Findings Of Fact The City of Boynton Beach, Florida, filed application number 24859 with the South Florida Water Management District (formerly the Central and Southern Florida Flood Control District) for an annual allocation of 3.89 billion gallons (10.7 mgd) for a public water supply system for its service area of 18,351 acres for a period of ten years. The application was dated February 26, 1976. A supplemental engineering report was submitted on April 26, 1977, and a water withdrawal management plan on August 18, 1977. The delay in completing the documentation for the application was due to the applicant's completion of a test well program and hydrogeological evaluation of the aquifer capability of the 34 acre tract known as the "Jarvis Property," the proposed site of eight future wells. (Composite Exhibit 1) The existing raw water supply system for Boynton Beach consists of four separate well fields, comprising a total of 14 wells with a total rated capacity of 9700 gpm. Wells 1 through 5 were built during the period 1946-1958. Wells 6 through 11 were built from 1961-1973, and wells 12 through 14 were completed in 1976. The application seeks approval for eight additional wells, numbers 16 through 22 to be located on the "Jarvis Tract." It is proposed that wells numbers 15 and 16 be built immediately upon approval of the application and that the remaining six new wells be constructed at a rate of two per year through 1982, subject to demand. The city presently operates a water treatment plant with a treatment capacity of 8 mgd and is expanding that facility to a capacity of 16 mgd. It is anticipated that this expansion and the new well field will meet projected water demands in the service area through 1987. (Testimony of Swan, Composite Exhibit 1, Exhibit 2) The Applicant's present wells tap the shallow aquifer overlying the Hawthorne formation. These wells range in depths from 54 to 115 feet below ground surface. The planned wells will reach 180 to 230 foot depths. The shallow aquifer is largely recharged by local precipitation and a surface canal system. There are two major canals located near the Applicant's well fields in distances ranging from directly adjacent to approximately one mile. Canal E-4 is located on the western boundary of the proposed Jarvis well field which would provide direct recharge in the area. Withdrawal of water from wells number 1-5 had to be curtailed due to a landward movement of the freshwater/saltwater interface. The wells at present are used for emergency standby purposes only. After wells number 12-14 were put into operation, it was discovered that the withdrawals affected residential shallow irrigation wells nearby. Three of the residents have filed objections to the application for this reason. This problem will be resolved by the development of the Jarvis well field which will allow curtailment of pumpage from wells numbers 12-14. Well number 14 presently is not in operation due to an unknown polluted condition. The curtailment of use of wells 1-5 will aid in controlling any salt water intrusion. A U.S. Geological Survey saltwater monitoring well in the area indicates that there has not been any net landward movement of the saltwater/freshwater interface in the shallow aquifer since 1973. The Applicant's water withdrawal management plan which will substantially reduce the pumpage from wells 6-14 will also reduce the threat of saltwater intrusion by maintaining the aquifer water levels in the area at a higher elevation. (Exhibits 2-4, 6, Testimony of Gresh, Higgins, Kiebler) The City of Boynton Beach currently has a population of 51,000 and it is projected that by 1987 the population will reach 71,000 which is the maximum limit of its water treatment facilities. The city plans to build a new treatment plant and well field in the western portion of the area when the capacity of the current and proposed well fields are reached. It would be uneconomic to place the currently proposed well field in that area due to the requirement of building a raw water line for a distance of approximately four miles. (Composite Exhibit 1, Testimony of Cessna) The South Florida Water Management District staff recommends that the application be approved in its entirety for a period of ten years, subject to 18 special conditions which are acceptable to the Applicant. The district staff concluded that sufficient water is available in the Applicant's area to support the 1987 level of withdrawals and that the proposed consumption rate reflects a reasonable use of water. The staff further found that there would be a minimal impact on existing users in the area and that westward lateral intrusion of saltwater from the coastline will be reduced. (Exhibit 2-3, Testimony of Higgins)
Recommendation That the application be approved and that a water use permit be issued to the Applicant pursuant to application number 24859 for a ten year allocation of 3.8 billion gallons, subject to the special conditions recommended by the South Florida Water Management District staff. DONE and ENTERED this 21st day of February, 1978, in Tallahassee, Florida. COPIES FURNISHED: Gene Moore, Esquire City Attorney City of Boynton Beach Post Office Box 310 Boynton Beach, Florida 33425 THOMAS C. OLDHAM Hearing Officer Division of Administrative Hearings Room 530, Carlton Building Tallahassee, Florida 32304 (904) 488-9675 Steve Walker, Esquire 3301 Gun Club Road Post Office Box 3858 West Palm Beach, Florida 33402
Findings Of Fact Oliver DeWitt and Donald F. Richters, employees of the Southwest Florida Water Management District, were called, testified, and identified Composite Exhibit 1, the staff record of this application. Frank applied for a permit after the fact to construct a bulkhead within the mean annual floodplain of Lake Eustis. The investigation clearly revealed that fill had been placed behind a bulkhead built in Lake Eustis. Referring to the drawing marked "A" attached to the application found in Exhibit 1, the area marked in blue by the witnesses is the area filled and bulkheaded by the applicant. The applicant did not appear or present evidence to support its application.
Recommendation The Hearing Officer having considered the law and the facts would recommend denial of the application. DONE and ORDERED this 23rd day of February, 1976. STEPHEN F. DEAN, Hearing Officer Division of Administrative Hearings Room 530, Carlton Building Tallahassee, Florida 32304 (904) 488-9675 COPIES FURNISHED: Jay T. Ahern, Esquire Counsel for SWFMD Irene T. Frank Route 2, Box 55 Tavares, Florida 32778
Findings Of Fact The Petitioner in this matter is Capeletti Brothers, Inc., a Florida corporation. .The Respondent is the State of Florida, Department: of Environmental Regulation, an agency of the State of Florida with regulatory authority granted pursuant to Chapter 253, Florida Statutes, and Chapter 403, Florida Statutes, and those rules attendant thereto. Through its Petition as received by the State of Florida, Department: of Environmental Regulation, the present: Petitioner has filed a formal proceeding pursuant to Subsection 120.57(1), Florida Statutes, and through this Petition has challenged the Department's assertion of jurisdiction to require an-environmental permit and in the alternative has requested that the permit be granted if it is determined that a permit is necessary. (The jurisdictional question was ruled on by order dated December 7, 1979.) The Petitioner's activity which fostered the current dispute between the parties involved the Petitioner's intention to excavate certain property in Broward County, Florida, and through such excavation remove rock fill material constituted primarily of limestone and leave in place a quarry containing water. The Petitioner holds an option to purchase the property in question subject to the granting of necessary environmental permits to conduct the excavation. The terms and conditions of that option to sell may be found in the Petitioner's Exhibits 10 and 11, admitted into evidence. The Petitioner had intended to use the fill material in the furtherance of a road building project by contract entered into between the Petitioner and the State of Florida, Department of Transportation, the contract award being made on February 23, 1977. The parties to that contract terminated the contract prior to any permit for dredging having been granted; however, Petitioner still desires to excavate at the site for the purpose of obtaining fill material for future building projects and the nature of the option to purchase would allow the Petitioner to continue to pursue its efforts at obtaining a permit, notwithstanding the termination of the original agreement between Capeletti Brothers, Inc., and the State of Florida, Department of Transportation. The Respondent has issued a Notice of Intent to Deny the permit by a letter dated March 26, 1979, and a copy of the Notice of Intent to Deny may be found as Exhibit "A" to the Petition. This Notice of Intent to Deny followed the receipt and review of Capeletti Brothers, Inc.'s application for permit dated October 18, 1978. In addition, the Respondent has asserted permit jurisdiction based upon grounds not set forth in the Notice of Intent to Deny. This claim for jurisdiction is a claim for jurisdiction under the provisions of Chapters 253 and 403, Florida Statutes, and their associated rules. A copy of the application for permit may be found as Petitioner's Exhibit No. 1 admitted into evidence and this application contains sketches showing the location of the proposed project with reference to the surrounding terrain and other features. The proposed project site consists of approximately forty-four acres of land located south of Andytown, Florida, and west of State Road 25 (U.S. 27). The site is surrounded by Alligator Alley to the north; State Road 25 to the east, with a contemplated borrow canal to be constructed between State Road 25 and the project location, immediately adjacent to State Road 25; to the west by Florida Power and Light patrol road, with a borrow canal running north and south located west of the patrol road and Levee 37 further west of the borrow canal, this levee being maintained by the South Florida Water Management District. To the south of the project is an access road which grants access to the Florida Power and Light patrol road. The quarry which is to be dug on the acreage in question will not intersect either of the borrow canals referred to above. Upon completion, the pit area will consist of approximately twenty-two acres of open excavation approximately forty feet deep with a littoral zone constituted of sawgrass. At the conclusion of the project, all fill material that has been excavated will have been removed from the project site and the access road to the project site destroyed. The pit will be left full of water that has entered the pit at the excavation during the dredging. That water will be constituted primarily of groundwater located immediately below the surface in pockets found in the limestone fill material. The displacement of limerock will allow the groundwater to fill the void. Although the water which enters the excavation site will be primarily groundwater, the waters within its boundaries will eventually have the characteristics of surface waters due to the design of the activity being much like a natural pond. Approximately four thousand feet south of the project site is an abandoned rock quarry with an access road from State Road 25 and approximately two miles south of the project site is an active rock quarry operated by Rosen, Rosen and Tupler. The nature of the Rosen, Rosen and Tupler quarry is similar to that as contemplated by the Petitioner's plan. There are other rock quarries of similar nature located in the vicinity of the project site. The project site does not receive surface flows or sheet flows from adjacent properties due to the fact that the project site is surrounded by dykes and borrow canals which block surface flows or sheet flows from any adjacent properties. The surface water flow on the property is in a more or less southeasterly direction. The rainfall that occurs at the project site causes the project site to be inundated at times with standing water as deep as six or eight inches. This water will not exit the property except in times of high incidence of rain, when the water may overflow the Florida Power and Light access road and make entry into the borrow canal adjacent to State Road 25, gaining such access at the southeast of the project site. At present, part of the borrow canal east of the project site and adjacent to State Road 25 has been filled in. As stated before, this area will be replaced by a future excavation of a borrow canal in the area now covered. The surface water which stands on the project site normally percolates into the ground or evaporates into the atmosphere. The primary vegetation at the project site is sawgrass. The project: as contemplated would remove some of these grasses and attached heavy muck soils, but there would remain a sawgrass zone between the contemplated borrow canal located east of the project and the Levee 37 borrow canal located west of the project. The borrow canals located to the east and west of the project site flow south to the South New River Canal, which runs generally east and west. The waters collected in the South New River Canal are subject to being pumped through the pumping station S-9 which distributes water to the west or the water may be carried through the South New River Canal in an easterly direction, eventually entering the South New River, a natural waterway subject to navigation. The South New River is approximately twenty miles from the project site. The South New River empties into the Atlantic Ocean. Those waters which are pumped westerly through pumping station S-9 may enter other natural waterways and eventually the Gulf of Nexico by transportation through a series of artificial canals and natural water connections. Although the Petitioner does not intend to introduce contaminants at the proposed project site during the preparation stage; stage of excavation and stage of evacuation, the testimony concerning the project site and an active quarry of similar nature in the immediate vicinity, and other similar quarries, establishes that it could be reasonably expected that oils, greases and lead would be dispersed in the area of the quarry pit, the immediately adjacent wetlands and at times of high incidence of rainfall, into the borrow canals adjacent to the property. However, before the contaminants reach the borrow canals by overland sheet flow, they will be filtered out by the wetlands. The contamination into the pit would find its way into the Biscayne Aquifer, the Aquifer at the project site being only a foot or so beneath the surface., The introduction of contaminants into the Biscayne Aquifer at the project site will eventually lead to the direct mixing of those contaminants with portions of the Biscayne Aquifer adjacent to the project site, in particular west of the project site in the containment area which is part of the system of submerged lands of the state and to the borrow canal east of the project site. There is also the possibility of copper, zinc, iron, chromium, manganese, dieldrin and polychlorinated biphenyls contaminants being introduced into the pit (quarry). in association with the project, though this possibility is more remote than in the case of the substances previously mentioned and the possibility is so remote that it is not reasonably expected to occur. Therefore, these are not substances for which the Petitioner must do actual testing to show that they do not exceed water quality standards in order to establish necessary reasonable assurances. The facts presented did not give rise to even a potentiality for the presence of other regulated substances that might exceed applicable water quality standards, with the exception of phenols which are reported next. Phenolic-type compounds were found in the active and inactive quarry pits similar to the proposed installation These compounds as detected in the sample and reasonably expected at the project are naturally occurring phenomena and not the direct product of the mining activity. The mining will create turbid conditions and there will be fluctuations in dissolved oxygen concentrations and BOD values and changes in pH values in the pit. The above-referenced contamination and variations in values would be injurious to human health or welfare, animal and plant life and property and, as a consequence, interfere with the enjoyment of life and property, if found to exceed the Respondent's applicable water quality standards. The Petitioner, if allowed to carry out the project, has given specific reasonable assurance that it will not violate the Respondent's applicable water quality standards related to the turbidity, dissolved oxygen, BOD, lead, oils and greases, and pnenols. See Rule 17-3.05(2), Florida Administrative Code. Other substances-and conditions found in that subsection of the rule not being reasonably expected to occur, necessary reasonable assurance has been established for those. There will be no discharges of heated water. See Rule 17-3.05(3), Florida Administrative Code. The project site does not involve outstanding Florida waters within the meaning of Rules 17-3.041 and 17-4.242(1), Florida Administrative Code. Testimony offered in the course of the hearing shoes that in similar projects in terms of their location and purpose, the State of Florida, Department of Environmental Regulation, has at times disclaimed its jurisdiction to require a permit and at other times granted permits.
Findings Of Fact Petitioner has a lease on a 160-acre tract of land along the northern boundary of Palm Beach County which has been zoned and used for several years to mine rock used in local road building operations. This tract of land is surrounded on the east, south and west by some 1,000 acres of land owned by Intervenor, Vanguard Farms. The Vanguard Farms property is used to grow citrus and sugarcane. The geology of the area in the vicinity of this application is such that some three feet of Everglades top soil overlies the limestone. The land surface is about fifteen (15) feet NGVD and the water level table fluctuates from twelve (12) to fourteen (14) feet NGVD for the dry and wet seasons. The Vanguard Farms property, which surrounds Petitioner's property in Palm Beach County, is a wet area bordered on the west by Lake Okeechobee and on the east by high ground water elevation. The area has an excess of rainfall over evapotranspiration and excess water will always be generated. In order to render Vanguard Farms arable it is necessary to drain the property and pump excess water from the land. The existing rock pit is some 6.7 acres in area. In order to economically mine rock from this pit it is necessary to remove stable overburden and expose the limerock to provide a stable platform on which the mining equipment can be operated. Since the water table is generally above the top of this limerock, it is necessary to remove water from the pit to expose the rock to be quarried. During earlier operations water from the pit dewatering was pumped into a canal which flowed onto intervenor's property. In the application now under consideration, no water from the dewatering operation will be pumped off the 160 acres controlled by Petitioner. A 25-acre holding pond has been constructed on this site as well as a 9-acre overflow pond. The holding pond was constructed by piling the overburden, and possibly some limerock, in a rectangular shape some ten feet above the surface (25 feet NGVD). This material with which this 10-foot high levee is formed was excavated with a dragline and shaped with a tractor. Condition 28, of the conditions proposed by Respondent for the grant of this application, requires all dikes, levees and berms behind which water is to be retained to be inspected for structural adequacy. A report of such inspection and steps necessary to correct the deficiencies noted shall be submitted, and the report is to be signed and sealed by a Florida registered professional engineer. Perimeter ditches on the north, south and east sides of Petitioner's lands will intercept seepage from the retention pond and surface waters flowing onto this property. These perimeter ditches are connected to the rock pit to which such waters will flow. Water moving westward across the property will be intercepted by the rock pit. Without the rock pit excess water generated in this area will flow onto Vanguard's adjacent land. This condition will exist when the pit is not in operation. However, when the pit is in operation, the water will be retained on Petitioner's property by those limiting conditions requiring the maintenance of water level elevation in the perimeter ditch to be kept either equal to or below the water level elevation of Vanguard Farms. Under this condition, all water will be routed between the pit and retention pond. Conditions of the permit which Respondent proposes to issue include that the water level in the retention pond not exceed 18.5 feet NGVD, that the holding pond be interconnected with the overflow pond, that the water level in the perimeter ditches be maintained by use of a flashboard riser at 10.8 feet NGVD, that dewatering operations cease upon notification by District staff of any adjacent property owners experiencing water-related problems, and that a direct connection between holding pond and rock pit be established for emergency discharge of water from the holding pond back into the rock pit.
The Issue The issue to be determined in this case is whether Respondents, United States Sugar Corporation (“USSC”), Sugar Farms Co-op (“SFC”), and Sugar Cane Growers Cooperative of Florida (“SCGC”) (collectively “the Applicants”) are entitled to the Everglades Works of the District permits (“WOD Permits”), issued to them by the South Florida Water Management District (“District”).
Findings Of Fact The Parties Audubon is a not-for-profit organization dedicated to restoring and conserving natural ecosystems, focusing on birds and their habitats. Audubon has a substantial interest in the protection of the Everglades and other ecosystems in the area. Audubon’s interest is affected by the proposed agency action because the WOD Permits authorize agricultural discharges that affect these ecosystems. The District is a Florida public corporation with the authority and duty to administer regulatory programs in chapter 373, and Florida Administrative Code Title 40E, including a program for regulating discharges from the Everglades Agricultural Area (“EAA”) into works of the District. The EAA is located south of Lake Okeechobee and comprises about 570,000 acres. The majority of EAA agriculture is sugarcane, with some row crops, such as radishes, leafy vegetables, and corn, and turf sod. During fallow periods, rice is also grown. The Applicants are owners and lessees of agricultural lands in the EAA. Background Some essential background for this case is set forth in rule 40E-63.011: The Everglades is a unique national resource. It has a high diversity of species, and provides habitat for large populations of wading birds and several threatened and endangered species, including wood storks, snail kites, bald eagles, Florida panthers, and American crocodiles. Large portions of the northern and eastern Everglades have been drained and converted to agricultural or urban land uses. Only 50% of the original Everglades ecosystem remains today. The remainder is the largest and most important freshwater sub-tropical peatland in North America. The remaining components of the historic Everglades are located in the Water Conservation Areas (WCAs) and Everglades National Park (ENP). ENP and Loxahatchee National Wildlife Refuge (WCA 1) are Outstanding Florida Waters, a designation which requires special protection for the resource. Large portions of the Everglades ecosystem have evolved in response to low ambient concentrations of nutrients and seasonal fluctuations of water levels. Prior to creation of the Everglades Agricultural Area (EAA), nitrogen and phosphorus were mainly supplied to large areas only in rainfall. Phosphorus is the primary limiting nutrient throughout the remaining Everglades. Sawgrass has lower phosphorus requirements than other species of Everglades vegetation. A substantial portion of EAA nutrients is transported to the remaining Everglades either in dissolved or in particulate form in surface waters. The introduction of phosphorus from EAA drainage water has resulted in ecological changes in substantial areas of Everglades marsh. These changes are cultural eutrophication, which is an increase in the supply of nutrients available in the marsh. The increased supply of phosphorus in Everglades marshes has resulted in documented impacts in several trophic levels, including microbial, periphyton, and macrophyte. The areal extent of these impacts is increasing. In 1988, the United States sued the District and the Florida Department of Environmental Regulation, now the Department of Environmental Protection (“DEP”), in federal court, alleging that the agencies failed to enforce Florida’s water quality standard for nutrients in waters of Loxahatchee Wildlife Refuge and Everglades National Park. The principal pollutant of concern was phosphorus. Audubon, USSC, and certain members of SCGC and SFC intervened in the federal case. In February 1992, the parties resolved their dispute through a settlement agreement approved by the federal court (“the Consent Decree”). The Consent Decree required the District and DEP to take action to meet water quality standards by December 31, 2002. At that time, the nutrient water quality standard was a narrative standard, prohibiting the discharge of nutrients so as to cause “an imbalance in natural populations of aquatic flora and fauna.” The Consent Decree directed the District to construct 34,700 acres of stormwater treatment areas (“STAs”) so that nutrient-laden surface water discharged from the EAA could be treated before discharge to the Everglades Protection Area (“EvPA”), which includes Loxahatchee Wildlife Refuge, Everglades National Park, and the Water Conservation Areas. STAs are large freshwater wetlands which remove phosphorus from the water column through physical, chemical, and biological processes such as sedimentation, precipitation, plant growth, and microbial activity. The first STAs were constructed and in operation in 1993. The Applicants operate in the S-5A Basin within the EAA. Their surface water is conveyed to STA-1W for treatment before being discharged to the EvPA. The Consent Decree required the District to initiate a regulatory program by 1992 to require permits for discharges from internal drainage systems (farms) in the EAA. The regulatory program was to be based on agricultural best management practices (“BMPs”). The goal of the program, as stated in the Consent Decree, was to reduce phosphorus loads from the EAA by 25 percent over the base period (1979-1988). In 1992, the District promulgated rule chapter 40E-63, which required EAA farmers to obtain WOD permits and to implement agricultural BMP plans. The BMP plans address fertilizer use and water management. Permittees must also implement a water quality monitoring plan. The rules require reduction of the total phosphorus loads discharged from the EAA Basin, as a whole, by 25 percent from historic levels. See Fla. Admin. Code R. 40E-63.101. If the EAA, as a whole, is in compliance, individual permittees are not required to make changes to their operations. See Fla. Admin. Code R. 40E-63.145(3)(d). If the 25 percent reduction requirement is not met, the rule contemplates that individual permittees in the EAA would have to reduce nutrient loads in their discharges. See Fla. Admin. Code R. 40E-63.145(3)(e).1/ The Consent Decree also required the District to obtain permits from the Department for discharges from the STAs to the EvPA and to conduct research and adopt rules to “numerically interpret” the narrative standard. In 1994, the Florida Legislature enacted the Everglades Forever Act (“the Act”), chapter 94-115, Laws of Florida, which is codified in section 373.4592. The Legislature authorized the district to proceed expeditiously with implementation of the Everglades Program. See § 373.4592(1)(b), Fla. Stat. The “Everglades Program” means the program of projects, regulations, and research described in the Act, including the Everglades Construction Project. The Everglades Construction Project involved the construction of 40,452 acres of STAs, which is 5,350 acres more than was required by the federal Consent Decree. The Act acknowledged the BMP regulatory program for the EAA that the District had established in rule chapter 40E-63, and stated: Prior to the expiration of existing permits, and during each 5-year term of subsequent permits as provided for in this section, those rules shall be amended to implement a comprehensive program of research, testing, and implementation of BMPs that will address all water quality standards within the EAA and Everglades protection Area. See § 373.4592(4)(f)2., Fla. Stat. The Act required DEP to issue permits to the District to construct, operate, and maintain the STAs. See § 373.4592(9)(e), Fla. Stat. The Act required development of a numeric water quality phosphorus standard for the EvPA by 2003. See § 373.4592(4)(e), Fla. Stat. The Act set the goal of achieving the phosphorus standard in all parts of the EvPA by December 31, 2006. In June 1995, modifications were made to the Consent Decree. The deadline for achieving water quality standards in the EvPA was changed from December 31, 2002, to December 31, 2006. The STAs were increased from 34,700 acres to 40,452 acres. The chronological developments outlined above indicate the intent of the Legislature and the parties to the Consent Decree to conform state law and the Consent Decree to each other. In 2001, DEP initiated rulemaking that lead to its adoption of the Phosphorus Rule, rule 62-302.540, in 2003. The rule set a numeric phosphorus criterion for the EvPA of 10 parts per billion (“ppb”), applied through a four-part test in which attainment is determined separately for “unimpacted” and “impacted areas” of the EvPA. See Fla. Admin Code R. 62- 302.540(4). In conjunction with this rulemaking, the DEP and District developed the Everglades Protection Area Tributary Basins Long Term Plan for Achieving Water Quality Goals (“Long- Term Plan”) in March 2003. The Long-Term Plan provided remedial measures and strategies divided into pre-2006 projects and post- 2006 projects. The pre-2006 projects included structural and operational modifications to the existing STAs, implementation of agricultural and urban BMPs in areas outside the EAA or C-139 basins, and construction of several restoration projects congressionally mandated by the Comprehensive Everglades Restoration Plan. Modeling of treatment capabilities of the STAs after implementation of the pre-2006 projects predicted that the 10 ppb standard for phosphorus could be achieved, but not consistently. Therefore, the Long-Term Plan required the District to identify and evaluate methods to improve phosphorus reductions, and if the phosphorus criterion was not achieved by December 31, 2006, to implement post-2006 modifications and improvements. The post- 2006 strategies include projects to expand and improve the STAs. They do not include changes to the BMP program. In 2003, the Legislature substantially amended the Act. It incorporated the Long-Term Plan into the Act, finding that it “provides the best available phosphorus reduction technology based on a combination of the BMPs and STAs.” § 373.4592(3)(b), Fla. Stat. The Long-Term Plan contemplates maintenance of the BMP program in the EAA, with refinements derived from BMP research. Recent Conditions and Events As previously stated, chapter 40E-63 requires the total phosphorus load from the EAA to be reduced by not less than 25 percent from historic levels. Since full implementation of the BMP regulatory program, annual phosphorus loads have been reduced by approximately 50 percent. Despite the efforts and projects undertaken, the phosphorus standard was not being achieved as of December 31, 2006, in all parts of the EvPA. In 2007, the DEP issued a permit to the District for discharges from the STAs to the EvPA (referred to as the “Everglades Forever Act” or “EFA permit”). The permit required the District to design and construct several regional water management projects, including structural enhancements to STA-1W, and the construction of 6,800 acres of additional STAs. The permit and its compliance schedules provided interim relief through 2016 from the water quality based effluent limitation (WQBEL) necessary to achieve the 10 ppb phosphorus standard. The 2007 EFA permit was not challenged by Audubon or any other entity. The District, DEP, and the United States Environmental Protection Agency began working together in 2010 to develop new strategies for achieving compliance with the phosphorus standard in the EvPA. The agencies determined that compliance could be achieved by expanding the STAs by 7,300 acres (6,500 acres would be added to STA-1W) and constructing flow equalization basins to store up to 110,000 acre feet of stormwater runoff. These basins are designed to attenuate peak flows into the STAs in order to improve the processes that remove phosphorus. In September 2012, DEP issued the District a new EFA permit, which authorized continued operation of the District’s S-5A pump station, STA-1W, and the related conveyance systems by which stormwater runoff from the S-5A Basin is ultimately discharged to the EvPA. The permit was issued with a Consent Order, requiring the District to expand STA-1W by 6,500 acres of effective treatment area in accordance with a timeline and the District’s Restoration Strategies. The 2012 EFA Permit and Consent Order were not challenged by Audubon or any other entity. In 2013, the Legislature amended the Act again. The Act’s reference to the Long-Term Plan was revised to include the District’s Restoration Strategies Regional Water Quality Plan, which called for expanding the STAs and constructing flow equalization basins. See § 373.4592(2)(j), Fla. Stat. The Legislature added a finding that “implementation of BMPs, funded by the owners and users of land in the EAA, effectively reduces nutrients in waters flowing into the Everglades Protection Area.” See § 373.4592(1)(g), Fla. Stat. The 2013 amendments indicated the Legislature’s intent to codify into law the strategies developed by the District and other regulatory agencies to achieve water quality standards in the EvPA. Those strategies do not materially change the BMP program in the EAA. The Act and the rules of the District create programs for achieving restoration of the EvPA that rely heavily on the STAs. Over the years, the STAs have repeatedly been enlarged and enhanced. In contrast, the requirement for farmers in the EAA to reduce their phosphorus loading by 25 percent has not changed in 21 years. It is beyond the scope of this proceeding to question the wisdom of the programs that have been established by statute and rule. Whether Additional Water Quality Measures Are Required A principal dispute in this case is whether the WOD Permits must include additional water quality measures to be implemented by the Applicants. Section 373.4592(4)(f)4. provides that, as of December 31, 2006, all EAA permits shall include “additional water quality measures, taking into account the water quality treatment actually provided by the STAs and the effectiveness of the BMPs.” Audubon asserts that the requirement for additional water quality measures has been triggered. The District does not interpret the statute as requiring additional water quality measures under current circumstances. The interpretation of the statute is primarily a disputed issue of law and is addressed in the Conclusions of Law. There, it is concluded that additional water quality measures are not required. Whether the BMP Plans are Adequate Audubon contends that the WOD Permits should be denied because the Applicant’s existing BMP plans are not “tailored” to particular soils, crops, and other conditions. This contention is based on section 373.4592(4)(f)2.c., which states in relevant part: BMPs as required for varying crops and soil types shall be included in permit conditions in the 5-year permits issued pursuant to this section. Audubon showed that the Applicants have similar BMP plans for the thousands of acres covered in the three WOD Permits, and contends that this similarity proves that BMPs are not being tailored to specific farm conditions. However, soils and crops are similar throughout the EAA. The soils of the EAA are almost entirely muck soils and the primary crop is sugarcane with some corn or other vegetable rotated in. The Applicants use many of the same BMPs because they have similar soils and grow similar crops. There are three main categories of BMPs implemented in the EAA: nutrient and sediment control BMPs, particulate matter and sediment control BMPs, and water management BMPs. See Fla. Admin. Code R. 40E-63.136, Appendix A2. The BMPs proposed by the Applicants are based on research in the EAA and recommendations specifically for EAA soils and the crops grown there. The Applications do not identify the specific BMPs that will be implemented, but only the number of BMPs that will be selected from each of the BMP categories (i.e., sediment control). The Applicants must use BMPs on the District’s list of approved BMPs unless an alternative BMP is requested and approved. The lack of greater detail was explained as necessitated by the need for flexibility during the life of the permit to adapt BMPs to varied crops and conditions. Audubon does not believe the BMP plans are tailored enough, but there is no rule criterion for determining how tailored BMP plans must be, except they must achieve the overall goal of reducing phosphorus loading in discharges from the EAA by at least 25 percent. This goal is being achieved.2/ Audubon did not show that any particular BMP being used by an Applicant was the wrong BMP for a particular soil and crop, or identify the BMP that Audubon believes should be used. Audubon failed to prove that the Applicants’ BMP plans do not meet applicable requirements. Whether the Applications Are Complete Audubon contends that the WOD Permits must be denied because the Applications are incomplete. Many of Audubon’s completeness issues deal with minor discrepancies of a type that are more appropriately resolved between the District and applicants, not violations of criteria that are likely to affect a third party’s interest in environmental protection. Rule 40E-63.130 lists the requirements for a permit application for activities in the EAA Basin. An Application Guidebook is incorporated into chapter 40E-63, which contains instructions for completing the application. For applications to renew a permit, the practice of the District is to not require the resubmittal of information that was previously submitted to the District and which has not changed. The Application Guidebook explains this practice. The Applicants supplemented their applications at the final hearing to provide information that Audubon claimed was omitted from the Applications.3/ Audubon contends that the Applications are incomplete because some application forms are not dated and other forms are not signed by appropriate entities. The District explained its rule interpretation and practices associated with the forms. Additional signatures and dates were submitted at the final hearing. Audubon failed to demonstrate that the Applications are incomplete based on the identity of the persons who signed application forms or the lack of dates. Audubon contends the Applications are incomplete because copies of contracts or agreements are not included as required by rule 40E-63.132(3). Audubon failed to prove that contracts and agreements exist that were not included. Audubon contends the Applications are incomplete because they do not contain a completed Form 0779, entitled “Application For A Works Of The District Permit,” as required by rule 40E-63.132(5). In some cases, the information for Form 0779 had been previously submitted and was unchanged, so the District did not require it to be resubmitted for the permit renewal. Additional information was provided at the final hearing. Audubon failed to prove that the Applications are incomplete based on missing information on Form 0779. Audubon contends that the Applications are incomplete because documentation regarding leased parcels was missing. Pursuant to rule 40E-63.130(1)(a), individual permit applications must be submitted by the owner of the land on which a structure is located and any entity responsible for operating the structure, and the permit application must include the owners of all parcels which discharge water tributary to the structure. Applications may be submitted by a lessee if the lessee has the legal and financial capability of implementing the BMP Plan and other permit conditions. The District explained that when applications are submitted by a lessee who will be the permittee or co-permittee, the District requires the lessee to be a responsible party for the entire term of the permit, which is five years. If the lessee is a not a co-permittee, the District does not require information about the lease and does not require the lessee’s signature. If the lessee is a co-permittee, but the lease expires during the term of the permit, the District requires the applicant to modify the permit when the lease expires. Audubon failed to prove that the Applications are incomplete based on lease information Audubon contends that the Applications are incomplete because they fail to show that the Applicants participated in an education and training program as required by rule 40E- 63.136(1)(g). The preponderance of the evidence shows that the Applicants participated in education and training programs. Audubon failed to prove that the Applications are incomplete for any of the reasons raised in its petition for hearing or advanced at the final hearing. Water Quality Standards in the EAA Audubon presented some evidence of algal accumulations in ditches and canals, but the evidence was insufficient to prove the Applicants are violating water quality standards applicable in the EAA. Summary Audubon failed to carry its burden to prove that the Applicants are not entitled to the WOD Permits.
Recommendation Based on the foregoing Findings of Facts and Conclusions of Law, it is RECOMMENDED that South Florida Water Management District issue Permit Nos. 50-00031-E, 50-00018-E, and 50-00047-E. DONE AND ENTERED this 10th day of February, 2014, in Tallahassee, Leon County, Florida. S BRAM D. E. CANTER Administrative Law Judge Division of Administrative Hearings The DeSoto Building 1230 Apalachee Parkway Tallahassee, Florida 32399-3060 (850) 488-9675 Fax Filing (850) 921-6847 www.doah.state.fl.us Filed with the Clerk of the Division of Administrative Hearings this 10th day of February, 2014.
The Issue Whether FDOT has provided reasonable assurances that the activities it proposes to conduct pursuant to proposed District SWM Permit Application No. 940606-10, WRM Permit Application No. 940606-2-D and modification to ROW Permit No. 2584 will comply with the relevant permit criteria set forth in Chapters 373 and 403, F.S., and applicable rules and criteria promulgated thereunder.
Findings Of Fact THE PARTIES Petitioner, 1000 Friends of Florida (1000 Friends), is a not-for-profit, tax exempt membership corporation, organized and existing under the laws of the State of Florida. The principal office of 1000 Friends is 926 East Park Avenue, Tallahassee, Florida 32314 and it also maintains an office at 3305 College Avenue, Ft. Lauderdale, Florida 33314. Petitioner, Florida Bay Initiative, Inc. (FBII), is an entity incorporated under the laws of Florida with its principal office located at 250 Australian Avenue South, Suite 500, West Palm Beach, Florida 33401. Petitioner, the Florida Keys Fishing Guides Association, is an association of sport fishing guides who live in the Florida Keys and is headquartered at 138 Royal Lane, Islamorada, Florida 33036. Petitioner, Michael Collins, is a private individual. His address is 138 Royal Lane, Islamorada, Florida 33036. Petitioner, Charles W. Causey, is a private individual. His address is Post Office Box 448, Islamorada, Florida 33036. Petitioner, the Florida Keys Concerned Citizens Coalition (FKCC), is a not-for-profit Florida corporation whose address is West Shore Drive, Big Pine Key, Florida 33043. Petitioner, AG Intus, Inc., filed a Notice of Voluntary Dismissal on August 9, 1996. DOAH Case 95-5524, the proceeding filed by Intus, was previously consolidated with the other cases to this proceeding. On August 12, 1996, the Intus case was severed from this proceeding and the Intus hearing cancelled. Respondent, the South Florida Water Management District (the District or SFWMD), is a public corporation in the State of Florida existing by virtue of Chapter 25270, Laws of Florida, 1949, and operating pursuant to Chapter 373, F.S., and Title 40E, F.A.C., as a multi-purpose water management district, with its principle office in West Palm Beach, Florida. Respondent, the Florida Department of Transportation (FDOT), is an agency of the State of Florida. Its District Six address is 1000 N.W. 111th Avenue, Miami, Florida 33172. Intervenor, Monroe County, is a political subdivision of the State of Florida. For the purposes of this proceeding the address for Monroe County is c/o Apgar and Pelham, 909 East Park Avenue, Tallahassee, Florida 32301. The District, FDOT and Monroe County did not object to the standing of the Petitioners at the formal hearing and represented that they will not object to the standing in the event of an appeal. Based on the representations of the Respondents, the Petitioners were not required to put on a case as to their standing. THE THREE PERMIT APPLICATIONS FDOT has applied to the District for a Wetland Resource Management (WRM) permit, a Surface Water Management (SWM) permit, and a Right of Way (ROW) occupancy permit. On June 6, 1994, the Applicant submitted applications for surface water management and wetland resource management permits for the purpose of widening and modifying this 20.4 mile stretch of U.S. 1. The surface water management permit application is identified as Application No. 940606-10. The wetland resource management permit application is identified as Application No. 940606-2-D. On October 24, 1995, the District issued Staff Reports on Permit Application No. 960606-10 and Permit Application No. 94060-2-D. These Staff Reports recommended issuance of the permits subject to general and special conditions as specified therein. An addendum to the staff report was issued November 3, 1995. On September 27, 1994, the Applicant submitted a request to modify its existing ROW Occupancy Permit to enable it to replace the bridge where U.S. 1 crosses the C-111 Canal. The land encompassed by the ROW occupancy permit challenged in this proceeding is located in Section 16 and 17, Township 59 South, Range 39 East, Dade County, Florida. A draft right-of-way occupancy permit with standard limiting and special conditions was produced as part of a package that went to the Governing Board and others. The proposed authorization for use of the ROW is for the following: REMOVAL OF EXISTING U.S. HIGHWAY 1 BRIDGE AND REPLACEMENT WITH A NEW FIXED BRIDGE. PROJECT INCLUDES CONSTRUCTION OF A NEW SERVICE/ACCESS ROAD, 2 DETENTION PONDS, 2 CATCH BASINS, 2-15" R.C.P. OUTFALLS, BOAT RAMP WITH LOADING DOCK, PARKING AREA, PEDESTRIAN GATE AT S-197, FENCING AND WILDLIFE CROSSING ALL WITHIN THE NORTH AND SOUTH RIGHT OF WAY OF C-111 (STATION 938+00 - 955+00). The draft right-of-way occupancy permit modification, identified as “SFWMD PERMIT NO. MOD 2548," should correctly be identified at “SFWMD PERMIT NO. MOD 2584.” The numbers “8” and “4” were inadvertently transposed. STIPULATIONS AS TO APPLICABLE LAW The parties have accurately set forth the applicable permitting criteria and the appropriate Basis of Review in their prehearing stipulation. CRITERIA FOR ROW PERMIT Rule 40E-6.301, Florida Administrative Code, provides, in pertinent part, as follows: In determining whether an occupancy permit should be issued, the District shall consider whether the proposed activity: interferes with the present or future construction, alteration, operation or maintenance of the works of the District; is consistent with the policy and objectives of Chapter 373 F.S., the legislative declaration of policy contained in Section 373.016, F.S. and the state water policy, Chapter 17-40, F.A.C.; has an actual or potential negative impact upon environmentally sensitive areas, which include: wetlands; endangered or threatened species habitat; aquatic preserves; outstanding Florida waters; federal, state and privately owned parks and wildlife management areas; designated areas of critical state concern; lands purchased by federal, state and local governments for the purpose of environmental protection, water resource protection and esthetics; and lands which contain native terrestrial plant species in significant amounts. Environmentally sensitive areas include areas on and off- site that are affected by activities which occur on, or are initiated from, the District’s works; degrades water quality within the receiving water body or fails to meet the provisions of Ch. 373, F.S., the state water policy, and Ch. 40E, F.A.C.; involves a discharge of wastewater from a new wastewater source or an increased discharge from an existing wastewater source; will discharge debris or aquatic weeds into District lands or works or cause erosion or shoaling within the works of the District; is supported by financial assurances, which will ensure that the proposed activity will be conducted in accordance with Chapter 373, F.S., and Chapter 40E-6, F.A.C.; presents an increased liability risk to the District; meets the general and specific criteria in the Basis of Review which is incorporated by reference in Rule 40E- 6.091, F.A.C.; interferes with actual or potential public use of the District’s works or public, recreational or other facilities not within the District’s works; is consistent with local zoning and other private land uses in the area; interferes with the quality or quantity of a public or private water supply; meets applicable criteria in Chapters 40E-61 and 40E-62, F.A.C.; ROW occupancy permits typically have standard limiting conditions which are incorporated as part of the permit. The permit may also have special limiting conditions. CRITERIA FOR PERMITTING THE SWM SYSTEM Rule 40E-4.301(1), Florida Administrative Code, contains the following criteria that, at the times pertinent to this proceeding, were used by SFWMD in determining whether to permit a surface water management system: In order to obtain or modify a permit under this chapter, an applicant must give reasonable assurances that the surface water system: provides adequate flood protection and drainage, without causing over- drainage, will not cause adverse water quality and quantity impacts on receiving waters and adjacent lands regulated pursuant to Chapter 373, F.S., will not cause discharges which result in any violations, in surface waters of the state, of the standards and criteria of chapter 17-302, F.A.C., will not cause adverse on-site or off-site impacts on surface and groundwater levels and flows, including impacts to sources of water supply and wetland hydrology, will not cause adverse environmental impacts, can be effectively operated and maintained, will not adversely affect public health and safety, is consistent with the State Water Policy, chapter 17-40, F.A.C., for a DRI with a signed Preliminary Development Agreement with the Florida Department of Community Affairs, pursuant to section 380.06(8), F.S., provides a surface water management system for that portion of the site approval for development which is able to operate separately from the surface water management system for the balance of the project site and still meet applicable District criteria. meets any applicable basin criteria in chapter 40E-41, F.A.C., will not otherwise be harmful to the water resources of the District, will not interfere with the legal rights of others as defined in subsection 17-40.401(8), F.A.C., is not against public policy, will meet general and specific criteria in the document described in subsection 40E-4.091(1)(a), F.A.C., (0) will meet criteria for isolated wetlands, which are found in Appendix 7 of the document described in rule 40E- 4.091(1)(a), F.A.C., (p) will meet the criteria for above ground impoundments, which are found in Appendix 6 of the document described in rule 40E-4.091(1)(a), F.A.C. The SFWMD has adopted certain procedures and criteria contained in a document, referred to as “Basis of Review for Surface Water Management Permit Applications Within The South Florida Water Management District” (BOR). Subsection 40E-4.091(1)(a), F.A.C. incorporates this document by reference into Chapter 40E-4, F.A.C. The BOR is a document that is “described in subsection 40E-4.091(1)(a), F.A.C.,” within the meaning of Rule 40E-4.301(1), F.A.C. The BOR establishes a rebuttable presumption that water quality criteria are met through specified volumetric retention and detention requirements. These performance based criteria are designed to be flexible. CRITERIA FOR THE WRM PERMIT In 1992 DEP entered into an Operating Agreement with the District, which delegated to the District responsibility for issuing wetland resource management (WRM) permits, which are required for dredge and fill activities in wetlands. Both DEP and the District implement the same wetland resource permit and MSSW permit rules. The District agrees with DEP's interpretation and application of the WRM permitting rules and non-rule policy, and applies the same when issuing such permits. Section 403.918, Florida Statutes (1991), provides the pertinent criteria that must be applied by the District in determining whether to grant or deny the WRM permit. That criteria requires the applicant to provide reasonable assurance that water quality standards will not be violated. In addition, for projects in OFW, the applicant must provide reasonable assurance that the project is clearly in the public interest. THE PUBLIC INTEREST TEST The District is required to balance the following criteria, found at Section 403.918(2)(a), Florida Statutes (1991), in determining whether a project is clearly within the public interest: Whether the project will adversely affect the public health, safety, or welfare or the property of others; Whether the project will adversely affect the conservation of fish and wildlife, including endangered species, or their habitats; Whether the project will adversely affect navigation or the flow of water or cause harmful erosion or shoaling; Whether the project will adversely affect the fishing or recreational values or marine productivity in the vicinity of the project; Whether the project will be of a temporary or permanent nature; Whether the project 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. MITIGATION If the applicant is unable to otherwise meet the public interest test, the District shall, pursuant to Section 403.918(2)(b), Florida Statutes, “consider measures proposed by or acceptable to the applicant to mitigate adverse effects which may be caused by the project . . .” The District thereafter re-evaluates the project to determine whether the project, as mitigated, meets the public interest test. The criteria for mitigation is found in Chapters 373 and 403, Florida Statutes, Title 40 E (including the Basis of Review) and Rule 62-312, Florida Administrative Code. Rule 62-312.330, Florida Administrative Code, states the general criteria for evaluating mitigation proposals as follows: The goal of the mitigation proposal shall be to offset the expected adverse impact of the project that have resulted in the project being deemed unpermittable such that the resulting project with mitigation is not contrary to the public interest or, in the case of Outstanding Florida Waters, is clearly in the public interest. Each project must be separately evaluated to determine whether the proposed mitigation is sufficient. Rule 62-312.340, Florida Administrative Code, provides guidelines that are to be used in evaluating proposed mitigation projects. GENERAL DESCRIPTION OF THE PROJECT AREA FDOT proposes to widen a 20.4 mile portion of U.S. 1 in southern Dade County and northern Monroe County. Approximately seven miles of the project area is in Monroe County and approximately thirteen miles is in Dade County. The northern terminus of the project is the intersection of U.S. 1 and Card Sound Road, which is located in Dade County south of Florida City. The southern terminus of the project is the intersection of U.S. 1 and Abaco Road on Key Largo in Monroe County. The corridor of the proposed project passes through Sections 6, 7, 16, 18, 21, 27, 28, Township 59 South, Range 39 East; Sections 24, 25, 36, Township 58 South, Range 38 East; Sections 16, 19, 30, 31, Township 58 South, Range 39 East, Sections 16, 30, 31, Township 60 South, Range 40 East; Sections 25, 26, Township 60 South, Ranges 39 East, Dade and Monroe Counties, Florida. U.S. 1 is the main highway between northern Monroe County and southern Dade County. The only other road between Monroe County and Dade County is Card Sound Road. The Florida Keys is designated as an Area of Critical State Concern, pursuant to Section 380.0552, Florida Statutes. The Dade County portion of the road, north of the C- 111 canal, lies within typical Everglades habitat, which is classified as environmentally protected lands of Dade County. Most of the project corridor in Dade County is part of or adjacent to the Everglades National Park. Valuable wetlands exist throughout the project corridor. The following bodies of water will receive discharges if the surface water management system is permitted: C-111 Canal, Jewfish Creek, Lake Surprise, Blackwater Sound, Barnes Sound, Little Blackwater Sound, Long Sound, Manatee Bay, Sarge Lake, andManatee Creek. The receiving bodies of water are Outstanding Florida Waters (OFWs) or are connected to OFWs. THE EXISTING ROADWAY As it presently exists in the project area, U.S. 1 is a two lane undivided highway with two passing zones that are each one mile in length. Each travel lane on the existing facility is twelve feet wide. The existing shoulder on either side of the road consists of four feet of pavement and six feet of grassed area. FDOT Exhibit 7 accurately depicts the existing roadway typical section. Exotic vegetation, generally limited to the areas immediately adjacent to the highway, exist throughout the project corridor. These exotic species are present because FDOT has failed to properly maintain its right of way. A clear zone is an unobstructed area that includes the shoulder of the roadway and typically extends beyond the shoulder. The purpose of the clear zone is to provide a driver who has lost control of his or her vehicle a sufficient clear recovery area to regain control of the vehicle so that it can be maneuvered back onto the road. The clear zone for the existing road is inadequate to provide a safe recovery area. There is at present a two lane bridge over Manatee Creek, a two-lane bridge crossing the C-111 Canal, a bascule bridge, which is a drawbridge, over Jewfish Creek, and a two lane causeway through Lake Surprise. The two existing passing zones are located in Dade County. The first is south of U.S. 1’s intersection with the C-111 canal between mile markers 113-115. The second passing lane is approximately four miles south of the northern terminus of the project between mile markers 120-122. Each existing passing zone is undivided and consists of two northbound lanes and two southbound lanes, with each travel lane being twelve feet in width. The shoulders in the passing zones are the same as for the typical section. A surface water management (SWM) system is defined by Rule 40E-4.021(5), Florida Administrative Code , as being "the collection of devices, improvements or natural systems whereby surface waters are controlled, impounded, or obstructed.". There is no surface water management system presently associated with the road. The roadbed is elevated approximately five feet above mean sea level according to the National Geodetic Vertical Datum and was constructed on the old railroad bed of the Florida East Coast Railroad. No hydrologic culverts have been placed within the roadbed. Consequently, surface water flow between the eastern and western sides of the road north of the C-111 Canal has been cut off. C-109 AND C-111 CANALS In the 1960's, the C-109 and C-111 canals were constructed as part of an overall water management system in the area. As a result of the roadbed and the canals, water has been impounded on the western side of U.S. 1 at a level higher than on the eastern side. Due to cutoff of waterflow by the roadbed embankment, historic freshwater flow between the eastern and western sides of the project area has been restricted, which has resulted in an adverse impact on the Everglades ecosystem north of the C-111 Canal. The restricted water flow has resulted in less fresh water being available for shorter periods of time. Consequently, aquatic life has had reduced opportunities to develop. The restricted flow also has impeded the ability of aquatic life to reach freshwater areas during times of drought. On the east side of the road marine conditions have displaced what naturally should be freshwater conditions. PROJECT HISTORY While FDOT has been aware of traffic safety and hurricane evacuations concerns on the roadway for a long time, the current project originated in 1986 when Monroe County identified this project as a need in its 1986 Comprehensive Plan. Pursuant to agency practice, the proposed project was incorporated into FDOT's five year work program and a study was performed pursuant to FDOT’s Project Development and Environment (PD&E) Manual. FDOT's PD&E manual describes the process by which FDOT determines whether to construct or improve a road. The PD&E process includes an Environmental Impact Statement (EIS) to analyze existing conditions, assess the need for improvement, and develop alternatives. A Draft EIS is performed and circulated for comment to governmental agencies and the public. Based upon comments and further review a Final EIS is prepared. Metric Engineering ("Metric") began the PD&E study of the project in 1988 pursuant to a contract with FDOT. Metric identified seven factors which it concluded supported the need for the project. First, the improved corridor would improve the linkage between the four lane road at the northern terminus and the four lane road at the southern terminus. Second, the project would improve navigation by replacing the existing bascule bridge at Jewfish Creek. Third, the project would improve the level of service for the road. Fourth, the project would improve the safety of the road. Fifth, the project would improve the clearance time for hurricane evacuation. Sixth, the project was consistent with the long range transportation plans adopted by Monroe County. Seventh, the project would accommodate increased traffic, which can be expected with or without the project. Based on the needs evaluation, Metric performed a corridor analysis to determine the best way to get from Florida City to Key Largo, including improving only Card Sound Road, improving only U.S. 1, or improving a combination of the two. Metric concluded that the best resolution was to improve the project corridor. Metric also analyzed various alternatives in an effort to reduce the size of the typical section of the roadway in the U.S. 1 corridor and thereby minimize environmental impacts of the project. Because of concerns from Everglades National Park that no aspects of the project construction occur within its boundaries, FDOT agreed to conduct all construction east of FDOT's existing right of way line. The conclusions of the Metric studies were memorialized in a Final EIS and Final Engineering Report published in 1992. Conclusions regarding alternatives and project needs were then incorporated into the permit application and have continued to be updated. The 1992 version of the project was for a four lane roadway with four lane bridges throughout the project corridor. Subsequent to its June 6, 1994, permit applications to the District for a four lane roadway, FDOT went through an extensive process of providing the District with additional information in an effort to provide the District with the necessary reasonable assurance that the proposed project would comply with the permit criteria. The final series of modifications contained the three lane alternative, which will be described in detail below and is now the subject of this proceeding. The three lane proposal is a compromise that FDOT agreed to in an effort to minimize the direct, secondary, and cumulative impacts of the project. Monroe County passed Resolution No. 315-1995 on September 7, 1995, asking FDOT to build a three-lane road on a four-lane embankment. This resolution provided, in part, that “. . . Monroe County finds that the '3-lane alternative' as described in the Statement of Agency Commitments is the most viable proposal of those considered, because it balances the needs for a widened highway with safeguards designed to address secondary impacts.” The secondary impacts referred to in the resolution included concerns that two southbound lanes would result in more growth. The rationale behind the resolution was that more growth would result from two southbound lanes than from one southbound lane with the proposed passing zones. In response to the request of Monroe County and in response to a similar request made by the District, FDOT notified the District by letter dated September 5, 1996 of FDOT's decision to redesign the project to change the roadway from four to three lanes. FDOT HAS MINIMIZED THE IMPACTS OF THE PROJECT During the PD&E process prior to permit application FDOT studied project needs and alternative alignments, and conducted corridor analyses. FDOT originally considered a proposal that included approximately 250 acres of wetlands impacts. At the District's suggestion, FDOT revised its proposal prior to the permit application to reduce the wetland impacts and project footprint. The application submitted contained approximately 165 acres of impact. FDOT changed the typical section of the proposed roadway again after substantial interagency coordination in an effort to reduce wetlands impacts even further. FDOT agreed to reduce the footprint by changing the design of the median from 22 feet and a Jersey barrier (which is a minimum barrier) to 20 feet with a tri-beam rail barrier. The more substantial barrier was added because the median was narrowed. Additionally, instead of ten-foot paved shoulders on each side of the median, FDOT would use two-foot paved shoulders with sixteen feet of grass in the middle. These minimization efforts resulted in a wetland impacts decrease from 164 acres to 149.07 acres, the current impact of the project. Avoidance, or choosing alternate routes to avoid impacts to wetlands, was not a possible option because only wetlands and open waters exist between the northern and southern terminus of the project. FDOT explored all reasonable alternatives to the proposed project, including a two lane alternative proposed by a consultant for FBII. As discussed below, FDOT did not adopt the two-lane alternative, because the alternative did not address all of FDOT's identified needs for the project. FBII prepared a report with a two-lane alternative to the proposed project. FBII's original proposal included one 12-foot northbound lane with a 10-foot paved shoulder covered with thermoplastic rumble strips to deter vehicular use of the shoulder. In the southbound direction, FBII proposed a 12-foot travel lane with a 4-foot paved shoulder, essentially the same as currently exists. That proposal was analyzed by Metric Engineering on behalf of FDOT. FDOT rejected the FBII alternative for several reasons. First, though the 10-foot northbound shoulder theoretically may be used by cars during hurricane evacuation, removal of the rumble strips would be impractical due to lack of time to do so under threat of a hurricane, and due to the costs involved. It would be unrealistic to require people to otherwise drive over the rumble strips, without removal, because they are designed to prevent such access. Using the 10-foot shoulder during an evacuation would result in there being no shoulder area to remove accident vehicles from the roadway which would otherwise threaten to restrict the flow of traffic or cease it altogether. The reduced width of the shoulder lane below the standard 12-foot lane would also decrease the flow of evacuees. FBII's proposal for a two-lane fixed-height bridge at Jewfish Creek would not completely eliminate rear-end collisions at the bridge. The two-lane alternative proposed by FBII is not a signed and sealed cross section. The proposal by FBII does not include the area necessary for a SWM system or for clear zones. FBII did not do an analysis to determine whether its proposal complies with pertinent FDOT roadway and traffic design standards or with pertinent highway safety and improvement standards. The FBII proposal does not account for removal of the Lake Surprise causeway or construction related impacts from barge traffic. FBII did not do a wetlands survey to determine the impact of its two-lane proposal. At the Final Hearing, Petitioners presented for the first time a new proposal to use "flexible diverters" to pave a third northbound lane and to block that lane from travel traffic with poles. However, no research was conducted into the feasibility of such a proposal, nor was it adequately thought out. Such a use of "flexible diverters" is unprecedented in FDOT's history, is impractical to implement, and would violate FDOT's design standards contained in its Manual on Uniform Traffic Control Devices. Petitioners also presented for the first time at the Final Hearing a proposal to add an 8 to 10 foot paved northbound shoulder which could be converted to a travel lane with traffic control cones in the event of an evacuation. This plan is also not feasible, because the resulting lanes would not be wide enough to safely accommodate evacuating traffic, and because the contradiction between existing road striping and the placement of cones would likely cause accidents, which would halt evacuation. The proposals submitted by FBII do not sufficiently improve hurricane evacuation or traffic safety and, consequently, are not acceptable alternatives to the project. FDOT can do nothing else to minimize the impacts of the project and still address the needs for the project. Minimization of wetlands impacts was accomplished to the greatest extent possible. FDOT has proposed mitigation to offset the impacts that could not be avoided. THE PROPOSED PROJECT - IN GENERAL STIPULATION AS TO DESIGN AND CONSTRUCTION Petitioners stipulated that the design and construction specifications of the roadway proposed to be permitted in this case comply with all applicable design and construction standards for structural integrity, and adequately describe the three-lane divided roadway proposed to be constructed on a four-lane roadbed/embankment. PROPOSED LANES, SHOULDERS, AND MEDIAN FDOT proposes to widen the roadway in the project area to a three lane divided roadway with two northbound lanes and one southbound lane, plus three passing zones. The proposed project will be constructed on a four lane roadbed embankment. FDOT does not presently have plans to add the fourth lane to this roadway. FDOT Exhibit 8 contains an accurate description of the proposed typical section of the roadway. The typical section will consist of two twelve-foot northbound lanes with a six-foot paved shoulder and a four foot stabilized area adjacent to the paved shoulder; a twenty-foot median consisting of a two-foot paved shoulder, sixteen feet of grass and a tri-beam guardrail in the middle as a separator; and one twelve-foot southbound lane with an eight-foot paved shoulder. The proposed typical section also includes a storm water management system that will be described in more detail below. The proposed typical section includes a clear zone thirty feet in width, which is adequate. THE THREE PASSING ZONES The existing passing zone located in Dade County between mile markers 113 and 115 is one mile in length. FDOT proposes to alter this passing zone to 1.44 miles in length. The existing passing zone located in Dade County between mile markers 120 and 122 is also one mile in length. FDOT proposes to alter this passing zone to 2 miles in length. In addition, FDOT proposes to construct a 1.5 mile long passing zone between mile markers 110 and 112 in Monroe County. If permitted, the proposed project will include 2 passing zones in Dade County and 1 passing zone in Monroe County, for a total of 3 passing zones. The total length of the passing zones will equal 4.94 miles. ELEVATION There are no plans to change the elevation of the existing roadway. HYDROLOGIC CULVERTS The project contemplates the construction of 25 hydrologic culverts north of the C-111 Canal. These culverts will remain capped until further hydrological studies are completed and input from all concerned regulatory agencies can be obtained. It has not yet been determined how these culverts will be utilized to maximize the improvement to the ecosystem north of the C-111 Canal. WILDLIFE CROSSINGS INCLUDING THE C-111 BRIDGE The project contemplates the construction of three wildlife crossings north of the C-111 Canal in Dade County with fencing designed to funnel wildlife through the crossing. These crossing, sometimes referred to in the record as “panther crossings” are located between mile markers 118-119, 122-123, and 126-127 and will be constructed as overland bridges. In addition, the replacement bridge over the C-111 Canal (located between mile markers 116-117 in Dade County) is intended to serve as a wildlife crossing and will also employ fencing to funnel wildlife through the crossing. All four of these structures will be constructed as four-lane bridges, but will be striped for three lanes with rumble strips on the southbound fourth lane to discourage vehicular traffic in that lane. There will be an eight foot outside shoulder. FDOT proposes to construct 18 culverts south of the C-111 Canal for crossings by crocodiles, alligators, manatees, and other wildlife. These crossings will consist of 15 box culverts and 3 bridges. MANATEE CREEK BRIDGE The proposed bridge at Manatee Creek would be constructed as a four lane bridge, but would be striped for three lanes with rumble strips on the southbound fourth lane to discourage vehicular travel in that lane. There would be an eight foot outside shoulder. BRIDGING JEWFISH CREEK AND LAKE SURPRISE Jewfish Creek, which is part of the Intracoastal Waterway, and Lake Surprise would be bridged by a continuous structure. The Jewfish Creek bascule bridge would be replaced by a high-level four-lane fixed bridge. The Lake Surprise causeway would be replaced by a low-level four-lane bridge. The total distance for this bridging is approximately 2.35 miles. AREA OF PROJECT THAT WILL BE OPERATED WITH FOUR-LANES The three passing lanes (4.94 miles) and the bridge over Jewfish Creek and Lake Surprise (2.35 miles) would be operated with four lanes. Those areas total 7.29 miles of the 20.4 mile project corridor. Approximately 43 percent of the proposed roadway would have four lanes of pavement. Excluding the areas where the fourth lane will be blocked from travel with rumble strips, only 35 percent of the completed project will contain four travel lanes. This area consists of the three passing zones and the bridges over Jewfish Creek and Lake Surprise. THE PROPOSED SWM SYSTEM The proposed project would provide for a SWM system consisting of inlets, culverts, swales, berms and dry/wet retention areas. For the typical roadway section, runoff from the paved roadway surfaces will be directed to roadside swales designed to provide retention for 50 percent of 2.5 inches times the impervious area. The SWM system for the bridges will collect runoff in inlets and culverts and direct it to either swales or dry or wet retention ponds. The berms of the SWM system provide additional protection by restricting spills of pollutants, such as petroleum from overturned tankers or other vehicle accidents, from running into the surrounding waters. The berms and swales of the SWM are designed to catch pollutants and prevent their discharge into the surrounding waters. FDOT Exhibit 18 consists of four separate drainage reports submitted to the District in 1995 in connection with the project, one report for each section of the project. The reports accurately document the drainage calculations, the drainage design, the rationale behind the drainage design, and compliance of the design with the laws and regulations of the permitting agencies for the original four-lane proposal. On or about September 5, 1995, FDOT submitted revised drainage calculations to the District, determining the amount of stormwater treatment for the three-lane project. The revised calculations established that at least 95% percent of all stormwater runoff from the project would be captured in the proposed SWM system. Because the swale design was based on the originally proposed four-lane road, retention will be in excess of the required volume for most sections of the roadway. The required retention volume for this project is approximately 166 percent of what is required by the BOR. The surface and subsurface geology of the roadway consists of Miami oolite limestone overlain with Perrine maral. Underlying this is Thompson formation, anastasia and Key Largo limestone. Based on these constituencies, the swales proposed by the SWM system would be effective in rapidly removing heavy metals and phosphorous. The revised calculations established that approximately five percent of the project area will not have a SWM system. These areas will not have a SWM system because properly-sized retention systems in those areas can not be constructed without causing a disproportionate, adverse impact to surrounding wetlands. FDOT has provided reasonable assurances that the proposed SWM system’s total water quality treatment exceeds the District's permitting requirements and provides sufficient treatment to exceed the BOR requirements. The water discharged from the proposed system would be of higher quality than that currently discharged, which is not treated. FDOT has provided reasonable assurances that the proposed SWM system complies with the permitting criteria found in Rule 40E.301(1)(a)-(p), Florida Administrative Code. The following findings are made as to that criteria. Rule 40E-4.301(1)(a), F.A.C. The parties stipulated that Rule 40E-4.301(1)(a), F.A.C., pertaining to flood protection and the adequacy of drainage, is not at issue in this proceeding. Rule 40E-4.301(1)(b), F.A.C. The quality of water being discharged from the SWM system will be of substantially higher quality than the existing discharges. Consequently, it is concluded that the system will not cause adverse water quality impacts within the meaning of Rule 40E-4.301(1)(b), F.A.C. In addition, the evidence established that there will likely be less water discharged from the roadway if the project is constructed because of the amounts of water that will likely be retained in the swales that are a part of the SWM systems. Rule 40E-4.301(1)(c), F.A.C. Because the receiving bodies of water are designated Outstanding Florida Waters, the District is required to apply the DEP's most stringent water quality requirements -- the antidegredation requirements for discharge to OFWs, to this project. Those standards will be discussed in more detail below. The evidence established that the proposed project will not violate those requirements. Rule 40E-4.301(1)(d), F.A.C. Impacts to sources of water are not at issue. The District reviewed the potential effect of the SWM system upon on-site and off-site impacts to surface or groundwater levels and flows. The evidence supports the District's conclusion that no adverse impacts will be caused. Petitioners failed to present any evidence on groundwater levels and flows. Consequently, it is found that the criteria found at Rule 40E-4.301(1)(d), F.A.C., has been satisfied. The 25 hydrologic culverts north of C-111 have the potential to re-establish historic surface water flow in the area. They were sized, based on rainstorm events, to help equalize water levels from one side of the road to the other. The culverts are capable of transferring water from west to east to assist in the historic restoration of flows. In order to assure the proper usage of the culverts, they will remain gated until the District develops a management plan in conjunction with other agencies. The District will determine the maintenance entity. The FKAA water main runs beneath this section of the road. As a result, there is no other more hydrologically efficient alternative for the placement of the culverts. The culverts would also provide a means for overwash from storm events, over the U.S. 1 roadbed, to flow back to its point of origin, stabilizing the roadbed and allowing release of the accumulated salt water. Rule 40E-4.301(1)(e), F.A.C. In addition to providing for a net improvement in water quality, the project will offset any adverse impacts through mitigation and other environmental enhancements for which no mitigation credits are being assigned, as described below. Rule 40E-4.301(1)(f), F.A.C. FDOT has a history of adequate maintenance of SWM systems, and has provided reasonable assurance that it has the staff and budget to comply with District operation and maintenance requirements. FDOT will also be able to comply with the District's requirements to control exotic plants and other foliage along project corridor. Rule 40E-4.301(1)(g), F.A.C. The SWM system will not adversely affect public health and safety. The dispute as to the public interest test focused more on the WRM permitting requirements. Findings as to the public interest test are discussed in more detail below. Rule 40E-4.301(1)(h), F.A.C. The evidence established that the SFM system is consistent with State Water Policy. Rule 40E-4.301(1)(i), F.A.C. This project does not pertain to a DRI and, consequently, this criteria is not applicable. Rule 40E-4.301(1)(j), F.A.C. There are no basin criteria applicable to this project. Rule 40E-4.301(1)(k), F.A.C. The evidence established that the SWM system will not be harmful to the water resources of the District. While there will be adverse environmental impacts caused by the project, those adverse impacts have, as will be discussed in more detail below, adequately offset by mitigation. Rule 40E-4.301(1)(l), F.A.C. This issue was not at issue in this proceeding. Rule 40E-4.301(1)(m), F.A.C. As will be discussed in greater detail in a subsequent section of this Recommended Order, the project is not against public policy. For the reasons set forth in that subsequent section, it is found that the project is clearly in the public interest. Rule 40E-4.301(1)(n), F.A.C. Rule 40E-4.091(1)(a), F.A.C., constitutes the BOR. As discussed in detail above, the SWM system complies with the BOR. Rule 40E-4.301(1)(o), F.A.C. There are no isolated wetlands pertaining to this project. Rule 40E-4.301(1)(p), F.A.C. There are no above ground impoundments, as described in Appendix 6 of the BOR, pertaining to this project. WATER QUALITY - DISCHARGES INTO OFW Because the project will involve discharges into Outstanding Florida Waters, it was necessary for FDOT to establish that the discharges from the SFW system will not degrade those OFWs. The evidence established that FDOT's proposed project complies with and exceeds applicable water quality standards and permitting criteria. There will be no significant degradation of ambient water quality as a result of the project. It is expected that there will be a net improvement in ambient water quality resulting from the proposed project, as opposed to the continued degradation if nothing is done to treat stormwater runoff. In FDOT Exhibit 46, FDOT provided baseline water quality data in the form of STORET data for waters adjacent to the project area. STORET is a centralized repository and database for water quality data throughout Florida. It is Florida's principal source of water quality data. STORET contains the best scientific database on water quality in Florida. The STORET data set forth in FDOT Exhibit 46 provided sufficient evidence on ambient water quality for the waters adjacent to the proposed project. In addition to providing the water quality data in FDOT Exhibit 46, FDOT is required by Special Permit Condition 37 to submit appropriate water quality data in the surrounding waters prior to any construction activities. SFWMD Exhibits 5 and 6 contain amendments to Proposed Agency Action made after the beginning of the formal hearing. These amendments include a requirement that an appropriate water quality monitoring plan be submitted within 30 days of the permit issuance. FDOT has provided reasonable assurances that water quality standards will be met and that there will be appropriate water quality monitoring during construction. DIRECT IMPACTS OF THE PROJECT The proposed roadway design will result in the following direct impacts to wetlands adjacent to the roadway corridor: 1) the dredging of 11,028 cubic yards of material from 2.1 acres, 2) the placement of 1,689,553 cubic yards over 147.0 acres of wetlands, and 3) 6.9 acres of (potential) permanent impact due to shading and 4.1 acres (potential) of temporary impacts from the Jewfish Creek Bridge construction activities to seagrass habitat. In order to determine the project's direct impacts, the area surrounding the project was surveyed to determine the number of affected acres. This was done by using a computer aided design ("CAD") system, and by categorizing the various forms of wetlands and associated flora and fauna into the following communities: mangrove, emergent freshwater, open water, and tidal, consisting of seagrass and non-vegetated bottoms. Using these categories and the CAD system, every square foot of direct impacts were accounted for. The adverse direct wetland and surface water impacts of this project are as follows: 1) 27.83 acres Non- Vegetated Tidal Bottom; 2) 11.27 acres Seagrasses; 3) 46.85 acres Mangroves; 4) 42.35 acres Sawgrass/Cattail/Spikerush; 5) 14.31 acres Shrub Wetlands; and 6) 6.46 acres Open Fresh Water; totaling 149.07 acres. Though some wetlands to be impacted may be of lesser quality, FDOT stipulated that all wetlands to be directly impacted by the project should be considered to be high quality wetlands for the purpose of mitigating the impacts. The impacted wetlands are part of larger wetland systems. Petitioners assert that the District should have required studies as to impacts as to the larger wetland systems. The evidence established that the District appropriately considered the type and location of the wetlands involved so that additional study suggested by Petitioners was unnecessary. Petitioners also assert that impacts to isolated wetlands should have been studied. The evidence established that there will be no such impacts. SECONDARY AND CUMULATIVE IMPACTS RECOGNIZED BY SFWMD In addition to the direct impacts of the project, the District is required to analyze secondary and cumulative impacts. A project's secondary impacts are those that, though outside of the project footprint, are very closely linked and causally related to the project. This is a "but for" test. Secondary impacts are those impacts which, if not for the proposed project, would not occur. Both positive and negative secondary impacts are considered. When there are both positive and negative secondary impacts caused by a project, the permitting agency must consider the severity of the impacts and balance these together with the other factors in the public interest test to determine whether or not the project is clearly in the public interest. WRM statutes, and DEP rules and policies pertaining to those statutes do not regulate growth or traffic increases, per se. Only if such increases are very closely linked and causally related to the project will they be considered. The District identified several secondary impacts that would be temporary in nature since they would occur while the project is being constructed. One is the use of a barge facility, primarily at Jewfish Creek, where the anchoring of the barge may result in temporary impacts to seagrass during construction. This impact is addressed by a component of the seagrass mitigation at Boca Chica, discussed below. Another impact is turbidity associated with the dredge and fill and the barge activities. That issue is appropriately addressed by permit conditions, through the use of turbidity control screens and other techniques. The District also identified secondary impacts directly associated with the project footprint that would be permanent in nature. The removal of the exotic vegetation potentially opens up the areas adjacent to the road north of the C-111 canal to off-road vehicles or four-wheel driving and the potential impacts caused by those vehicles. That impact is appropriately addressed by fencing north of the C-111 canal. When a road is widened, animals have a greater distance to travel back and forth from one side of the road to the other. A wider road exposes such animals to greater risk of being hit by a motor vehicle while crossing the road. That impact is addressed in this project by the fencing, the wildlife crossings, and the wildlife box culverts. The crossings are designed for large mammals and some species, such as the Indigo snake, will likely not use these crossings. The wildlife crossings will not entirely mimic the crossing patterns of all wildlife that need to cross U.S. 1 and will result in some wildlife habitat fragmentation. The fencing that will be erected to funnel wildlife through the crossings will fragment the habitat of some species by altering wildlife crossing patterns and blocking access of some species to certain areas of habitat. The greater weight of the evidence established that any habitat fragmentation should, when compared to existing conditions, be minimal. The District appropriately evaluated the advantages and disadvantages of using wildlife crossing and hydrological culverts and appropriately concluded that there would be a net benefit to wildlife as a result of their construction. The District properly concluded that the culverts, bridges and fencing located south of the C-111 canal, construction of wildlife crossings and fencing north of the C- 111 canal, construction of the hydrologic culverts, and removal of the Lake Surprise Causeway are positive secondary benefits of the project. These benefits should be considered when applying the public interest test. THE FKAA PIPELINE RELOCATION The project requires the relocation of two segments of the existing pipe owned by the Florida Keys Aqueduct Authority (FKAA) around Jewfish Creek Bridge. The segments total approximately 1.5 miles. The District inspected the area where the pipeline will be relocated to assist in determining its impact. The pipeline relocation is a temporary disturbance during construction. It is a small linear facility, which will not generate pollution in and of itself. The pipeline relocation is not expected to result in a violation of State water quality standards. The FKAA is responsible for obtaining the necessary permits for the relocation. Direct impacts to wetlands will occur in a 4 to 5 foot wide strip along the length of the relocated aqueduct. The FKAA has submitted a permit application to the DEP for a permit to relocate the aqueduct. DEP believes that adequate mitigation can be achieved to make the project permittable. Once the FKAA submits an adequate mitigation plan, then relocation of the aqueduct will not be an adverse secondary impact caused by the U.S. 1 project. The permit for the subject project should contain a condition that the FKAA obtain a permit for the relocation of these two segments of its pipeline. THE C-111 BOAT RAMP There is an existing boat ramp designed for small boats to access District canals that is located on the north side of the C-111 canal. As a result of the proposed project, it will be relocated to the southern side of the project. This relocation is a relatively minor project requiring a cut in the canal bank and a fourteen-foot wide slab for the boat ramp. When the District considered the potential impacts associated with this relocation in conjunction with the impact of the proposed project, it was determined to be a relatively insignificant impact in terms of the project as a whole. Relocation of the boat ramp is not expected to result in a violation of state water quality standards. All direct, cumulative, and secondary impacts, whether positive or negative, should be considered in balancing the public interest test. ARE THERE ADDITIONAL SECONDARY AND CUMULATIVE IMPACTS Petitioners assert that there are additional cumulative and secondary impacts that the District failed to consider. Petitioners argue that the project cannot meet permitting criteria if those additional impacts are considered. The additional impacts pertain to additional development throughout Monroe County because of the “rate of growth ordinance” (ROGO), additional development along the project corridor, impacts to the coral reefs of the Keys, impacts to Key Deer, generalized impacts, and impacts from increased number of “day trippers." For the reasons discussed below, it is found that the District has considered all appropriate direct, secondary, and cumulative impacts of the project. The additional impacts that Petitioners assert should have been considered are not causally connected or directly linked to the project. THE RATE OF GROWTH ORDINANCE Monroe County adopted its Year 2010 Comprehensive Plan (the "Plan") to meet the requirements of Chapter 163, F.S. The Plan, adopted May 15, 1993, is unusual in that the County limits future growth based on a carrying capacity analysis of its hurricane evacuation clearance time. No other jurisdiction in Florida, and few others in the United States, have used a carrying capacity planning approach. To implement the carrying capacity limitation, Monroe County determined the total number of dwelling units that could be permitted while maintaining an acceptable hurricane evacuation clearance time of 24 hours. This number of dwelling units, less an allowance for vested development and development in municipalities, was the basis for a ROGO that was adopted by the County in 1992. The ROGO allocates the available units at a uniform annual rate of growth (currently, 255 units per year). The ROGO regulates all proposed new residential buildings, including hotels, motels, and other transient tourist accommodations as well as permanent residences. The number of building permits that Monroe County can issue is, at present, directly related to how rapidly the County can be evacuated in the event of a hurricane. The lower the clearance time, the greater the number of permits that can be issued. The Comprehensive Plan requires that the County be able to evacuate within a 24-hour period. As of March 7, 1995, the hurricane evacuation time for Monroe County was determined to be 21.25 hours.1 The project is expected to reduce by six or seven hours the modeled hurricane evacuation capacity for Monroe County, regardless of whether it consists of three or four lanes. This is because both the three lane and four lane plans provide for two northbound lanes. Because of the rate of growth provisions in county law, this reduction of clearance times results directly in an increase in the number of building permits that the county can issue annually. Under ROGO, Monroe County can, with this project, issue 255 permits each year through the year 2026. Without this project, Monroe County can issue 255 permits each year only through the year 2001. Alternatively, without this project, the county can issue 88 permits each year through the year 2010 if it chooses to issue permits over a longer period of time. Following extensive litigation before the Division of Administrative Hearings in an unrelated proceeding2, the Administration Commission entered a final order on December 12, 1995, that approved approximately 97 percent of the Plan. In addition, the Administration Commission has published a proposed rule to bring the remainder of the Plan into compliance and assure its financial feasibility. The central feature of the proposed rule is a five- year work program, with annual reviews by the Administration Commission. It is likely that the proposed rule will eventually result in the complete revision of the ROGO. The proposed rule provides that Monroe County's annual rate of growth be revised within five years, no later than December 31, 2001, "to establish a rate of growth and a set of development standards that ensure that any and all new development does not exceed the capacity of the county's environment and marine systems." A carrying capacity study will comprehensively assess water quality, habitat protection, and public facility issues to determine the capacity of the Keys to sustain further development. The proposed project is but one of many factors that will be considered in future rate of growth regulations. If the expected revisions occur, it would be speculative to predict what development would be allowed. While the studies are underway the rate of growth will remain at 255 units per year. The rate of growth will be reviewed annually, and may be reduced a minimum of 20% if the goals of the studies are not being met. The DCA has determined that Monroe County’s Comprehensive Plan and its land development regulations are sufficient to prevent or mitigate any potential adverse secondary impacts of the project caused by development. The DCA has consistently supported the proposed project, even in its earlier four-lane configuration, because it was consistent with Monroe County's 1986 Comprehensive Plan, and because the project would improve hurricane evacuation clearance times and improve water quality in the vicinity of the roadway. The 1986 plan supported widening of the roadway to four lanes based on projected travel demand. The DCA prefers the current, three-lane proposal to the earlier four-lane. On September 7, 1995, the Monroe County Commission adopted Resolution 315-1995 in support of the proposed project because "it balances the needs for a widened highway with safeguards designed to address secondary impacts." Lorenzo Aghemo, an expert in comprehensive planning, served as Monroe County Planning Director during the development of the Plan and ROGO. In Mr. Aghemo's opinion, the widening of the roadway to either three or four lanes would generate minimal growth pressure in Monroe County, particularly because the Plan limits the rate of growth. Because the Keys are designated by Section 380.0552, F.S., as an area of critical state concern, the DCA is charged with oversight of Monroe County's Comprehensive Plan, its LDRs, and all development that takes place in Monroe County. Additionally, the Administration Commission may amend Monroe County's plan or regulations by rule (See Section 380.0552(9), F.S.). There is virtually no action that Monroe County can take related to the use of land without review and approval of a state agency. The Administration Commission’s proposed rule demonstrates its intent to revise comprehensively Monroe County's ROGO within five years to ensure that future development does not exceed the capacity of the Keys' environmental resources. It also demonstrates the Administration Commission's intention to closely monitor growth and development in the Keys during the five-year study period. Some of the studies required by the proposed rule are already underway: 1) the DCA has entered into a contract with the ACOE to complete the environmental carrying capacity study; 2) the HRS study of advanced on-site waste water treatment systems is underway; 3) Monroe County is developing the required Marathon central sewer facilities plan; and 4) Monroe County and HRS have begun the cesspit identification and elimination process. Caution should be exercised in relying on this or on any other proposed rule. Likewise, caution should be exercised in relying on changes to ROGO that may or may not occur. It is likely that the present status of the law will be changed in the near future so that future development will be based on environmental carrying capacity as opposed to hurricane evacuation clearance times. However, for the purposes of this proceeding the District should accept the fact that the issuance of future building permits is closely linked and causally related to the project. Consequently, it is found that under the present status of the law, the issuance of additional building permits in Monroe County is closely linked or causally related to the project. MONROE COUNTY LDRS AND DCA OVERSIGHT Although Petitioners established that there is a causal relation between the project and the existing status of the law governing the number of building permits that can issued in the future, the evidence was insufficient to establish at a level above speculation that adverse environmental impacts will result because of the issuance of those building permits. The Monroe County Comprehensive Plan contains land development regulations that govern all development in Monroe County. These regulations are among the most stringent in the State and are designed to avoid or minimize adverse environmental impacts caused by development. All development orders in Monroe County are closely scrutinized by the Department of Community Affairs to ensure compliance with applicable permitting criteria. Those regulations and the DCA’s close scrutiny are intervening factors that break any causal relation between the project and the speculative adverse environmental impacts that the Petitioners assert will be caused by future issuance of building permits by Monroe County. Petitioners failed to establish that the impacts of future development are very closely linked or causally related to the project. Consequently, it is found that such impacts are not secondary or cumulative impacts of the project. DEVELOPMENT ALONG THE PROJECT CORRIDOR A major portion of the area next to the road has little or no development potential because it is either water, land in public ownership, or land slated for public ownership. The areas east of the road are mostly in private ownership, but are primarily submerged lands and mangrove areas. The Crocodile Lakes National Wildlife Refuge is federally owned and is managed by the U.S. Fish and Wildlife Service (USFWS). The Southern Glades lands, located immediately west of the project and Everglades National Park (ENP) in Dade County, have been acquired by the District and are managed by the Florida Game and Freshwater fish Commission (FGFWFC). The Model Lands Basin in Dade County is in private ownership but proposed for public acquisition in the future. The land adjoining the roadway in Dade County is designated as open area or environmentally sensitive. Almost half of the land along Monroe County's portion of the roadway is in public ownership. At least 90% of the land in private ownership is mangroves or wetlands that cannot be developed. The small area of uplands is currently being used by a resort marina which will not be allowed to develop further under the new comprehensive plan. There is very little potential for future development in the project area. The comprehensive plan designation for areas in Dade County are open space, and the ones in Monroe County have the conservation designation. The District's regulatory programs consider areas adjacent to the project as sensitive wetland habitats. Based on the District's regulatory authority and comprehensive plan designation for those lands, which would have to be obtained prior to obtaining a permit for development, it is very unlikely that those lands could be developed. Florida Rock and Sand Co. (FRS) has a permit to mine approximately 1,100 acres of wetlands. As part of its mitigation program, FRS will donate this land to the District once its mining and mitigation projects are complete. The FRS mitigation lands are preserved as a permit condition and will ultimately be transferred to the District. This land will not be developed. In addition, the District established that the U.S. 1 project and the FRS project do not constitute a cumulative impact that the District failed to consider. The evidence established that development along the project corridor will not be a secondary or cumulative impact of the project. IMPACTS ON CORAL REEF SYSTEM The evidence was insufficient to establish a close link or causal connection between the project and the coral reef system. As reflected elsewhere, it is found that there will be no degradation of ambient water quality as a result of the project. Therefore, there is no need to resolve the conflicting testimony as to the present status of the coral reef system. IMPACT ON KEY DEER There are no key deer in the project area. The nearest key deer habitat, Big Pine Key, is approximately 70 miles from the southern terminus of the project. The evidence is insufficient to establish that there is a very closely linked and causally related connection between the project and key deer mortality on Big Pine Key. GENERALIZED IMPACTS The Petitioners presented certain opinion testimony that the Keys cannot be developed in an environmentally sensitive manner because of potential adverse impacts of new development in Monroe County, or new boats operating in the waters of the Florida Keys. The credibility of that testimony need not be evaluated because the evidence was not sufficient to tie those generalized concerns into the specific regulatory criteria of the permitting agency. There was insufficient evidence to establish that those alleged impacts would be very closely linked or causally related to the proposed project. DAY TRIPPERS Induced demand is new travel that occurs solely because additional capacity is added to a highway. Petitioners' transportation experts, Michael Replogle and Robert Morris, testified that FDOT's traffic studies, and FDOT's projected rate of traffic growth of approximately 3 percent annually, are incorrect because the studies do not predict the amount of "induced demand" that would result from the proposed project. Petitioners assert that induced demand would generate an unknown number of people who drive to the Keys for the day from south Dade County, referred to as “day trippers,” will have an impact on the Keys that has not been evaluated. The assertion that this potential impact has not been analyzed is rejected as being contrary to the greater weight of the evidence. Induced demand is accounted for in Monroe County's Long Range Transportation Plan, which was never evaluated by Mr. Replogle or Mr. Morris. The Long Range Transportation Plan was prepared by an experienced traffic engineering consulting firm, Barton-Aschman, using an FDOT- approved traffic demand model, the FSUTMS model, that includes all traffic generators and attractors, and all travel on U.S. 1 on weekdays and weekends. The FSUTMS model does not restrict demand based on the existing road capacity. The model uses an "unrestrained assignment" that incorporates the total predicted trip generation on recreational facilities, hotels, and all other attractors. The Long Range Traffic Plan was used to develop the Monroe County Comprehensive Plan, which takes into consideration the projected increases in traffic and makes appropriate provisions for those increases. FDOT has provided reasonable assurances that it has properly projected the amount of traffic for the project corridor after the project is completed and that the projected increases have been appropriately addressed by Monroe County's Comprehensive Plan. MITIGATION - IN GENERAL For the reasons discussed above, it is found that there are no secondary or cumulative impacts that the District failed to consider. Petitioners also contend that the mitigation proposal is insufficient to offset the direct and secondary impacts recognized by the District. This is a large dredge and fill project that will permanently fill 149 acres of wetlands. The wetlands that will be adversely impacted by the project include OFWs that provide a great variety of functions and serve as habitat for fish and wildlife, including threatened and endangered species. The wetlands are unique and of high quality. Mitigation for direct, secondary and cumulative impacts was considered as part of the permit evaluation. In- kind mitigation is considered to be most effective, but out- of-kind mitigation may be offered by the applicant where it is impractical to conduct in-kind mitigation due to historic changes in the project area or sensitivity of the habitat type for which mitigation is offered. Such mitigation is also appropriate to address regional alteration of an ecosystem, such as the Everglades ecosystem alteration caused by the original roadway embankment. FDOT developed a conceptual mitigation plan that took into account project impacts on the freshwater, marine and estuarine components of the ecosystems involved, as well as the impacts on threatened and endangered species of wildlife which may be affected by the project. FDOT coordinated the plan's development with the National Parks Service, U.S. Fish and Wildlife Service, the Army Corps of Engineers, the National Marine Fisheries Service, the U.S. Environmental Protection Agency, the Dade County Department of Environmental Resources Management, the Florida Game and Fresh Water Fish Commission, and the Florida Department of Environmental Protection. The conceptual mitigation plan evolved as a result of project modifications and agency comments into what is now proposed as mitigation for the project. The current proposal is summarized in FDOT Exhibit 26, consisting of Attachment H to FDOT's SWM and WRM permit applications. The timing of their construction falls into two general categories: mitigation previously permitted and concurrent mitigation. UPFRONT MITIGATION Typically, mitigation is done concurrently with project construction rather than prior to permit issuance. Mitigation is often done afterwards because of construction timing constraints. Here, FDOT applied for and, in May 1994 received, permits to conduct mitigation prior to applying for the permits at issue, with the understanding that performance of these activities does not require the District to issue permits for the proposed projects. A total of 385.22 acres of mitigation has already been completed. The applicant received 203.02 mitigation credits from the District on May 12, 1994, for several mitigation projects that the applicant proposes to apply to the proposed U.S. 1 widening project provided it is approved. Table 2 of Attachment H to FDOT Exhibit 26 sets forth the four mitigation projects that constitutes the up- front portion of the mitigation for the project. This table sets forth the acres mitigated, the conversion factor for the mitigation, and the resulting mitigation credit awarded. The four mitigation activities already authorized are: enhancement of the wetland habitat in the Harrison Tract located adjacent to Barnes Sound within the Crocodile Lakes National Wildlife Refuge on the north end of Key Largo (70.37 acres credit for 252.6 acres of restoration); removal of the spoil mounds on the eastern bank of the C-111 canal east of U.S. 1 located on the District’s ROW (10.65 acres credit); the back filling of the C-109 canal levee located on the District ROW within the Southern Glades Save Our River project (112.7 acres credit); and the removal of the roadside spoil mounds on the west side of U.S. 1 located between C-111 and the Dade Work Camp Road within the District’s Southern Glades Save Our Rivers Project (9.30 acres credit). The mitigation projects pertaining to the roadside spoil removal along U.S. 1, the backfill of the C-109 Canal, and the removal of spoil along the C-111 Canal are similar projects because they each involve existing deep ditches cut through wetlands. When these deep ditches were cut, the spoil material from the ditch was deposited alongside the ditch. This resulted in areas that were previously Everglades wetlands becoming spoil, supporting the growth of exotic species and, for the most part, not exhibiting wetland functions. FDOT is proceeding with the backfilling the C-109 canal located between mile markers 122.5 and 117, and removal of the corresponding spoil mounds created during construction of the C-109 canal. In connection with this mitigation, marsh areas, tree islands and deep water aquatic refugia have been restored. In this area, there has been considerable attraction of wildlife subsequent to restoration, including otters, alligators, and turtles, which could not previously use the habitat because the canal was too deep. Upon completion waterflow between the east and the west will be restored, and the area will be restored to a wetland habitat from its current uplands habitat type. Backfilling of the C-109 canal is part of an interagency effort with the ACOE to restore as closely as possible to natural conditions the flow of water in the C-111 watershed area. C-111 mitigation includes removal of roadside spoil along the C-111 canal to restore the natural condition of the area. The mitigation was devised in coordination with the National Maine Fisheries Service (NMFS), which required mitigation for non-vegetated habitat types. Restoration also includes preserving some spoil areas as islands to maintain habitat for endangered species of plants. When the C-111 spoil mounds are scraped down, the fill will not fill the whole ditch. The ditch will, therefore, be a bit more valuable but will not be completely restored to its former elevation. FDOT will also remove roadside spoil along the west side of U.S. 1, upon which exotic species of plants had grown, and returning the area to its original grade. The Harrison Tract is a known habitat and nesting area for American crocodiles. Its wetlands functions were altered or eliminated by prior development of the land by its original owners. Restoration includes regrading the area to restore its original wetlands functions, including habitat for young and adult crocodiles. FDOT's mitigation of the Harrison Tract also includes restoration of tidal flushing to increase contributions of nutrients and food sources to the surrounding tidal bay system. Crocodiles have been observed using the restored areas. FDOT has installed additional nesting berm habitat, basking habitat and shallow lagoon habitat to promote juvenile crocodile development. The District established that the credit awarded for this mitigation and the conversion ratios utilized for determining this credit were consistent with agency practice and its pertinent rules. FDOT was given a 1:1 credit ratio for areas involving full restoration of wetlands. In other portions of the Harrison Tract mitigation involving restoration of flushing to existing wetlands, FDOT was given not full credit, but credit based on the severity of limitation of the existing wetland functions. Based on this evaluation, mitigation credits were given in a range of a 3:1 ratio for restoration of severely disrupted or non-existent wetlands to a 20:1 ration for restoration of higher quality but not fully functional wetlands. FDOT is being awarded 70 mitigation credits for the 252 acres in the Harrison Tract that are being restored or enhanced. CONCURRENT MITIGATION Based on the mitigation ratios developed by the District, additional mitigation credits were required. Consequently, the project contemplates mitigation that will be undertaken concurrently with the construction of the project in addition to the upfront mitigation. FDOT proposes to earn these additional credits by projects involving creation and/or restoration of emergent vegetation, mangrove and seagrass habitats. FDOT’s proposal to mitigate mangrove impacts with "out of kind" mitigation of emergent vegetation habitats was viewed by the District as being necessary and appropriate because there were no sufficiently large areas of mangrove habitat suitable for restoration. Table 7 of Attachment H to FDOT Exhibit 26 sets forth the four mitigation projects that constitutes the concurrent portion of the mitigation for the project. This table sets forth the acres mitigated, the conversion factor for the mitigation, and the resulting mitigation credit awarded. In addition, the table references certain credit for the placement of the hydrological culverts. As will be discussed later, that credit was withdrawn at the formal hearing. The four mitigation activities that will constitute the concurrent portion of the mitigation plan are: the removal of the Lake Surprise causeway (2.90 acres credit); the scrape down of the Jewfish Bridge approaches (0.67 acres credit); the restoration of the FGFWFC road (10.34 acres credit); and the Boca Chica project (27.17 acres credit) The Lake Surprise Causeway removal mitigation involves 5.26 acres of on-site seagrass restoration and 0.54 acres of unvegetated bottom mitigation through the excavation of 52,220 cubic yards of material. Lake Surprise historically was a shallow tidal lake supporting seagrasses before a causeway was built across the lake over the seagrasses. FDOT proposes to remove the causeway and restore the previous elevation, after which it is anticipated that seagrasses that grow on the east side of the causeway will fully recruit naturally to the excavated area. Removing the Lake Surprise Causeway will establish 5.26 acres of seagrass, for which FDOT received 2.63 acres of on-site mitigation credit based on a 2:1 ratio. Through natural recruitment after removal of the causeway, there is a high likelihood that the entire 5.26 acres will recolonize with seagrass. FDOT minimized the seagrass impacts to the greatest extent possible. The mitigation credit pertaining to Lake Surprise does not include credit for the removal of the causeway itself. This awarded credit is for the restoration of seagrass areas. The mitigation pertaining to the Jewfish Creek Bridge approaches proposes the scrape down of 1.33 acres of existing fill to allow the area to become recolonized with mangroves. Boca Chica is located in southern Monroe County over one hundred miles from the southern terminus of the project. This site was chosen by FDOT as a site for seagrass mitigation project after FDOT reviewed several other potential sites. Two other sites were rejected. The area around the C- 111 canal was rejected because the land proposed for use was in private ownership. Several defunct marinas in Port Bougainville were rejected due to poor conditions not conducive to seagrass growth. Boca Chica was finally chosen as the site because it was a large enough area with light and hydrological flow conditions conducive to seagrass growth. The evidence establishes that the Boca Chica site is the most viable for seagrass mitigation. The seagrasses to be impacted at Lake Surprise are healthy and productive turtle grass, manatee grass and cuban shoalgrass. Turtle grass is considered an extremely valuable “climax community” of seagrasses which hold sediments in place, cleanse water quality, and forms the base of the food chain. It is valuable to sea turtles, manatees and recreationally important fish and shellfish. The cuban shoalgrass that will colonize at Boca Chica is a pioneer colonizer species that grows in disturbed areas. It is not as valuable to the marine system as turtle grass. The Boca Chica seagrass mitigation permit condition proposed to offset impacts to 11.27 acres of seagrass. This will involve the removal of 306 cubic yards of sediment and hydraulically dredging approximately 1,175 cubic yards of spoil material. The proposed permit conditions state that FDOT shall provide future maintenance of the culvert areas to maintain adequate flushing. FDOT will plant 25.92 acres of seagrasses to mitigate for the remaining 8.64 acres of impacts, for a mitigation ratio of 3:1. In addition, 8.46 acres of seagrass will be planted to mitigate for the barren bottom area that will be affected, and 1.62 additional acres will be planted to compensate for any unexpected impacts to Boca Chica based on the necessary improvements. Overall, there will be of 36 acres of seagrass mitigation by FDOT, for which FDOT is receiving 27.17 acres credit. FDOT will also increase the water flow between the east and west lagoons of Boca Chica, and maintain the culverts connecting the two sides, in order to further promote growth of seagrass therein. FDOT is responsible for 80% survival of each acre of seagrass mitigation, as well as monitoring once a year for five years. Based on historical data obtained from Boca Chica during past mitigation efforts, there is a high likelihood that the entire 36 acres of mitigation will survive, and that the remaining 74 acres of the Boca Chica lagoons will experience natural recruitment of seagrass as a result of FDOT's efforts. The FGFWFC access area was built by excavating a ditch, and putting fill on the wetlands and creating a dirt road bed. After the C-109 canal is backfilled, the access road will no longer be needed. The mitigation project will excavate the existing road bed, back fill it into the ditch, thereby recreating the wetlands that were there previously. FDOT will receive 10.34 mitigation credits based on a 1:1 ratio of acres restored. EVALUATION OF MITIGATION There is no mitigation in this permit for any wetland impact beyond the direct loss of the specific 149 acres that will be dredged or filled. Mitigation was provided only for the direct, footprint impacts of the project. None of the up front mitigation involves the creation of wetlands, which entails converting areas that were not previously wetlands or open water and turning them into wetlands. It will likely take between 20 and 50 years for the mitigation areas to achieve full functional value required by the South Florida Water Management District mitigation permit. In the interim, there will be a net loss of wetland functional value. With time, the proposed mitigation has a high likelihood of success. Based on FDOT's past successes in mitigation of construction-related impacts, FDOT is able to comply with permit conditions relating to best management practices associated with the construction of bridges and pilings and turbidity screens around road construction, as well as restoration of seagrasses and mangroves. Petitioners assert that the District erred in determining the credit to be given for the up-front portion of the mitigation. While it is true that the SFWMD Rules do not mention "up-front" mitigation, the District has the authority to consider all aspects of a mitigation project in weighing its relative value. Consulting engineering inspectors have been retained by FDOT to insure that all permitting requirements are met during mitigation and construction, and that the technical special provisions for protection of threatened and endangered species are complied with by FDOT. The proposed permits contain appropriate conditions that require FDOT to monitor and maintain the mitigation areas. FDOT will be responsible in perpetuity for maintaining the tidal flushing connection at the Boca Chica mitigation site. Special permit condition 6 to the SWM and WRM staff reports require wetland and upland monitoring. If wetland and upland monitoring or other information demonstrate that additional adverse impacts have occurred due to this project, FDOT would be required to offset the loss of any additional wetland impacts. MITIGATION IS APPROPRIATE The evidence established that the mitigation projects were fairly and appropriately reviewed by SFWMD and that the mitigation credits were fairly and appropriately awarded. The evidence also established that there is appropriate mitigation for the direct, secondary, and cumulative impacts of this project. ACTIVITIES NOT RECEIVING MITIGATION CREDIT Mitigation credits for the 25 hydrologic culverts north of C-111 were originally included in the permit staff reports. Those mitigation credits were removed in an addendum to the staff reports, introduced as District's Exhibits 5 and 6. These credits were not necessary to offset project impacts. After the staff report was issued, they became a point of contention by the Petitioners because they will not be utilized until a management plan is developed. Since they were not necessary to meet mitigation requirements, the credits were removed from this project. These credits were never included in the mitigation ratios for these permit applications. The addendum removed the 9.6 credits initially contemplated for the culverts. No credit has been awarded for the relocation of threatened and endangered species of plants, such as Joewood and Bay Cedar by FDOT from the C-111, C-109 and roadside spoil mitigation areas. These species have been relocated to tree islands constructed by FDOT on the mitigation sites, or to other areas that would not be impacted by the project. FDOT also was not given mitigation credits for: (1) the wildlife crossings and the fencing that will funnel wildlife through these crossings; (2) installation of pipe culverts north of the C-111 canal and bridges and box culverts south of C-111; and which, in addition to providing a corridor for aquatic species, will increase the tidal flushing of the area; (3) the removal of the Lake Surprise Causeway, which will restore historical hydrological flow between the eastern and western sides of Lake Surprise; (4) FDOT's commitment to improve and maintain the flushing of the west lagoon culverts in Boca Chica (mitigation is in the east lagoon); and (5) FDOT's contribution of $300,000 to assist Monroe County in performing a carrying capacity study for the County. Additionally, FDOT will preserve the Jewfish Creek Bridge abutment, which will be preserved for local historical purposes. FDOT will prepare the Jewfish Creek Bridge pilings for an artificial reef at Long Key during construction. THE PUBLIC INTEREST TEST It is appropriate for the SWFMD to consider, in balancing the public interest test, to consider traffic safety and hurricane evacuation.3 Because of FDOT's expertise in those areas, it is appropriate for the permitting agency to give great weight to highway safety concerns, including hurricane evacuation, presented by FDOT. The application of the public interest test does not involve consideration of non-environmental factors other than those expressly set forth in the statutes such as navigation or preservation of historical or archaeological resources. Specifically, aesthetics, quality of life, the potential for a project to cause increased crime, and school overcrowding are not properly considered within any of the seven factors contained in Section 403.918(2)(a), Florida Statutes (1991). The District concluded that the project is clearly in the public interest based upon consideration and balancing of the following factors: hurricane evacuation improvements, public safety improvements, a SWM system where no SWM system currently exists; wildlife crossings and fencing north of the C-111 canal where no such crossings or fencing currently exist; wildlife box culverts to accommodate crocodiles, alligators, manatees and marine life where no such culverts currently exist; and hydrologic culverts, which have the potential to assist in the restoration of hydrologic flows, and the mitigation projects, both upfront and concurrent. SECTION 403.918(2)(a), FLORIDA STATUTES Section 403.918(2)(a), Florida Statutes, requires the permitting agency to determine “[w]hether the project will adversely affect the public health, safety, or welfare or the property of others." The property of others is not at issue. As discussed below, the evidence clearly established that the project will greatly enhance the safety of the road during normal operations and facilitate evacuation in the event of a hurricane. There will be clear benefits to the public safety as a result of this project. As part of the PD&E process, FDOT, through Metric, prepared "A Safety Evaluation" of the existing roadway. The safety analysis was based on FDOT accident statistics for the years 1983-1988, as well as engineering review of the conditions causing the accidents. Specifically, FDOT based their safety analysis on the following: 1) calculation of the abnormally high accident rate on the roadway based on the rate quality control formula set forth in the FDOT Highway Safety Improvement Guidelines, and approved by the Federal Highway Administration; 2) copies of the actual crash reports filed with the Florida Division of Highway Safety and Motor Vehicles, which provided detail greater than that generally available through FDOT's own accident data reports, and which formed the basis of the collision diagram in the Safety Evaluation (FDOT Exhibits 36; and 3) and its August 1996 update thereto (FDOT Exhibit 41), on-site evaluation and review of the roadway to determine geometrics of the roadway, locations of driveway accesses and side roadways and the degrees at which roadways intersected. Metric prepared an update of the Safety Evaluation for the years 1989-1994, to determine the continuing validity of the Safety Evaluation, as well as to review alternative proposals to the original proposed roadway configuration. In preparing the update, the recent accident data (FDOT Exhibit 37) and the underlying research in the Safety Evaluation were used by Metric Engineering in reaching its conclusions. The Safety Evaluation performed by Metric in 1989 established high accident rates on the roadway based on a detailed segmental analysis of the roadway. In August of 1996, the Safety Evaluation was updated by Metric, which update confirmed the findings of the Safety Evaluation, and further stated that accident frequency on the Monroe County portion of the roadway exceeded the state average accident rate and the abnormally high accident rate for the years 1990 through 1994 (notwithstanding the rear-end accidents occurring at Jewfish Creek). Fatal accidents on the Dade County portion exceed the state average on the same stretch by 37 percent for the same years. The most severe accidents occur on the Dade County portion. The Monroe County portion of the roadway exceeds the statewide average in the abnormally high accident rate four out of the last five years that FDOT studied. The Dade County portion does not exceed the accident frequency or the number of accidents, but the fatality rate in Dade County is much higher than the state average. Presently an abnormally high accident rate exists in three locations along the project corridor, two of which are in the vicinity of the Jewfish Creek bridge. The third location is north of the bridge on Cross Key. Replacing the Jewfish Creek Bridge with the fixed-height bridge proposed by FDOT will substantially increase the safety on the project corridor. The District considered this to be an important positive element in the public interest balancing test. The existing 2:1 slopes of the roadway make it difficult for drivers to recover from running off the roadway, resulting in a greater frequency of this type of accident. Moreover, the existing clear zone is not large enough to overcome the 2:1 slope to allow safe recovery of errant vehicles. As a result, catastrophic crashes occur rather than safe recoveries. Also, as with hurricane evacuation discussed in the following section, actual accidents on the roadway prevent traffic from accessing or leaving the Keys, and also prevent emergency vehicles from rapidly accessing the Keys and a crash site. This occurs because there is little or no shoulder or clear zone along the sides of the road to allow emergency vehicles to efficiently access an accident site, and in the event of a severe, head-on type collision, the roadway is blocked off. U.S. 1 through the project corridor is regarded as so unsafe for travel that Monroe County law enforcement officials call it "death alley." There are many head-on collisions due to the two-lane, no-median alignment. Law enforcement is difficult and dangerous along the roadway, because it has very few areas wide enough to allow law enforcement officials to detain driving violators. It is also very dangerous, for the same reasons, for a driver to pull off the roadway with a broken-down vehicle. High rates of speed and impaired drivers contribute to the accident rates along the project corridor. The efforts of law enforcement to control speeders and drunk drivers is impeded since it is practically impossible for enforcement officers to turn their vehicles around to pursue violators without running a high risk of causing an accident on their own. The project would significantly improve safety on the roadway by reversing the problems identified in the this section, as well as the previous sections of this Recommended Order. The project would virtually eliminate head-on collisions which largely contribute to serious injuries and fatalities along the roadway. The project would also help eliminate problems with emergency vehicle access to accident sites and restoration of service in the event of accidents, and would increase the roadway's level of service as discussed below. Improved level of service was an additional need considered by FDOT during the PD&E process. While the District did not consider the traffic level of service by itself to be weighted as part of the positive public interest criteria in this project, the impacts of resulting congestion are relevant to the public interest consideration of traffic safety as discussed in the foregoing sections. Lower quality level of service, as presently exists on the roadway through level of service F, adversely affects the safety of the roadway. When traffic levels rise, driver frustration increases leading to drivers passing in no-passing zones and potentially resulting in head-on collisions and high-severity accidents. Additionally, due to the narrow shoulders of the existing roadway, accident vehicles pose a threat to and impede normal traffic flow on the roadway. The Highway Capacity Manual set the standards for traffic engineering and is used in all fifty states. The manual classifies the existing roadway as a two-lane arterial rural road. Applying the standards for measuring level of service for two-lane rural roads set forth in the Highway Capacity Manual, FDOT determined that the existing level of service on the roadway is E, which is a very poor level of service that does not meet the established standard of level of service C required by the Highway Capacity Manual. Monroe County uses a speed based method of calculating level of service. Using that method, the level of service for U.S. 1 is at an acceptable level. The parties disagree as to which method of calculating the level of service is appropriate. That conflict is resolved by finding that the method used by FDOT is the appropriate method because of its wide acceptance and long-term use. Traffic volume in the area of the southern terminus of the project is growing at a rate average annual rate of 3.07 percent. In the present condition of the roadway, level of service will degrade to F, or forced-flow conditions, by the year 2006. Even with the improvements proposed by FDOT, the level of service in the northbound direction would improve to level of service B, but the level of service in the southbound direction would remain at level of service D or E due to the single southbound land configuration. Hurricanes pose a serious threat to the safety and welfare of residents and visitors of the Keys. Monroe County is the most vulnerable hurricane-prone area in the United States because it is surrounded by tropical waters, land elevation is low throughout the islands, and the evacuation routes are limited to U.S. 1, an extended route that starts in Key West and runs to the mainland, and Card Sound Road. The greatest potential for loss of life during a hurricane in the Keys is from storm surge. Storm surge is a dome of water near the center of a hurricane which is created by the winds on the water's surface. In a category 3, 4 or 5 storm, the entire land mass in the path of the storm will be inundated. Because of the wind and storm surge associated with hurricanes, the best response to a hurricane warning in the Keys is to evacuate people to the mainland away from the water and the storm surge threat. Accordingly, Monroe County orders a mandatory evacuation in a category 3, 4, or 5 hurricane, and no shelters are opened. There is little or no disagreement as to the vulnerability of the Keys to hurricanes or as to the danger posed by a hurricane. There is disagreement as to whether the proposed project is needed for improved hurricane evacuation. The conflicting evidence in this regard is resolved by the following findings, which are based on the more credible, substantial evidence. The existing road does not have sufficient hurricane evacuation capacity to meet the present and projected future needs of Monroe County residents and visitors. In current hurricane evacuations, the two northbound lanes on U.S. 1 between mile marker 90 and 106 are split at Key Largo. Sixty percent of the traffic is directed up the northbound lane of U.S. 1; forty percent of the traffic is diverted onto the northbound lane of Card Sound Road. One southbound lane of U.S. 1 and Card Sound Road must remain open for emergency vehicles to reach an accident or a disabled vehicle, or to bring emergency supplies into the Keys. Improving the roadway is critical to the success of Monroe County's hurricane evacuation plan. FDOT relied on hurricane evacuation and needs modeling performed by Monroe County and the ACOE to confirm the need for improvements. All of the models used indicated that the project corridor is the controlling roadway segment for improving hurricane evacuation of the Keys. Additionally, FDOT relied on the Lewis Report of January 15, 1993, a study commissioned by the Governor of Florida. Recommendation No. 17 of the Lewis report recommends that FDOT expedite the design and construction of the project, which is viewed as being critical for increasing the rate of emergency evacuation. Dr. Robert Sheets, former director of the National Hurricane Center, testified that the failure to make improvements to the roadway would be "unconscionable." Dr. Sheets and Billy Wagner, the Director of Emergency Management for Monroe County, presented very compelling and very persuasive testimony that this project is essential for hurricane evacuation purposes. The proposed project is the minimum transportation improvement that will achieve a significant improvement in evacuation safety and clearance time. With the present two- lane configuration and narrow shoulders, evacuating traffic would be halted completely by a vehicle breakdown or an accident blocking one lane. Replacement of the Jewfish Creek Bridge will also facilitate the hurricane evacuation need for the project. In addition to improving the rate of evacuation, the project will make an evacuation safer. Emergency personnel cannot reach accidents on the roadway during an evacuation because, in certain segments, no roadbed exists adjacent to the northbound lane. A second northbound lane and wider road shoulders would enable disabled vehicles to be serviced and removed from the highway. The proposed changes to the road would improve emergency vehicles' access to an accident scene. The elevation of the roadway at Lake Surprise is so low that it can be flooded easily by a storm. The proposed project would replace the existing muck bed of the roadway with more stable material. The existing roadway is subject to settling and washout during storm events, which reduce the safety of the roadway itself and reduce the evacuation capacity of the roadway. If washout occurs, moving equipment to the islands for recovery efforts following a hurricane will be difficult or impossible. The proposed project will prevent erosion and reduce the effects of storm surge and wave action on the road during a hurricane. When the project has been completed, three lanes of evacuating traffic, two lanes from U. S. 1 and a third from Card Sound Road, will converge at Florida City. Representatives of FDOT, the Monroe County Sheriff's Department, the Florida Department of Law Enforcement and Monroe County Emergency Management have planned to manage the northbound traffic when it reaches Florida City during an evacuation. Several feasible alternatives exist, but additional planning is needed to prevent a monumental bottleneck at the northern terminus of the project. While it is clear that this project will not resolve all problems that exist as to hurricane evacuation, it is also clear that this project is essential to improve hurricane evacuation. SECTION 403.918(2)(a)2, FLORIDA STATUTES Section 403.918(2)(a)2, Florida Statutes, requires the permitting agency to consider “[w]hether the project will adversely affect the conservation of fish and wildlife, including endangered species, or their habitats.” The District considered the effect of the direct loss of dredging and filling 149.07 acres of wetland. As set forth in previous sections, it is found that this loss will be offset by the mitigation. For use during construction of the project, FDOT will adhere to technical special provisions and special permit conditions 9 through 13 to protect manatees, crocodiles, alligators, indigo snakes, marine turtles, and valuable trees, palms and other wildlife, to minimize or preclude any impacts to those species. Additionally, any osprey nests around the Jewfish Creek Bridge area at the time of construction will be relocated by FDOT if necessary. As part of the development of the FEIS, as required by the Federal Highway Administration under the National Environmental Protection Act, FDOT obtained official letters of concurrence from the USFWS and NMFS that the project would cause no adverse impacts to endangered species under section 7 of the Endangered Species Act. That process also established the project's consistency with Florida Coastal Zone Management Program, as determined by the State Clearinghouse within the Office of the Governor, in coordination with DEP, the Department of National Resources and FGFWFC. The project also contains provisions to impact positively or enhance the conservation of fish and wildlife, including threatened or endangered species and their habitat, as described below. These were positive factors that further helped neutralize and offset the 149.07 acres of direct impacts. In addition, FDOT is required to evaluate the effectiveness of the fencing along the entire project corridor, discussed below, and report to the District on that effectiveness. If the District determines that the fencing could be more effective, it may require FDOT to implement those suggestions. South of the C-111 canal, construction of box culverts and bridges addresses impacts to the American crocodile, a listed endangered species. Problems were identified with placement of existing culverts, which did not provide enough clear space and which caused the crocodile to cross over the roadway rather than through the culvert. To address this problem, 15 larger box culverts and three bridges will be placed within the roadway. These provide the necessary clear space to allow the crocodile to safely pass under rather than over the road. The location of the box culverts was chosen by reviewing crocodile mortalities associated with road crossings. Placement of these box culverts and bridges will also improve the hydrological flow of water within the project area, provide a crossing area for manatees, and allow greater dispersal of the crocodile population throughout Florida Bay. Species expected to use these box culverts include aquatic and aquatic water dependent species in the area. They were primarily targeted for crocodiles, alligators, and manatees, but certain fishes, turtles, frogs and other species in the wetlands along the project corridor will utilize the culverts. The box culverts will have 100 feet of wingback fencing extending north and south of each culvert. The intent of the wingback fencing is to funnel wildlife into the box culverts. Intermittent or wingback fencing is appropriate south of the C-111 canal for two primary reasons. First, the animals which will be guided into the box culverts are aquatic dependent. The area south of the C-111 canal is primarily water, washed mangrove areas and tidal creeks. Crocodiles tend to move in tidal creeks. Second, it was not possible to ensure continuous fencing along all portions of the project south of the C-111 canal because there are existing businesses. It could not be assured that these businesses would keep a gate closed. The project originally proposed continuous fencing alongside the road where it abuts ENP. Continuous fencing was initially proposed because the initial application included a solid concrete barrier down the median of the road. If a crocodile did enter the road from the side with discontinuous fencing, after crossing one lane the crocodile would hit the barrier, but then easily find its way back to the area it came from. However, the project was later modified to include a tri-beam barrier because it lessens the footprint of the project and thereby lessens the wetland impact. Since the current application does not include a continuous barrier down the middle of the road, if a crocodile enters the road it would cross the tri-beam barrier, go across another lane of roadway before hitting a continuous fence. The animal would then run up and down that fence with nowhere to go except back across the road again. This would increase their exposure to a road kill. With the installation of bridges and culverts along the southern portions of the project corridor, there is no need for continuous fencing because aquatic wildlife, such as the American crocodile, will tend to follow the flow of water through the culverts rather than climb over the roadway. The FGFWFC and ENP oppose continuous fencing and prefer intermittent fencing south of C-111 canal since the project now includes a tri-beam barrier. Positive benefits also include construction of panther crossings at four locations north of the C-111 canal to account for impacts to the Florida panther, a listed endangered species, in the vicinity of the project, along with continuous fencing on both sides of the road north of the C- 111 canal. The crossings will be placed at locations that show historical use by wildlife, including areas at the Dade County Correctional Institute access roadway, the water control structure on the C-109 canal, and the berm of the C- 111 canal. The wildlife crossings are indicated by blue dots on FDOT's Exhibit 1. FDOT underwent years of extensive coordination with the environmental regulatory and resource agencies to design a project that would accommodate their ecosystem management plans. The location of the wildlife crossings was based upon radio telemetry data, collected from radio-collared panthers, and their typical corridor movement. The location was further chosen based on input from the USFWS and the FGFWFC. The continuous fencing north of the C-111 canal will prevent wildlife from crossing the road, and instead force them to use the wildlife crossings. The crossings were designed for panther use, the panthers being the shyest animal in the area. If panthers can be accommodated, then other threatened and endangered species and other wildlife are expected to use them. DOT studies of the effectiveness of wildlife crossings, with fencing, including crossings installed on Alligator Alley, establish that wildlife will use the crossings, both singly and in groups, and that the crossings substantially reduce, if not eliminate, automobile- related mortality of wildlife. Documented wildlife include panthers, wild turkeys, wading birds, alligators, deer, bobcats, black bears and raccoons. SECTION 403.918(2)(a)3, FLORIDA STATUES Section 403.918(2)(a)3, Florida Statutes, requires the permitting agency to consider “[w]hether the project will adversely affect navigation or the flow of water or cause harmful erosion or shoaling.” The replacement of the bascule bridge at Jewfish Creek with a 65-foot high fixed-height bridge will be a benefit to navigation. Because Jewfish Creek is part of the intracoastal waterway, the existing bridge has to be frequently raised or lowered to accommodate marine traffic. Because of the age of the existing structure, frequent breakdowns have been experienced. Marine traffic is stopped or delayed if the bridge cannot be raised or if there is a delay in raising the bridge. Vehicular traffic is stopped while the bridge is raised. Regarding the flow of water, the project incorporates wildlife box culverts and bridges, which will improve tidal flushing and the flow of water south of the C- 111 canal. The District considered this to be a positive consideration under the public interest test. The 25 hydrologic culverts north of the C-111 canal were also a positive factor in the test because the culverts provide future water management capability. Erosion and shoaling are neutral factors in the public interest test because the permit conditions contain a plan to control erosion and shoaling during construction and to provide for road stabilization after construction. In addition, there is a positive factor regarding shoaling in that the roadway area now has a lot of storm action, causing problems with erosion on the side of the road. The project provides for road stabilization, which is a neutral to positive factor in the public interest test. SECTION 403.918(2)(a)4, FLORIDA STATUTES Section 403.918(2)(a)4, Florida Statutes, requires the permitting agency to consider “[w]hether the project will adversely affect the fishing or recreational values or marine productivity of the project.” A positive factor pertaining to marine productivity is the box culverts and bridges south of C-111, which will allow marine species to travel beneath the road to access the water on both sides of the road. Removal of the causeway along Lake Surprise opens that water body back up to one contiguous system, which is also a positive factor. The seagrass mitigation addressed in previous sections will also improve marine productivity and provide habitat for fish. SECTION 403.918(2)(a)5, FLORIDA STATUTES Section 403.918(2)(a)5, Florida Statutes, requires the permitting agency to consider “[w]hether the project will be of a temporary or permanent nature.” The project is permanent, though some construction impacts are temporary in nature. Once temporary impacts have ended and the project is complete, the project will be a positive benefit, because of the construction of the SWM system, culverts, animal underpasses and other benefits as set forth above. SECTION 403.918(2)(a)6, FLORIDA STATUTES Section 403.918(2)(a)6, Florida Statutes, requires the permitting agency to consider “[w]hether the project will adversely affect or will enhance significant historical and archaeological resources under the provisions of s. 267.061.” This factor is not at issue. SECTION 403.918(2)(a)7, FLORIDA STATUTES Section 403.918(2)(a)7, Florida Statutes, requires the permitting agency to consider “[t]he current condition and relative value of functions being performed by areas affected by the proposed activity.” A percentage of wetlands immediately adjacent to the road are impacted by exotic vegetation. Areas further out are part of a significant wetland ecosystem and are considered high quality. This project contains an exotic control program within FDOT's right of way, which is a positive consideration in the public interest test. Wetlands are currently receiving untreated storm water, which runs off the road immediately into the adjacent wetlands and water bodies without treatment. The project will include a SWM system where none currently exists as is detailed in the previous sections. This is a positive factor in the public interest test. The direct impacts of the project on 149 acres of wetlands alongside the roadway is not as large or significant as the impact caused by placement of the original embankment and resulting cut off of the eastern and western portions of the Everglades north of the C-111 canal. Overall, the concurrent and upfront mitigation efforts of FDOT are of regional significance and benefit to Everglades ecosystem by helping to repair the damage caused by the original embankment. THE PROJECT IS CLEARLY IN THE PUBLIC INTEREST The District appropriately weighed all considerations in determining that the project is clearly in the public interest. The greater weight of the competent, credible evidence established that the project is clearly in the public interest. RIGHT OF WAY PERMIT APPLICATION The land encompassed by the ROW permit has been properly adopted as a "work" of the District, requiring District authorization via a ROW Permit Modification to FDOT. The District's real property interest in the C-111 ROW applicable to the ROW permit modification consists of both fee simple and easement interests. The evidence is clear that DOT's application for the permit modification was thoroughly reviewed by the District, consistent with the District's established ROW permit review process. The District presented uncontroverted evidence and expert testimony to establish by a preponderance of the evidence that issuance of the permit modification to FDOT is consistent with all applicable District statutes, rules and other criteria, including the District's conditions for issuance of ROW Permits set forth in Rule 40E-6.301, F.A.C. FBII offered no evidence or testimony to the contrary. FUTURE MODIFICATIONS Modifying the project at a later date to pave a second southbound lane would require a District ERP permit. The addition of impervious surface triggers the District's SWM jurisdiction in this regard. However, FDOT established that that it had no current plans for further widening. The permit conditions require secondary and cumulative impacts associated with the increased capacity be addressed in accordance with the rules and criteria in effect at the time of any application for future widening. In addition, the permits require that FDOT must comply with any more stringent water quality criteria in effect at the time of any future widening. MODIFICATIONS AT THE FINAL HEARING At the Final Hearing, the District issued an Addendum to Staff Report for each of the SWM and WRM permits. The amendments made non-substantive changes to the District's staff reports regarding fencing along the roadway, performance of a study of fencing on the roadway by FDOT, water quality sampling along the roadway, assignment of mitigation credits, and other technical changes in wording for purposes of clarification. The changes set forth in the District's Exhibits 5 and 6 do not create impacts to the environment beyond those addressed elsewhere herein.
Recommendation Based on the foregoing findings of fact and conclusions of law it is RECOMMENDED that the Governing Board of the South Florida Water Management District enter a Final Order that issues the three permits challenged in this proceeding (SWM Permit No. 940606-10, WRM Permit No. 9460606-2-D, and ROW Permit No. 2584) subject to the conditions contained in the staff reports on the SWM permit application and the WRM permit application and subject to the additional permit conditions reflected by District Exhibits 5 and 6 and by the Findings of Fact pertaining to the permit for the relocation of the FKAA pipe. DONE AND ENTERED this 11th day of April, 1997, in Tallahassee, Leon County, Florida. ___________________________________ CLAUDE B. ARRINGTON Administrative Law Judge Division of Administrative Hearings Hearings The DeSoto Building 1230 Apalachee Parkway Tallahassee, Florida 32399-3060 (904) 488-9675 SUNCOM 278-9675 Fax Filing (904) 921-6847 Filed with the Clerk of the Division of Administrative this 11th day of April, 1997.
Findings Of Fact By application number 21312, the applicant seeks a ten year water use permit for a total annual diversion of 3,831 million gallons to provide water and sewer services to an area containing approximately 7,300 acres. In September of 1969, the Florida Public Service Commission granted the applicant certificates of convenience and necessity. The existing facilities of the applicant include nine wells and an average capacity of 700 gallons per minute each. Based upon historical data and taking into accourt the reduction of construction in the service area, the projected 1984 water demand is 375 gallons per day per unit. This is equivalent to an average of 150 gallons per day per person, using a figure of 2.5 persons per living unit. The ultimate estimated population is to be 70,000 to 80,000 people with 28,000 to 32,000 living units. Based upon the average capacities of the wells, in order to meet the projected demand a total number of 22 or 23 wells will be required. This includes the nine existing wells, eleven proposed wells with the same 700 gallon per minute average and a fifteen percent standby capability of two or three additional wells. Rather than the total number of wells utilized -- 22 or 23, -- what is important is the total gallon per minute capacity of 15,400. An allocation based on this data would be equal to the applicant's requested annual maximum diversion of 3,831 million gallons and a daily maximum diversion of 18.37 million gallons. The requested diversion presents no threat of salt water intrusion. The proposed well sites will create no adverse impact upon the Fort Lauderdale well fields. While there is evidence of recharge to the aquifer from runoff waters, there is insufficient data to determine the exact amount which will be returned. For this reason, the staff report's water budget calculations are conservative.
Recommendation Based upon the above findings of fact and conclusions of law, it is recommended that a ten year permit be issued to the applicant for a maximum annual diversion of 3,831 million gallons; a maximum daily diversion of 18.37 million gallons and a maximum installed field capacity of 15,400 gallons per minute, utilizing 22 or 23 wells with a capacity of 700 gallons per minute each. It is further recommended that the applicant be subject to the conditions set forth on page 5 of the staff report (Exhibit 8) concerning the submission of monthly reports of daily pumpage and actual connections or population served, conformance with health department standards of the water quality of all wells, and the installation and maintenance of an observation well and monthly reports of the data obtained therefrom. Respectively submitted and entered this 10th day of May, 1976, in Tallahassee, Florida. DIANE D. TREMOR Hearing Officer Division of Administrative Hearings Room 530, Carlton Building Tallahassee, Florida 32304 COPIES FURNISHED: Mr. John R. Maloy Executive Director Central and Southern Florida Flood Control District P.O. Box V West Palm Beach, Florida 33402 Mr. Edward B. Deutsch 350 Southern Federal Building 400 North State Road 7 Margate, Florida 33063 Mr. John Wheeler P.O. Box V West Palm Beach, Florida 33402 Attorney for the Central and Southern Florida Flood Control District
The Issue The issue is whether the applicant for an Environmental Resource Permit ("ERP"), the City of Deltona ("City" or "Applicant"), has provided reasonable assurance that the system proposed complies with the water quantity, environmental, and water quality criteria of the St. Johns River Water Management District's ("District") ERP regulations set forth in Florida Administrative Code Chapter 40C-4, and the Applicant's Handbook: Management and Storage of Surface Waters (2005).
Findings Of Fact The District is a special taxing district created by Chapter 373, Florida Statutes, charged with the duty to prevent harm to the water resources of the District, and to administer and enforce Chapter 373, Florida Statutes, and the rules promulgated thereunder. The City of Deltona is a municipal government established under the provisions of Chapter 165, Florida Statutes. The Lake Theresa Basin is comprised primarily of a system of interconnected lakes extending from Lake Macy in the City of Lake Helen to the Butler Chain of Lakes (Lake Butler and Lake Doyle). The Lake Theresa Basin is land-locked and does not have a natural outfall to Lake Monroe and the St. Johns River. In 2003, after an extended period of above-normal rainfall in the Deltona area, the lakes within the land-locked Lake Theresa Basin staged to extremely high elevations that resulted in standing water in residential yards, and rendered some septic systems inoperable. Lake levels within the Lake Theresa Basin continued to rise and were in danger of rising above the finished floor elevations of some residences within the basin. On March 25, 2003, the District issued an Emergency Order (F.O.R. No. 2003-38) authorizing the construction and short-term operation of the Lake Doyle and Lake Bethel Emergency Overflow Interconnection. Since wetland and surface water impacts would occur, the Emergency Order required the City of Deltona to obtain an ERP for the system. The project area is 4.1 acres, and the system consists of a variable water structure on the west shore of Lake Doyle connected to a series of pipes, swales, water control structures, and wetland systems which outfall to a finger canal of Lake Bethel, with ultimate discharge to Lake Monroe and the St. Johns River. The first segment of the system extends downstream from the weir structure on the west shore of Lake Doyle via a pipe entrenched in the upland berm of the Sheryl Drive right-of-way. The pipe passes under Doyle Road and through xeric pine-oak uplands to the northeast shore of a large (approximately 15 acres) deepwater marsh. Water flows south through the deepwater marsh where it outfalls through four pipes at Ledford Drive. Two of the four pipes are overflow structures, controlled by canal gates. The pipes at Ledford Drive discharge into a ditch and into a large (greater than 20 acres) shallow bay swamp. The south end of the bay swamp is defined (and somewhat impounded) by a 19th Century railroad grade. Water flows through the bay swamp where it outfalls through five pipes at the railroad grade. Three of the five pipes are overflow structures, controlled by channel boards. The pipes at the railroad grade discharge to a 1500-foot long finger canal that was dug some time during the period 1940-1972 from the north central shore of Lake Bethel. The overflow interconnection system has three locations whereby the system can be shut down: 1) Lake Doyle--a control weir, controlled by three sluice gates; 2) Ledford Drive--two thirty-inch reinforced concrete pipes, controlled by canal gates; and 3) railroad grade--three thirty-inch reinforced concrete pipes, controlled by channel boards (collectively referred to as "Overflow Structures"). The Overflow Structures are designed to carry the discharge of water from Lake Doyle to Lake Bethel. With the Overflow Structures closed the system returns to pre-construction characteristics, meaning there will be no increase or decrease in the quantity or quality of water throughout the path of the system as a result of the project. An unequivocal condition of the permit is that the system would operate with all of the Overflow Structures closed. As an added assurance, the City proposes to place a brick and mortar plug in the Lake Doyle weir structure outfall pipe to prevent any discharge from the weir. The City has submitted to the District preliminary plans for a future phase in which the system would be modified for the purpose of alleviating high water levels within the Lake Theresa Basin when the water level in Lake Doyle rises above an elevation of 24.5 feet. The District shall require a separate permit application to be submitted for such future plans. Petitioner, Barbara Ash, has lived on Lake Theresa for 19 years. Ms. Ash lives upstream from the area of the weir that will be plugged in accordance with the ERP. She does not trust either the City of Deltona to comply with or the District to enforce the conditions of the ERP applied for by the City. Petitioner, Barbara Ash, also served as the qualified representative for Petitioners, Francell Frei, Bernard J. and Virginia Patterson, and Ted and Carol Sullivan. Ms. Ash represented that Ms. Frei has lived on Lake Theresa for 12 years, and both the Pattersons and the Sullivans live on Lake Louise, which is within the area of concern in this proceeding. Petitioner, Diana Bauer, has lived on Lake Theresa since February 2004. She fears that the lake will become too dry if the system is allowed to flow. She also believes the wildlife will be adversely affected if the water levels are too low since many species need a swampy or wet environment to thrive. She fears her property value will decrease as a result of the approval of the ERP. She also does not trust either the City to comply with or the District to enforce the conditions of the ERP. Petitioner, Howard Ehmer, lives two to three hundred yards down Lake Theresa from Ms. Bauer. He is concerned about the lake bed being too dry and attracting people on all terrain vehicles who enjoy driving around the lake bottom. He is concerned about his property value decreasing if the lake bed is dry. Further, when the lake level is too low, people cannot enjoy water skiing, boating, and fishing on Lake Theresa. Petitioner, Phillip Lott, a Florida native, has also owned and lived on property abutting Lake Theresa since 1995. Mr. Lott has a Ph.D. in plant ecology, and M.P.A. in coastal zone studies, an M.B.A. in international business, and a B.S. in environmental resource management and planning. Mr. Lott has been well acquainted with the water levels on Lake Theresa for many years. Based upon his personal observations of the lake systems in the Deltona area over the years, Mr. Lott has seen levels fluctuate greatly based upon periods of heavy and light rainfall. Mr. Lott is concerned that the District will permit the City to open the weir to let water flow through the system and cause flooding in some areas and low water levels in other areas. He fears that the District will allow the water to flow and upset the environmental balance, but he admits that this ERP application is for a closed system that will not allow the water to flow as he fears. Mr. Lott similarly does not trust the City to comply with and the District to enforce the conditions of the ERP. Petitioners, James E. and Alicia M. Peake, who were represented by Steven L. Spratt at hearing as their qualified representative, live on Lake Louise, which is interconnected with the Lake Theresa basin. The Peakes are concerned that if the level of Lake Louise drops below 21 feet, nine inches, they will not be able to use the boat launch ramps on the lake. Petitioner, Steven L. Spratt, also lives on Lake Louise, and is concerned about the water levels becoming so low that he cannot use the boat launch on the lake. He has lived on the lake since 2000, and remembers when the water level was extremely low. He fears that approval of the ERP in this case will result in low levels of water once again. Petitioner, Gloria Benoit, has live on Lake Theresa for two years. She also enjoys watching recreational activities on the lake, and feels that approval of the ERP will devalue her lakefront property. Ms. Benoit appeared at the first day of the hearing, but offered no testimony on her behalf. J. Christy Wilson, Esquire, appeared prior to the final hearing as counsel of record for Petitioners, Steven E. Larimer, Kathleen Larimer, and Helen Rose Farrow. Neither Ms. Wilson nor any of the three Petitioners she represented appeared at any time during the hearing, filed any pleadings seeking to excuse themselves from appearing at the final hearing, or offered any evidence, testimony, pre- or post- hearing submittals. Petitioner, Gary Jensen, did not appear at hearing, did not file any pleadings or papers seeking to be excused from appearing at the final hearing, and did not offer any evidence, testimony, pre- or post-hearing submittals. Both the City and the District recognize that areas downstream from the project site, such as Stone Island and Sanford, have experienced flooding in the past in time of high amounts of rainfall. The system proposed by the City for this ERP will operate with the overflow structures closed and a brick and mortar plug in the outfall pipe to prevent water flow from Lake Doyle to Lake Bethel. So long as the overflow structures are closed, the system will mimic pre-construction flow patterns, with no increase in volume flowing downstream. The District has considered the environment in its proposed approval of the ERP. The area abutting the project is little urbanized and provides good aquatic and emergent marsh habitat. With the exception of the western shore area of the deepwater marsh ("west marsh area"), the bay swamp and remaining deepwater marsh area have good ecological value. In the 1940's, the west marsh area was incorporated into the drainage system of a poultry farm that occupied the site. This area apparently suffered increased nutrient influxes and sedimentation that contributed to a proliferation of floating mats of aquatic plants and organic debris. These tussocks reduced the deepwater marsh's open water and diminished the historical marsh habitat. Water under the tussocks is typically anoxic owing to total shading by tussocks and reduced water circulation. Thick, soft, anaerobic muck has accumulated under the matted vegetation. Exotic shrubs (primrose willow Ludwigia peruvania) and other plants (cattails Typha spp.) dominate the tussocks. The construction of the project, from the 2003 Emergency Order, resulted in adverse impacts to 1.3 acres of wetlands having moderately high- to high ecological value and 0.2 acres of other surface waters. The 0.2 acre impact to other surface waters was to the lake bottom and the shoreline of Lake Doyle where the weir structure was installed. The 0.3 acres of wetland impacts occurred at the upper end of the deepwater marsh where the pipe was installed. The largest wetland impact (1.0 acre) was to the bay swamp. The bay swamp is a shallow body dominated by low hummocks and pools connected inefficiently by shallow braided channels and one acre is filled with a 1-2 foot layer of sediment following swamp channelization. Disturbance plants (e.g., primrose willow, Ludwigia peruvania, and elderberry Sambucus Canadensis) now colonize the sediment plume. Pursuant to the District's elimination and reduction criteria, the applicant must implement practicable design modifications, which would reduce or eliminate adverse impacts to wetlands and other surface waters. A proposed modification, which is not technically capable of being done, is not economically viable, or which adversely affects public safety through endangerment of lives or property is not considered "practicable." The City reduced and/or eliminated the impacts to the lake bottom and shoreline of Lake Doyle and deepwater marsh, to the extent practicable. The impacts were the minimum necessary to install the weir structure and pipe for the system; the weir structure and pipe were carefully installed on the edges of the wetland and surface water systems, resulting in a minimum amount of grading and disturbance. To compensate for the loss of 1.3 acres of wetlands and 0.2 acres of other surface waters, the City proposes to preserve a total of 27.5 acres of wetlands, bay swamp, marsh, and contiguous uplands. Included in this 27.5 acres are 6.4 acres of the west marsh, which are to be restored. The parties stipulated that the mitigation plan would adequately compensate for losses of ecological function (e.g. wildlife habitat and biodiversity, etc.) resulting from the project. Water quality is a concern for the District. Lake Monroe is included on the Florida Department of Environmental Protection's verified list of impaired water bodies for nitrogen, phosphorous, and dissolved oxygen. Water quality data for Lake Monroe indicate the lake has experienced high levels of nitrogen and phosphorous and low levels of dissolved oxygen. Prior to construction of the project, there was no natural outfall from the Lake Theresa Basin to Lake Monroe and therefore no contribution from this basin to nitrogen and phosphorous loadings to Lake Monroe. Lake Colby, Three Island Lakes (a/k/a Lake Sixma), and the Savannah are surface waters within the Lake Theresa Basin for which minimum levels have been adopted pursuant to Florida Administrative Code Chapter 40C-8. The system will operate with the overflow structures closed and a brick and mortar plug in the outfall pipe to prevent water flow from Lake Doyle to Lake Bethel, resulting in no outfall from the Theresa Basin to Lake Monroe. Minimum flows established for surface waters within the Lake Theresa Basin will not be adversely impacted. Under the first part of the secondary impact test, the City must provide reasonable assurance that the secondary impacts from construction, alteration, and intended or reasonable expected use of the project will not adversely affect the functions of adjacent wetlands or surface waters. The system is designed as a low intensity project. As proposed, little activity and maintenance are expected in the project site area. The reasonably expected use of the system will not cause adverse impacts to the functions of the wetlands and other surface waters. None of the wetland areas adjacent to uplands are used by listed species for nesting or denning. In its pre-construction state, the project area did not cause or contribute to state water quality violations. Under the second part of the secondary impact test, the City must provide reasonable assurance that the construction, alteration, and intended or reasonably expected uses of the system will not adversely affect the ecological value of the uplands to aquatic or wetland dependent species for enabling existing nesting or denning by these species. There are no listed threatened or endangered species within the project site area. Under the third part of the secondary impact test, and as part of the public interest test, the District must consider any other relevant activities that are closely linked and causally related to any proposed dredging or filling which will cause impacts to significant historical and archaeological resources. When making this determination, the District is required, by rule, to consult with the Division of Historical Resources. The Division of Historical Resources indicated that no historical or archaeological resources are likely present on the site. No impacts to significant historical and archaeological resources are expected. Under the fourth part of the secondary impact test, the City must demonstrate that certain additional activities and future phases of a project will not result in adverse impacts to the functions of wetlands or water quality violations. The City has submitted to the District preliminary plans for a future phase in which the system would be modified for the purpose of alleviating high water levels within the Lake Theresa Basin when the level in Lake Doyle rises above an elevation of 24.5 feet. Based upon the plans and calculations submitted, the proposed future phase, without additional measures, could result in minor increases in the loadings of nitrogen and phosphorous to Lake Monroe. Lake Monroe is included on the Florida Department of Environmental Protection's verified list of impaired water bodies due to water quality data indicating the lake has experienced high levels of nitrogen and phosphorous, and low levels of dissolved oxygen. Under this potential future phase, there would be an outfall from the Lake Theresa Basin to Lake Monroe. To address the impact on water quality of this potential future phase, the City has submitted a loading reduction plan for nitrogen, phosphorous, and dissolved oxygen. The plan includes compensating treatment to fully offset the potential increased nutrient loadings to Lake Monroe. Specifically, the loading reduction plan includes: Construction and operation of compensating treatment systems to fully offset anticipated increased nutrient loadings to Lake Monroe. Weekly water quality monitoring of the discharge from Lake Doyle for total phosphorous and total nitrogen. A requirement that the overflow structure be closed if the total phosphorous level reaches 0.18 mg/l or higher or the total nitrogen level reaches 1.2 mg/l or higher in any given week and will remain closed until levels fall below those limits. The implementation of these water quality mitigation measures will result in a net improvement of the water quality in Lake Monroe for nitrogen, phosphorous, or dissolved oxygen. The future phase was conceptually evaluated by the District for impacts to wetland functions. The future phase as proposed could result in adverse impacts to wetland functions. Operation of the system with the overflow structures open could impact the bay swamp and deepwater marsh. The City has demonstrated that any adverse impacts could be offset through mitigation. Based upon the information provided by the City and general engineering principles, the system is capable of functioning as proposed. The City of Deltona will be responsible for the operation, maintenance, and repair of the surface waster management system. A local government is an acceptable operation and maintenance entity under District rules. The public interest test has seven criteria. The public interest test requires the District to evaluate only those parts of the project actually located in, on, or over surface waters or wetlands, to determine whether a factor is positive, neutral, or negative, and then to balance these factors against each other. The seven factors are as follows: the public health, safety, or welfare of others; conservation of fish and wildlife and their habitats; fishing, recreational value, and marine productivity; temporary or permanent nature; 5) navigation, water flow, erosion, and shoaling; 6) the current condition and relative value of functions; and 7) historical and archaeological resources. There are no identified environmental hazards or improvements to public health and safety. The District does not consider impacts to property values. To offset any adverse impacts to fish and wildlife and their habitats, the City has proposed mitigation. The areas of the project in, on, or over wetlands do not provide recreational opportunities. Construction and operation of the project located in, on, or over wetlands will be permanent in nature. Construction and operation of the project located in, on, or over wetlands will not cause shoaling, and does not provide navigational opportunities. The mitigation will offset the relative value of functions performed by areas affected by the proposed project. No historical or archaeological resources are likely on the site of the project. The mitigation of the project is located within the same drainage basin as the project and offsets the adverse impacts. The project is not expected to cause unacceptable cumulative impacts.
Recommendation Based upon the Findings of Fact and Conclusions of Law, it is RECOMMENDED that a Final Order be entered granting the City of Deltona's application for an environmental resource permit with the conditions set forth in the Technical Staff Report, and dismissing the Petitions for Formal Administrative Hearing filed by Gary Jensen in Case No. 04-2405, and by Steven E. Larimer, Kathleen Larimer, and Helen Rose Farrow in Case No. 04-3048. DONE AND ENTERED this 27th day of May, 2005, in Tallahassee, Leon County, Florida. S ROBERT S. COHEN 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 27th day of May, 2005. COPIES FURNISHED: George Trovato, Esquire City of Deltona 2345 Providence Boulevard Deltona, Florida 32725 Diana E. Bauer 1324 Tartan Avenue Deltona, Florida 32738 Barbara Ash, Qualified Representative 943 South Dean Circle Deltona, Florida 32738-6801 Phillip Lott 948 North Watt Circle Deltona, Florida Howard Ehmer Nina Ehmer 32738-7919 1081 Anza Court Deltona, Florida 32738 Francell Frei 1080 Peak Circle Deltona, Florida 32738 Bernard T. Patterson Virginia T. Patterson 2518 Sheffield Drive Deltona, Florida 32738 Kealey A. West, Esquire St. Johns River Water Management District 4049 Reid Street Palatka, Florida 32177 J. Christy Wilson, Esquire Wilson, Garber & Small, P.A. 437 North Magnolia Avenue Orlando, Florida 32801 Gloria Benoit 1300 Tartan Avenue Deltona, Florida 32738 Gary Jensen 1298 Tartan Avenue Deltona, Florida 32738 James E. Peake Alicia M. Peake 2442 Weatherford Drive Deltona, Florida 32738 Steven L. Spratt 2492 Weatherford Drive Deltona, Florida 32738 Ted Sullivan 1489 Timbercrest Drive Deltona, Florida 32738 Kirby Green, Executive Director St. Johns River Water Management District 4049 Reid Street Palatka, Florida 32177
The Issue Petitioners challenge the South Florida Water Management District’s (the District) proposed action to issue Individual Environmental Resource Permit (ERP) 50-06558-P to authorize conceptual approval of a surface water management (SWM) system to serve 1,919 acres of a phased, multiple-use development referred to as the Palm Beach County Biotechnolgy Research Park (BRP) and to authorize construction and operation of Phase 1A of that proposed project. The ultimate issue is whether the Applicants provided reasonable assurances that the proposed activities will not be harmful to the water resources of the District; will not be inconsistent with the overall objectives of the District; and will comply with the water quantity, environmental, and water quality criteria of the District’s ERP regulations, which are set forth in Part IV of Chapter 373, Florida Statutes, Florida Administrative Code Chapter 40E-4, et. seq.; and the Basis of Review for Environmental Resource Permit Applications Within the South Florida Water Management District – September 2003 (BOR).1
Findings Of Fact THE PARTIES The Florida Wildlife Federation, Audubon Society of the Everglades, and Jupiter Farms Environmental Council, Inc. (d/b/a Loxahatchee River Coalition) are not-for-profit corporations in existence prior to 2003 with more than 25 members in Palm Beach County. Palm Beach County Environmental Coalition was formed in 1997 and is a private, county-wide, non-profit citizen’s organization. Ms. Ketter, Mr. Bell, Ms. Larson, and Mr. Christensen are individuals affected by the proposed BRP. The Respondents stipulated that the parties who remained Petitioners after Mr. Silver’s withdrawal as a Petitioner have standing to bring this proceeding. The District, a public corporation existing by virtue of Chapter 25270, Laws of Florida, 1949, operates pursuant to Chapter 373, Florida Statutes, and Title 40E, Florida Administrative Code, as a multipurpose water management district with its principal office in West Palm Beach, Florida. The County is a duly-constituted governmental entity. THE PROJECT SITE AND ADJACENT LANDS The site of the project is generally referred to as the Mecca Farms, which is a contiguous tract of 1,919 acres of land. At present, the Mecca Farms is used for farming and mining operations. There presently exists a permitted, SWM system on the Mecca Farms that was first permitted in 1979, and has been modified from time to time since then. The existing SWM system includes 73 acres of ditches and a 272-acre above-ground impoundment area. The Mecca Farms site is located within the C-18 Basin. There are no jurisdictional wetlands or delineated surface waters on the Mecca Farms. The following, which is taken from the Staff Report (SFWMD Ex. 1), accurately describes the project site and its adjacent lands: The project site consists of 1,919 acres presently supporting an active orange grove with approximately 73 acres of associated drainage and irrigation ditches/canals and a 30-acre active sand mining operation. The ditches/canals are presently maintained at an elevation of approximately 17 feet NGVD.[3] These ditches/canals provide drainage conveyance to a 272-acre above- ground impoundment located in the northeast corner of the site utilizing four (4) 22,000 gpm pumps. The above-ground impoundment discharges to the west leg of the C-18 Canal via gravity discharge. Project site ditches and canals also connect directly to the C-18 Canal through an 18,000 gpm pump. An additional 224-acre agricultural area east of the 1,919 acres of orange groves is connected to and drains into the canal/ditch system on the project site. This adjacent area was leased from the adjacent land owner by the grove owner for use as row crops and was connected to the grove canal/ditch system for better control of drainage and irrigation. The area is no longer used for row crops. There is also a small area on the site that contains caretaker housing and an equipment maintenance building for the orange groves. These facilities were originally permitted in 1979 under Surface Water Management Permit No. 50-00689-S and subsequent modifications. The citrus grove and primary drainage facilities have been in existence since the 1960s. The Hungryland Slough is located north of the project site, separated from the project site by the C-18 Canal. This area is comprised primarily of publicly-owned natural areas, including an area referred to as Unit 11, which is owned in the majority by Palm Beach County. To the west is the J.W. Corbett Wildlife Management Area (CWMA) owned and managed by the Florida Fish and Wildlife Conservation Commission (FFWCC). To the east, a large area of low-intensity agricultural land exists under the ownership of Charles Vavrus and within the City of Palm Beach Gardens. These lands contain extensive wetlands that are adjacent to the Loxahatchee Slough to the east. The Acreage, a low-density residential area, is located directly to the south of the project site. The only access to the site at this time is an unpaved extension of Seminole Pratt-Whitney Road (SPW), connecting the site at its southwestern corner to the Acreage. THE PROPOSED PROJECT The subject application is for conceptual approval of the SWM system for the BRP and for construction and operation of Phase 1A of the project. All of the proposed Phase 1A construction will occur on the Mecca Farms site. The following, taken from the Staff Report, accurately describes the proposed project: The [BRP] is a phased multiple use development planned for approximately 1,919 acres and will consist of land uses related to science and technology, biotechnology, biomedical, and other related research and development industries and manufacturing. Additionally, proposed support and complementary land uses include educational, institutional, residential, commercial, and recreational facilities, along with utilities and a large created natural area. THE PROPOSED SWM SYSTEM The proposed SWM system will consist of several interconnected lakes that will provide wet detention for storm water runoff from the property site and from 39 acres of off- site flows from SPW Road and a proposed Florida Power and Light (FPL) Substation. The lakes will collect, store, and treat the runoff. The storm water will pass through the lakes, through a 247-acre area referred to as the “Natural Area” (which will be created as part of the mitigation plan), and discharged to the C-18 Canal. To provide additional water quality treatment, these lakes will include planted littoral zones and the southern lake will include a filter marsh. The Natural Area will, in subsequent construction phases, be constructed on the western boundary of the Mecca site with discharge to the C-18 canal, which is adjacent to the northern boundary of the Mecca Farms. The southern boundary of the Natural Area will be the north boundary of the lake that is to be constructed on the southern end of the property. This is the area that is available for use as a flow-way (which will be discussed in greater detail in a subsequent section of this Recommended Order). The Natural Area will be a wetland type system that will move water slowly through that system providing additional storage and water quality benefits prior to discharging through a gravity control structure into the C-18 Canal. The C-18 Canal discharges to either the Northwest or Southwest Fork of the Loxahatchee River, depending on how structures are operated downstream. Discharges travel in the C-18 Canal for approximately nine miles before reaching the Loxahatchee River. The existing SWM system for the Mecca Farms currently discharges to the C-18 Canal, as will the proposed SWM system. The proposed project will not discharge to the CWMA or the Hungryland Slough. The Grassy Waters Preserve and the Loxahatchee Slough are several miles from the project site and will not be affected by the project’s proposed activities. The following, which is taken from the Staff Report, accurately describes the proposed SWM system. The proposed conceptual surface water management system which will serve the 1,919-acre site will consist of site grading, storm water inlets and culverts which will direct all runoff to a series of interconnected lakes for water quality treatment and attenuation of the peak runoff rate. Pumps will control the runoff rate from the developed site into the adjacent onsite BRP natural area. The BRP natural area will discharge into the C-18 canal via a gravity control structure. The system has been designed to accommodate 39 acres of off-site flows from SPW [Road] and a proposed Florida Power and Light (FPL) Substation. The existing control elevation of the citrus grove is 17.0’ NGVD. The proposed control elevations are 18.0’ NGVD for the developed area and 19.0’ NGVD for the natural area. The control elevations are being raised to provide a “step down” of water elevations from wetlands to the north, west and east of the site (20.5’ to 21.0’) to lower elevations to the south (17.0’). PHASE 1A CONSTRUCTION The following, which is taken from the Staff Report, accurately describes the proposed Phase 1A construction: The Phase 1A construction activities will allow the applicant to proceed with lake excavation, clearing and site grading of 536 acres in the southern portion of the site. No permanent buildings or parking areas are proposed at this time. Stormwater from Phase 1A and the remainder of the site, to remain in agricultural use, will be treated in the Phase 1A lakes and then pumped into the existing impoundment for additional water quality treatment and attenuation prior to discharging to the west leg of the C-18 Canal via the existing weir structures. The existing 18,000 gpm pump that connects the on-site ditches and canals directly to the C-18 Canal will remain, but will only be used if the impoundment is full. (See Special Condition No. 21). Approval of Phase 1A authorizes the use of the existing, previously permitted surface water management facilities, therefore, the previous permit no. 50-00689-S is superceded by this permit. The 224 acre agricultural area east of the existing grove that is connected to the grove canal/ditch system will be severed as part of Phase 1A. The pipe connecting this area will be removed and portions of the berm around this area will be regraded so the area will sheetflow into the adjacent pasture land’s canal/ditch system as it did previously [sic] to being connected to the grove system. Of the 536 acres involved in the Phase 1A construction, 87 acres will become lake bottom and 449 acres will remain pervious area, subject only to grading. CONCEPTUAL APPROVAL Pertinent to this proceeding, Florida Administrative Code Rule 40E-4.021(5) defines the term “conceptual approval” to mean an ERP issued by the District which approves a conceptual master plan for a surface water management system or a mitigation bank. Florida Administrative Code Rule 40E-4.305, pertains to conceptual approvals and provides, in relevant part, as follows: Conceptual approvals constitute final District action and are binding to the extent that adequate data has been submitted for review by the applicant during the review process. A conceptual approval does not authorize construction, alteration, operation, maintenance, removal, or abandonment of a surface water management system or the establishment and operation of a mitigation bank. * * * For phased projects, the approval process must begin with an application for a conceptual approval which shall be the first permit issued for the project. An application for construction authorization of the first phase(s) may also be included as a part of the initial application. As the permittee desires to construct additional phases, new applications shall be processed as individual or standard general environmental resource permit applications pursuant to the conceptual approval. The conceptual approval, individual and standard general permits shall be modified in accordance with conditions contained in Chapters 40E-4 and 40E-40, F.A.C. Issuance of a conceptual approval permit pursuant to Chapter 40E-4, F.A.C., shall not relieve the applicant of any requirements for obtaining a permit to construct, alter, operate, maintain, remove, or abandon a surface water management system or establish or operate a mitigation bank, nor shall the conceptual approval permit applicant be relieved of the District’s informational requirements or the need to meet the standards of issuance of permits pursuant to Chapters 40E-4 or 40E-40, F.A.C. . . . PERMITTING CRITERIA In order to obtain an ERP, an applicant must satisfy the conditions for issuance set forth in Florida Administrative Code Rules 40E-4.301 and 40E-4.302. The conditions for issuance focus on water quantity criteria, environmental criteria, and water quality criteria. Florida Administrative Code Rule 40E-4.301 contains the following permitting conditions applicable to this proceeding: In order to obtain a standard general, individual, or conceptual approval permit ... an applicant must provide reasonable assurance that the construction, alteration, operation, maintenance, removal, or abandonment of a surface water management system: will not cause adverse water quantity impacts to receiving waters and adjacent lands; will not cause adverse flooding to on-site or off-site property; will not cause adverse impacts to existing surface water storage and conveyance capabilities; will not adversely impact the value of functions provided to fish and wildlife and listed species by wetlands and other surface waters; will not adversely affect the quality of receiving waters ...; will not cause adverse secondary impacts to the water resources; will not adversely impact the maintenance of surface or ground water levels or surface water flows ...; will not cause adverse impacts to a work of the District ...; will be capable, based on generally accepted engineering and scientific principles, of being performed and of functioning as proposed; will be conducted by an entity with the sufficient financial, legal and administrative capability to ensure that the activity will be undertaken in accordance with the terms and conditions of the permit, if issued; and will comply with any applicable special basin or geographic area criteria established in Chapter 40E-41 F.A.C. Florida Administrative Code Rule 40E-4.302 provides the following Additional Conditions for Issuance of Permits applicable to this proceeding: In addition to the conditions set forth in section 40E-4.301, F.A.C., in order to obtain a standard general, individual, or conceptual approval permit under this chapter or Chapter 40E-40, F.A.C., an applicant must provide reasonable assurance that the construction, alteration, operation, maintenance, removal, and abandonment of a system: Located in, on, or over wetlands or other surface waters will not be contrary to the public interest, or if such an activity significantly degrades or is within an Outstanding Florida Water, that the activity will be clearly in the public interest, as determined by balancing the following criteria as set forth in subsections 4.2.3 through 4.2.3.7 of the Basis of Review for Environmental Resource Permit Applications Within the South Florida Water Management District: Whether the activity will adversely affect the public health, safety or welfare or the property of others; Whether the activity will adversely affect the conservation of fish and wildlife, including endangered or threatened species, or their habitats; Whether the activity will adversely affect navigation or the flow of water or cause harmful erosion or shoaling; Whether the activity will adversely affect the fishing or recreational values or marine productivity in the vicinity of the activity; Whether the activity will be of a temporary or permanent nature; Whether the activity will adversely affect or will enhance significant historical and archaeological resources under the provisions of Section 267.061, F.S.; and The current condition and relative value of functions being performed by areas affected by the proposed activity. Will not cause unacceptable cumulative impacts upon wetlands and other surface waters as set forth in subsections 4.2.8 through 4.2.8.2 of the Basis of Review. . . . THE BASIS OF REVIEW The District has adopted the BOR and incorporated it by reference by Florida Administrative Code Rule 40E- 4.091(1)(a). The standards and criteria found in the BOR are used to determine whether an applicant has given reasonable assurances that the conditions for issuance of an ERP have been satisfied. Section 1.3 of the BOR provides, in part, as follows: . . . Compliance with the criteria established herein [the BOR] constitutes a presumption that the project proposal is in conformance with the conditions for issuance set forth in Rules 40E-4.301 and 40E-4.302, F.A.C. WATER QUANTITY The term “control elevation” describes the level of freshwater water bodies established by a SWM system. The existing SWM system has a control elevation of 17’ NGVD. The control elevation for the proposed lake system will be raised to 18’ NGVD, and the control elevation for the proposed Natural Area will be raised to 19’ NGVD. Raising the control elevations will permit more treatment of storm water prior to discharge and will permit a more controlled discharge. In addition, raising the control elevation will lessen seepage onto the project site from adjacent wetlands. The Applicants provided reasonable assurances that the proposed project will not cause adverse water quantity impacts to receiving waters and adjacent lands, thereby satisfying the criteria set forth in Florida Administrative Code Rule 40E- 4.301(a). The Applicants provided reasonable assurances that the proposed project will not cause adverse flooding to on-site or off-site property, thereby satisfying the criteria set forth in Florida Administrative Code Rule 40E-4.301(b). The Applicants provided reasonable assurances that the proposed project will not cause adverse impacts to existing surface water storage and conveyance capabilities, thereby satisfying the criteria set forth in Florida Administrative Code Rule 40E-4.301(c). VALUE OF FUNCTIONS OF WETLANDS AND SURFACE WATERS Florida Administrative Code Rule 40E-4.301(d), requires the Applicants to establish that “. . . the construction, alteration, operation, maintenance, removal, or abandonment of a surface water management system . . .” “. . . will not adversely impact the value of functions provided to fish and wildlife and listed species by wetlands and other surface waters.” The District established that the term “value of functions,” as used in the rule, refers to habitat and life support functions. Because there are no wetlands or delineated surface waters on the Mecca Farms site, there are no direct adverse impacts to the functions that wetlands provide to fish and wildlife. The Applicants have provided reasonable assurances to demonstrate that the value of functions provided to fish and wildlife and listed species by wetlands and other surface waters will not be adversely affected. The existing project site does not contain nesting areas for wetland-dependent endangered or threatened wildlife species or species of special concern. The potential for use of the existing project site for nesting by such species is minimal. The existing project site does contain habitat for the American Alligator and foraging habitat for wading birds and birds of prey. The primary foraging habitat on the existing site is around the perimeter of the existing 272-acre impoundment area in the northeast portion of the site. The existing impoundment will be replaced by on-site storm water treatment lakes and the BRP Natural Area that will have shallow banks planted with wetland plant species common to the area. Wildlife is opportunistic; and wading birds commonly feed in areas where there is water, wetland vegetation and wetland plants. The end result will be that the proposed project will have more and better foraging habitat acreage than the existing site. The Natural Area will provide a wetland buffer between the developed area and CWMA that will prevent any adverse impacts both to the wetlands and other surface waters in CWMA and to the value of the functions those wetlands and other surface waters provide to fish, wildlife, and listed species. The Natural Area will provide a wetland buffer between the developed area and Unit 11 that will prevent any adverse impacts both to the wetlands and other surface waters in Unit 11 and to the value of the functions those wetlands and other surface waters provide to fish, wildlife, and listed species. There was no competent evidence that the proposed project would impact the ability of the Florida Fish and Wildlife Conservation Commission to manage the CWMA through control burns or otherwise, thereby adversely affecting the diversity or abundance of fish and wildlife (including endangered species and their habitats). Petitioners attempted to raise the issue of mosquito control in their Petitions and at the Final Hearing. The allegations pertaining to mosquito control were struck by the District and Special Condition Number 26 was added before the Petitions were referred to DOAH. Petitioners made no attempt to amend their Petitions and have not challenged Special Condition 26. The Addendum to Staff Report (SFWMD Ex. 2) contains the following Special Condition Number 26: “Upon submittal of an application for construction of any buildings, the permittee shall submit a mosquito control plan for review and approval by District Staff.” Since there will be no buildings containing people or other facilities which would encourage the use of mosquito spraying, it is appropriate for the mosquito control condition to apply to only future phases of construction. There was no competent evidence of impacts attributable to pesticides associated with the application for the SWM system or for Phase 1A construction and operation that would adversely affect the diversity or abundance of fish and wildlife including endangered species and their habitats. The Applicants have satisfied the criteria set forth in Florida Administrative Code Rule 40E-4.301(d). WATER QUALITY The primary concern during Phase 1A construction will be erosion control. Best Management Practices (“BMPs”) are operational and design elements used to either eliminate or reduce the amount of pollutants at the source so they do not get into a SWM system or move downstream. To contain erosion in Phase 1A, the Applicants will use the following BMPs: Silt screens and turbidity barriers within existing ditches and around the perimeter of property. Planned construction sequencing to reduce movement and stock piling of material; Slope stabilization and seeding or sodding of graded areas; and Containment of construction materials with berms. All erosion and turbidity control measures will remain in place until the completion of the on-site construction and approval by the District’s post-permit compliance staff. The Applicants provided reasonable assurances that the proposed Phase 1A construction activities will not adversely impact the quality of receiving waters and that those activities will not violate State water quality standards. Section 5.2.1, BOR, requires that a SWM system provide wet detention for the first one inch of runoff. The proposed SWM system will provide wet detention for one and one-half inches of runoff. The Applicants provided reasonable assurances to demonstrate that the technical criteria in the BOR will be met. Under Section 1.3 of the BOR, compliance with the criteria in the BOR constitutes a presumption that the Proposed Project is in conformance with the conditions for issuance. This presumption was not rebutted by the Petitioners. The lake system will include planted littoral zones to provide additional uptake of pollutants. A filter marsh is also included in the southern lake. All of the storm water runoff from the lakes will pass through the filter marsh, which will be planted with wetland plants. The filter marsh will provide additional polishing of pollutants, uptake, and filtering through the plants. The discharge will then go into the BRP, which will provide the discharge additional uptake and filtering. BMPs utilized during the Operations and Maintenance phase will include regular maintenance inspections and cleaning of the SWM system, street-sweeping, litter control programs, roadway maintenance inspections and repair schedule, municipal waste collection, pollution prevention education programs, pesticides, herbicides and fertilizer storage, and application training and education. The littoral zones, filter marsh, BRP natural area, and BMPs were not included in the water quality calculations and are over and above rule requirements. The Applicants provided reasonable assurances to demonstrate that the proposed project will not adversely affect the quality of receiving waters. Therefore, Rule 40E- 4.301(1)(e), F.A.C., will be satisfied and water quality standards will not be violated. HAZARDOUS SUBSTANCES Pursuant to Section 5.5.5 of the BOR, commercial or industrial zoned projects shall provide at least one-half inch of dry detention or retention pretreatment as part of the required retention/detention, unless reasonable assurances can be offered that hazardous materials will not enter the project's SWM system. The Addendum to Staff Report reflects the following Special Condition 25 pertaining to hazardous materials: Upon submittal of an application for construction of commercial or industrial uses the permittee shall submit a plan that provides reasonable assurances that hazardous materials will not enter the surface water management system pursuant to the requirements of section 5.2.2(a) of the Basis of Review. Applicable permitting criteria does not require the Applicants to present a hazardous substances plan at this point because no facilities that will contain hazardous materials are part of the Phase 1A construction. SECONDARY IMPACTS Florida Administrative Code Rule 40E-4.301(1)(f) and Section 4.1.1(f) of the BOR, require an applicant to provide reasonable assurances that the proposed activities will not cause adverse secondary impacts to the water resources. A secondary impact is an indirect effect of a project resulting in adverse effects to wetlands or other surface waters. The District considers those adverse effects that would not occur "but for" the activities that are closely linked and causally related to the activity under review. This standard is discussed further in the Conclusions of Law section of this Recommended Order. The County’s Exhibit 3 is a secondary impact analysis identifying the secondary impacts that may potentially result from the proposed project. These impacts are: 1) the widening of SPW Road; 2) the construction of an FPL substation; 3) the extension of PGA Boulevard; and 4) the potential relocation of a runway at North County Airport. The secondary impact analysis performed pursuant to the Uniform Mitigation Assessment Method (UMAM) contained in Florida Administrative Code Chapter 62-345 reflects that up to 153.3 acres of wetlands may be partially or completely impacted by these secondary impacts, resulting in approximately 71.21 units of functional loss. Where future activities are expected to directly impact wetlands, secondary impacts were assessed based on the loss of all current functional value within the direct footprint of that activity. Additionally, an assessment was conducted to determine the degree of partial functional loss where impacts beyond the footprint of these activities are anticipated. SPW Road is an existing dirt road which is in the County's five-year road plan to widen as a four-lane paved road. Because the widening of the existing dirt road to a four-lane paved road is part of the five-year road plan, the impacts of that widening are not attributable to the subject project. However, as part of the proposed project, it is proposed to widen SPW Road to a six-lane paved road. The additional impacts associated with the widening from four to six lanes will be caused by, and are linked to, the proposed project. These impacts amount to approximately 2.2 acres. The FPL substation, which is proposed to service the proposed project, may result in 1.6 acres of potential direct impacts to wetlands. In addition, 1.0 acre of potential indirect secondary impacts may occur to wetlands that are not going to be dredged and filled. Those indirect secondary impacts may have some adverse impact on the functional value to those wetlands for wildlife utilization. The extension of PGA Boulevard to the Mecca Farms site has the potential to result in 45.6 acres of direct impacts to wetlands and 56.6 acres of indirect secondary wetland impacts which will not be dredged or filled, but will be in close proximity to the road. The secondary impact assessment for PGA Boulevard assumed the incorporation of wildlife crossings to minimize habitat fragmentation. If the airport runway needs to be shifted, potential direct wetland impacts to an additional 22.7 acres may occur. Indirect impacts to 23.6 acres of wetlands in close proximity could also occur. Runway relocation may or may not be necessary due to the PGA Boulevard extension; however, the analysis assumed the need for the relocation. Each of the projects listed above as potential secondary impacts will require a separate construction and operation permit from the District. The issuance of this permit does not in any way guarantee the issuance of permits for any of these identified potential secondary impacts. MITIGATION PLAN The Applicants provided a conceptual mitigation plan using UMAM to demonstrate how potential secondary impacts could be offset. Mitigation options have the potential to provide more than twice the functional gain than the functional loss from the identified secondary impacts. The conceptual mitigation options include: 194 acres of the land that had been acquired for future mitigation needs in Unit 11. 227 acres of the BRP natural area. 32.6 acres in the southern lake wetland along with proposed upland habitat. Sufficient mitigation is available in these options to offset the potential secondary impacts. The mitigation for the four potential secondary impacts is not required to be implemented now because the impacts are not occurring now. Section 4.2.7 of the BOR requires that the District consider those future impacts now and that a conceptual mitigation plan be provided to demonstrate and provide reasonable assurances that those impacts, in fact, can be offset in the future. The Governor and Cabinet sitting as the Board of Trustees considered and approved a request for public easement of approximately 30 acres to use a portion of CWMA for SPW Road, an FPL substation, and the land area that may be needed by District in the future for the connection to the flow-way. As consideration in exchange for the public easement over 30 acres, the County will transfer fee simple title of 60 acres to the State. This public easement also provides a benefit for CERP as it includes the small portion that the District is going to need for its future CERP project to connect to the flow-way on the proposed project site. The Applicants provided reasonable assurances that mitigation will offset secondary impacts to wetlands and other surface waters. UNIDENTIFIED SECONDARY IMPACTS Testimony at the final hearing raised a question as to whether there is nesting or roosting by listed wading bird species in adjacent off-site wetlands outside the eastern boundary of the project site. Evidence was inconclusive on nesting or roosting in these areas. Because the status of adjacent listed wading bird nesting or roosting is uncertain, the District suggested in its Proposed Recommended Order that a special condition requiring a wildlife survey prior to construction near the eastern project boundary be added to the permit as follows: Prior to application for construction within 1000 feet of the eastern boundary of the above-ground impoundment, the applicant shall conduct a wildlife survey to identify any nesting or roosting areas in the adjoining off-site wetlands utilized by listed species of wading birds. If such nesting or roosting areas are found the permittee shall, if determined necessary by the District, incorporate additional buffers or other appropriate measures to ensure protection of these wetland functions. The District represented in its Proposed Recommended Order that the County has no objection to adding the foregoing condition. CUMULATIVE IMPACTS Pursuant to Section 373.414(8), Florida Statutes, the District is required to consider cumulative impacts upon wetlands and other surface waters delineated in Section 373.421(1), Florida Statutes, within the same drainage basin. Cumulative impacts are the summation of unmitigated wetland impacts within a drainage basin. The cumulative impact analysis is geographically based upon the drainage basins described in Figure 4.2.8-1 of the BOR. Cumulative impacts are unacceptable when they would result in unacceptable adverse impacts to the functions of wetlands and surface waters within a drainage basin. There are no wetlands or other surface waters delineated pursuant to Section 373.421(1), Florida Statutes, on the Mecca Farms site. Therefore, no cumulative impacts are created by the direct impacts of the project. Cumulative impacts may be created by a project's secondary impacts. If a wetland impact has been appropriately mitigated on-site within the drainage basin, there is no residual impact, and therefore no cumulative impact. The PGA Boulevard extension, a portion of the SPW Road widening, and the airport runway relocation are located within the C-18 Basin. The proposed mitigation options are all located in the C-18 Basin and will offset those impacts. Those potential secondary impacts are considered to meet the cumulative impact requirements of Section 373.414(8), Florida Statutes. The Applicants provided reasonable assurances that the proposed project will not result in cumulative impacts to the C-18 Basin. The FPL substation is located within the L-8 Drainage Basin. The majority of the SPW Road expansion is located within the C-18 Basin, but a portion is located on the basin line between the C-18 Basin and the L-8 Basin. Because the mitigation for the L-8 impacts are proposed in a different basin, the Applicants were required to conduct a cumulative impact analysis for the L-8 Basin impacts. Based on the Florida Land Use Cover Classification System, there are 43,457 acres of freshwater wetlands within the L-8 Basin. Approximately 41,000 acres of the wetlands in L-8 Basin are in public ownership. This total constitutes approximately 95 percent of all the wetlands in the L-8 Basin. Public ownership of these wetlands provide a high level of assurance that these lands will be protected in perpetuity. The Respondents established that proposed mitigation can fully offset the potential impacts from the SPW Road expansion and the FPL substation and the approximately four acres of impacted wetlands in the L-8 Basin. The Applicants provided reasonable assurances that there are no unacceptable adverse cumulative impacts on the L-8 Basin.4 GROUND WATER FLOWS, SURFACE WATER FLOWS, AND MINIMUM FLOWS AND LEVELS Florida Administrative Code Rule 40E-4.301(1)(g) requires an applicant to provide reasonable assurances that the proposed activity will not adversely impact the maintenance of surface or ground water levels or surface water flows established pursuant to Section 373.042, Florida Statutes. The term "maintenance of surface and groundwater levels or surface water flows" in Florida Administrative Code Rule 40E-4.301(1)(g) means that a project will not adversely impact the maintenance of surface water flows that contribute to meeting the minimum flow for the water body. An adverse impact to the maintenance of surface or groundwater levels or surface water flows may occur when a project discharging to a water body with a designated minimum flow level is proposed to be diverted. An analysis was done to compare the peak discharge rate from the existing SWM system on the Mecca Farms site with the projected peak discharge rate from the proposed SWM system. The analysis showed that the peak discharge rate under the proposed system will be less than that of the existing system. That result was expected since the proposed system will have higher control elevations, which, as noted above, will provide better treatment and permit a better control of the discharge into the C-18 Canal. Under the existing SWM system, storm event water in a dry period is frequently stored in the existing impoundment for future irrigation purposes. Under the proposed SWM system such storm event water will be discharged downstream, which will benefit those downstream areas during dry periods. The proposed system will also provide better control over pulse discharges during heavy storm events. The Applicants provided reasonable assurances that the proposed activities will not adversely impact the maintenance of surface or ground levels or surface water flows as required by Florida Administrative Code Rule 40E-4.301(1)(g). THE DISTRICT’S OBJECTIVES Sections 373.414 and 373.416, Florida Statutes, require an applicant to provide reasonable assurances that a regulated activity will not be harmful to the water resources and will not be inconsistent with the overall objectives of the District. Congress initially authorized the Central and Southern Florida (“C&SF”) Project in 1948. Thereafter extensive work was undertaken pertaining to flood control; water supply for municipal, industrial, and agricultural uses; prevention of saltwater intrusion; and protection of fish and wildlife. The work included construction of a primary system of 1000 miles each of levees and canals, 150 water-control structures, and 16 major pump stations. Unintended consequences of the C&SF Project have included the irreversible loss of vast areas of wetlands, including half of the original Everglades; the alteration in the water storage, timing, and flow capacities of natural drainage systems; and the degradation of water quality and habitat due to over-drainage or extreme fluctuations in the timing and delivery of fresh water into the coastal wetlands and estuaries. In 1992, Congress authorized the C&SF Project Comprehensive Review Study, which is generally referred to as the “Restudy.” The objective of the Restudy was to reexamine the C&SF Project to determine the feasibility of modifying the project to restore the South Florida ecosystem and provide for the other water-related needs of the region, such as water supply and flood protection. In April 1999, the U.S. Army Corps of Engineers issued the Central and Southern Florida Project Comprehensive Review Study Final Integrated Feasibility Report and Programmatic Environmental Impact Statement (“Restudy Report”). The Restudy Report recommends a comprehensive plan for the restoration, protection, and preservation of the water resources of Central and South Florida. The resulting plan is known as CERP. The North Palm Beach County Part I project, which includes restoration of the Northwest Fork of the Loxahatchee River (“NWFLR”), is a component of CERP. The successful completion of CERP and the successful restoration of the NWFLR are high-priority objectives of the District. The Loxahatchee River is an important feature of the South Florida ecosystem, nationally and internationally unique, and an important natural and economic resource. Rules pertaining to MFL for the NWFLR and for the recovery of the NWFLR are found at Florida Administrative Code Rule 40E-8.011; 40E-8.221(4); and 40E-8.421. Recovery goals, which are not presently being met, have been established; and strategies to meet those goals have been identified. The Mecca Farms site is located within the boundaries of the CERP North Palm Beach County Part I project and has the potential to affect CERP and the restoration of the NWFLR. Projects that potentially would affect or would be within or adjacent to a CERP project are evaluated on a case-by- case basis to determine whether a proposed project would not be inconsistent with CERP and other District objectives. There was a dispute between Respondents and Petitioners as to whether the proposed project was inconsistent with the District’s objectives, including CERP and its goals pertaining to the restoration of the NWFLR. Petitioners contend that the District has insufficient evidence that the Mecca Farms will not be needed for the construction of a reservoir. That contention is rejected. The greater weight of the credible evidence established that sufficient storage is available at a superior site known as the Palm Beach Aggregates (PBA) site in the L-8 Basin, which is a unique geological site that will provide in-ground storage of water.5 Water from the PBA storage site can be conveyed to the NWFLR to increase dry season flows. Water can be stored at the PBA site in the wet season to prevent potentially damaging high flows. The L-8 Basin, which is adjacent to the C-18 Basin, receives more water during the wet season than it uses. This means that at present a significant amount of water must be discharged to tide (lost) during the wet season to provide for flood protection in this area. As envisioned, the water currently lost to tide could be stored at the PBA site for use during the dry season. By combining the water storage in the L-8 Basin with connective flow-ways to the C-18 Canal, water demands within the C-18 Basin, including the NWFLR, can also be met by the PBA storage site.6 An increase in freshwater flows to the NWFLR will further the District’s restoration goals for the NWFLR. Storage at PBA has regional benefits for other significant natural areas because it will provide additional flows to the Loxahatchee Slough and Grassy Waters Preserve. Those additional flows will further the District’s CERP goals. Since October of 2003, County staff and the District’s ERP staff have coordinated review of the subject project with the District’s CERP Planning and Federal Projects Division and other District staff working on projects in this region. The County asked the District to determine if the Mecca Farms’ site could in some way accommodate CERP objectives, and three alternatives were considered: 1) no action; 2) a reservoir; and 3) a flow-way. As opposed to a reservoir, the more valuable and the more practical, use of the Mecca Farms site would be as part of the system to convey the stored water to the areas that would most benefit from its discharge. The proposed flow-way in the BRP Natural Area would be an integral part of that conveyance system and would provide the District with greater flexibility in managing and directing the discharge of the water stored at the PBA site. Prior to the development of the flow-way concept as part of the proposed development, CERP identified a single route to take water from PBA to the NWFLR. The flow-way will provide an additional route from PBA to the NWFLR. That additional route will provide the District with greater operational flexibility. The flow-way will complement the L-8 Basin flow- way and help reduce peak flows to the NWFLR and the Estuary. The flow-way also provides a potential route allowing excess water to be brought back from the C-18 Basin to the PBA site for storage. There are no other potential routes that allow water to be directed from the C-18 Basin in the wet season to the PBA site. The flow-way provides a feature that was not part of the CERP original plan and is therefore an unanticipated benefit for CERP. The Applicants provided reasonable assurances that the proposed project is not inconsistent with the District’s objectives.7
Recommendation Based on the foregoing findings of fact and conclusions of Law, it is RECOMMENDED that the District issue the subject ERP for the conceptual approval of the SWM system for the BRP and the Phase 1A construction and operation subject to the general and special conditions set forth in the Staff Report and the Amended Staff Report. It is further RECOMMENDED that the District add the following special condition: Prior to application for construction within 1000 feet of the eastern boundary of the above-ground impoundment, the applicants shall conduct a wildlife survey to identify any nesting or roosting areas in the adjoining off-site wetlands utilized by listed species of wading birds. If such nesting or roosting areas are found the permittee shall, if determined necessary by the District, incorporate additional buffers or other appropriate measures to ensure protection of these wetland functions. DONE AND ENTERED this 3rd day of December, 2004, in Tallahassee, Leon County, Florida. S CLAUDE B. ARRINGTON 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 3rd day of December, 2004.
