authorized by the permit to be altered or trimmed to accommodate construction or access operations. From a hydrographic standpoint, the project is approvable. Section 4.2.4.5 of the BOR, entitled "Where Ambient Water Quality does not Meet State Water Quality Standards," provides in part: If the site of the proposed activity currently does not meet state water quality standards, the applicant must demonstrate compliance with the water quality standards by meeting the provisions in 4.2.4.1, 4.2.4.2, and 4.2.4.3, as applicable, and for the parameters which do not meet water quality standards, the applicant must demonstrate that the proposed activity will not contribute to the existing violation. The proposed project will result in a net improvement of the water quality standards, and will not contribute to any exceedances where exceedances exist. Section 4.2.7 of the BOR requires that an applicant provide reasonable assurances that a regulated activity will not cause adverse secondary impacts to the water resource as described in paragraphs (a) through (d) of the section. The section stresses the import of protection of endangered species such as the manatee: Aquatic or wetland dependent fish and wildlife are an integral part of the water resources which the District is authorized to protect under Part IV, Chapter 373, F.S. Those aquatic or wetland dependent species which are listed as threatened, endangered or of special concern are particularly in need of protection. As discussed elsewhere, the applicant has failed to provide reasonable assurances that the proposed project will not cause adverse impacts to the manatee. Florida Administrative Code Rule 18-21.004(1)(a) provides that "all activities on sovereignty lands must not be contrary to the public interest except for sales which must be in the public interest." "Public interest means 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. In determining the public interest in a request for . . . lease . . . in sovereignty lands . . ., the board shall consider the ultimate project and purpose to be served by said . . . lease . . . ." Fla. Admin. Code R. 18-2.003(40). While conditioned upon the construction of the surface water management system that will provide a net improvement in water quality to a water body that does not meet water quality standards, implementation of the Marina Management Plan, and execution of a DEP-approved lease agreement, the proposed activity has not been shown to be not contrary to the public interest because of adverse secondary impacts to manatees.
Recommendation Based on the foregoing Findings of Fact and Conclusions of Law, it is RECOMMENDED that a final order be entered by the Department of Environmental Regulation that the application by the Deep Lagoon Club Ltd. for a Consolidated Environmental Resource Permit and Sovereign Submerged Lands Authorization be denied. DONE AND ENTERED this 17th day of October, 2003, in Tallahassee, Leon County, Florida. S DAVID M. MALONEY Administrative Law Judge Division of Administrative Hearings The DeSoto Building 1230 Apalachee Parkway Tallahassee, Florida 32399-3060 (850) 488-9675 SUNCOM 278-9675 Fax Filing (850) 921-6847 www.doah.state.fl.us Filed with the Clerk of the Division of Administrative Hearings this 17th day of October, 2003. COPIES FURNISHED: Thomas W. Reese, Esquire 2951 61st Avenue South St. Petersburg, Florida 33712-4539 Francine M. Ffolkes, Esquire Department of Environmental Protection 3900 Commonwealth Boulevard Mail Station 35 Tallahassee, Florida 32399-3000 Mark A. Ebelini, Esquire Knott, Consoer, Ebelini, Hart & Swett, P.A. 1625 Hendry Street Post Office Box 2449 Fort Myers, Florida 33902-2449 Kathy C. Carter, Agency Clerk Office of the General Counsel Department of Environmental Protection 3900 Commonwealth Boulevard Mail Station 35 Tallahassee, Florida 32399-3000 Teri L. Donaldson, General Counsel Department of Environmental Protection 3900 Commonwealth Boulevard Mail Station 35 Tallahassee, Florida 32399-3000
Findings Of Fact Respondent is permitted by Petitioner to treat sick and injured wildlife under a wildlife rehabilitation permit, the latest and current permit being issued to Respondent on January 21, 1983. Respondent has been engaged in the business of treating sick and injured wildlife -- including both birds and mammals -- under permit from Petitioner for at least three (3) years. Petitioner issues wildlife rehabilitation permits to those persons demonstrating to Petitioner the degree of expertise in treating sick and injured wildlife necessary to assure safety to the treated animals. In addition, Petitioner monitors wildlife rehabilitation permittees to assure that sick and injured wildlife are treated humanely and caged in a safe and sanitary manner so as to protect the health and safety of the wildlife treated and the public. In order to monitor such permittees, periodic inspections of the premises where sick and injured wildlife is treated are made by Petitioner. In addition, Petitioner required such permittees to maintain records and to submit the same to Petitioner upon Petitioner's request. Wildlife rehabilitators are notified of this requirement through an informational packet provided them by Petitioner, which specifies that permittees must keep records of specimens cared for and submit reports of same to Petitioner upon request. The requirement that records be maintained and reported to the Petitioner upon request is applied to all of the one hundred (100) wildlife rehabilitators permitted by Petitioner. Examination of records is routinely requested by Petitioner when inspecting the premises where sick and injured wildlife is kept. On at least two occasions, Petitioner requested the production of records maintained by Respondent in connection with Petitioner's inspection of Respondent's wildlife rehabilitation facilities. On neither occasion did Respondent produce records for Petitioner's inspection. On February 3, 1983, Petitioner notified Respondent by letter that Respondent should submit a report of the numbers and types of wildlife accepted for rehabilitation and the disposition of said wildlife. The letter directed Respondent to submit his report immediately and to maintain records for examination by Petitioner in conjunction with future inspections. No report was submitted to Petitioner by the Respondent. On September 8, 1983, in response to a citizen complaint, Petitioner initiated an investigation of the wildlife rehabilitation operation of Respondent. In conjunction with its investigation of Respondent, Petitioner requested of Respondent the production of the wildlife rehabilitation records on September 22, 1983. Respondent did not produce the records as requested. Petitioner again requested Respondent to produce the records on September 23, 1983, and again Respondent failed to produce the records for Petitioner. Respondent did provide, on two separate occasions, documents to the U.S. Fish and Wildlife Service, a federal agency. The documents submitted to the U.S. Fish and Wildlife Service purported to reflect numbers of birds treated by Respondent during 1982. The documents failed to reflect the type of treatment, the specific disposition of said birds, any reference to mammals, or any recording of numbers or types of mammals. The two separate documents submitted are in irreconcilable conflict as to numbers and types of birds treated. In addition, the documents contain no reference to certain birds delivered by Petitioner to respondent's wildlife rehabilitation facility during 1982. Said documents were never submitted by Respondent to Petitioner. On no occasion has Respondent produced any records or reports for 1982 to Petitioner in connection with Respondent's wildlife rehabilitation. On November 1, 1983, Respondent was informed by letter dated October 27, 1983, that Petitioner intended to revoke Respondent's wildlife rehabilitation permit due to Respondent's failure to comply with the record keeping and reporting requirements of the wildlife rehabilitation permit.
Recommendation Based on the foregoing findings of fact and conclusions of law, it is RECOMMENDED: That the Petitioner Game and Fresh Water Fish Commission enter a final order revoking the wildlife permit of the Respondent Jack Kassewitz, Jr. DONE and ORDERED THIS 15th day of May, 1984, in Tallahassee, Florida. SHARYN L. SMITH Hearing Officer Division of Administrative Hearings The Oakland Building 2009 Apalachee Parkway Tallahassee, Florida 32301 (904) 488-9675 Filed with the Clerk of the Division of Administrative Hearings this 15th day of May, 1984.
The Issue The issue for resolution in this proceeding is whether the Department of Environmental Regulation (DER) should approve Petitioner's construction of a dock on Lake Kissimmee in Polk County, Florida. Such approval would require the grant of an after-the-fact permit.
Findings Of Fact Earl W. Thomas, the Petitioner, owns approximately 15.5 acres on the western shore of Lake Kissimmee near Lake Wales, in Polk County, Florida. On March 15, 1984, Petitioner filed an application with the Department of Environmental Regulation (DER) to construct a 3,160 square foot dock at his property on Lake Kissimmee. The dock is described in drawings attached to the application as 550 feet long with a 60 foot "T" segment at the end. The application form is styled, "Joint Application, Department of the Army/Florida Department of Environmental Regulation for Activities in Waters of the State of Florida". The activity described in the application is "proposed pier for mooring private boat -- no fuel pumps or toilet facilities to be constructed on pier". (Petitioner's exhibit #5) Thomas received a letter dated March 28, 1984 from the Army Corps of Engineers acknowledging the application and granting General Permit SAJ-20. The letter authorized construction but provided that it did not obviate the need for any other required federal, state or local permits. A form letter from the Florida Department of Natural Resources (DNR) dated April 26, 1984, informed Thomas that a letter of consent from the Board of Trustees of the Internal Improvement Trust Fund would be required. A form letter from DER dated May 10, 1984 acknowledged receipt of the application and stated that evaluation of the project would be delayed until receipt of DNR consent. The DNR letter of consent was issued on June 28, 1984, signed by Ted Forsgren, Chief, Bureau of State Lands Management, and referencing the use of approximately 2,366 square feet of state-owned submerged land for a private docking facility. The letter states, "Please consider this the authority sought under Section 253.77, Florida Statutes, to pursue this project." (Petitioner's exhibit #9) Thomas commenced construction, and the dock was completed by July 28, 1984. As completed, the dock is approximately 480 feet long, with a 24 foot "T" cross at the end. During construction, in a letter dated July 24, 1984, to the DER Tampa office, Ed Moyer, then Fishery Biologist with the Florida Game and Fresh Water Fish Commission stated, "Our office is opposed to the issuance of a permit to construct a 600' [sic] dock on the west shore of Lake Kissimmee. " (Respondent's exhibit #2) Basis for the opposition was that the structure would obstruct boat traffic along a navigable path parallel to Mr. Thomas' shoreline. In a letter dated September 17, 1984, signed by James W. MacFarland, Director, Division of State Lands, DNR informed Thomas that it was rescinding its prior consent due to receipt of additional information from DER and conversations with the Game and Fresh Water Fish Commission. The letter also states "...It appears that the information represented to us did not actually represent your proposed activity or address the severe navigational problems caused by your construction of a facility approximately 600 feet [sic] in length. ..." (Petitioner's exhibit #10) On September 18, 1984, DER issued its Intent to Deny Thomas' application. This document provides, in pertinent part: * * * On October 14, 1984 [sic] Bill Ackerman, Field Inspector for Polk County, inspected the proposed pier site and the adjacent lake. Approximately 200' waterward from the west shore of the lake is a 20' wide approximately 4' deep navigation channel which is used by area boaters during sudden winds from the east as a safe haven path which protects them from the chop of the open lake. Based on his personal experiences and site inspection on this lake and the opinion and the recommenda- tion of the Florida Game and Fresh Water Fish Commission, the agency has come to the conclu- sion that the proposed dock will both obstruct and hinder navigation in this natural lake channel, contrary to the provision of Chapter 253.123, F.S. In addition, the proposed dock's obstruction of the existing channel will cause boaters to prop dredge a new access channel around the dock, causing substantial wetland losses, resuspension of nutrient laden bottom sedi- ments and turbidity. * * * [Petitioner's exhibit #11] In response to this notice, Petitioner requested a formal hearing. Nothing in the record of this proceeding explains the inconsistency in the dates in the notice of intent to deny. The notice itself was issued on September 18, 1984 and the October 14, 1984, reference is clearly in error. The permit file of the DER includes a form dated 6/11/84, styled "Permit Application Appraisal", referencing an on-site inspection by Bill Ackerman on 10/14/82. [Respondent's exhibit #3] This form appraisal describes the project as a 600' long private dock, with a 48 square foot "T" at the end, and 2400 square feet of over-water surface area. The appraisal references a fence that Thomas built allegedly on state submerged lands in the lake, and a dispute with DNR over that fence. The appraisal also describes a boat path about 200' from shore and parallel to the shore within the grassy weeds, providing a safe passage for small boats caught in the lake in sudden storms or high waves. The appraisal recommends denial of the permit for navigation reasons, but recommends that the permit could be approved if the fence were removed and the length of the dock were reduced. The inspector and apparent author of the appraisal report, Bill Ackerman, died several years ago. No witness could explain the source of the various references to a 600' dock, since the application was for a 550' long dock, including the width of the "T" cross, and the dock that was built was 480' long. The appraisal report is the only evidence from DER's file of that agency's review of the project, and it is evident that the site visit was conducted approximately 1 1/2 years prior to the application in issue, perhaps related to the fence, which is not at issue in this proceeding. However, Edwin Moyer, the Florida Game and Fresh Water Fish Commission staff person who wrote the July 1984 opposition letter, testified and confirmed that the boat trail described in the appraisal did exist in 1984. This trail, called a "kicker trail", was not a dredged path, but rather was created like many others by the operation of boat propellors through the weeds and grasses along the shore of the lake. If unused, these trails disappear, and new ones are created. At the Thomas site, Lake Kissimmee is approximately 5 miles wide. Small boats need the trails as the vegetation protects them from high waves. Thomas' dock intersected the kicker trail described in the DER appraisal report and by Edwin Moyer. New trails, however, now exist beyond the end of Thomas' dock and still within the dense vegetation which extends some 360 feet waterward from the end of the dock. An "outside" trail runs parallel to the shoreline, approximately 350 feet beyond the dock, and is used by small to medium motorboats. An "inside" trail is located about 60 feet beyond the end of the dock and is used exclusively by airboaters, who can run in just inches of water and who experience severe handling problems in deep water or heavy waves. Airboats don't require trails, as they can travel on top of the vegetation. Regular motorboats, such as bass boats and jon-boats, require more water. The water depth at the end of Thomas' dock fluctuates from about one to five feet deep; not including the approximate 1.5 feet of muck on top of the sand at the lake bottom at the Thomas site. The water elevation in Lake Kissimmee is controlled by the South Florida Water Management District, with a regulated high of 52.5 ft. NGVD to a regulated low of 49.0 ft. NGVD, with an even lower 48.5 ft. NGVD every three years. At the time of hearing, the water level was 50.3 ft. NGVD, or approximately 2.4 ft. deep at the end of Thomas' dock, not including the depth of the muck. Even if the Thomas dock did not exist, regular motor boats would have trouble navigating closer to shore, due to the shallowness of the water. Moreover, there are stumps and posts closer to shore, which present a greater danger to boaters, including seasoned airboaters, than Thomas' dock which is fully visible and which includes a light at the end which remains lit, with reflectors along the edges. Airboats running close to the shore have to veer out into deeper water as they approach the Thomas site, to avoid the dock. This is a nuisance, according to Garrett Whatley, an airboat operator who races on Saturday evenings. But the greater nuisance, as he concedes, are the posts and steel pipes in the water near the shore which are not marked and which can crack up a boat. In bypassing the dock, these obstructions are also avoided. Some Lake Kissimmee boaters consider Thomas' dock a navigational aid. The west side of the lake is not developed and the dock provides a prominent landmark, particularly for snail fishermen and other night boaters. The Gleasons and the Gilberts are neighbors of Earl Thomas. They each have 200 ft. docks which have been permitted by DER. The Gleasons have a 24 ft. pontoon boat which they moor at the end of a 70 ft. catwalk extending from the end of their dock. Even then, the water is only about 12 inches deep and they have to pole the boat out to avoid plowing into the muck on the lake bottom. The vegetation line at Thomas' site is thicker and farther out than at the Gleason's. George Gilbert also has a pontoon boat which he has to pole to access his dock. He has a kicker trail at the end of his dock, but the water is too shallow to use it. DER has granted him a permit to extend his dock another 100 feet. DER considers 300 feet a reasonable length for docks in the area and the agency tries to keep them a uniform length for navigational purposes. Removal of all or a portion of Thomas' dock can be accomplished without water quality damage so long as the removal is closely controlled. The pilings would have to be enclosed with a screen to limit turbidity during the removal process. Even if the act of removal could be controlled, the turbidity caused by boats interacting with the sediment closer to shore would be a recurring problem without the dock as it now exists. A shorter dock would necessitate the use of catwalks or other temporary access to boats unable to navigate the shallow water. Those boats moored away from the dock would still be an obstruction, and if unlit, would be less visible to night fishermen than the existing structure. The Thomas dock, as it now exists, is not a navigational hazard. Its removal would be more damaging than to permit it to remain.
Recommendation Based on the foregoing, it is hereby recommended that the Department issue its final order granting Petitioner's application for the dock as it now exists. That is, the application for a 550 foot dock should be deemed amended to provide for a 480 foot dock, as built. RECOMMENDED this 7th day of January, 1991, in Tallahassee, Leon County, Florida. MARY CLARK Hearing Officer Division of Administrative Hearings The DeSoto Building 1230 Apalachee Parkway Tallahassee, Florida 32399-1550 (904)488-9675 Filed with the Clerk of the Division of Administrative Hearings this 7th day of January, 1991. APPENDIX TO RECOMMENDED ORDER, CASE NO. 84-4164 The following constitute specific rulings on findings of fact proposed by the parties. Findings of Fact Proposed by Petitioner Adopted in paragraph 2. Adopted in paragraph 5. Adopted in paragraph 6. Adopted in paragraph 7. Adopted in paragraph 9. Adopted in paragraph 10. Adopted in paragraph 11. Addressed in Preliminary Statement. Adopted in paragraph 7. 10.-14. Adopted in paragraph 17. 15.-18. Adopted in substance in paragraphs 16 and 20. Findings of Fact Proposed by Respondent Adopted in paragraph 2, except that the dock was to be 550 feet long. Adopted in paragraph 7. Adopted in paragraph 5. Adopted in paragraph 10. Adopted in substance in paragraphs 16 and 20. 6.-9. Adopted in summary in paragraph 17. Adopted in paragraph 12. Adopted in paragraph 15. Adopted in paragraph 16, by implication. Adopted in paragraph 18. 14. Rejected as unnecessary. 15.-16. Adopted in substance in paragraph 20. 17. Rejected as unnecessary. 18. Adopted in paragraph 16. 19. Adopted in paragraph 18. 20. Rejected as unnecessary. 21. Adopted in paragraph 22. COPIES FURNISHED: Carlyn Harper, Esquire P.O. Box 2807 Orlando, FL 32802 Douglas H. MacLaughlin Asst. General Counsel DER-Twin Towers Ofc. Bldg. 2600 Blair Stone Rd. Tallahassee, FL 32399-2400 Dale H. Twachtmann, Secretary DER-Twin Towers Ofc. Bldg. 2600 Blair Stone Rd. Tallahassee, FL 32399-2400 Daniel H. Thompson General Counsel DER-Twin Towers Ofc. Bldg. 2600 Blair Stone Rd. Tallahassee, FL 32399-2400
The Issue The issue is whether Petitioner is entitled to additional compensation for fishing nets that he sold to the State of Florida under the Net Buy-Back Program.
Findings Of Fact Petitioner is a commercial fishers who is an affected person under the Florida Net Ban, which is set forth in the Florida Constitution, Article X, Section 16. Section 370.0805(5), Florida Statutes, which became effective on July 1, 1995, establishes the Net Buy-Back Program. The program enables eligible persons previously engaged in the commercial fishing industry to sell fishing nets to the State of Florida. The Legislature appropriated $20 million to the Seafood Workers Economic Assistance Account (the Account) to fund the payments authorized in Section 370.0805, as well as agency expenses in administering the program. Section 370.0805(3)(b) directs Respondent to purchase nets "according to the availability of funds on a first-come, first-served basis determined by the date of receipt of each completed application." By Net Buy-Back Application signed on July 5, 1995, and filed with Respondent on the same day, Petitioner applied to sell nets to the State of Florida. His application form is completely filled out and shows two saltwater-product license numbers, one for an individual and one for a vessel. The application form calls for the applicant to list the "TOTAL NUMBER OF YARDS OF EACH NET TYPE THAT YOU INTEND TO SELL." The form lists five categories of nets: gill (49 meshes or less); gill (50 meshes or more); beach, purse, seine; trawl; and trammel. The former gill net is a shallow-water gill net. The latter gill net is a deepwater gill net. Petitioner listed on his application 800 yards of shallow-water gill nets, 4600 yards of deepwater gill nets, two trawls, and 600 yards of trammel nets. After checking a data base maintained by the Department of Environmental Protection, Respondent found only one of Petitioner's two listed saltwater-product licenses. Respondent thus processed Petitioner's application as though he had only one license. By letter dated August 8, 1995, Respondent advised Petitioner that he was eligible "to receive compensation for 8 nets" and set an appointment for him to turn in the nets on September 6, 1995. On September 6, 1995, Petitioner appeared at the appointed site with nets to sell to the State of Florida. He delivered 4800 yards of seine nets, for which he received a voucher for $27,998.40. Prior to paying the voucher, Respondent discovered that the Account might be exhausted before Respondent had paid for all of the nets that fishers might lawfully seek to sell to the State. Respondent thus dishonored Petitioner's voucher, as well as the vouchers held by numerous other fishers, while Respondent considered changes in its administration of the program. The purpose of the Net Buy-Back Program, as provided by Section 370.0805(5)(a), Florida Statutes, was to allow, "[a]ll commercial saltwater products licensees and persons holding a resident commercial fishing license" to apply to Respondent "to receive economic assistance to compensate them for nets rendered illegal or useless by the constitutional limitation on marine net fishing." The emphasis was on economic assistance. Section 370.0805(5)(a) authorizes Respondent to make payments only "in nonnegotiable amounts not intended to reflect the actual value of the nets." Section 370.0805(5)(a) assigns payment amounts of $3500 for beach, purse, or seine nets of at least 600 yards in length; $500 for trawls and shallow-water gill nets of at least 600 yards in length; and $1000 for trammel nets of at least 600 yards in length and deepwater gill nets of at least 600 yards in length. Section 370.0805(5)(a) states that, except for trawls, nets of less than 600 yards in length shall be "valued proportionately." Section 370.0805(5)(c) limits the number of nets that a commercial fishers could sell, based on his annual earnings from the sale of eligible saltwater products. The limits range from four nets, for licensees whose annual earnings average from $2500 to $4999 in earnings, to ten nets, for licensees whose annual earnings average more than $30,000. Respondent relied on another data base from the Department of Environmental Protection to determine the average yearly earnings of applicants. The Department of Environmental Protection maintains records of each licensee's trip tickets, which disclose earnings. The only other limit in the statute as to the type and number of nets to be purchased is that, under Section 370.0805(5)(d), "[n]o licensee may be paid for more than two. . . trawls." Respondent reviewed the applications that it received from the initial 951 fishers who filed applications. This was a large majority of the 1104 fishers who would eventually sell their nets to the State under the Net Buy-Back Program. The purpose of the review was to determine whether the funds in the Account would be sufficient to cover the nets that the State was to be purchasing. Respondent found from the applications that seine nets represented only about five percent of the nets that fishers intended to sell to the State. Relying on this information, Respondent calculated the potential encumbrance of $6.5 million on the Account, based on an average payment of $1000 per net. Applications contained few seine nets because commercial fishers initially resisted selling their best nets to the State of Florida. The Net Buy-Back Program provided for payment of only $3500 per seine net, even though many seine nets were worth $10,000. And commercial fishers were optimistic at first that their legal challenges to the constitutional amendment would succeed. Applying liberal eligibility criteria, such as calculating the number of nets that each applicant could sell based on the number of licenses that he held, Respondent raised its estimate of the potential encumbrance to $8.775 million. But in recalculating the potential encumbrance on the Account, Respondent still assumed that the average payment per net would be $1000. Respondent began receiving nets on August 3, 1995. Through the first three weeks of August, Respondent purchased seine nets in roughly the same five-percent mix that it had used in calculating the potential encumbrances on the Account. After this point, however, fishers started turning in much larger numbers of seine nets than they had listed in their applications. During this first phase of the program, Respondent paid fishers for whatever types of nets they presented at their net buy-back appointment. Respondent would pay a fishers entitled to sell eight nets for seine nets if he turned in seine nets, even though he had listed only gill nets on his application. This policy jeopardized the solvency of the Account because the payments to fishers turning in all seine nets were 3.5 times greater than the figures that Respondent had used in calculating the potential encumbrance on the Account. From the fishers's perspective, the program acquired an element of chance, as applicants with earlier appointment times-which did not necessarily correspond with earlier-filed applications-netted fine catches of economic assistance at the expense of their counterparts, upon whom destiny had bestowed later appointment times. By late August, the applicants, less sanguine about their litigation prospects (as the fishers suggest) and more inventive in recasting old gill nets as seine nets (as Respondent suggests), began turning in seine nets in large numbers, so that Respondent was purchasing nearly all seine nets. Eventually, the cumulative effect of this trend raised the total mix of seines purchased from five percent, during the first three weeks, to sixty percent. After a brief period of trying to stay the course, Respondent decided on September 6, 1995, that it had to take action or else the Account would be exhausted before the State had purchased all of the nets listed on the applications. Respondent immediately suspended further payments on issued vouchers and applied new criteria to persons holding unpaid vouchers, as well as to applicants who had not yet received vouchers. This action stopped payment on all vouchers issued from around August 28 through September 6. At the time that it stopped payment on outstanding vouchers, Respondent had approved the purchase of nets from about 750 fishers. About 450 of these applicants received their money prior to the suspension of payments, leaving about 300 applicants, including Petitioner, holding worthless vouchers. However, a large number of the 450 applicants who were actually paid for their nets prior to September 6 sold a relatively large percentage of gill nets rather than seine nets. As of September 6 (retroactive to August 28), Respondent began the second phase of the Net Buy-Back Program. In this phase, Respondent paid for seine nets, but only up to the greater of the number of seines shown on the application or the number of seines based on past use of seines. Respondent determined the latter figure from the trip tickets, which also contained information as to types of catch, from which Respondent could infer the type of net used. As in the first phase, Respondent continued to insist the fishers turn in seines if they were being paid for seines. The 300 fishers holding dishonored vouchers filed a class action suit. Petitioner's voucher for his first eight nets was covered in this legal action and is not the subject of this case. Petitioner received slightly more than $10,000 on his claim for about $28,000. In the meantime, Respondent discovered that Petitioner in fact held two licenses, as he had represented on his application. By letter dated October 5, 1995, Respondent advised Petitioner that it had reconsidered his application and determined that he had the right to sell 16 nets, not eight nets, but none could be a seine net. Respondent issued Petitioner a new voucher for these additional eight nets. This voucher is in the amount of $7996.80 for 4800 yards of deepwater gill net. On October 13, 1995, Petitioner turned in eight nets and received his money. Petitioner's application lists no seine nets. His application, as noted above, lists one and one-third shallow- water gill nets (i.e., 800 yards), eight deepwater gill nets, two trawls, and one trammel net. Petitioner claimed that he turned in seine nets. If turned in during the first or second phase of the program, Respondent would have treated these nets as seine nets. But it is Petitioner's unique fortune to have been intimately involved with all three phases of the Net Buy-Back Program. Evidently dissatisfied with the effects of the restrictions introduced by the second phase of the program, Respondent added a third phase by promulgating an emergency rule defining "seine nets," effective October 2, 1995. This third phase, which did not change Respondent's policy of paying for the greater number of seines as shown on the application or the trip tickets, restricted the kinds of nets that fishers could turn in as seine nets. Rule 38BER95-1 provides that, for the purpose of "the implementation of the Net Buy-Back Program" described in Section 370.0805(5): "Gill net" means a wall of netting suspended vertically in the water, with floats across the upper margin and weights along the bottom margin which captures fish by entangling them in the meshes, usually by the gills. Any net offered for the net buy- back program that consists of at least fifty- one percent (51 percent) gill net, shall be considered a gill net. "Seine" means a small-meshed net suspended vertically in the water, with floats along the top margin and weights along the bottom margin, which encloses and concentrates fish, and does not entangle them in the meshes. No net offered for the net buy-back program shall be considered a seine if the wings are composed of entangling mesh. * * * THIS RULE SHALL TAKE EFFECT IMMEDIATELY UPON BEING FILED WITH THE DEPARTMENT OF STATE. Effective Date: October 2, 1995 Under the emergency rule, Respondent's nets were not seines, but were gill nets because they were at least 51 percent, by area, gill net. At the time of the final hearing, Respondent estimates that the Account balance is about $300,000 with about 160 contested claims remaining to be resolved.
Recommendation It is RECOMMENDED that the Department of Labor and Employment Security enter a final order dismissing the petition for additional payment from the Account. ENTERED on October 3rd, 1996, in Tallahassee, Florida. ROBERT E. MEALE Administrative Law Judge Division of Administrative Hearings The DeSoto Building 1230 Apalachee Parkway Tallahassee, Florida 32399-1550 (904) 488-9675 SUNCOM 278-9675 Fax Filing (904) 921-6847 Filed with the Clerk of the Division of Administrative Hearings this October 3rd, 1996. COPIES FURNISHED: Secretary Douglas L. Jamerson Department of Labor and Employment Security 303 Hartman Building 2012 Capital Circle Southeast Tallahassee, Florida 32399-2152 Edward A. Dion General Counsel Department of Labor and Employment Security 303 Hartman Building 2012 Capital Circle Southeast Tallahassee, Florida 32399-2152 John Wayde Campbell 1103 67th Street Northwest Bradenton, Florida 34209 Louise T. Sadler Senior Attorney Department of Labor and Employment Security 2012 Capital Circle, Southeast Suite 307, Hartman Building Tallahassee, Florida 32399-2189
Findings Of Fact The following are the facts to which the parties have stipulated: Respondent is the holder of a pound net registration issued on November 30, 1983, by Dennis E. Holcomb, Director, Division of Fisheries, for the Executive Director of the Game and Fresh Water Fish Commission (Commission). The registration authorizes the Respondent to operate pound nets for Commercial purposes on certain areas of the St. Johns River, subject to law and Commission rules. On April 30, 1986, Petitioner pled guilty to illegal fishing with pound nets and was adjudged guilty and fined by the County Court of Putnam County, Florida. As a result of this Conviction, Respondent's pound net registration was temporarily revoked for a period of six (6) months dating from June 23, 1986 until December 23, 1986. On October 15, 1986, during the afore-mentioned revocation period, Respondent pled guilty to illegal fishing with unpermitted pound nets, and was adjudged guilty and fined by the County Court of Putnam County, Florida. Based on the Respondent's conviction of illegal fishing with pound nets during the revocation period, the Commission found just cause to permanently revoke Respondent's pound net registration and filed an Administrative Complaint on March 30, 1987 against Respondent to effectuate that revocation. Based on Respondent's unrebutted testimony which I found to be credible, the following relevant facts are found: That in addition to the fine imposed on the Respondent by the County Court of Putnam County, Florida on October 15, 1986, for illegal fishing, the Commission seized and Confiscated two (2) of Respondent's pound nets worth approximately $6,000.00. Respondent, subsequent to October 15, 1986, continues to fish pound nets as the designee of other parties holding pound net registrations, without incident and in compliance with the law and Commission rules. The Respondent is substantially dependent upon pound net fishing for his livelihood and has been prohibited from fishing his pound nets since June 23, 1986. Respondent's pound net registration was not reinstated at the end of the revocation period ending on December 23, 1986.
Recommendation Having considered the foregoing Findings of Fact and Conclusions of Law, the evidence of record and the conduct and demeanor of Use witness, it is, therefore, RECOMMENDED that the Commission enter a Final Order temporarily revoking Respondent's pound net registration for a period of twelve (12) months beginning December 23, 1986. Respectfully submitted and entered this 11th day of August, 1987, in Tallahassee, Florida. WILLIAM R. CAVE Hearing Officer Division of Administrative Hearings The Oakland Building 2009 Apalachee Parkway Tallahassee, Florida 32399-1550 (904) 488-9675 Filed with the Clerk of the Division of Administrative Hearings this 11th day of August, 1987.
Findings Of Fact Petitioner owns a single family residence on a lot (Lot 2) abutting Lake Buffum in Polk County, Florida. This property has a 60 foot frontage on the lake. Petitioner subsequently purchased and now owns an adjacent lot (Lot 3) with a lake front frontage of approximately 73 feet. Petitioner has placed a dock on the westerly edge of Lot 2 from which he suspends and lowers a power boat to the surface of Lake Buffum. Lot 3 is westerly of Lot 2. Lake Buffum is a class III water body which classification provides for management for recreation; and propagation and maintenance of a healthy, well- balanced population of fish and wildlife. Petitioner was cited for violation of Section 369.20, Florida Statutes, by spraying herbicide on aquatic plants without a permit. He subsequently applied for a permit to control aquatic plants in front of his property and was issued a permit allowing him to control an access corridor to his property 50 feet wide. Petitioner here seeks an access corridor 60 feet wide. When Petitioner was issued his permit, the plat showing his dock in the center of the 50 foot access corridor was attached. Petitioner desired to clear aquatic plants on the western side of his dock as there is deeper water on that side of the dock to permit access to the dock with his boat. This is due to the angle of the shore line. The plat showing the dock in the middle of the 50 foot corridor obviously caused some confusion on the part of the Petitioner as the approach to his hoist on the dock is parallel to the shoreline. Accordingly, clear water to approach the dock from the west is what Petitioner needs to dock his boat. The permit granted is for a 50 foot corridor without specifying where at right angles to the coast line the corridor should be placed. Accordingly, if desired, Petitioner could clear a corridor starting at the western side of his dock and extending 50 feet to the west. In coordination with the Florida Game, Freshwater Fish and Wildlife Service, the Respondent has adopted a general policy of granting a permit to clear aquatic plants on waterfront property with a corridor of one-half width of the lot fronting the lake but limited to 50 feet for lots of 100 feet width and greater. Since Petitioner has approximately 133 feet of shoreline, he was granted a permit to control aquatic plants in a 50 foot corridor. This general policy is not absolute, but varies with the quantity of aquatic plants on a particular lake and whether the permit is desired for the use of the general public, such as a public boat ramp provided by a county or municipality. The amount of aquatic plants most beneficial to the propagation of fish and wildlife on lakes is between 40% and 70% coverage of the lakes. On the lakes with more than 70% coverage, Respondent may grant a 100 foot corridor in which the upland property owner is issued a permit to control aquatic plants. Lake Buffum is a sparsely vegetated lake with a coverage varying between 1.8% and 4%. Although the property around the lake is sparsely developed, an extra 10 feet of aquatic plant control would have some adverse effect in this lake which is far below the average coverage. More importantly, however, is the cumulative impact of granting Petitioner a 60 foot corridor which would require the granting of similar corridors to all other applicants on Lake Buffum.
Recommendation Based on the foregoing Findings of Fact and Conclusions of Law, it is RECOMMENDED that Dan L. Moody's petition to be granted a permit to clear a 60 foot corridor of aquatic plants below the high water line at his property on Lake Buffum be denied. DONE AND ENTERED this 12th day of March, 1993, in Tallahassee, Leon County, Florida. K. N. AYERS Hearing Officer Division of Administrative Hearings The DeSoto Building 1230 Apalachee Parkway Tallahassee, Florida 32399-1550 (904) 488-9675 Filed with the Clerk of the Division of Administrative Hearings this 12th day of March, 1993. COPIES FURNISHED: Dan D. Moody, Esquire 945 East Broadway Fort Meade, Florida 33841 Nancy L. Harvey, Esquire Nona Schaffner, Esquire 3900 Commonwealth Boulevard MS #35 Tallahassee, Florida 32399-3000 Donald Duden, Acting Executive Director Department of Natural Resources 3900 Commonwealth Boulevard MS #10 Tallahassee, Florida 32399-3000 Kenneth Plante, General Counsel Department of Natural Resources 3900 Commonwealth Boulevard MS #10 Tallahassee, Florida 32399-3000
The Issue Whether the amendments respondent proposes to Rules 46- 22.001, 46-22.002 and 46-22.003, Florida Administrative Code, and the new rules it proposes, 46- through 46-22.007, or any of them, constitute an invalid exercise of delegated legislative authority, within the meaning of Section 120.54(4), Florida Statutes, (1985)?
Findings Of Fact Comprised largely of commercial fishermen, the petitioners are organizations which represent commercial fishing interests, including not only commercial fishermen, but also fish houses, fish processors, and at least one restaurateur. The parties have stipulated that petitioners have standing to bring this rule challenge. The intervenor, Florida Conservation Association (FCA), is an organization to which recreational fishermen and "a number of people ... involved in the sports fishing industry" (T VIII. 7), including fishing guides, marina owners, bait and tackle dealers, tackle manufacturers, and "motels that ... cater to a fishing clientele," (T.VIII. 8) belong. According to the intervenor's executive director, "one of the primary goals of the organization ... has been to work towards gamefish status for redfish, which would be basically what we have been trying to do with the rule, for game fish status." (T.VIII 6.) Respondent Marine Fisheries Commission (MFC) is charged by statute with regulating fishing in the salt waters of the state, which extend nine nautical miles from shore. (T.I.29) The rules and rule amendments the MFC has proposed for redfish were published on July 11, 1986, in Volume 12, No. 28 of the Florida Administrative Weekly on pages 2595, 2596 and 2597. They read, as follows: * 46-22.001 Purpose, Intent and Repeal of Other Laws. The purpose and intent of this chapter are to protect, manage, conserve and replenish Florida's depleted red drum (redfish) resource, species <<Sciaenops ocellata,>> which has suffered extreme declines in abundance in recent years and which is now overfished throughout the state. This chapter will <<implement measures designed to reduce fishing pressure on this species; including>> [[initially impose]] minimum and maximum size limits, <<bag limits, closed season, and prohibition of sale,>> for [[harvestable]] redfish <<harvested from state waters,>> [[to provide interim protection for the resource while a comprehensive management scheme is being formulated for later promulgation in this chapter.]] Accordingly, it is the intent of this chapter to repeal and replace those portions of section 370.11(2)(a)4., Florida Statutes dealing with redfish. This chapter is not intended, and shall not be construed, to repeal any other portion of section 370.11(2)(a)4., Florida Statutes; any other subdivision of section 370.11, Florida Statutes; or any other general or local law directly or indirectly relating to or providing protection for the redfish resource. * * * 46-22.002 Definitions "Harvest" means the catching or taking of a fish by any means whatsoever, followed by a reduction of such fish to possession. <<"Harvest" also includes the intentional killing of a fish, whether or not it is subsequently reduced to possession.>> Fish that are caught but immediately returned to the water free, alive and unharmed are not harvested. In addition, temporary possession of a fish for the purpose of measuring it to determine compliance with the minimum or maximum size requirements of this chapter shall not constitute harvesting such fish, provided that it is measured immediately after taking, and immediately returned to the water free, alive and unharmed if undersize or oversize. <<"Land," when used in connection with the harvest of a fish, means the physical act of bringing the harvested fish ashore.>> (3)(2) "Person" means any natural person, firm, entity or corporation. (4)(3) "Red drum" or "redfish" means any fish of the species <<Sciaenops Ocellata,>> or any part thereof. <<"Native redfish" means any redfish harvested from the territorial waters of the State of Florida.>> (5)(4) "Total length" means the length of a fish as measured from the tip of the snout to the tip of the tail. (6) <<"Vessel" means and includes every description of water craft used or capable of being used as a means of transportation on water, including nondisplacement craft and any aircraft designed to maneuver on water.>> 46-22.003 Size Limits. No person shall harvest in or from the [[following designated]] waters of the State of Florida at any time, or unnecessarily destroy, any redfish of total length less than <<18 inches.>> [[that set forth as follows:]] [[(a) In the Northwest region as hereinafter defined, redfish of total length less than 16 inches. In the remainder of the state, redfish of total length less than 18 inches.]] [[For purposes of this subsection, the tern "Northwest region" shall mean and include all state waters along the Gulf of Mexico north and west of a straight line drawn from Bowlegs Point in Dixie County, southwesterly through marker 16, and continuing to the outer limit of state waters.]] [[No person shall harvest in or from the waters of the state of Florida at any time, or unnecessarily destroy, any redfish of total length greater than 32 inches, except that one (1) redfish larger than this maximum size limit may be harvested per person per day. No person shall possess at any time more than one redfish larger than 32 inches in total length, harvested from state waters.]] <<(2)(a) No person shall harvest in or from the waters of the State of Florida at any time, or unnecessarily destroy, more than one (1) redfish per day of total length greater than 32 inches.>> (b) <<No person shall possess more than one (1) redfish of total length greater than 32 inches, harvested from waters of the State of Florida.>> [[(3) It is unlawful for any person to possess, transport, buy, sell, exchange or attempt to buy, sell or exchange any redfish harvested in violation of this chapter.]] * * * <<46-22.004 Prohibition on Sale and Commercial Harvest of Native Redfish. It is unlawful for any person to: Buy, sell exchange or attempt to buy, sell or exchange any native redfish. Harvest, possess or transport, for purposes of sale or with intent to sell, any native redfish. The prohibitions contained in subsection (1) of this section do not apply to non-native redfish that have entered the State of Florida in interstate commerce. However, the burden shall be upon the person possessing such redfish for sale or exchange to show, by appropriate receipt(s), bill(s) of sale, or bill(s) of lading, that such redfish originated from a point outside the waters of the State of Florida, and entered the state in interstate commerce. It is unlawful for any wholesale or retail seafood dealer or restaurant to possess, buy, sell, or store any native redfish, or permit any native redfish to be possessed, bought, sold or stored on, in, or about the premises or vehicles where such wholesale or retail seafood business or restaurant is carried on or conducted; provided, however, that native red fish which have been lawfully harvested may be kept on the premises of a restaurant for the limited purpose of preparing such red fish for consumption by the person who harvested them, so long as such redfish are packaged or on strings with tags bearing the name and address of the owner clearly written thereon. When any person buys, sells, possesses or transports non-native redfish under circumstances requiring documentation under this section, failure to maintain such documentation, or to promptly produce same at the request of any duly authorized law enforcement or conservation officer, shall constitute a separate offense under this chapter and shall also constitute prima facie evidence that such red fish were harvested from Florida waters and are being transported and/or possessed for purposes of sale.>> <<46-22.005 Season, Bag and Possession Limits. (1) During the months of March and April, the harvest of redfish in or from state waters or possession of native redfish is prohibited. Possession of redfish by any person aboard a vessel fishing in state waters during such months constitutes prima facie evidence that such redfish were harvested out-of-season in state waters. (2)(a) Except as provided in subsection (1), all persons are subject to a bag limit of five (5) native redfish per person, per day, and a possession limit of five (5) native redfish per person. Only one (1) native red fish larger than 32 inches total length may be harvested per person, per day, and no more than one (1) such redfish may be possessed by any person at any time. Possession of redfish in excess of the applicable bag or possession limit by any person aboard a vessel fishing in state waters constitutes prima facie evidence that such red fish were harvested from state waters. (3) Nothing in this section shall be construed to permit the harvest of native red fish from any area during any time, or the use of any gear where same is otherwise prohibited by law.>> * * * <<46-22.006 Other Prohibitions. The harvest of any redfish in or from state waters by or with the use of any treble hook in conjunction with live or dead natural bait is prohibited. Gigging, spearing or snagging (snatch hooking) of redfish in or from state waters is prohibited. It is unlawful for any person to possess, transport, buy, sell, exchange or attempt to buy, sell or exchange any redfish harvested in violation of this chapter. When any provision of this chapter is violated by a person aboard a vessel, the operator of that vessel, if different from such person, shall be deemed to have assisted and participated in the violation and such assistance and participation shall constitute a separate offense under this chapter. All redfish harvested from Florida waters shall be landed in a whole condition. The possession, while on state waters, of redfish that have been deheaded, sliced, divided, filleted, ground, skinned, scaled or deboned is prohibited. Mere evisceration or "gutting" of redfish, or mere removal of gills from redfish, before landing is not prohibited. Preparation of red fish for immediate consumption on board the vessel from which the fish were caught is not prohibited.>> <<46-22.007 Severability. If any provision of this rule chapter, or its application to any person or circumstances is held invalid; the invalidity shall not affect other provisions or applications of the chapter which can be given effect without the invalid provision or application, and to this end the provisions of this rule chapter are declared severable.>> Petitioners' Exhibit No. 1 (Added language underscored, de- leted language struck through) * Note: In the above quotation, language added to the statute is within the <<>>; deleted language is within the [[]]. The proposed rules and rule amendments under challenge are designed to replace the initial redfish rules, which took effect September 12, 1985, and remain in force. Since before the current rules' adoption, statutory provisions have imposed a statewide 12-inch minimum size limit for redfish, Section 370.11(2)(a)4, Florida Statutes (1985), and forbidden the use of purse seines. Section 370.08(3), Florida Statutes (1985). Youth and Age The redfish, also known as red drum and, to ichthyologists, as Sciaenops ocellatus, has a life span of 25 to 35 years. The adult redfish or "bull reds" swim offshore in deep water ordinarily, but not always, in schools. They are commonly found with schools of blue runner and little tunny. Respondent's Exhibit No. 29, 2-1. Schools of adult redfish are not found in inshore waters. But adults do approach the mouths of estuaries to spawn in the fall, mostly in September. Eggs borne by incoming tides and newly hatched, microscopic redfish larvae swimming inland make their way through the passes and well up into the bays and bayous along Florida's coasts, often all the way into fresh water, where rivers empty into the estuaries. By April of the following year, some redfish spawned in September have attained a length of 12 inches. By the following September, all redfish spawned a year earlier have reached 12 inches in length. A redfish gains one to five pounds a year. (T.I.31) When they are 18 to 26 inches long, they weigh from 3 to 6 pounds. On average, an 18 inch redfish is about a year and a half old. Juvenile redfish also swim in schools, often with sea trout, mullet and catfish. Once a redfish reaches three or four pounds, man is one of the few creatures in the estuaries big enough to eat it. (T. I. 45) But scientists put the mortality rate for juvenile redfish at 30 percent. (T.58) Only when they are about 4 1/2 years old do redfish leave the juvenile population's estuarine habitat for the blue waters the adult population inhabits. On average they then weigh 12 to 14 pounds and have obtained a length of 29 to 30 inches. Tagging studies and age frequency data suggest that as few as two percent of redfish recruits, or perhaps only a tenth of that number, survive long enough to escape the estuary. (T.I.63) For at least the last ten years, the escapement rate has been on this order of magnitude, and the escapement rate may have been dropping during this period. (T.I.67) The size distribution of redfish taken offshore reflects significantly lower numbers of spawners escaping during the last 20-some years than previously. Spawning redfish tend to return to the point on the coast where they themselves were spawned, but this is by no means a hard and fast rule: "Drift", also called diffusion or filtration, is known to occur. Redfish range throughout the Gulf of Mexico and are found in the Atlantic Ocean as far north as New Jersey. Because redfish caught offshore are taken with purse seines, they cannot legally be landed in Florida. They are mostly brought ashore in Louisiana and mostly caught in that part of the Gulf. Juvenile redfish in the Florida Keys are not believed to swim back and forth between the Gulf and the Atlantic, but adult redfish may. Blackened Redfish Commercial fishing offshore requires a six-figure investment in boat and equipment and a crew of several men. Until relatively recently, the big offshore operations largely ignored redfish, in favor of fish that could be sold at higher prices. But a dramatic increase in the demand for redfish has provided the economic incentive to make redfish an important target of the offshore fishery since 1982 or 1983. (The redfish's new-found popularity has been attributed to a New Orleans chef, who made famous a dish called "blackened redfish.") For whatever reason, massive catches of red fish offshore have depleted the adult stock of redfish in the last four or five years by as much as half, by some estimates. Before 1983, catches averaged less than 100,000 pounds a year. In the first half of 1986, some 7,000,000 pounds of redfish were taken in federal waters in the Gulf of Mexico. In other species, declines in the number of spawners have precipitated collapses of fisheries. The pattern has been, however, that declines in spawning populations have initially caused increases, rather than decreases, in juvenile populations. In the case of the yellow croaker, for example, the juvenile population initially increased ashe adult population dwindled. Only after 80 percent or more of the spawning stock was wiped out did a dramatic drop in the juvenile population ensue, spelling the end of the fishery. Whether the juvenile redfish stock has diminished in consequence of the decline of the spawner population is not clear. According to anecdotal evidence from Steinhatchee, the redfish catch there has increased over the last five years. The evidence did not establish whether fishermen's efforts to catch juvenile redfish at Steinhatchee or elsewhere in shallow state waters have changed significantly in recent years. Steinhatchee fishermen report large schools of two to four pound redfish beginning in October. Such reports are often unreliable evidence of general conditions, however. Trends in catch data are evidence of population trends, but they require careful interpretation. For one thing, experts generally believe the commercial catch to be under-reported and the recreational catch to be overestimated. (T.I.48-9) Constant catches in response to increasing effort may reflect a decline in population. Even increasing catches are not incompatible with population decline, considered in conjunction with other factors. The most recent catch data from Charlotte Harbor suggest smaller catches last year and the year before than in immediately prior years, during which the trend was generally up. But last year's statistics particularly are subject to revision and should be treated as preliminary only. To some extent, moreover, last year's change from a 12-inch to an 18-inch minimum size limit in Charlotte Harbor would account for any decrease in catch. The Charlotte Harbor redfish catch reported for 1984 is comparable to catches reported in the mid 1950s, 1964, and 1969, and exceeds the redfish catches reported in 1967, 1966, and certain earlier years. In short, the Charlotte Harbor data since 1983 neither confirm the previous upward trend nor establish any change in trend. Catch statistics with regard to the state as a whole are similarly inconclusive. In 1979, fishermen caught 3,177,590 pounds of redfish in Florida waiters. The total catch fell by more than a third to 1,917,005 pounds in 1980, and climbed to 3,160,122 pounds in 1981, about the level of two years before, even excluding recreational catches in January and February. In 1982, the total catch increased some two and a half times to 8,977,274 pounds, although MFC's executive director suspects that the recreational catch estimates, and, therefore, the totals for 1982 are inflated. The total redfish catch fell to 5,738,260 pounds in 1983, then rose to 6,375,250 pounds in 1984. Table 5, Petitioner's Exhibit No. 4. These catches do not include adult redfish in any significant numbers. (T. I.33) Fish Scaling MFC staff used a computer model developed by one of the commissioners, William W. Fox, Jr., to predict the effects regulatory changes would have on the escapement rate. This computer model, the generalized exploited population simulator (GXPOPS), has been used to predict the population dynamics of such diverse species as pandalic shrimp, with its "protandric hermaphroditic life history strategy," Petitioner's Exhibit No. 8, p. 38, and grouper, a "protogynic hermaphroditic population." Id. Redfish have distinct genders and differ from grouper and shrimp in other important attributes. Computer models are the only tools available for predicting population changes in response to regulatory changes, however; and, as far as the evidence showed, no other computer model has been more closely tailored to redfish or would be any more likely to predict the effects of regulatory changes on redfish populations more accurately than GXPOPS. Various GXPOPS generated tables are in evidence displaying data stated in millions of pounds of redfish, or in millions of fish, but nobody knows how many redfish are in the sea, so that a principal use of the numbers is as ratios; more than one scale has been used, and not all the tables are directly comparable. The MFC considered what biological or resource objective to set in terms of a proportional increase in the rate of escapement. The greater the fraction of juvenile recruits that survive long enough to escape the estuaries, the more rapidly the diminished spawning stock could be replenished offshore. Although there is some confusion on the point, it is not an unfair characterization to say that the MFC adopted a 50-fold increase in the escapement rate as its biological goal for redfish. If, as may be the case, the present escapement rate is only 0.2 percent, a 50-fold increase would only bring the escapement rate to half the level advocated by the Gulf of Mexico Fisheries Management Council. If, as may also be the case, a dramatic decrease in the number of recruits is either imminent or already in progress, even a 50-fold increase in the rate of escapement may not increase the number of spawners leaving the estuaries to the levels needed to preserve the redfishery. The evidence falls far short of showing that the MFC has set the escapement rate goal too high. On the contrary, the evidence established that the MFC set the escapement rate goal so low that attaining the goal will not guarantee the continued viability of the redfish fishery. If, as respondent's executive director testified, it is like driving toward a cliff in the fog, the wisest thing might be to stop the car till the fog clears. Means To An End Once a biological or resource goal has been set, the question becomes how to reach the goal. The MFC considered two options that the GXPOPS model predicted would meet its resource goal without closing down the commercial fishery: a five-month closed season together with a 17 inch minimum size limit; and a six-month closed season together with a 16-inch minimum size limit, There are numerous other approaches that would not involve conferring gamefish status on the redfish. Exhibit 1 to Dr. Fox's deposition; Dr. Austin's testimony. It may be that prohibiting redfishing for three, instead of only for two months would have permitted continuation of the commercial fishery. (T.XI. 52-4) In regulated fisheries throughout the world "there is a fairly clear hierarchy," (T.X. 72), among types of regulations. Minimum-size limits, then closed seasons, then catch restrictions (bag limits for recreational fishermen and quotas for commercial fishermen) are preferred, in that order, both because within each category the magnitude of change necessary to accomplish the same result increases in descending order; and because the complexity of assumptions that must be made to predict the effect of the regulation increases for each category in descending order. In the present case, for example, an increase of three inches in the minimum size limit applicable in peninsular territorial waters, from 18 to 21 inches, would be a less drastic change than leaving the minimum size limit at 18 inches and closing state waters to the taking of redfish for five months, although either change would accomplish approximately the same increase in the escapement rate. The only assumptions that underlie minimum size restrictions concern age size correlations and the "mortality that occurs when fish have to be released [because they are too small], which is relatively well known in this fishery." (T.X. 74) Predicting the effect of closed seasons requires more complex assumptions about seasonal abundance of the fish, the likelihood that fishermen's efforts A to catch the species will drift into the open season, and the chances that scofflaws will shorten the closed season de facto. In general, a prohibition against possession is more readily enforcible than a prohibition against disposition. It is a simple matter to count the number or to measure the size of fish a person has in his possession. Proving an intent to sell is more difficult. Other Management Plans On July 20, 1986, the United States Secretary of Commerce closed the federal conservation zone, which is the area more than nine and less than 200 nautical miles out from shore, to the taking of redfish. The Gulf of Mexico Fisheries Management Council (GMFMC) has recommended that the original ban, which was to have been effective only through September 23, 1986, be extended for another 90 days pending adoption of regulations prescribing a permanent ban. The GMFMC has also recommended that the Gulf states adopt regulations that would allow at least a fifth of redfish recruits to escape the estuaries. As of January 1984, Alabama prohibited the taking of red fish smaller than 14 inches and the taking of more than two redfish larger than 36 inches, placed geographic and temporal restrictions on the use of nets, limited recreational catch to 25 fish per day and imposed a possession limit of 50 on recreational fishermen. Respondent's Exhibit No. 29, 7-16 and 17. Alabama forbids the sale of native redfish. Alabama Administrative Code Section 220-3- 12. As of January 1984, Mississippi placed gear restrictions on fishermen taking redfish, prohibited the taking of redfish in certain places (including Redfish Bayou!) and of a size less than 14 inches, limited to two per day the number of redfish exceeding 30 inches in length, limited recreational catch to 10 redfish per day, imposed a possession limit of 30 redfish, closed state waters to commercial fishing from September 15th to November 15th, and authorized closing of the commercial fishery for the remainder of any year in which landing reports indicate 200,000 pounds have been taken. Respondent's Exhibit 29,7-14,15. As of January 1984, Louisiana closed certain areas to commercial fishing, disallowed the use of certain gear by commercial fishermen in certain other areas, and imposed gear restrictions on all fishermen. Recreational fishermen were limited to two redfish per day more than 36 inches in length but were subject to no minimum size limit. Recreational fishermen were entitled to take no more than 50 spotted sea trout and redfish combined per day, and subject to a 100-fish possession limit. Commercial fishermen were subject to a 16-inch minimum size limit but to no maximum size limit. Effective August 30, 1986, counsel advise, recreational fishermen are permitted to keep no more than two red fish greater than 30 inches in length and possession of redfish on board a vessel carrying a purse seine is illegal, citing Act. No. 613, 387, 611, 660. As of July 1984, commercial fishing for redfish had been outlawed in Texas, although licensed fish importers may, and do, sell redfish from Mexico and other states. No redfish less than 16 inches long or greater than 30 inches in length could be taken. The weekend use (1:00 p.m. Friday to 1:00 p.m. Sunday) of nets and trot lines was forbidden. As of September 4, 1986, the minimum size limit was 18 inches, and hook and line was the only lawful way to take redfish. Respondent's Exhibit No. 2, pp. 78A. At the time Texas dilettantized its redfishery, commercial fishermen were taking most of the catch. Fishermen must use either fishing poles or a single "sail line" which is a "special trotline[] with one end on shore, pier or jetty, and with the other end attached to a wind-powered device or sail and attended at all times." Respondent's Exhibit No. 29, 7-7. Florida Fisheries Fishing gear and methods in Charlotte Harbor, the principal site for commercial redfishing in Florida, have been constant for some time. Since the 1950s fishermen have used synthetic, instead of natural, fibers for their nets. In December, January and February, cold fronts in Charlotte Harbor seem to "concentrate the fish" into schools that experienced fishermen can spot. There is also a "night fishery" in the summer months, when redfish are taken at first light or "dawn pink." Petitioner's Exhibit No. 9, p 31. Ninety percent of the red fish commercial fishermen catch in Charlotte Harbor are taken with trammel nets, deployed from flat-bottomed shallow draft boats 19 to 24 feet long, with beams of five to eight feet. Although "pole skiffs" are sometimes used in very shallow water (four inches or less), the boats are mostly powered by outboard motors, mounted forward in wells. In Steinhatchee, the fishermen call these boats "bird dogs." Even the largest of them can be handled by a single fisherman, and can be built with materials that cost less than $3,000. None could be safely taken very far off shore. Undersize or other undesirable fish taken in trammel nets can be returned to the water alive. Ordinarily trammel nets consist of two outer "walls" of larger mesh flanking a central, finer mesh curtain or "bunt." When the fishermen encircle the fish, the three components of the net stand vertically in the water; the lines along the upper edges of each bunt are kept on the surface by floats, while the weighted lines along the bottom edges fall to the bottom. Fish swimming through an opening in one wall and into the small- mesh bunt push the finer netting through openings in the other wall, which creates a pouch or pocket in which the fish remains ensnared, when the fisherman hauls in the trammel net. Gill nets, which are also sometimes used, consist of a single swatch with mesh calibrated to stop fish of a certain size. Smaller fish swim through while larger fish are repelled. Fish taken by gill nets die from injuries they sustain when they become lodged in an opening in the net. In Steinhatchee almost half the red fish sold to the fish houses are caught by hook and line fishermen who have salt water products licenses, which can be bought for $25 and authorize the holder to sell his catch. In Charlotte Harbor, the "bucket brigade" as they are there called makes a contribution, although a less significant one, to the commercial catch. Hook and line fishermen have the advantage, an important one in the Steinhatchee fishery, of being able to take their boats up the river into fresh water. Eighty percent of redfish are caught from boats. Making a Payday Commercial fishermen take only an eighth to a quarter of the redfish caught in Florida state waters. As far as the evidence showed, not a single commercial fisherman in Florida depends exclusively on the sale of juvenile redfish for his income. Redfish comprise less than one percent of the food fin fish commercial fishermen catch in Florida waters. Almost all of the approximately 1800 commercial fishermen in Florida who catch redfish in state waters depend on the sale of other fish for most of their income. At a given time, certain species are available and certain species are not; and the prices they fetch vary. Mullet may bring as little as $.25 a pound while pompano can go for as much as $3.10 per pound. Commercial fishermen in Charlotte Harbor, whose annual income averages $11,334 after expenses, take mullet, sea trout, pompano, mackerel, jacks and sand bream as well as redfish. Not every fisherman targets each of these fish, but the overwhelming majority do seek mullet, which they call their "bread and butter" fish. Even for those fishermen whose equipment and skills enable them to pursue several species, the different species are not readily interchangeable. Rather than offering each load of fish they catch to the highest bidder, commercial fishermen like the individual petitioners who testified in the present case, ordinarily sell their catch to a single fish house, year after year. This practice offers some protection against seasonal market fluctuations. When roe mullet begin to run in the fall, demand for these and other fish exceeds the supply. But, during the summer months, the fish house operators will not buy mullet from fishermen with whom they have not already established a relationship. Because supply greatly exceeds demand in summertime and because freezer space is limited, fish house operators impose quotas even on fishermen with whom they have longstanding relationships. The fish houses do not sell all of the catch locally. About half leaves Florida. Exporters drive refrigerated semi-trailers to the fish houses where they buy fish by the 100-pound box for resale out of state. Georgia, their nearest destination, is several hundred miles from Charlotte Harbor, the principal site of redfishing in Florida waters. Except during the roe mullet run, these drivers call ahead to inquire of the fish houses how many "fancy fish" they have, "fancy fish" meaning redfish or sea trout. If a fish house has no redfish or sea trout on hand, the drivers may pass it by altogether or, at best, buy only a few boxes of mullet. Explicitly or otherwise, fish houses with redfish to sell may condition their sale on the buyer's taking, along with each box of redfish, four to ten boxes of mullet, depending on market conditions. Fishing For Fun According to those who have studied the question most carefully, including Dr. Holland, who testified at hearing, the attractiveness of recreational fishing trips depends less than might be expected on the hope of catching any fish at all, much less one of a particular species, when several are available. Very few recreational fishermen "limit the goals of their fishing experience to catching fish. The majority are more interested in perceiving freedom, escaping from responsibilities, and enjoying an outdoor natural environment." Petitioner's Exhibit No. 17, p. 137. Things like "being exposed to polluted surroundings... ruin[] a fishing trip more than not catching a fish. These conclusions are based on answers given by a sample of fishing association members who actively fish (an average of 31 days a year)." Petitioner's Exhibit No. 17, p. 136. As Mr. Raulerson explained with reference to tourists who fish in Florida's salt waters, the prospect of catching a fish may be less significant than the prospect of being out on the water in weather much warmer than what the tourist has left behind; and sighting a porpoise can be the principal benefit tourists derive from a fishing trip. For most recreational anglers, keeping a fish to eat is even less important than catching it. The only one of the intervenor's witnesses who testified on the point, Richard A. Shapley, a Tallahassee resident and an IBM employee who goes fishing every weekend, characterized himself as "more of a sports fisherman than a fish eater," (T.VII p. 16) and candidly admitted that he would not be particularly bothered by having to release all the redfish he caught. Currently, only 7.6 percent of sports fishermen catch more than five redfish per trip. Their catch amounts to eleven percent of the recreational catch, which has accounted for three quarters to seven eighths of all the redfish harvested in Florida waters. Almost five percent (4.975 percent) of marine sport fishermen in Florida caught (but did not necessarily seek) or sought (but did not necessarily catch) redfish, according to the most reliable statistics available for the period 1979 to 1984. An economist employed by the Sport Fishing Institute (SFI), whose "programs serve the long-term interests of the sport fishing industry, which provides the base of ... [SFI's] financial support," Respondent's Exhibit No. 1, p. 1, offered the opinion that up "to $121,416,000 in [1985] retail marine sport fishing expenditures can be attributed to redfish." Respondent's Exhibit No. 1, p. 11. Marine sport fishing is without doubt an important source of income for many Floridians, and retail marine sport fishing expenditures figure significantly in the state's economy, but the SFI estimate of retail expenditures attributable to redfish is a very substantial overstatement. To obtain the figure of $121,416,000, SFI's economist used a study that attributed to fishing not only all sums expended on fishing trips, but also all food and lodging expenditures for the whole of each day on which a tourist did any fishing; then assumed that catching or seeking redfish was the sole motivation for 4.975 percent of the fishing trips sportsmen made in Florida's salt waters. Neither of these assumptions bears up under scrutiny. Even on the assumption, which the evidence showed to be contrary to fact, that all fishing trips arise wholly from a desire to catch fish, the use of the 4.975 percent factor was not justified. At least for purposes of the present case, retail expenditures made by fishermen who had no desire or intention to catch redfish can hardly be said to be attributable to the availability of redfish. In addition, the number of recreational fishing trips taken by anglers in pursuit of redfish should, at the very least, be reduced to allow for trips on which the hope of taking other species was the dominant purpose. End of An Era If the proposed rule changes take effect, commercial fishing for redfish in Florida waters will come to an end. The effects on commercial fishermen would be overwhelmingly adverse. The one possible silver lining is that the loss of redfish as a commercial species would make mullet so much harder to sell that marginal commercial fishermen would look for other work, leaving more fish for the more skilled full-time commercial fishermen. Red fish sell for about eighty cents per pound ex-vessel. At least one fish house has had recent offers of $1.45 or $1.50 per pound for redfish. The economic impact statement puts the secondary wholesale value of redfish at 2.8 times the ex-vessel price. Grocery stores, seafood markets and restaurants sell redfish at retail. On the assumption that the retailers could substitute imported redfish for native redfish, if commercial fishing is banned by the proposed rule, the economic impact statement ignores retail losses and predicts a "total annual longterm commercial loss ... [of] approximately $4.733 million in income [which] could force some fishermen and fish houses that rely primarily on redfish out of business." Petitioners' Exhibit No. 5, p. 2. The economic impact statement's analysis assumed a loss of commercial catch of only 961,646 pounds, the 1982-1984 average. On the same assumption, an economist analyzing the problem from the perspective of sport fishermen, predicted the total economic impact of closing the commercial fishery would be $6,494,629 annually, taking retail sales into account and using certain multipliers. Respondent's Exhibit No. 1, pp.9 and 10. Neither of these calculations takes into account the economic value of redfish as leverage in mullet sales, although the economic impact statement does mention that "having no redfish to sell will hurt the mullet sales." Petitioners' Exhibit No. 5, p. 21 Fewer, Fatter Fish for Frying If the proposed rules take effect and the fishery does not collapse, the escapement rate will increase by a factor of 58.43 and, except for the fish that escape, the recreational fishermen will have available not only the fish now caught by commercial fishermen, but also all of the predicted increase in the weight of the redfish catch. The present recreational catch, estimated at 2.1 million pounds, before the new minimum size regulations took effect on September 12, 1985, would grow to 5.65 million pounds at equilibrium three or four years out. Petitioners' Exhibit No. 4, p. 10, All of this increase would be attributable to an increase in the average size of the fish caught, because, over the same period, the number of fish caught by recreational anglers would fall from 1,190,000 to 1,030,000. Id. The precise effects these changes would have on the recreational fishing industry are not clear. The two-month closed season would have an adverse affect, since some 7.4 percent of recreational fishing trips on which redfish are caught or sought now occur in March or April. On the other hand, there would be more redfish, they would weigh more on average, and they would be more likely to be caught not only during the ten months they could lawfully be taken, but also during the two months when the law would require fishermen to release them, if caught. The proposed rule would make it more likely that unskilled fishermen who would not otherwise have caught a redfish will catch redfish, and that those who would otherwise have caught less than five will be more likely to catch as many as five. T.X. Skilled fishermen might be discouraged by the proposed five fish bag limit. Increased abundance would presumably be irrelevant to the 7.6 percent of recreational anglers now catching more than the proposed bag limit of five. They may, indeed, be lured to Alabama where the bag limit is 25, or to some other site. The effects a change in the availability of redfish might have on recreational fishing were the subject of much testimony at the hearing. The economic impact statement assumed a response elasticity for non-residents" of 0.1203, i.e., that an increase of eight percent in pounds of redfish available would cause an increase of approximately one percent of the number of fishing trips on which redfish were caught or sought. The 0.1203 figure is "Green's coefficient," and was used by Green to correlate changes in numbers of fishing trips taken by non-residents already in Florida with changes in multi-species catch (in pounds) per trip, not with changes in the total number of pounds of a particular species available to be caught. As far as the evidence showed, moreover, the weight of fish in Green's study was a good proxy for numbers of fish. In the present case, the increase in weight would occur despite a reduction in the number of fish caught and kept. Despite all the problems, however, Green's coefficient is a much more satisfactory measure of elasticity than any other offered at hearing. The economic impact statement summed up the situation fairly by saying with respect to recreational fishing, "little is known of the effects of being able to harvest less of one species of fish, especially in saltwater where a multitude of species are available as substitutes." Petitioner's Exhibit No. 5, p. 3. The converse is also true, although fishermen "tend to go to the spot where... [they] think... [they] can catch the most fish." But the proposed rules would decrease, not increase, the numbers of redfish that recreational fishermen could take. (T.V. 148) Studies in evidence show that increased availability of fish attract fishermen to the site of the increase. Even if it is assumed that bigger fish attract fishermen just as greater numbers of fish do, it does not follow that the total number of fishing trips occurring everywhere increases, rather than that fishing has fallen off at alternate sites within the fisherman's geographical range. (T.V. 147-148) For many tourists the geographical range will be determined by factors unrelated to fishing. Tourists, including tourists who eventually go fishing in salt water here, come to Florida for many different reasons. Perhaps the children want to go to Disneyworld. Whether a fishing trip is among their recreational pursuits once they arrive depends on how attractive a fishing trip seems in relation to other recreational possibilities. This depends, in turn, on a host of other factors, including, for example, relative cost. The cost of a fishing trip is five times more important than the availability of fish, as a variable determining whether the fishing trip will be taken. Even anglers choosing a Florida vacation in order to go fishing will not necessarily take the availability of redfish into account. Enforcement Considerations Size restrictions are more easily enforced against commercial fishermen than against recreational fishermen, because almost the entire commercial catch moves through licensed, frequently inspected fish houses, while the low numbers of marine patrol officers make enforcement of such regulations against recreational fishermen a haphazard affair. The so-called night fishery for redfish during summer months occurs at first light. Even if fish are taken while it is dark, they must, with few exceptions, move through easily monitored channels if they are to be distributed commercially. Closed seasons create the possibility of erosion when they begin, by fishermen jumping the gun, and when they end, by fishermen persisting unlawfully. Redfish can be frozen, which makes it difficult to determine just when they were caught. Under the proposed rule, however, frozen redfish can be imported, so the possibility of passing off native red fish as imports would exist, just as, in a mixed fishery with a closed season, the possibility of passing off redfish taken out of season as having been taken lawfully would exist. There is also the possibility, if bag limits apply to recreational, but not to commercial, fishermen that recreational fishermen will buy salt water products licenses to escape the bag limits. Such a strategy would appeal to recreational anglers who successfully fish for redfish now. Data from other, similar fisheries suggest that successful anglers' catch goes up proportionally much less than marginal or unsuccessful fishermen's catch in response to increased abundance. Recreational vs. Commercial Economic analyses of intergroup reallocations assume that the marginal utility of income is the same in each group. Since this is unlikely to be the case, such analyses are of limited importance. The accepted way to compare economic benefits attributable to commercially caught redfish and those attributable to redfish caught recreationally is to sum the producer's surplus and the consumer's surplus for the commercial catch and to do the same calculation for the recreational catch, and then compare the two. But there was virtual unanimity that adequate data do not exist to make these calculations. This makes the expenditures approach to valuation of red fish taken recreationally one of the few possibilities for quantifying their economic importance. But in a very real way, this approach is all wrong. Attributing fishermen's food and lodging costs to redfish they catch is analogous to allocating to each redfish sold in a restaurant the entire price of the meal, the babysitter's wages, and costs incurred for transportation to the restaurant. An increase in the price of gasoline results in an increase in the value assigned to redfish taken by recreational fishermen, although higher gasoline prices actually make fishing trips and the fish they might yield less attractive. Dr. Austin offered the most interesting approach, an approach which it is instructive to apply to the numbers Mr. Davis supplied on the last day of hearing. Dr. Austin's technique requires identifying the increase in recreational catch attributable to closing the commercial fishery. A close approximation is possible. The proposed rules would close down the commercial fishery by two overlapping devices: the bag limit and the ban on sale. Mr. Davis supplied the GXPOPS predictions of equilibrium effects for the "18 inch option," which differs from the proposed rules in that it has no bag limits does not forbid the sale of native redfish, and has no closed season. According to Mr. Davis, respondent's executive director, recreational fishermen would take 3,950,000 pounds and commercial fishermen would take 1,112,000 pounds of redfish at equilibrium, with the 18 inch option, assuming the fishery did not collapse. At equilibrium under the proposed rules, again assuming the fishery did not collapse, the total annual catch (which would all be recreational) is predicted to amount to 5,650,000 pounds. At equilibrium, the recreational catch with the proposed rules in place would exceed the recreational catch under the 18 inch option by 1,700,000 pounds 1/ (5,650,000 minus 3,950,000 equals 1,700,000). There would be no commercial catch under the proposed rules, but the 18 inch option would result in annual commercial catches of 1,112,000 pounds, at equilibrium. With the methodology developed at page four of the economic impact statement, Petitioners' Exhibit No. 5, it is possible to predict a 5.2 percent increase in recreational trips, or an increase of 14,641 fishing trips annually attributable to choosing the proposed rule over the 18 inch option. (283,078)(.1203)(1,700,000 divided by 3,950,000). If the proposed rules are adopted, the commercial sector's loss, at equilibrium, of 1,112,000 pounds a year may be said to have made possible the increase in recreational trips. Dividing the number of pounds lost by the number of trips gained yields the number of pounds of catch commercial fishermen would have to forego, in order to induce each additional recreational trip. Dividing 1,112,000 by 14,641 yields 76 pounds of commercial catch foregone for each recreational trip induced. The economic impact statement values each recreational trip at $53, citing Bell's study. Petitioner's Exhibit No. 5, p. 7. This compares with the retail price of 76 pounds of redfish - at $2.70 per pound - of $205.20. Another way to view the economic consequences of reallocation from the commercial to the recreational sector is to compare the relative costs of production, and efficiencies of distribution. Commercial fishermen produce redfish at an approximate cost of $.50 per pound, then introduce them into marketing channels, where they become available to all segments of the population. In contrast, SFI's economist acknowledged that it costs recreational fishermen somewhere between $19.94 and $31.37 per pound to harvest redfish, which is then available only to the sportsman and his circle of acquaintance. In short, the evidence did not establish an economic justification for closing down the commercial fishery and reallocating most of the fish that would have been taken commercially to the recreational sector. Neither the economic impact statement nor its author, who testified at hearing, claimed a net economic benefit would flow from a reallocation of redfish from the commercial to the recreational fishery. The issue of reallocation is, at bottom, a political question. Let Them Eat Mullet Although some people, like Mr. Shapley, may not be particularly interested in eating redfish, redfish is believed by many to be desirable as food. This includes people who do not own boats or go fishing. If native redfish becomes unavailable to Florida consumers, who would otherwise have eaten it, they will have to substitute frozen, imported redfish, or another species of fish or some other source of protein.
