The Issue Whether Save the Manatee Club has standing in this proceeding? Whether the exemptions in paragraphs (3), (5) and (6) of Rule 40D-4.051, Florida Administrative Code, (the Exemptions) are "invalid exercises of delegated legislative authority" as defined in paragraphs (b) and (c) of Section 120.52(8), Florida Statutes? Whether the Exemptions violate the prohibitions and restrictions on agency rulemaking contained in the last four sentences of Section 120.52(8), Florida Statutes?
Findings Of Fact The parties Petitioner, Save the Manatee Club, Inc., is a not-for- profit corporation dedicated to protecting the manatee. Respondent, The Southwest Florida Water Management District, is one of five water management districts in the State of Florida. A public corporation created pursuant to Chapter 61- 691, Laws of Florida, the District's geographic boundaries encompass a number of counties or some part of them including the three counties on the shores of Tampa Bay: Hillsborough, Pinellas and Manatee. See Section 373.069(2)(d), Florida Statutes. Within this boundary, the District is generally charged with the protection of water resources and with the management and storage of surface waters of the State pursuant to Part IV, Section 373.403 et seq., Florida Statutes. Intervenor, South Shores Properties Partners, Ltd., is a limited partnership composed of a subsidiary of Tampa Electric Company (TECO) and another business organization, Shimberg Cross Company, referred to by its President Glen Cross as "actually SCSS" (Tr. 133), apparently an acronym for Shimberg Cross Company. Mr. Cross' company is the general partner in the South Shores partnership. South Shores was formed in anticipation of closing on a contract entered by Shimberg Cross to purchase a parcel of real estate in Hillsborough County. The closing proceeded in January of 1998. On January 23, 1998, eight days or so before the closing, South Shores was formed as "a limited partnership organized under the laws of the State of Florida." (Petitioner's Exhibit no. 15). It succeeded to the contract rights of Shimberg Cross and then, pursuant to the closing, became the owner of the real estate subject to the contract. South Shores hopes to sell the property to Atlantic Gulf Communities, an organization that will actually develop it. If the arrangement with Atlantic Gulf Communities is not consummated, South Shores will look for another developer or develop the property itself. No matter what party (if any) is the actual developer, South Shores, as the present owner, now seeks the benefit of the Exemptions in support of a District- issued conceptual permit for development of the parcel in Hillsborough County (the Parcel). The Parcel and Its Proposed Development The Parcel is 720 acres in southwestern Hillsborough County. South Shores proposes to use it for a multi-phase, mixed-use project. The development project is denominated "Apollo Beach aka (sic) Bay Side" (Petitioner's Exhibit 13) on the draft of the conceptual permit attached to the District's Notice of Proposed Agency Action. Atlantic Gulf Communities calls it "Harbor Bay". (Petitioner's Exhibits 3 and 4). (It will be referred to in this order as Apollo Beach/Bay Side). If all goes as planned by South Shores, the Parcel's developer (whether South Shores, Atlantic Gulf Communities, or some other party) will be able to provide the residential portion of Apollo Beach/Bay Side with direct access by boat to Tampa Bay through an existing canal system on the Parcel. For now access to the bay is blocked by an earthen berm or "plug." With the plug in place, boat access to the bay from the canals can only be achieved by means of a boat lift. A lagoon is also part of South Shores' development plans for Apollo Beach/Bayside. Not yet excavated, the lagoon will allow residents to harbor boats close to their residences. If the lagoon is dug, a boat lift (different from the one necessary to allow boats to cross the plug if left in place) will be constructed to give the boats access to the canal system. With access to the canal system established, once the plug is removed, the boats will have unrestricted access to Tampa Bay. In the "Abstract" section of the conceptual permit proposed for issuance by the District, the project was described as follows: Apollo Beach (a.k.a. Bay Side) is a proposed multi-phase, mixed use development on approximately 720.0 acres in . . . Southwestern Hillsborough County. The project will include single-family and multi- family residential areas and commercial sites. The property is in close proximity to Tampa Bay, West of U.S. Highway 41 and immediately south of the existing Apollo Beach development. The site is presently undeveloped but does contain an existing manmade canal system that is tidally connected to Tampa Bay. The Applicant has demonstrated that the proposed project has an Environmental Resource Permit exemption pursuant to Chapters 40D-4.051(3)(5) and (6), F.A.C. and will only require Standard General Permits for Minor Surface Water Management Systems for the future construction in accordance with Chapter 40D-4.041(4), F.A.C. Because of this exemption, this Conceptual Permit will only review the storm water quality aspects of the project in accordance with 40D-301(2) and will not address storm water quantity issues or impacts to wetland/fish and wildlife habitats. The project will include the realignment of existing Leisley Road and the construction of a roadway system to serve the proposed residential and commercial areas. The project will also include the excavation of a "fresh water Lagoon" approximately 136 acres in size. Most of the proposed single-family residential lots will be constructed on the "Lagoon" or existing canal system. Surface water runoff from the upland portions of the project will be treated in 25 proposed ponds or isolated wetlands prior to discharge to the "Lagoon" or existing canal system. (Petitioner's Exhibit no. 13.) The ultimate effects to manatees of the proposed development project, if completed, were described by Ms. Thompson, the Club's witness: A typical project such as this one will introduce a good number of powerboats into the system, in this case, Tampa Bay. And manatees are impacted by powerboats either through propeller injuries or through collision with the hull of a fast-moving boat and the results are either death or in some cases sublethal injuries that may have other consequences such as inability to reproduce, et cetera. . . . [T]he very same boats can affect manatee habitat by prop scarring, boats going over sea grass beds and destroying the grasses. They also, in shallow water, kick up . . . turbidity which can affect light attenuation reaching the sea grass beds. And then there are the water quality issues which have secondary impacts to the sea grass beds . . . (Tr. 96). The Exemptions preliminarily afforded South Shore by the District will allow the removal of the plug in the canal system. Because removal of the plug will facilitate access to Tampa Bay by power boats harbored in the lagoon, it is the issue about the development of the Parcel that most concerns the Club in its efforts to protect manatees in Tampa Bay and elsewhere. Standing of Save the Manatee Club (i). The Manatee The manatee is the "Florida State marine mammal." Section 370.12(2)(b), Florida Statutes. Designated an endangered species under both federal and state law, 50 CFR s. 17.11 and Rule 39-27.003, Florida Administrative Code, the manatee is protected by the federal Endangered Species Act and by the federal Marine Mammal Protection Act. In Florida, the manatee enjoys, too, the protection of the Florida Endangered Species Act and the Florida Manatee Sanctuary Act. The State of Florida has been declared to be "a refuge and sanctuary for the manatee." Id. The Club's Purpose and Activities The Club's primary purpose is to protect the manatee and its habitat through public awareness, research support and advocacy. Long active in efforts to protect the manatee, the Club has achieved special status in manatee protection in Florida. In 1996, it was the recipient of a resolution by the Florida Legislature's House of Representative recognizing its endeavors on behalf of the manatee. The Club has been designated a member of the Manatee Technical Advisory Council provided by the Florida Manatee Sanctuary Act. See sub-sections (2)(p) and (4)(a) of section 370.12(2)(p) and (4)(a), Florida Statutes. The Department of Environmental Protection annually solicits recommendations from the Club regarding the use of Save the Manatee Trust Fund monies. In furtherance of its efforts, the Club has frequently participated before the Division of Administrative Hearings in administrative litigation involving manatees and manatee habitat on behalf of itself and its members. (iii). The Club's Membership The Club has approximately 40,000 members. The number of individual persons who are members of the Club, however, is far in excess of this number because many members are groups that receive membership at discounted fees. For example, a family may be one member or, as is quite common, an entire elementary school classroom may be one member. One-quarter of the Club's membership resides in Florida. Approximately 2,200 of the members are on the west coast of Florida with 439 in Hillsborough County, 584 in Pinellas and 165 in Manatee. The total number of members is therefore about 1,188 in the three counties whose shores are washed by Tampa Bay. (iv). Tampa Bay Tampa Bay is "prime essential manatee habitat." (Tr. 65). At least two factors make this so: the Bay's sea grass beds (manatee feeding areas) and warm water sources, particularly in winter, three of which are "power plant effluence." (Tr. 77). Not surprisingly, therefore, the Club has funded long- term research on the manatee in Tampa Bay. It has "provided about ten years of financial support for aerial surveys to count manatees in Tampa Bay and determine their distribution and the health of the sea grass beds . . ." (Tr. 75), a research project which finished last year. This research has contributed to other manatee research in the Bay leading the Club's witness at hearing to conclude, "[t]here's no other place in the state of Florida that has as long a term, as comprehensive a [manatee] database as Tampa Bay." (Tr. 76). Other activities in Tampa Bay conducted by the Club include the placement of manatee awareness signs. And the Club's staff biologist sits on the Tampa Bay Manatee Awareness Coalition established by the Tampa Bay National Estuary Program. In sum, the quality of manatee habitat in Tampa Bay is enough to make it especially important to the Club. But, its importance to the Club takes on added significance because it is the site of one of only three adoption programs the Club sponsors in Florida. The Tampa Bay Adoption Program The Tampa Bay Adopt-a-Manatee Program was established in April of 1999. The six manatees subject to the Tampa Bay Manatee Adoption Program (as of October 7, 1999) have been adopted by 1,229 members, 284 of which have been schools. (Petitioner's Exhibit 9). Those adopting receive a photo of the manatee, a biography, a scar pattern sheet, and a map showing their manatees' favorite habitat areas along the west coast of Florida. Of the six "Tampa Bay Adoption" program manatees, five have been seen in Tampa Bay and one south of Tampa Bay in the Marco Island area. Of the five seen in the bay, four "winter at the warm water discharge area of Tampa Electric Company's power plant" (Petitioner's Exhibit No. 5, Tr. 67) where they can be observed by members of the Club and the Tampa Bay adoption program as well as by the public. The TECO Power Plant The TECO power plant area is the major warm water refuge for manatees known to frequent Tampa Bay, particularly during the winter. The waters near the plant have been observed to be the host of more than 100 manatees at one time, following the movement of cold fronts through the area. The plant has a manatee-viewing center, one of the two principal places in the state for viewing manatees in the wild. The Club's membership handbook gives detailed information about how to see manatees at the TECO viewing center. During the winter months, the Club frequently directs its members to the TECO viewing center. Precisely how many individuals, either as members of the Club through a group membership or as members, themselves, actually have viewed manatees at the TECO viewing center or elsewhere in Tampa Bay was not established. Nor was any competent estimate made of how many might visit the TECO viewing center in the future. The viewing center and the power plant are in the vicinity of Apollo Beach/Bay Side, the development project South Shores seeks to have approved for an Environmental Resource Permit (the ERP). The SWFWMD ERP Program Chapter 373, Florida Statutes, governs water resources in the state and sets out the powers and duties of the water management districts, including their permitting powers. Part IV of the chapter covers the management and storage of surface waters. According to SWFWMD rules, "'Environmental Resource Permit' means a conceptual, individual, or general permit for a surface water management system issued pursuant to Part IV, Chapter 373, Florida Statutes." Rule 40D-4.021, Florida Administrative Code. The permit issued to South Shores in this case through the application of the challenged Exemptions, is a conceptual Environmental Resource Permit. See Petitioner's Exhibit no. 13 and Rule 40D-4.021(2), Florida Administrative Code. The conceptual permit preliminarily issued South Shores is one that was reviewed by the Club's staff, just as it reviews many permit applications for potential effects to manatees. Because of use of the Exemptions as proposed by the District to South Shores, however, any review the Club conducted to assure that the permit met all general permitting criteria was of no use. Much of those criteria were not applied by the District to the application. If the Exemptions were not available to South Shores, the District would have to employ ERP permitting criteria to the surface water management activities associated with the development project, including removal of the plug, lagoon construction, and boat lift installation. The Exemptions, therefore, keep the Club from participating in what otherwise would be the process for the District's administrative decision on the application of those criteria. In sum, the Exemptions preempt the Club's participation in the state mechanism provided by ERP permitting criteria for assessing, inter alia, threats to the manatee and its habitat from harms associated with the proposed development project. The District recognized this effect of the permit in the draft of the permit. The draft states: "Because of this Exemption, this Conceptual Permit will . . . not address . . . impacts to . . . wildlife habitat." (Petitioner's Exhibit no. 13). The Exemptions, therefore, prevent the Club from carrying out functions useful to protection of manatee habitat, that is, participation in the District's application of wildlife habitat protection criteria. The non-application by the District of permit criteria related to wildlife habitat protection and the Club's inability to assure itself that the criteria are correctly applied poses the danger that manatee habitat will be lost, diminished or damaged. If the Club is ultimately proved right in its assertion that the manatee and its habitat will be damaged by the South Shores development without application of permitting criteria related to wildlife habitat, then the approved application increases the threat that Club members will encounter greater difficulty in observing, studying and enjoying manatees in the wild and in Tampa Bay in particular. Standing of South Shores to Intervene The District has no opposition to South Shores' intervention. As for the Club's position with regard to South Shores intervention, the Club stipulated to South Shores' standing to intervene in a notice filed with its proposed order. South Shores benefits, moreover, from the application of the Exemptions to its proposed project. In light of not having to show compliance with permitting criteria otherwise applicable, South Shores will escape some permitting costs and therefore, enjoys economic benefit. Furthermore, by allowing South Shores to avoid the requirements of compliance with ERP permitting criteria, the Exemptions facilitate fulfillment of the obligation of South Shores to obtain a permit to develop. The District's Rule-making Authority The District governing board has been granted general authority by the Legislature to adopt rules to implement the provisions of Chapter 373, Florida Statutes, the Florida Water Resources Act of 1972: The governing board of the district is authorized to adopt rules . . . to implement the provisions of law conferring powers or duties upon it. Section 373.113, Florida Statutes. The Legislature has framed this authority in relationship to the District's power to administer the Chapter and its Part IV: In administering the provisions of this chapter the governing board has authority to adopt rules . . . to implement provisions of law conferring powers or duties upon it. Section 373.113, Florida Statutes. In another provision in Chapter 373, the district has been given rule-making authority that exceeds the authority to implement specific provisions granted typically to most administrative agencies in Florida. This authority is broad indeed. Tied to water use in general, it is bound only by unspecified conditions as warranted: . . . governing boards, . . . may: Adopt rules . . . affecting the use of water, as conditions warrant, . . . Section 373.171, Florida Statutes. The Exemptions; Specific Authority and Laws Implemented The Exemptions are as follows: 40D-4.051 Exemptions. The following activities are exempt from [ERP] permitting under this chapter: * * * (3) Any project, work or activity which has received all governmental approvals necessary to begin construction and is under construction prior to October 1, 1984. *(4) Any project, work or activity which received a surface water management permit from the District prior to October 1, 1984. * * * Any phased or long term buildout project, including a development of regional impact, planned unit development, development with a master plan or master site plan, or similar project, which has received local or regional approval prior to October 1, 1984, if: The approval process requires a specific site plan and provides for a master drainage plan approved prior to the issuance of a building permit, and The Developer has notified the District of its intention to rely upon this exemption prior to April 1, 1985. Projects exempt under this subsection shall continue to be subject to the District's surface water management rules in effect prior to October 1, 1984. As specific authority, the Rule containing the Exemptions references 373.044, 373.113, 373.149, 373.171, and 373.414(9), Florida Statutes. For "Law Implemented", the Rule lists Sections 373.406, 373.413 and 373.414(9), Florida Statutes. Section 373.414(9) is cited by the Rule both as specific authority and as one of the laws implemented. The first of the statutory provisions cited by the Rule as a law implemented is Section 373.406, Florida Statutes. It reads: 373.406 Exemptions.- The following exemptions shall apply: Nothing herein, or in any rule, regulation, or order adopted pursuant hereto, shall be construed to affect the right of any natural person to capture, discharge, and use water for purposes permitted by law. Nothing herein, or in any rule, regulation, or order adopted pursuant hereto, shall be construed to affect the right of any person engaged in the occupation of agriculture, silviculture, floriculture, or horticulture to alter the topography of any tract of land for purposes consistent with the practice of such occupation. However, such alteration may not be for the sole or predominant purpose of impounding or obstructing surface waters. Nothing herein, or in any rule, regulation, or order adopted pursuant hereto, shall be construed to be applicable to construction, operation, or maintenance of any agricultural closed system. However, part II of this chapter shall be applicable as to the taking and discharging of water for filling, replenishing, and maintaining the water level in any such agricultural closed system. This subsection shall not be construed to eliminate the necessity to meet generally accepted engineering practices for construction, operation, and maintenance of dams, dikes, or levees. All rights and restrictions set forth in this section shall be enforced by the governing board or the Department of Environmental Protection or its successor agency, and nothing contained herein shall be construed to establish a basis for a cause of action for private litigants. The department or the governing board may by rule establish general permits for stormwater management systems which have, either singularly or cumulatively, minimal environmental impact. The department or the governing board also may establish by rule exemptions or general permits that implement interagency agreements entered into pursuant to s. 373.046, s. 378.202, s. 378.205, or s. 378.402. Any district or the department may exempt from regulation under this part those activities that the district or department determines will have only minimal or insignificant individual or cumulative adverse impacts on the water resources of the district. The district and the department are authorized to determine, on a case-by- case basis, whether a specific activity comes within this exemption. Requests to qualify for this exemption shall be submitted in writing to the district or department, and such activities shall not be commenced without a written determination from the district or department confirming that the activity qualifies for the exemption. Nothing in this part, or in any rule or order adopted under this part, may be construed to require a permit for mining activities for which an operator receives a life-of-the-mine permit under s. 378.901. Certified aquaculture activities which apply appropriate best management practices adopted pursuant to s. 597.004 are exempt from this part. For the most part, this section sets out general classes of exemptions. And it allows the District to consider whether an activity comes within an exemption on a "case-by-case" basis. See Section 373.406(6), Florida Statutes. But, none of these "exemptions" appear to have anything to do with the grandfather protections provided by the Exemptions at issue in this proceeding. See paragraphs 93-96, below. Section 373.413, Florida Statutes, in pertinent part, reads: (1) Except for the exemptions set forth herein, the governing board or the department may require such permits and impose such reasonable conditions as are necessary to assure that the construction or alteration of any stormwater management system, dam, impoundment, reservoir, appurtenant work, or works will comply with the provisions of this part and applicable rules promulgated thereto and will not be harmful to the water resources of the district. The department or the governing board may delineate areas within the district wherein permits may be required. Other than to make reference in subsection (1)to the existence of exemptions under Part IV of Chapter 373: "Except for the exemptions set forth herein . . .", Section 373.413 does not deal at all with exemptions. Certainly, it does not make reference with any specificity to the subject matter of the Exemptions at issue in this proceeding. Cited both as "specific authority" and "law implemented" is paragraph (9) of Section 373.414, Florida Statutes. Unlike Sections 373.406 and 373.413, it has a connection to the Exemptions at issue in this proceeding as is seen from perusal of the underscored language, below: (9) The department and the governing boards, on or before July 1, 1994, shall adopt rules to incorporate the provision of this section, relying primarily on the existing rules of the department and the water management districts, into the rules governing the management and storage of surface waters. Such rules shall seek to achieve a statewide, coordinated and consistent permitting approach to activities regulated under this part. Variations in permitting criteria in the rules of individual water management districts or the department shall only be provided to address differing physical or natural characteristics. Such rules adopted pursuant to this subsection shall include the special criteria adopted pursuant to s. 403.061(29) and may include the special criteria adopted pursuant to s. 403.061(35). Such rules shall include a provision requiring that a notice of intent to deny or a permit denial based upon this section shall contain an explanation of the reasons for such denial and an explanation, in general terms, of what changes, if any, are necessary to address such reasons for denial. Such rules may establish exemptions and general permits, if such exemptions and general permits do not allow significant adverse impacts to occur individually or cumulatively . . . (emphasis supplied.) History of the Exemptions The Exemptions have been adopted twice and amended several times. One of the amendments and the second adoption followed omnibus legislation in the environmental permitting arena: the amendment in the wake of the passage of the Warren S. Henderson Wetlands Protection Act of 1984, and the second adoption in the aftermath of the Florida Environmental Reorganization Act of 1993. (i). Amendment after the Henderson Act The Warren S. Henderson Wetlands Protection Act of 1984, (the "Henderson Act", later codified as Part VII of Chapter 403, Florida Statutes) was enacted through Chapter 84-79, Laws of Florida. Approved by the Governor on June 1, 1984 and filed in the Office of the Secretary of State on the same day, (see Laws of Florida, 1984, General Acts, Vol.1, Part One, p. 224) the Act had an effective date of October 1, 1984. The Henderson Act does not amend any provision in Part IV of Chapter 373, Florida Statutes, the part of the Water Resources Act which delineates water management district authority over the program for permitting related to the management and storage of surface waters ("MSSW"). Nonetheless, between the adoption of the Henderson Act and its effective date, the District amended and adopted rules in Chapters 40D-4 and 40D-40 of the Florida Administrative Code because of the Act's passage. Rule 40D-4.011 set out the policy for the amendments and adoptions: (2) The rules in this chapter implement the comprehensive surface water management permit system contemplated in part IV of Chapter 373, Florida Statutes. As a result of the passage of Chapter 84-79, Laws of Florida, the Warren G. Henderson Wetlands Protection Act of 1984, the District has adopted the rules in this Chapter and Chapter 40D-40 to ensure continued protection of the water resources of the District including wetlands and other natural resources. (Exhibit OR 4, See the page containing paragraph (2) of Rule 40D- 4.011 in the exhibit.) /1 Exhibit OR 4, a document officially recognized during this proceeding, is denominated "SWFWMD's Rule Amendment No. 116." The exhibit contains a letter on SWFWMD letterhead, signed by Dianne M. Lee for "J. Edward Curren, Attorney - Regulation" dated September 5, 1984. Under cover of the letter is a rule package filed by the District with the Secretary of State on September 11, 1984. Included in the package is the newly amended Rule 40D-4.051. The amended 40D-4.051 contains subparagraphs (3), (5) and (6), the Exemptions challenged in this proceeding. They are worded precisely as they remain worded today. Consistent with the policy expressed in Rule 40D-4.011, Florida Administrative Code as filed in September of 1984, the effective date of the amendment to the Rule containing the Exemptions was the effective date of the Henderson Act: October 1, 1984. The Exemptions contained in the amendment filed in September of 1984 are "grandfather provisions." The first two are designed to protect certain projects, work or activities from the requirements of the Henderson Act if they had governmental approvals on October 1, 1984. The third is designed to protect from the Act "phased or long term buildout project[s]" that meet certain requirements, among them receipt of governmental approvals by October 1, 1984. At the time of the 1984 amendments, the Rule cited to Sections 373.044, 373.113, 373.149 and 373.171 for "Specific Authority," that is, the statutory source for the district's authority to make rules. For "Law Implemented" the Rule cited to Section 373.406, Florida Statutes. At that time, Section 373.406 contained only four subsections. These four are worded substantially the same as the first four subsections of the section today. Although Section 373.406 was the only law implemented by the Rule in 1984, the section is neither mentioned in nor part of the Henderson Act. The section, itself, does not make mention of the Henderson Act or of protection from it based on government approvals obtained by October 1, 1984. Section 373.406, Florida Statutes, in its form both immediately before and after the Henderson Act provided exemptions that appear to have nothing to do with the Exemptions challenged in this proceeding. The only connection between Section 373.406, Florida Statutes, in 1984 and the Exemptions at issue in this proceeding when amended into the Rule in 1984 appears to be the use of the term "exemptions." The exemptions set out in the Section 373.406, Florida Statutes, as it existed in 1984, are not related to grandfather protection from the effects the Henderson Act had on the District's permitting considerations. Following the amendment to the Rule containing the Exemptions, the Rule was amended further. It was amended on October 1, 1986, March 1, 1988, and January 24, 1990. None of these amendments appear to have affected the Exemptions under consideration in this proceeding. The Rule became the subject of rule promulgation by the District again, however, as a result of a second omnibus act of the Legislature in the environmental permitting arena, the Florida Environmental Reorganization Act of 1993. (ii). The Reorganization Act of 1993 Nine years after the passage of the Henderson Act, the Legislature enacted the Florida Environmental Reorganization Act of 1993 (the "Reorganization Act"). Passed as Chapter 93-213, Laws of Florida, the Session Law declares its underlying policy: Declaration of Policy.-- The protection, preservation, and restoration of air, water, and other natural resources of this state are vital to the social and economic well-being and the quality of life of the citizens of this state and visitors to this state. It is the policy of the Legislature: To develop a consistent state policy for the protection and management of the environment and natural resources. To provide efficient governmental services to the public. To protect the functions of entire ecological systems through enhanced co- ordination of public land acquisition, regulatory, and planning programs. To maintain and enhance the powers, duties, and responsibilities of the environmental agencies of the state in the most efficient and effective manner. To streamline governmental services, providing for delivery of such services to the public in a timely, cost-efficient manner. Section 2., Ch. 93-213, Laws of Florida. The Reorganization Act carried out this policy in a number of ways. Among these, it merged the Departments of Environmental Regulation (DER) and Natural Resources into the Department of Environmental Protection. In so doing and at the same time, it incorporated DER's dredge and fill permitting program instituted by the Henderson Act into the programs of the water management districts for the Management and Storage of Surface Waters (MSSW). The permitting program that resulted from the consolidation of DER's dredge and fill permitting program with the District's MSSW permitting program is what has been referred to in this order as the Environmental Resource Permitting or ERP program. With regard to rules under the new ERP program, the Reorganization Act amended Section 373.414, Florida Statutes. Two sentences in subsection (9) of the amended section bear repeating: The department and the governing boards [of the water management districts], on or before July 1, 1994, shall adopt rules to incorporate the provisions of this section, relying primarily on the existing rules of the department and the water management districts, into the rules governing the management and storage of surface waters. * * * Such rules may establish exemptions . . . if such exemptions . . . do not allow significant adverse impacts to occur individually or cumulatively. . . . As discussed earlier in this order, the Henderson Act did not directly create exemptions in the District's MSSW permitting program. Nonetheless, the District through the Exemptions of Rule 40D-4.051, Florida Administrative Code, provided "grandfather" protections in the wake of the Act effective October 1, 1984. Whereas grandfather concerns were raised in front of the District after the Henderson Act, grandfather concerns and concerns about other situation that should be entitled to exemptions were raised to the Legislature during the advent of the Reorganization Act. These concerns were addressed in the Florida Environmental Reorganization Act, itself. The Act provided specific exemptions that were self- executing. Included were ones providing grandfather protection for certain activities approved under Chapter 403, Florida Statutes, (DER's dredge and fill program) from imposition of new ERP permitting criteria expected to be promulgated in the wake of the Reorganization Act. The are contained in subsections (11) through (16) of Section 373.414, Florida Statutes. None of these exemptions make reference to the Exemptions at issue in this case. Of these provisions, only one addresses activities subject to rules adopted pursuant to Part IV of Chapter 373 prior to the anticipated ERP permitting criteria: An application under this part for dredging and filling or other activity, which is submitted and complete prior to the effective date of [the anticipated ERP rules] shall be reviewed under the rules adopted pursuant to this part [including the Exemptions in Rule 40D-4.051] and part VIII of chapter 403 in existence prior to the effective date of the [anticipated ERP rules] and shall be acted upon by the agency which received the application, unless the applicant elects to have such activities reviewed under the [anticipated ERP rules]. Chapter 93-213, Section 30, p. 2149 of Laws of Florida, 1993, General Acts, Vol. 1, Part Two, now Section 373.414(14), Florida Statutes. 2/ Rule Activity in 1995 In observance of the mandate in the first section of Section 373.414(9), Florida Statutes, the District undertook adoption of rules "to incorporate the provisions of [Section 373.414] . . . into the rules governing the management and storage of surface waters." These rules were the ERP rules anticipated by the Reorganization Act. They included the rules necessary for the District to administer under its ERP program its newfound authority over much of the dredge and fill permitting program formerly administered by DER and now consolidated with its permitting authority in its MSSW rules. Among the rules passed under the authority of the Reorganization Act's Section 373.414(9) is Rule 40D-4.051, the Rule containing the Exemptions subject to this proceeding. Filed with the Secretary of State on September 13, 1995, the adoption package for the new readopted states the following, in pertinent part: 40D-4.051 Exemptions The following activities are exempt from permitting under this chapter [Individual ERPs]: (1) - (7) - No change. (Exhibit OR 6, p. 14). The result of this adoption is that the Exemptions became part of the District's ERP Rules. They now apply to both the MSSW authority under Part IV, Chapter 373, Florida Statutes, which existed prior to the Reorganization Act, and, in a consolidated fashion, the District's authority conferred by the Reorganization Act to regulate certain dredge and fill activity formerly regulated by DER.
The Issue The issue to be determined in this case is whether proposed Florida Administrative Code Rule 40E-10.041(3)(d) of the South Florida Water Management District (“the District”) is an invalid exercise of delegated legislative authority.
Findings Of Fact The Conservancy is a non-profit Florida corporation with its offices in Naples, Florida. It has 6,200 members residing in Southwest Florida. The mission of the Conservancy is to protect the environment and natural resources of Southwest Florida. The Caloosahatchee River is an important focus of the Conservancy’s organizational activities and objectives. A substantial number of the members of the Conservancy use the Caloosahatchee River for drinking water, boating, fishing, wildlife observation, and scientific research. The proposed rules create a prospective reservation of water in the not-yet-operational Caloosahatchee River (C-43) West Basin Reservoir “for fish and wildlife.” The Conservancy’s interests would be substantially affected by the proposed reservation. The District is a regional water management agency created, granted powers, and assigned duties under chapter 373, Florida Statutes (2013). It is headquartered in West Palm Beach, Florida. Proposed rule 40E-10.041(3) states: (3) Caloosahatchee River (C-43) West Basin Storage Reservoir: All surface water contained within and released, via operation, from the Caloosahatchee River (C-43) West Basin Storage Reservoir is reserved from allocation. The water reserved under this paragraph will be available for fish and wildlife upon a formal determination of the Governing Board, pursuant to state and federal law, that the Caloosahatchee River (C-43) West Basin Storage Reservoir is operational. The reservation contained within this subsection and the criteria contained in section 3.11.4 of the Applicant’s Handbook for Water Use Permit Applications within the South Florida Water Management District, incorporated by reference in Rule 40E-2.091, F.A.C., shall be revised in light of changed conditions or new information prior to the approval described in paragraph (3)(b) above. Pursuant to subsection 373.223(4), F.S., presently existing legal uses for the duration of a permit existing on [RULE ADOPTION DATE] are not contrary to the public interest. The Conservancy challenges only paragraph (3)(d), contending that it modifies or contravenes the implementing statute, section 373.223(4).
The Issue The issue to be determined is whether Respondent Land Trust #97-12 (“Land Trust”) is entitled to an Environmental Resource Permit (“ERP”) for its proposed project on Perico Island in Bradenton, Florida.
Findings Of Fact The Parties Petitioner Joseph McClash is a resident of Bradenton, Florida, who uses the waters in the vicinity of the project for fishing, crabbing, boating, and wildlife observation. Petitioner Manasota-88, Inc., is an active Florida nonprofit corporation for more than 20 years. Manasota-88 has approximately 530 members, most of whom (approximately 300) reside in Manatee County. The mission and goal of Manasota-88 includes the protection of the natural resources of Manatee County, including Anna Maria Sound and Perico Island. Petitioner FISH is an active Florida nonprofit corporation in existence since 1991. FISH owns real property in unincorporated Cortez in Manatee County and maintains a Manatee County mailing address. FISH has more than 190 members and more than 150 of them own property or reside in Manatee County. The mission and goal of FISH includes protection of the natural resources of Manatee County, including Anna Maria Sound and Perico Island. Intervenor Suncoast Waterkeeper, Inc., is an active Florida nonprofit corporation in existence since 2012. The mission of Suncoast Waterkeeper is “to protect and restore the Suncoast’s waterways through enforcement, fieldwork, advocacy, and environmental education for the benefit of the communities that rely upon coastal resources.” Suncoast Waterkeeper provided the names and addresses of 25 members residing in Manatee County. A substantial number of the members of Suncoast Waterkeeper use the area and waters near the proposed activity for nature-based activities, including nature observation, fishing, kayaking, wading, and boating along the natural shorelines of Anna Maria Sound and Perico Island. Intervenor Sierra Club, Inc., is a national organization that is a California corporation registered as a foreign nonprofit corporation in Florida. Sierra Club has been permitted to conduct business in Florida since 1982. The mission of Sierra Club includes protection of the natural resources of Manatee County, which include Anna Maria Sound and Perico Island. Sierra Club provided the names and addresses of 26 members who live in Manatee County. A substantial number of the members of Sierra Club use the area and waters near the proposed project for nature-based activities, including observing native flora and fauna, fishing, kayaking, wading, and boating along the natural shorelines of Anna Maria Sound and Perico Island. Respondent Land Trust is the applicant for the challenged ERP and owns the property on which the proposed project would be constructed. Respondent District is an independent special district of the State of Florida created, granted powers, and assigned duties under chapter 373, Florida Statutes, including the regulation of activities in surface waters. The proposed project is within the boundaries of the District. The Project Site The project site is 3.46 acres of a 40.36-acre parcel owned by Land Trust. The parcel includes uplands, wetlands, and submerged lands, on or seaward of Perico Island, next to Anna Maria Sound, which is part of Lower Tampa Bay. Anna Maria Sound is an Outstanding Florida Water. The project site is adjacent to a large multi-family residential development called Harbour Isles, which is currently under construction. Access to the Land Trust property is gained through this development. The Land Trust parcel contains approximately seven acres of high quality mangroves along the shoreline of Anna Maria Sound. They are mostly black and red mangroves, with some white mangroves. The mangroves on the project site amount to a total of 1.9 acres. Mangroves have high biological productivity and are important to estuarine food webs. Mangroves provide nesting, roosting, foraging, and nursery functions for many species of wildlife. Mangroves also provide a buffer from storm surge and help to stabilize shorelines. Wildlife species found on the project site include ibises, pelicans, egrets, spoonbills, mangrove cuckoos, bay scallops, fiddler crabs, mangrove tree crabs, horseshoe crabs, marsh rabbits, raccoons, mangrove bees, and a variety of fish. No endangered species have been observed on the project site, but mangroves are used by a number of listed species. The Proposed Project The proposed project is to construct a retaining wall, place fill behind the wall to create buildable lots for four single-family homes, construct an access driveway, and install a stormwater management facility. The stormwater management facility is a “Stormtech” system, which is an underground system usually used in situations where there is insufficient area to accommodate a stormwater pond. Riprap would be placed on the waterward side of the retaining wall. The retaining wall would be more than 35 feet landward of the mean high water line in most areas. Petitioners contend the proposed retaining wall is a vertical seawall, which is not allowed in an estuary pursuant to section 373.414(5). “Vertical seawall” is defined in section 2.0(a)(111), Volume I, of the Environmental Resource Permit Applicant’s Handbook (“Applicants Handbook”) as a seawall which is steeper than 75 degrees to the horizontal. It further states, “A seawall with sloping riprap covering the waterward face to the mean high water line shall not be considered a vertical seawall.” The retaining wall is vertical, but it would have riprap covering its waterward face and installed at a slope of 70 degrees. The retaining wall is not a vertical seawall under the District’s definition. Stormwater Management Stormwater in excess of the Stormtech system’s design capacity would discharge into Anna Maria Sound. Because Anna Maria Sound is an Outstanding Florida Water, District design criteria require that an additional 50 percent of treatment volume be provided. The Stormtech system meets the District’s design criteria for managing water quality and water quantity. Projects which meet the District’s design criteria are presumed to provide reasonable assurance of compliance with state water quality standards. Petitioners’ evidence was not sufficient to rebut this presumption. Petitioners contend the District waiver of water quality certification for the proposed project means that Land Trust was not required to meet water quality standards. However, that was a misunderstanding of the certification process. All state water quality criteria are applicable. Petitioners contend water quality monitoring should be imposed for this project. However, section 4.7 of the Applicant’s Handbook, Volume II, provides that if the applicant meets the District’s design criteria, water quality monitoring is not required. Petitioners failed to prove the proposed stormwater management system cannot be constructed, operated, or maintained in compliance with applicable criteria. Wetland Impacts In order to create buildable lots, 1.05 acres of the 1.9 acres of mangroves on the project site would be removed and replaced with fill. A swath of mangroves approximately 40 feet wide would remain waterward of the retaining wall. The proposed direct and secondary impacts to the functions provided by wetlands were evaluated using the Uniform Mitigation Assessment Method (“UMAM”) as required by Florida Administrative Code Chapter 62-345. UMAM is used to quantify the loss of functions performed by wetlands considering: current condition, hydrologic connection, uniqueness, location, fish and wildlife utilization, time lag, and mitigation risk. The District determined the filling of 1.05 acres of wetlands would result in a functional loss of 0.81 units and the secondary impacts resulting from installation of the retaining wall would result in a loss of 0.09 units for a total functional loss of 0.9 units. Petitioners contend the functional loss would be greater. Petitioners contend the wetland delineation performed by Land Trust and confirmed by the District did not extend as far landward as the hydric soils and, therefore, the total acreage of affected wetlands would be greater. However, Petitioners did not produce a wetland delineation for the project site, and their evidence was not sufficient to rebut Land Trust's prima facie evidence on this issue. Petitioners’ experts believe the secondary impacts caused by the proposed project would be greater than calculated, including fragmentation of the shoreline mangrove system, damage to the roots of mangroves near the retaining wall, and scouring effects caused by wave action associated with the retaining wall. Respondents assert that the analysis by Petitioners’ expert Jacqueline Cook relied on federal methodology and that “the science used in her analysis is not contained in the state or district rule criteria.” Reliance on science is always appropriate. However, Ms. Cook’s use of a federal impact assessment methodology creates doubt about whether her scoring is consistent with UMAM. Despite the unreliability of Ms. Cook’s UMAM score, it is found that Respondents’ UMAM score under-calculated secondary impacts due to scour and other effects of changed water movement that would be caused by the retaining wall. It was not explained how the loss of storm buffering and erosion prevention functions of wetlands are accounted for in the UMAM score. Elimination or Reduction of Impacts Section 10.2.1 of the Applicant’s Handbook, Volume I, states that in reviewing a project the District is to consider practicable design modifications to eliminate or reduce impacts to wetland functions. Section 10.2.1.1 explains: The term “modification” shall not be construed as including the alternative of not implementing the activity in some form, nor shall it be construed as requiring a project that is significantly different in type or function. A proposed modification that is not technically capable of being completed, is not economically viable, or that adversely affects public safety through the endangerment of lives or property is not considered “practicable.” A proposed modification need not remove all economic value of the property in order to be considered not “practicable.” Conversely, a modification need not provide the highest and best use of the property to be “practicable.” In determining whether a proposed modification is practicable, consideration shall also be given to cost of the modification compared to the environmental benefit it achieves. Land Trust originally proposed constructing a surface water retention pond. The Stormtech stormwater management system would cause less wetland impact than a retention pond. Land Trust contends the use of a retaining wall reduces wetland impacts because, otherwise, more mangroves would have to be removed to account for the slope of the waterward side of the fill area. However, this proposition assumes the appropriateness of the size of the fill area. Land Trust also contends wetland impacts are reduced by using the adjacent development to access the proposed project site, rather than creating a new road. However, the evidence did not establish that Land Trust had a practicable and preferred alternative for access. Unlike the Stormtech system, the retaining wall and access driveway were not shown to be project modifications. The proposed project would cause fewer impacts to wetlands if the fill area was reduced in size, which was not shown to be impracticable. Reducing the size of the fill area would not cause the project to be significantly different in type or function. Land Trust did not demonstrate that it implemented reasonable design modifications to eliminate or reduce impacts to wetland functions. Mitigation Land Trust proposes to purchase credits from the Tampa Bay Mitigation Bank, which is 17 miles north of the proposed project site. The Tampa Bay Mitigation Bank is in the Tampa Bay Drainage Basin. The project site is in the South Coastal Drainage Basin. Pursuant to section 10.2.8 of the Applicant’s Handbook, Volume I, if an applicant mitigates adverse impacts within the same drainage basin, the agency will consider the regulated activity to have no unacceptable cumulative impacts upon wetlands and other surface waters. However, if the applicant proposes to mitigate impacts in another drainage basin, factors such as “connectivity of waters, hydrology, habitat range of affected species, and water quality” will be considered to determine whether the impacts are fully offset. The parties disputed whether there was connectivity between the waters near the project site and the waters at the Tampa Bay Mitigation Bank. The more persuasive evidence shows there is connectivity. There was also a dispute about the habitat range of affected species. The evidence establishes that the species found in the mangroves at the project site are also found at the mitigation bank. However, local fish and wildlife, and local biological productivity would be diminished by the proposed project. This diminution affects Petitioners’ substantial interests. The loss or reduction of storm buffering and erosion prevention functions performed by the mangroves at Perico Island cannot be mitigated for at the Tampa Bay Mitigation Bank. Cumulative impacts are unacceptable when the proposed activity, considered in conjunction with past, present, and future activities would result in a violation of state water quality standards, or significant adverse impacts to functions of wetlands or other surface waters. See § 10.2.8.1, Applicant’s Handbook, Vol. I. Section 10.2.8(b) provides that, in considering the cumulative impacts associated with a project, the District is to consider other activities which reasonably may be expected to be located within wetlands or other surface waters in the same drainage basin, based upon the local government’s comprehensive plan. Land Trust did not make a prima facie showing on this point. Land Trust could propose a similar project on another part of its property on Perico Island. Anyone owning property in the area which is designated for residential use under the City of Bradenton’s comprehensive plan and bounded by wetlands could apply to enlarge the buildable portion of the property by removing the wetlands and filling behind a retaining wall. When considering future wetland impacts in the basin which are likely to result from similar future activities, the cumulative impacts of the proposed project would result in significant adverse impacts to wetland functions in the area. Public Interest For projects located in, on, or over wetlands or other surface waters, an applicant must provide reasonable assurance that the project will not be contrary to the public interest, or if such activities significantly degrade or are within an Outstanding Florida Water, are clearly in the public interest, as determined by balancing the criteria set forth in rule 62- 330.302(1)(a), and as set forth in sections 10.2.3 through of the Applicant’s Handbook. Rule 62-330.302, which is identical to section 373.414, Florida Statutes, lists the following seven public interest balancing factors to be considered: Whether the activities will adversely affect the public health, safety, or welfare or the property of others; Whether the activities will adversely affect the conservation of fish and wildlife, including endangered or threatened species, or their habitats; Whether the activities will adversely affect navigation or the flow of water or cause harmful erosion or shoaling; Whether the activities will adversely affect the fishing or recreational values or marine productivity in the vicinity of the activity; Whether the activities will be of a temporary or permanent nature; Whether the activities 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 regulated activity. The Parties stipulated that the proposed project would not have an adverse impact on public health, navigation, historical resources, archeological resources, or social costs. Land Trust proposes to give $5,000 to the City of Palmetto for an informational kiosk at the City of Palmetto’s public boat ramp. A District employee testified that this contribution made the project clearly in the public interest. Reasonable assurances were not provided that the proposed project is clearly in the public interest because of the adverse cumulative effects on the conservation of fish and wildlife, fishing and recreational values, and marine productivity of Anna Maria Sound, an Outstanding Florida Water.
Recommendation Based on the Findings of Fact and Conclusions of Law set forth above, it is RECOMMENDED that the Southwest Florida Water Management District issue a final order that denies the Environmental Resource Permit. DONE AND ENTERED this 25th day of June, 2015, 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 25th day of June, 2015. COPIES FURNISHED: Christian Thomas Van Hise, Esquire Abel Band, Chartered Post Office Box 49948 Sarasota, Florida 34230-6948 (eServed) Martha A. Moore, Esquire Southwest Florida Water Management District 7601 Highway 301 North Tampa, Florida 33637 (eServed) Douglas P. Manson, Esquire MansonBolves, P.A. 1101 West Swann Avenue Tampa, Florida 33606 (eServed) Joseph McClash 711 89th Street Northwest Bradenton, Florida 34209 (eServed) Ralf G. Brookes, Esquire Ralf Brookes Attorney 1217 East Cape Coral Parkway, Suite 107 Cape Coral, Florida 33904 (eServed) Justin Bloom, Esquire Post Office Box 1028 Sarasota, Florida 34230 (eServed) Robert Beltram, P.E., Executive Director Southwest Florida Water Management District 2379 Broad Street Brooksville, Florida 34604-6899
The Issue The issue in this case is whether the South Florida Water Management District (SFWMD, or District) should issue a Modification to Environmental Resource Permit (ERP) No. 36-00583- S-02, Application No. 050408-15 to Plantation Development, Ltd. (PDL), for construction and operation of a surface water management system serving a 78.11-acre condominium development known as Harbour Pointe at South Seas Resort, with discharge into wetlands adjacent to Pine Island Sound.
Findings Of Fact Based on the evidence and arguments, the following facts are found: The Parties PDL, the applicant, is a limited partnership which is the successor to Mariner Group, Inc. (Mariner). SFWMD has jurisdiction over PDL's application, as amended, and has given notice of its intent to grant PDL's application, as amended, with certain conditions. Petitioners, CCA and SCCF, and Intervenor, CSWF, are Florida not-for-profit corporations that challenged the proposed ERP. Development and Permit History The property subject to PDL's application was part of approximately 310-acres on the northern end of Captiva Island in Lee County, Florida. Redfish Pass is to the immediate north, separating Captiva Island from North Captiva Island. Farther to the north is Cayo Costa Island, a large island to the south of Boca Grande Pass. Most of Cayo Costa is a State Park. To the south of Captiva Island is Sanibel Island, the site of the Ding Darling National Wildlife Refuge. To the northeast of Sanibel Island and to the east of the rest of the string of barrier islands just mentioned is Pine Island Sound, which is to the west of Pine Island. Pine Island Sound is a state-designated Aquatic Preserve and Outstanding Florida Water (OFW). Pine Island Sound also is state-designated Class II water, but shell-fishing is prohibited in the immediate vicinity of Captiva Island. To the east of Pineland Island is Little Pine Island, which is surrounded by the Matlacha Pass Aquatic Preserve, which includes the Matlacha Pass National Wildlife Refuge. All of these features are part of the Charlotte Harbor National Estuary (CHNE). San Carlos Bay is farther south. The Lee County mainland is to the east of Matlacha Pass and San Carlos Bay. The 310-acre site was purchased by Mariner in 1972 for development of a resort that became known as the “South Seas Plantation.” Mariner's property included both Captiva Island proper and a smaller island immediately to the east across Bryant Bayou to the north and Chadwick Bayou farther to the south. Bryant Bayou has a narrower inlet from the north, and Chadwick Bayou has a narrower inlet to the south. Both inlets lead to Pine Island Sound. When Mariner purchased the property, it theoretically was possible to develop a maximum of 3,900 dwelling units on the 310-acre property, pursuant to Lee County zoning. In 1973, Mariner submitted an application to Lee County for the right to develop of 912 dwelling units on its 310 acres. PDL characterizes this as a "voluntary down-zoning" for the purpose of protecting the environment and unusual for a developer to do at that point in time. However, it is speculative how much more than 912 dwelling units would have been approved by Lee County at the time. The purpose of Mariner’s application to Lee County was to create a resort where recreational, single family, multi- family, and some commercial uses would coexist in a resort setting. The overall development plan was to construct the resort while conserving many of the property’s natural resources, including several miles of mangrove and Gulf of Mexico shoreline. Lee County approved the rezoning and the concept of the South Seas Plantation in 1973. Mariner's development began with Captiva Island proper and included a marina, golf course, and a variety of residential condominiums and single-family home sites. Some of the residential units were sold, and others remained in Mariner's ownership. Mariner marketed the rental of units at South Seas Plantation and served as rental agent for units not owned by Mariner. Development of the marina included dredging, and spoil was deposited on the northern tip of the smaller island, helping to create approximately 1.4 acres of upland there. In the 1950's or 1960's, a natural sand-and-shell berm along the eastern shore of the smaller island was built up and maintained by addition of fill material to create a two-track sand/shell road, which was used for vehicular access to the northern tip via an east-west road that divided the smaller island roughly in half and connected it to Captiva Island proper and the main road at South Seas Plantation. At a later point in time, the east-west portion of the road was paved for better access to a drinking water plant, a wastewater treatment plant, and a helicopter pad used by the Lee County Mosquito Control District. In 1985, Mariner received from SFWMD a “Master Stormwater Permit” for its entire development (the 1985 Permit). At that time, SFWMD did not regulate wetland impacts, only surface water management systems. The Department of Environmental Regulation regulated wetland impacts through its dredge and fill permit program, and there was no evidence relating to any dredge and fill permitting on the property. The 1985 Permit was for surface water management systems for construction in uplands on the property. No surface water management systems were needed or permitted in any wetlands. The 1985 Permit included a surface water management system for an 18-unit hotel on the spoil uplands of the northern tip of the smaller island. Permit drawings showed plans for a golf course on much of the remainder of the smaller island, which consisted mostly of wetlands. Access to the facilities was envisioned to be by water taxi, with emergency access via the utility and sand/shell road. Together, the hotel and golf course was to become a part of the resort known as Harbour Pointe. The 1985 Permit was modified several times in the years since its initial issuance, during which time Chapter 373, Florida Statutes, was amended to give SFWMD authority to regulate activities in waters and wetlands. However, until the pending application, none of the modifications had wetland impacts. In 1998, Mariner negotiated the sale of ten resort properties it owned in Florida, including South Seas Plantation, to Capstar, which later became Meristar S.S. Plantation Co., LLC (Meristar). Meristar was a real estate investment trust which specialized in hotels. Because it was not in the development business, Meristar was not interested in purchasing the as-yet undeveloped Harbour Pointe portion of South Seas Plantation, or Mariner's remaining development rights. As a result, Meristar purchased all the developed land on South Seas Plantation but not the approximately 78 acres of undeveloped land which is the subject of the pending application, or any of Mariner's development rights. Thus, after the sale of South Seas Plantation, Mariner retained its development rights and the 78 acres of undeveloped land, which are the subject of PDL's application. In 2002, Lee County issued an Administrative Interpretation which clarified that those development rights consisted of a maximum of 35 more residential units. Eleven units subsequently were built, leaving a maximum of 24 residential units when PDL filed its application in this case. The 78-acre Harbour Pointe site consists of mangrove wetlands, privately owned submerged lands, the 1.4-acre upland area at the northern tip of Harbour Pointe and another 1.4 acres of upland, which contain a Calusa Indian mound, known as the Chadwick Mound for its location west of Chadwick Bayou. While agreements between Meristar and PDL contemplate that PDL's subsequent development at Harbour Pointe would be marketed as part of the South Seas Resort and share some amenities and services, the parcels which comprise the Harbour Pointe development are the only undeveloped lands PDL owns or controls. PDL has no contractual or other legal right to develop on property owned by Meristar. Because it was modified several times since issuance, the 1985 Permit has not expired. However, Harbour Pointe never was constructed, and that part of the 1985 Permit expired in that Mariner lost its entitlement to proceed with construction. Instead, development of Harbour Pointe would require a permit modification under the new laws and rules, which included the regulation of wetland impacts. The Application and Proposed ERP In October 2003, PDL applied to SFWMD to further modify the 1985 Permit for construction of a water taxi dock for access to Harbour Pointe. After being informed by SFWMD that modifications to the 1985 Permit for development of Harbour Pointe would be reviewed under current laws and regulations, PDL withdrew the application. In April 2005 PDL applied for modification of the 1985 Permit to construct six 9,500 square-foot, four-plex condominium buildings (each two stories over parking, and accommodating units having 3,600-3,800 square feet of air-conditioned living space), a pool and spa, a tennis court, an access road, a filter marsh and surface water management facilities. Additionally, the site plan deleted all boat docks, except for a single water taxi slip and possibly a dock for launching kayaks and canoes and proposed a drawbridge across the inlet to Bryant Bayou to connect the project site to the South Seas Resort and eliminate the need for the emergency access road on the smaller island. This application described a development site of 7.4 acres, which included 4.8 acres of direct impacts to (i.e., destruction and fill of) mangroves and .1 acre of shading impacts from construction of the drawbridge. The proposed mitigation for the mangrove impacts included: restoration (by removal and replanting) of .6 acre of the north-south sand/shell road, with resulting enhancement of the adjacent preserved mangrove wetlands through improved hydrologic connection across the former shell/sand road and improved tidal connection to Pine Island Sound to the east; and preservation of the rest of PDL's property. The preserved areas would include: approximately 36 acres of mangrove wetlands adjacent to and south of the impacted wetlands (included the road to be restored) (Parcel A); 24.5 acres of mangrove wetlands south of the utility road and east of the narrow inlet to Chadwick Bayou (Parcel B); 9.3 acres of mangrove wetlands (7.9 acres) and tropical hardwoods (1.4 acres, which includes the Chadwick Mound), south of the utility road and west of the inlet to Chadwick Bayou, (Parcel C); .9 acre of mangrove wetlands to the west of Parcel C and the South Seas Resort main road (Parcel D); and .8 acre of mangrove wetlands separated from Parcel A by Bryant Bayou and adjacent to the South Seas Resort main road. A monitoring program lasting at least five years was offered to ensure success of the restoration and mitigation proposal. The application itself incorporated some reduction and elimination of wetland impacts. The total site consists of five separate tax parcels which could be developed into a number of single-family home sites. Such a development plan would have greater direct impacts than the proposed project and would require the shell/sand road to be significantly widened to meet current code requirements. By using the bridge as access, .11 acre of wetlands would be disturbed, as compared to 3.9 acres of total impact that would occur because of the widening the road. This approach results in the entire project causing less wetland impact than would occur from the use of the road alone. After the application was filed, PDL responded to two written requests for additional information and several other questions raised during meetings, phone conversations, and email exchanges with one or more SFWMD staff members. During this process, the application was amended. The tennis court was eliminated, and the filter marsh was replaced by a five dry detention ponds. In addition, the resulting development was concentrated more into the northern tip of the island to reduce and eliminate the greater secondary impacts (from more "edge effect") to the preserved wetlands to be expected from a more linear site plan. These changes reduced the footprint of the proposed project to 5.24 acres, the building size to 6,400 square feet each, the residential unit size to 2,400 to 2,600 square feet each, and wetland impacts to 2.98 acres, plus .11 acre of shading impacts from construction of the drawbridge. In addition, since the project was more concentrated at the northern tip, another tenth of an acre of the sand/shell road was to be restored. A conservation easement was offered for the 73.31 acres to be preserved, including 71.10 acres of wetlands, in Parcels A through E. PDL also offered to purchase .11 credits of offsite mitigation from the Little Pine Island Wetland Mitigation Bank (LPIWMB). On February 2, 2006, SFWMD's staff recommended approval of the amended application with 19 standard general conditions and 30 special conditions. Some of the special conditions in the Staff Report addressed prevention of erosion, shoaling, silt, turbidity, and water quality problems during construction or operation; remediation of any such problems not prevented; and restoration of any temporary wetland impacts. A pre-construction meeting was required to discuss construction methods, including construction dewatering. Although PDL indicated that dewatering would not be necessary for construction of the project, the Staff Report recommended that a dewatering plan be submitted before any dewatering occurred and noted that PDL would have to obtain all necessary Water Use authorizations, unless the work qualified for a No-Notice Short-Term Dewatering permit pursuant to Rule 40E- 20.302(3) or is exempt pursuant to Rule 40E-2.051.1 On February 8, 2006, SFWMD's Governing Board gave notice of its intent to approve the amended application with two additional conditions that were added to the Staff Report: PDL was required to apply for and receive a permit modification for the roadway necessary to access the project (i.e., the road leading from the South Seas Resort main road to the proposed drawbridge), and the applicant for the road to the drawbridge was required to document that proposed construction was consistent with the design of the master surface water management system, including land use and site grading assumptions; and a perpetual maintenance program for restored and preserved areas, including removal of exotic and nuisance vegetation in excess of five percent of total cover between regular maintenance activities, or such vegetation dominating any one section, was required to ensure integrity and viability. The parties interpreted the first of the two additional conditions to mean that construction access to build the project would be via the new roadway and drawbridge. On May 30, 2006, to address certain issues raised by the pending challenge to SFWMD's intended action, PDL further amended the application to substitute two wet retention ponds and three dry retention ponds for the five dry detention ponds and to make associated minor changes to the proposed surface water management system's water quality treatment methods to further reduce water quality impacts from the discharge of the system into the adjacent preserved wetlands. In addition, in view of disagreements among the parties as to the ability of PDL's onsite mitigation proposal to offset wetland impacts, PDL offered to increase offsite mitigation by purchasing as many additional credits from the LPIWMB as necessary to completely offset wetland impacts, as determined by the Uniform Mitigation Assessment Methodology (UMAM). Water Quantity Impacts Pursuant to Rule 40E-4.301(1), 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. Section 6.0 of the Basis of Review for Environmental Resource Permit Applications Within the South Florida Water Management District (BOR), entitled Water Quantity Criteria, outlines the criteria that the applicant must meet for water quality at the project site. As outlined in BOR Section 6.2, the off-site discharge is limited to rates not causing adverse impacts to existing off- site properties. The proposed surface water management system consists of a series of swales, dry retention, and then a wet retention system with an outfall into the areas to the south. Ordinarily, stormwater runoff eventually will be absorbed into the ground. Any discharge associated with the system, typically only in conjunction with major rain events, will flow into a preserved wetland that will be hydrologically connected to Bryant Bayou and Pine Island Sound. As outlined in BOR Section 6.2, the off-site discharge rate is limited to historic discharge rates. As required by BOR Section 6.3, a storm event of 3-day duration and 25-year return frequency is used in computing off- site discharge rates. As required by BOR Section 6.4, building floors must be at or above the 100-year flood elevations. PDL conducted a hydrologic analysis of the existing condition of the property, analyzed the runoff patterns that would result during the 25-year rainfall event and then compared the development plan hydrologic analysis to the existing condition. The conclusion was that the development plan would not adversely affect offsite area. PDL analyzed a series of storm conditions for the protection of road elevations and the protection of finished floors. There are no off-site areas that contribute to runoff through this piece of property. The proposed system will not cause adverse water quantity impacts to waters and adjacent lands, flooding to onsite or offsite properties, or adversely impact existing surface water storage and conveyance capabilities. Water Quality Impacts Rule 40E-4.301(1)(e) requires an applicant to provide reasonable assurances that the proposed project will not adversely affect the quality of receiving waters so that State water quality standards will not be violated. BOR Section 5.0 is entitled Water Quality Criteria. BOR Section 5.1 states that projects shall be designed and operated so that offsite discharges will meet State water quality standards. BOR Section 5.2.1 requires that either retention or detention, or both retention and detention be provided in the overall system in one of the following three ways or equivalent combinations thereof: Wet detention volume shall be provided for the first inch of runoff from the developed project, or the total runoff of 2.5 inches times the percentage of imperviousness, whichever is greater. Dry detention volume shall be provided equal to 75 percent of the above amounts computed for wet detention. Retention volume shall be provided equal to 50 percent of the above amounts computed for wet detention. Retention volume included in flood protection calculations requires a guarantee of long term operation and maintenance of system bleed-down ability. BOR Section 5.9 states that all new drainage projects will be evaluated based on the ability of the system to prevent degradation of receiving water and the ability to conform to State water quality standards. In the design of the system, PDL proposed a series of best management practices. The first is to treat runoff through grassed swale areas adjacent to buildings and some of the internal roadways. From there, the water would discharge through a series of dry retention areas where there would be further removal and treatment. The water would discharge through a proposed wet retention area prior to outfall under more significant rainfall events, southward into the preserved wetland area. Because of the hydrological connection from there to Bryant Bayou and Pine Island Sound, a more detailed evaluation was conducted. PDL's detailed evaluation included source control measures. The first one is a construction pollution prevention plan. PDL also proposed an urban storm water management plan. PDL is going to provide guidance to property owners about pesticide and fertilizer management control. The Applicant also submitted a street-sweeping proposal. The design of the system incorporates an additional 50 percent water quality treatment volume, over and above the requirements of the BOR. The wet retention system, located to the north of the proposed outfall structure, incorporates submerged aquatic vegetation. That is not a requirement of the District. It is an extra measure that will remove additional levels of pollutants prior to outfall. PDL proposed an urban stormwater management plan. The plan requires annual inspection of the water management facilities, and it must be documented that the system is functioning as originally designed and built. The stormwater management system is capable, based on generally accepted engineering and scientific principles, of functioning as proposed. The stormwater management system satisfies the District's water quality criteria. Petitioners and Intervenor criticized the method used by PDL's water quality consultant, Dr. Harvey Harper, for projecting and evaluating water quality impacts to be expected from PDL's stormwater management design. They contended that the so-called "Harper method" has been criticized by other experts, none of whom testified. Dr. Harper ably defended himself against the criticism leveled at him. He testified that most if not all of the components he has incorporated into his evaluation method are not new but rather have been accepted and used by experts in his field for years. He also explained that he refined his evaluation method in response to some early criticism and that the method he used in this case has been peer-reviewed and accepted by the Department of Environmental Protection for evaluation of stormwater design criteria. While some of the assumptions incorporated in his evaluation method are simple averages of a relatively small samples, and sometimes averages of averages, Dr. Harper was confident in the ability of his method to accurately evaluate the expected water quality impacts from PDL's system. While there is potential for error in any projection, Dr. Harper's evaluation provided reasonable assurances that utilization of PDL's proposed stormwater management and treatment method will not result in violation of any State water quality standards or significantly degrade the water quality of Bryant Bayou or Pine Island Sound. Value of Wetland and Surface Water Functions In general, as part of the CHNE, the mangrove wetlands to be impacted by the proposed ERP are very important. The CHNE Coast Conservation Management Plan identifies three major threats to the estuary and local ecosystem: fish and wildlife habitat loss; water quality degradation; and hydrological alteration. The plan calls for the preservation of mangroves within the CHNE. A wide array of wildlife uses the habitat in the vicinity of the mangrove wetlands to be impacted. The site is in an important coastal fly-way for migratory birds, including numerous species of waterfowl and songbirds that migrate across the Caribbean and Gulf of Mexico to and from South and Central America. The project area also provides habitat for several listed wildlife species, including the American crocodile, wood stork, and West Indian manatee. The mangrove wetlands that will be impacted directly and indirectly by the proposed ERP are in relatively good condition and are very important due primarily to their location near Redfish Pass at the northern end of Captiva Island and to their relationship to the rest of the relatively large area of contiguous and relatively undisturbed wetlands in Parcels A through E. These attributes make them especially important as a nursery ground for several valuable fish species. Existing impacts attributable to the spoil and other disturbances in the adjacent uplands, the northernmost extent of the sand/shell road, and the South Seas Plantation/Resort development to the west across the inlet to Bryant Bayou keep these impacted wetlands from being of the very highest quality. Clearly, and obviously, the project will destroy and fill 2.98 acres of these wetlands. Indirect (secondary) impacts to the adjacent preserved wetlands will result from alteration of hydrology of the 2.98 acres of directly impacted wetlands. Instead of sheet-flowing across the uplands on the northern tip of Harbour Pointe into those wetlands, surface water on the 5.24- acre development project will be directed into a series of swales, to the dry retention ponds, and to the wet retention ponds with an outfall to the adjacent preserved wetlands to the south. Secondary impacts from the Harbour Pointe project will be similar to the existing secondary impacts to the 2.98 acres attributable to the adjacent spoil and the South Seas Plantation/Resort development, if not somewhat greater due to the absence of any buffer like the inlet. On the other hand, PDL's mitigation proposal will restore .7 acre of wetlands where the northern end of the north- south sand/shell road now exists. Eventually, the restored wetland would be expected to become an extension of the existing, adjacent red and basin black mangrove forest. In addition, the resulting improved hydrologic connection to Pine Island Sound will enhance the value of functions in the preserved wetlands, including possibly expanding the existing fish nursery and making it accessible to fish larvae and juvenile fish entering from the east as well as from the west via Bryant Bayou. There was much debate during the hearing as to whether the sand/shell road is natural or man-made and whether it is reducing what otherwise would be the natural tidal and hydrologic connection between the wetlands to the west of the road and Pine Island Sound. As indicated, a prior owner added fill material to the natural sand and shell berm in the 1950's and 1960's to create better vehicular access. See Finding 9, supra. The evidence was reasonably persuasive that those man-made changes have altered hydrology and tidal connection to some extent and that the restoration project will enhance the value and functions of the preserved wetlands to some extent. Impacts to the value of wetland and surface water functions, and corresponding mitigation for impacts, are required to be assessed using UMAM. See Fla. Admin. Code R. 62-345.100. While the mitigation assessment method might be uniform, its application and results are not. Three different experts used UMAM with differing results. SFWMD's expert, Mr. Cronyn, and PDL's consultants, Kevin L. Erwin Consulting Ecologist, Inc. (KLECE), conferred after their initial assessments, resulting in changed results by both (as well as correction of errors in initial scoring by Mr. Cronyn.) Dave Ceilley, an expert for Petitioners and Intervenor, scored the 2.98 acre impact area significantly higher in its current state than the final score of either Mr. Cronyn or KLECE, resulting in a higher functional loss from its destruction and filling. He also gave no credit for restoration of the sand/shell road, in contrast to KLECE and Mr. Cronyn, and scored PDL's mitigation proposal as it affected 36.6 acres of preserved wetlands (essentially, Parcel A) as a functional loss instead of a functional gain, as scored by KLECE and Mr. Cronyn. Mr. Ceilley also scored PDL's mitigation proposal as it affected 24.5 acres of preserved wetlands (Parcel B) as a functional loss instead of a functional gain, as scored by KLECE and Mr. Cronyn. Finally, he gave no credit for preservation of Parcels A through E via a conservation easement because he was under the mistaken impression that the land already was under a conservation easement in favor of Lee County. (Actually, PDL had agreed to preserve 65 acres of mangrove forest in return for the right to develop Harbour Pointe, although a conservation easement actually was imposed on only about six acres. Although not identified, the 65 acres probably would have included the preserved wetlands in the proposed ERP.) Mr. Cronyn gave credit for preservation of Parcels B through E. KLECE did not claim credit, because KLECE did not think it was necessary, but KLECE accepts Mr. Cronyn's assessment of those parcels. Mr. Ceilley's recent onsite field work was extremely limited, and much of his assessment was based general knowledge of the area and dated (14-year old) onsite field work. In addition, this was the first "real-life" UMAM assessment performed by Mr. Ceilley. His only other use of UMAM was for practice in training. Finally, his assessment was entirely independent without the input of any other consultants to aid him. In contrast, both KLECE and Mr. Cronyn had extensive prior experience using UMAM. In addition, KLECE functioned as a three- man team in performing its UMAM assessments and talked out any initial discrepancies and disagreements (albeit with Mr. Erwin being the final arbiter). KLECE and Mr. Cronyn also consulted with one another, as well as experts in other related fields before finalizing their respective UMAM assessments. KLECE was able to draw on field work conducted during over 200 man-hours onsite in recent years. While KLECE was the retained consultant and agent for the applicant in this case, Mr. Ceilley conceded that Mr. Erwin adheres to high ethical standards. Petitioners and Intervenor were critical of credit given in the UMAM assessments performed by Mr. Cronyn for preservation of Parcels B through E. (KLECE did not claim credit for their preservation in its UMAM assessment.) Petitioners and Intervenor contend that PDL already has agreed to preserve the wetlands in those parcels in return for the ability to utilize the remaining 24 residential units of development rights at Harbour Pointe and that development of the Chadwick Mound is unlikely. Actually, as found, PDL's agreement with the County only specified six of the 65 acres of wetlands to be preserved. Besides, the preserved wetlands in the proposed ERP would implement the agreement with the County. As for the Chadwick Mound, preservation without the proposed ERP is not a certainty, although residential development there would be difficult now that its existence is common knowledge. In any event, the relative unlikelihood of development in Parcels A through E, especially after development of 24 units at Harbour Pointe, was taken into consideration by Mr. Cronyn in determining the amount of credit to be given for their preservation. Taking all the evidence into account, Mr. Cronyn's UMAM assessment of the value of wetland functions with and without the proposed ERP are accepted. According to his assessment, the proposed ERP will result in a functional loss of .34 functional units, meaning an equivalent amount of mitigation credit would have to be purchased from the LPIWMB to offset wetland impacts. Based on the functional assessment used to permit that mitigation bank, approximately an additional .9 of a mitigation bank credit would be needed, in addition to the .11 already offered. The evidence as to cumulative impacts did not clearly define the pertinent drainage basin. Logically, the pertinent drainage basin either would encompass all land draining to surface waters connected to Pine Island Sound, which would include Little Pine Island, or would be limited to the land that is subject to the proposed ERP. If the former, all offsetting mitigation would be within the same drainage basin. If the latter, there would be no cumulative impacts, since the proposed ERP would complete all development. Reduction and Elimination of Wetland Impacts According to BOR Section 4.2.1.1, if a proposed surface water management system will result in adverse impacts to wetland or other surface water functions such that it does not meet the requirements of Sections 4.2.2 through 4.2.3.7, the District must consider whether the applicant has implemented practicable design modifications to reduce or eliminate such adverse impacts. The term "modification" does not mean not implementing the system in some form, or requiring a project that is significantly different in type or function, such as a commercial project instead of a residential project. Elimination and reduction also does not require an applicant to suffer extreme and disproportionate hardship--for example, having to construct a ten mile-long bridge to avoid half an acre of wetland impacts. However, Anita Bain, SFWMD's director of ERP regulation, agreed that, in interpreting and applying BOR Section 4.2.1.1, "the more important a wetland is the greater extent you would require elimination and reduction of impact." As reflected in Findings 17-19, supra, PDL explored several design modifications in order to reduce and eliminate impacts to wetland and other surface water functions. However, several options for further reducing and eliminating wetland impacts were declined. PDL declined to eliminate the swimming pool and move one or more buildings to the pool's location at the extreme northern tip of Harbour Pointe because that would not be a practicable means of reducing the Harbour Pointe footprint. First, the undisputed testimony was that a residential building could not be sited as close to the water's edge as a swimming pool could. Second, because it would block the view from some of Meristar's residential properties, and Meristar has the legal right to approve or disapprove PDL's development on Harbour Pointe. PDL declined to reduce the number of buildings because, without also reducing the number and/or size of the residential units, reducing the number of buildings would make it difficult if not impossible to accommodate all cul-de-sacs required by Lee County for use by emergency vehicles and meet parking needs beneath the buildings, as proposed. (In addition, it would reduce the number of prime corner residential units, which are more marketable and profitable.) PDL declined to further reduce unit size because a further reduction to 2,000 square feet would only reduce the footprint of the six proposed buildings by a total of 5,000 square feet--less than a ninth of an acre. Reducing unit size to much less than 2,000 square feet would make it difficult if not impossible to market the condos as "luxury" units, which is what PDL says "the market" is demanding at this time (and also what PDL would prefer, since it would maximize PDL's profits for the units.) But it was not proven that smaller condos could not be sold at a reasonable profit. PDL declined to reduce the number of condo units at Harbour Pointe (while maintaining the conservation easement on the remainder of PDL's acreage, which would not allow PDL to develop all of the 24 dwelling units it wants to develop and is entitled to develop on its 78 acres, according to Lee County). However, it was not proven that such an option for further reducing and eliminating wetland impacts would not be technically feasible, would endanger lives or property, or would not be economically viable. With respect to economic viability, SFWMD generally does not examine financial statements or profit-and-loss pro formas as part of an analysis of a site plan's economic viability. This type of information is rarely provided by an applicant, and SFWMD does not ask for it. As usual, SFWMD's reduction and elimination analysis in this case was conducted without the benefit of such information. Rather, when PDL represented that any reduction in the number of units would not be economically viable, SFWMD accepted the representation, judging that PDL had done enough elimination and reduction based on the amount of wetland impacts compared to the amount of wetlands preserved, in comparison with other projects SFWMD has evaluated. As Ms. Bain understands it, "it's almost like we know it when we see it; in that, you wouldn't ask an applicant to build a ten-mile bridge to avoid a half an acre wetland impact, so something that's so extreme that's obvious, rather than how much profit would a particular applicant make on a particular project." Although SFWMD did not inquire further into the economic viability of modifications to reduce and eliminate wetland and surface water impacts, Petitioners and Intervenor raised the issue and discovered some profit-and-loss pro formas that were presented and addressed during the hearing. A pro forma prepared in August 2003 projected a profit of $2.79 million for the first 8 of 12 units and an additional $1.72 million profit on the next four units (taking into account construction of a drawbridge and road to the west at a cost of $1.8 million). This would result in a total profit of $4.51 million, less $800,000 for a reserve to pay for maintenance of the drawbridge (which PDL said was required under timeshare laws). Another pro forma prepared in February 2004 projected profits of $11.99 million on 16 "big-sized" units (3,000 square feet), $11.81 million on 20 "mid-sized" units (2,200 square feet), and $13.43 million on 24 "mixed-size" units (16 "mid- sized" and 8 "small-sized" at 1,850 square feet), all taking into account the construction of the drawbridge and road at a cost of $1.8 million. After production of the earlier pro formas during discovery in this case, PDL prepared a pro forma on June 7, 2006. The 2006 pro forma projected net profit to be $4.9 million, before investment in the property. However, PFL did not make its investment in the property part of the evidence in the case. In addition, Petitioners and Intervenor questioned the validity of the 2006 pro forma. PDL answered some of the questions better than others. To arrive at the projected net profit, PDL projected significantly (33%) higher construction costs overall. The cost of the drawbridge and road to the west was projected to increase from $1.8 million to $2.5 million. Based on its experience, PDL attributed the increase in part to the effect of rebuilding activity after Hurricane Charlie and in part to the effect of Sanibel Causeway construction (both increased overweight charges and limitations on when construction vehicles could cross the causeway, resulting construction work having to be done at night, at a significantly higher cost). At the hearing, PDL did not present any up-to-date market surveys or other supporting information on construction costs, and the Sanibel Causeway construction is expected to be completed before construction on the Harbour Pointe project would begin. In addition, without a full enough explanation, PDL replaced the bridge operation and maintenance reserve of $800,000 with an unspecified bridge reserve fund of $2 million. On the revenue side of the 2006 pro forma, gross sales of $1.9 million per unit were projected, which is less than PDL was projecting per square foot in February 2004, despite the assumed increased construction costs. PDL also attributes this to the effects of Hurricane Charlie. Again, there were no market surveys or other information to support the pricing assumptions. Besides predicting lower price potential, the 2006 pro forma deducts a pricing contingency of $2.3 million. PDL did not calculate or present evidence on whether it could make a profit building and selling 16 or 20 units, thereby eliminating a building or two (and perhaps some road and stormwater facility requirements) from the project's footprint. The absence of that kind of evidence, combined with the unanswered questions about the 2006 pro forma for the maximum number of units PDL possibly can build, constituted a failure to give reasonable assurance that wetland and surface water impacts would be reduced and eliminated by design modifications to the extent practicable, especially given the very high importance of the wetlands being impacted. Public Interest Test An ERP applicant who proposes to construct a system located in, on, or over wetlands or other surface waters must provide reasonable assurances that the project 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.” § 373.414(1)(a), Fla. Stat.; Rule 40E-4.302(1)(a); and SFWMD BOR Section 4.2.3. This is known as the “Public Interest Test,” and is determined by balancing seven criteria, which need not be weighted equally. See Lott v. City of Deltona and SJRWMD, DOAH Case Nos. 05-3662 and 05-3664, 2006 Fla. Div. Adm. Hear. LEXIS 106 (DOAH 2006). The Public Interest criteria are as follows: Whether the activity will adversely affect the public health, safety or welfare or the property of others. There are no property owners adjacent to the site, and the closest property owners to the site are located across the inlet which connects Bryant Bayou to Pine Island Sound. While mangrove wetlands generally provide maximum protection from hurricanes, it does not appear from the evidence that existing conditions would provide appreciably more protection that the conditions contemplated by the proposed ERP. Otherwise, the project would not adversely affect the public health, safety or welfare, or property of others. Whether the activity will adversely affect the conservation of fish and wildlife, including endangered or threatened species, or their habitats. The proposed ERP would impact (fill and destroy) 2.98 acres of very important, high quality mangrove wetlands. Even with the restoration or creation of .7 acre of probable former wetlands and improvements in the hydrologic connection of the 36.5-acre preserved wetland (Parcel A) to Pine Island Sound, the proposed ERP probably will have a negative effect on the conservation of fish and wildlife, including listed species. However, the negative effect would not be considered "adverse" if the elimination and reduction requirements of BOR 4.2.1.1 are met. Whether the activity will adversely affect navigation or the flow of water or cause harmful erosion or shoaling. The proposed drawbridge will be constructed over the inlet connecting Bryant Bayou with Pine Island Sound, a distance of approximately 65 feet. Boaters use the inlet for navigation. However, by its nature, a drawbridge allows for and not adversely affect navigation. The proposed ERP does not contain specifics on operation of the drawbridge, but PDL's consultant, Mr. Erwin, testified that there would be no adverse effect on navigation, assuming that the bridge would remain in the open position between use for crossings by road. The drawbridge would not adversely affect 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. The question whether the proposed ERP will adversely affect fishing or recreational values is informed by both the UMAM functional assessment and the reduction and elimination analysis. If impacts to wetlands and surface waters are reduced and eliminated, and offset by mitigation, there should be no significant adverse effects on fishing and recreational values. Whether the activity will be of a temporary or permanent nature. The proposed development is permanent in nature. vi. Whether the activity will adversely affect or will enhance significant historical and archaeological resources under the provisions of Section 267.061, Florida Statutes. There are no significant archaeological resources on the Harbour Pointe project site. Although shell scatter left by the Calusa Indians has been found on Parcel A, they have been evaluated in the permit application process by Corbett Torrence, an archeologist, and found to be of limited historical or archaeological value. The reduced scope of the project avoids most of these areas. The proposed ERP will, however, enhance significant archaeological resources by placing a conservation easement on Parcel C, which is the site of the Chadwick Mound, one of the largest Calusa Indian mounds in Lee County. Further studies of this site could lead to a much better understanding of the Calusa culture. This Indian mound is a very valuable historical treasure, and its protection through inclusion in a conservation easement is very much in the public interest. vii. The current condition and relative value of functions being performed by areas affected by the proposed activity. This subject also was considered in the reduction and elimination analysis and in the UMAM functional assessment. As in the Findings the current condition and relative value of the functions being performed by the areas affected by the proposed activity are very valuable. That is why the reduction and elimination analysis is particularly important in this case. Assuming appropriate reduction and elimination, mitigation according to the UMAM assessment can offset unavoidable impacts to the functions performed by the areas affected by the proposed activity. Standing of CCA, SCCF, and CSWF CCA, SCCF, and CSWF each has at least 25 current members residing within Lee County and was formed at least one year prior to the date of the filing of PDL's application. CCA's mission statement includes protection of "our residents' safety, the island ecology, and the unique island ambience . . . ." CCA also is dedicated to "preserving and expanding, where possible, the amount of native vegetation on Captive Island" and preservation of natural resources and wildlife habitat on and around Sanibel and Captiva Islands. SCCF's mission is the preservation of natural resources and wildlife habitat on and around Sanibel and Captiva. It manages just over 1,800 acres of preserved lands, including mangrove forest habitat similar to that being proposed for development by PDL. Management activities involve invasive non- native plant control, surface water management, prescribed burning, native plant habitat restoration and wildlife monitoring. CSWF's purpose is to sustain and protect the natural environment of Southwest Florida through policy advocacy, research, land acquisition and other lawful means. Its four core programs are: environmental education; scientific research; wildlife rehabilitation; and environmental policy. Of CCA's 464 members, approximately 115 live within the boundaries of South Seas Plantation/Resort. Approximately 277 of SCCF's 3,156 members live on Captiva Island, and 40 live within the boundaries of South Seas Plantation/Resort. The members of CCA and SCCF who own property on Captiva Island rely on the mangrove systems for protection from storms. A substantial number of the Captiva Island residents and the other members of CCA and SCCF engage in recreational activities in the vicinity of PDL's property, including boating, fishing, bird-watching, wildlife observation, and nature study that would be adversely affected by significant water quality and wetland impacts from the proposed ERP. CSWF has 5,600 family memberships, approximately 400 in Lee County, and 14 on Sanibel. No members live on Captiva Island. There was no evidence as to how many of CSWF's members use the natural resources in the vicinity of the proposed ERP for recreational purposes or otherwise would be affected if there are water quality and wetland impacts from the proposed ERP.
Recommendation Based upon the foregoing Findings of Fact and Conclusions of Law, it is RECOMMENDED that the proposed ERP be denied; however, if wetland and surface water impacts are reduced and eliminated to the extent practicable, the proposed ERP should be issued with the additional conditions, as represented by PDL's witnesses: that the proposed drawbridge be left drawn except when in use for road access; that construction access be via the proposed drawbridge only; and that there be no construction dewatering. DONE AND ENTERED this 8th day of November, 2006, in Tallahassee, Leon County, Florida. S J. LAWRENCE JOHNSTON Administrative Law Judge Division of Administrative Hearings The DeSoto Building 1230 Apalachee Parkway Tallahassee, Florida 32399-3060 (850) 488-9675 SUNCOM 278-9675 Fax Filing (850) 921-6847 www.doah.state.fl.us Filed with the Clerk of the Division of Administrative Hearings this 8th of November, 2006.
Findings Of Fact Upon consideration of the oral and documentary evidence adduced at the hearing, the following relevant facts are found: The petitioner West Coast Regional Water Supply Authority (WCRWSA) was formed in 1974 by inter-local agreement under Chapter 373, Florida Statutes, as a supply entity to provide and develop sources of water for its members and other governmental entities. The members of WCRWSA include the two cities of St. Petersburg and Tampa and the three counties of Pinellas (intervenor herein), Hillsborough and Pasco. The petitioner and the intervenor own and operate permitted well fields which are regulated by the respondent Southwest Florida Water Management District (SWFWMD) and are therefore subject to the rules and regulations of SWFWMD. All parties have stipulated, and the evidence so demonstrates, that the WCRWSA and Pinellas County are substantially affected by the challenged proposed rule and therefore have standing to challenge its validity. The proposed rule being challenged in this proceeding was considered by the Governing Board of SWFWMD as a result of a prior rule being declared invalid in another proceeding. The prior rule, codified as Rule 16J-2.11(3), Florida Administrative Code, provided as follows: 16J-2.11 Conditions for a Consumptive Use Permit Issuance of a permit will be denied if the amount of water consumptively used will exceed the water crop of lands owned, leased or otherwise controlled by the applicant. (Except where determined otherwise, the water crop [precipitation less evapotranspiration] throughout the District will be assumed to be three hundred sixty-five thousand (365,000) gallons per year per acre.) By Final Order dated April 9, 1980, 1/ that rule was declared to be an invalid exercise of delegated legislative authority on the grounds that it exceeded SWFWMD's statutory authority under Chapter 373, Florida Statutes, it impermissibly conflicted with provisions of Chapter 373, Florida Statutes, it created property rights to water by virtue of land ownership contrary to Chapter 373 and the decision in the case of Village of Tequesta v. Jupiter Inlet Corp., 371 So.2d and 663 (Fla. 1979); and it was a hydrologically unsound method of determining the issuance or denial of consumptive use permits and was accordingly arbitrary and capricious in nature. The two subsections of proposed Rule 40D-2.301 being challenged in this proceeding read as follows: "40D-2.301. Conditions for Issuance of Permits. Among other factors to be considered by the Board in determining whether a particular use is consistent with the public interest will be: the maximum amount to be withdrawn of a single day; the average amount to be withdrawn during a single week, during a typical growing (or irrigation) season, during an extreme cold season, during a year of extreme drought an during the term of the proposed permit; the amount to be withdrawn in relationship to amounts being withdrawn from adjacent or nearby properties; the proximity of withdrawal points to location of points of withdrawal by others; the total amounts presently permitted from the entire basin, or other hydrologic unit; and the change in storage that such withdrawal and use will cause. If the proposed consumptive use will average less than 1,000 gallons per acre per day, in the absence of evidence to the contrary, the Board will presume that the quantity of water proposed for consumptive use is consistent with the public interest and the applicant will not be required to submit further evidence on this point. If the proposed consumptive use is to average 1,000 gallons or more per acre per day, the applicant must establish that the proposed use of water in such quantity is consistent with the public interest. (NOTE: Present subsections 6 through 11 will be renumbered consecutively following the above new subsections.) The factors listed in subsection (6) of the proposed rule are not all- inclusive. Each of the factors listed are resource related or hydrological considerations. The effect of each of the factors listed is appropriate for consideration by the Governing Board of SEFWMD when making a determination as to whether a consumptive use permit should be granted. With the exception of that portion of subsection (6) relating to a weekly average amount to be withdrawn, the factors listed in subsection (6) are covered by existing specific rules of SWFWMD. The word "acre" in the phrase "1,000 gallons per acre per day" is intended to mean land owned, leased or otherwise controlled by the applicant. The figure of 1,000 gallons per acre per day represents the average quantity of water which is available within the respondent's District for man's use and to maintain natural systems. The figure is a district wide estimation. It cannot be arbitrarily applied to any specific site within the District due to the fact that different parcels of land do not possess identical geologic or hydrologic characteristics. The amount of water which is available from a specific parcel of land is dependent upon geographical and hydrological factors which vary considerably from site to site. These factors include, among other things, the amount of rainfall the land receives, the water table, the existence of confining layers, soil and vegetation types, and transmissivity, storage and leakage coefficients. Withdrawals of water in small amounts per acre per day are generally less likely to have adverse hydrologic effects on the water resources within the District than are withdrawals in greater amounts. In most areas of the District, 1,000 gallons per acre per day can be withdrawn without jeopardizing or adversely affecting the resource or the availability of water for others. This would not necessarily be true of coastal areas where salt water intrusion is a possibility or in areas where wells presently exist which withdraw large quantities of water on a daily basis. Eighty-nine percent (89%) of the more than 6,000 consumptive use permits which have been issued by the SWFWMD are for amounts less than 1,000 gallons per acre per day.
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.
The Issue Whether a consumptive use permit for the quantities of water applied for should be granted.
Findings Of Fact Applicant Phillips Petroleum Company submitted application Number 7500103 for a consumptive use permit for an average daily withdrawal of 9,000,000 gallons of water a day to be withdrawn from the Florida Aquifer in DeSoto County, Florida. The application is for a new use and the withdrawal is for industrial use from four withdrawal points. The center of withdrawals will be located at Latitude 27 degrees, 14 minutes, 40 seconds north. Longitude 82 degrees, 2 minutes, 48 seconds west, in DeSoto County. Notice of the September 3, 1975 public hearing was published in a newspaper of general circulation, to wit: The Arcadian on August 14 and 21, 1975, pursuant to Section 373.146, Florida Statutes. Notice of the continuation of the hearing held at 10:30 a.m., December 11, 1974 were duly noticed. Sarasota County was granted leave to intervene as a party to the proceeding. Evidence was received and testimony was heard by all parties at the September 3, 1975 hearing and evidence was received and testimony was heard by she Applicant and Intervenor at the December 11, 1975 hearing, and although the attorneys for the Southwest Florida Water Management District took no further part in the December 11, 1975 hearing on the merits, depositions of the Southwest Florida Water Management District staff members, James Mann and Barbara Boatwright, were received. Phillips Petroleum Company owns approximately 15,200 acres of land in DeSoto County and Manatee County and proposes to commence a phosphate mining operation on that property using a total of 15 million gallons of water per day, 9,000,000 gallons per day (MGD) from DeSoto County and 6 million gallons per day (MGD) from Manatee County. This application for a permit is for the 9 million gallons of water to be withdrawn from an 8,700 acre parcel owned by the Applicant in DeSoto County, Florida. As such it presumptively seeks withdrawal and consumptive use of no more than the average annual water crop for this parcel. Pursuant to the water crop theory, the water crop for the 8,700 acres contro led by the Applicant in the Southwest Florida Water Management District is 8.7 million gallons of water per day. However, as shown by correspondence of a hydrologist from Southwest Florida Water Management District, a phosphate mining operation is only 90 percent consumptive and therefore the actual consumptive use is 7.8 million gallons per day and falls within the water crop theory assumption set forth in Rule 16J-2.11(3), F.A.C., infra. The statutory criteria for granting a consumptive use permit is found in Section 373.223, Florida Statutes, which states: "(1) To obtain a permit pursuant to the provisions of this chapter, the applicant must establish that the proposed use of water: Is a reasonable-beneficial use as defined in 474.019(5); and Will not interfere with any presently existing use of water; and Is consistent with the public interest. (2) The governing board of the department may authorize the holder of a use permit to transport and use ground or surface water beyond overlying land or outside the watershed from which it is taken if the governing board or department determines that such transport and use is consistent with the public interest." This statute has been supplemented by rules adopted by the Southwest Florida Water Management District and is found in Rule 16J-2.11, F.A.C.: "16J-2.11 Conditions for a Consumptive Use Permit. The intended consumptive use: Must be a reasonable, beneficial use. Must be consistent with the public interest. Will not interfere with any legal use of water existing at the time of the application. Issuance of a permit will be denied if the withdrawal of water: Will cause the rate of flow of a stream or other watercourse to be lowered below the minimum rate of flow established by the Board. Will cause the level of the potentiometric surface to be lowered below the regulatory level established by the Board. Will cause the level of the surface of water to be lowered below the minimum level established by the Board. Will significantly induce salt water encroachment. Will cause the water table to be lowered so that the lake stages or vegetation will be adversely and significantly affected on lands other than those owned, leased or otherwise controlled by the applicant. Issuance of a permit will be denied if the amount of water consumptively used will exceed the water crop of lands owned, leased, or otherwise controlled by the applicant. (Except where determined otherwise, the water crop [precipitation less evapotranspiration] throughout the District will be three hundred sixty-five thousand (365,000) gallons per year per acre.") The United States Geological Survey and the Florida Department of Environmental Relation have received data supplied to Southwest Florida Water Management District with the application for a consumptive use permit. Throughout the course of the hearing testimony was heard and evidence was received as to the "leakance value" of the parcel of land in question. "Leakance value" was defined as the moving of water from the surface down into the deeper aquifer. A geologist, Mr. Donald S. Kell, with the Department of Environmental Regulation, and who testified at the request of the Intervenor, Sarasota County, was of the opinion that insufficient data to determine leakance value in connection with the mining operation had been submitted and therefore further tests were needed. Mr. Jack Hickey of the United States Geological Survey was of the opinion that leakance value had not been obtained. The technical staff members of the Southwest Florida Water Management District were uncertain as to whether reliable leakance value had been obtained. It was the position of the Intervenor, Sarasota County, that due to the geological conditions of the proposed mining operation, this leakance value or surface recharge into the aquifer was insufficient and was not in conformity with Southwest Florida Water Management District's water crop theory assumption of 1,000 gallons per acre per day. Although evidence was presented on this point, it is the finding of this Hearing Officer that such evidence was insufficient to establish the basis of, any finding of fact or to rebut the assumption contained in the above referenced rule. The validity of this rule was not challenged and the presumption is that the rule is valid. The water used in the flotation process of applicants mining and benefication process would be recycled and reused in other areas of the phosphate operation. A letter of objection by Donald T. Yeats was examined and considered in this Order. The Applicant presented evidence that the construction of the facility would be in excess of $94 million expended over a period of 3 years, 61 percent of which would be spent in the region. 350 people would be employed at full production. Additional support jobs would employe from 200-400 people. Evidence was presented by the Applicant and was not rebutted by the Intervenor or by the Southwest Florida Water Management District as to each of the applicable conditions for a consumptive use permit in Chapter 16J-2.11, Rules of the Southwest Florida Water Management District, effectuating the provisions of Chapter 378, Florida Statutes.
Recommendation That the Southwest Florida Water Management District approve Phillips Petroleum Company's application for a consumptive use permit as requested, subject to the following terms and conditions: Prior to commencing withdrawals, Phillips Petroleum shall notify the District of said commencement; All production wells will be equipped with appropriate flow deters or other measuring devices; Phillips shall submit periodic reports of withdrawal to the District; and Phillips shall install appropriate observation wells or other monitoring facilities. DONE and ORDERED this 12th day of January, 1976. DELPHENE C. STRICKLAND Hearing Officer Division of Administrative Hearings Room 101, Collins Building Tallahassee, Florida 32301 (904) 488-9675 COPIES FURNISHED: Jacob D. Varn, Esquire Carlton, Fields, Ward, Emmanuel, Smith & Cutler 2000 Exchange Bank Building Tampa, Florida Jay T. Ahern, Esquire Southwest Florida Water Management District Post Office Box 457 Brooksville, Florida Richard E. Nelson, Esquire Richard L. Smith, Esquire Nelson, Payne, Hesse and Cyril 2070 Ringling Boulevard Sarasota, Florida
The Issue The issues are whether to (a) issue an Environmental Resource Permit (ERP) to the Department of Transportation (DOT) and Martin County (County) authorizing construction and operation of a surface water management system to serve a project known as the Indian Street Bridge; (b) issue DOT a letter of modification of ERP No. 43-00785-S authorizing roadway and drainage modifications to the Kanner Highway/Indian Street intersection; and (c) issue DOT a letter of modification of ERP No. 43-01229-P authorizing roadway and drainage modifications to Indian Street between the intersections of Kanner Highway and Willoughby Boulevard.
Findings Of Fact Based on the evidence presented by the parties, the following findings of fact are made: The Parties Petitioner Citizens for Smart Growth, Inc., is a Florida 501(c)(3) corporation with its principal place of business in Palm City, Florida. It was formed by Odias Smith in August 2001, who serves as its president. The original directors were Kathie Smith, Odias Smith, and Craig Smith, who is the Smiths' son. The composition of the Board has never changed. According to the original Articles of Incorporation, its objectives are "preserving and enhancing the present advantages of living in Martin County (Quality of Life) for the common good, through public education, and the encouragement of reasonable and considered decision making by full disclosure of impacts and alternatives for the most appropriate use of land, water and resources." The exact number of members fluctuates from time to time. There are no dues paid by any member. At his deposition, Mr. Smith stated that no membership list exists; however, Kathie Smith stated that she currently has a list of 125 names, consisting of persons who at one time or another have made a contribution, have attended a meeting, or asked to be "kept informed of what's going on or asked to be on a mailing list or a telephone list, so they could be advised when we have meetings." No meetings have been held since 2006. Therefore, the Petitions filed in these cases have never been discussed at any meetings of the members, although Ms. Smith indicated that telephone discussions periodically occur with various individuals. Kathie Smith believes that roughly 25 percent of the members reside in a mobile home park north of the project site on Kanner Highway on the eastern side of the St. Lucie River, she does not know how many members reside on the western side of the St. Lucie River, and she is unaware of any member who resides on the South Fork of the St. Lucie River immediately adjacent to the project. Although the three Petitions allege that "seventy percent of the members . . . reside and/or recreate on the St. Lucie River," and in greater detail they allege how those members use that water body or depend on it for their livelihood, no evidence was submitted to support these allegations that 70 percent (or any other percentage of members) use or depend on the South Fork of the St. Lucie River for recreational or other activities. Petitioners Odias Smith and Cathie Smith reside in Palm City, an unincorporated community just south of Stuart in Martin County. They have opposed the construction of the new bridge since they moved to Palm City in 2001. It is fair to infer that Mr. Smith formed the corporation primarily for the purpose of opposing the bridge. Their home faces north, overlooking the South Fork of the St. Lucie River, from which it is separated by Saint Lucie Shores Drive and a narrow strip of common-ownership property. A boat dock extends from the common-ownership property into the St. Lucie River, providing 5 slips for use by the Smiths and other co-owners. The home is located three blocks or approximately 1,000 feet from the proposed western landfall of the new bridge. Due to the direction that the house faces (north) and the site of the new bridge, the surface water management system elements associated with the bridge will not be visible from their property. Mr. Smith believes, however, that when looking south through a veranda window on the second floor of his home, he will be able to see at least a part of the new bridge. From the front of their house, they now have an unobstructed view of the existing Palm City Bridge, a large structure that crosses the St. Lucie River approximately six- tenths of a mile north of their home, and which is similar in size to the new bridge now being proposed by the Applicants. The Smiths' home is more than 500 feet from the Project's right- of-way, and they do not know of any impact on its value caused by the Project. While the Smiths currently engage in walking, boating, running, fishing, and watching wildlife in the neighborhood or the South Fork of the St. Lucie River, there was no credible evidence that the Project would prevent them from doing so after the bridge and other improvements are constructed. Also, there was no evidence showing that the ERP Letter Modifications will cause them to suffer any adverse impacts. In fact, as noted below, by DOT undertaking the Project, the neighborhood will be improved through reduced flooding, improved water quality, and new swales and ponds. The County is a political subdivision of the State. It filed one of the applications at issue in this proceeding. DOT is an agency of the State and filed the three applications being contested. The District has the power and duty to exercise regulatory jurisdiction over the administration and enforcement of ERP criteria pursuant to Part IV, Chapter 373, Florida Statutes, and Title 40E of the Florida Administrative Code. The Department of Environment Protection (DEP) has delegated certain authority to the District, including the authority to authorize an applicant to use sovereign submerged lands via a public easement within the District's geographic jurisdiction. The Project Construction of a new bridge over the St. Lucie River has been studied extensively by the Applicants for over twenty years. DOT has awarded the contract and nearly all of the right-of-way has been purchased. The Project will begin as soon as the remaining permits are acquired. The Project is fully funded through the American Recovery and Reinvestment Act of 2009 and County funding. The Project is located in the County and includes 62.06 acres of roadway bridge development and 12.45 acres of sovereign submerged lands. The Project begins on the west side of the St. Lucie River on County Road 714, approximately 1,300 feet west of Mapp Road in Palm City and ends on the east side of the St. Lucie River approximately 1,400 feet east of Kanner Highway (State Road 76) on Indian Street. It includes construction and operation of a surface water management system to serve the road and bridge project. The total length of the Project is approximately 1.96 miles (1.38 miles of roadway and 0.58 miles of bridge) while the total area is approximately 74.51 acres. After treatment, surface water runoff will discharge to the tidal South Fork of the St. Lucie River. The Project encompasses a bridge crossing the South Fork of the St. Lucie River and the Okeechobee Waterway. Both are classified as Class III waters. The bridge transitions from 4 to 6 lanes east of the Okeechobee Waterway and will require a 55-foot vertical clearance and a 200-foot horizontal clearance between the fender systems at the Okeechobee Waterway. The bridge will cross over a portion of Kiplinger Island owned and preserved by the County. A part of the island was donated to the County in 1993-1994 by The Kiplinger Washington Editors, Inc., and the Kiplinger Foundation, Inc. Audubon of Martin County owns another part of the island. The transfer of title to the County does not include any restriction on the use of the island for conservation purposes only. Documentation submitted at hearing refers to a "two hundred foot wide road right-of-way" easement that the bridge will cross and allows the County to designate where on the island parcel such an easement would be. Therefore, spanning the bridge over a portion of the island owned by the County is clearly permissible. The Project also includes the roadway transition and widening/reconstruction of (a) County Road 714 from the beginning of the Project to Mapp Road from 2-lane to a 4-lane divided roadway; (b) Southwest 36th Street from Mapp Road to the beginning of the bridge from a 2-lane rural roadway to a 4-lane divided roadway with wide roadway swales; and (c) Kanner Highway (along Indian Street) from a 4-lane to a 6-lane divided urban roadway. Drainage improvements on both sides of the St. Lucie River are associated with the roadway construction. DOT proposes to provide both on-site and off-site mitigation for wetland and surface waters impacts pursuant to a mitigation plan approved by the District. The ERP 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. Besides these rules, certain related BOR provisions which implement the rules must also be considered. The conditions for issuance primarily focus on water quality, water quantity, and environmental criteria and form the basis of the District's ERP permitting program. The parties have stipulated that the Project either complies with the following rule provisions or they are not applicable: Rules 40E-4.301(1)(a), (b), (g), (g), (h), and (k), and 40E- 4.302(1)(a)3. and 6. All other provisions remain at issue. Where conflicting evidence on these issues was submitted, the undersigned has resolved all evidentiary conflicts in favor of the Applicants and District. Based on the parties' Stipulation, the following provisions in Rule 40E-4.301(1) are in dispute and require an applicant to provide reasonable assurances that the construction, alteration, operation, maintenance, removal, or abandonment of a surface water management system: 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 such that the water quality standards set forth in chapters 62- 4, 62-302, 62-520, 62-522, 62-550, F.A.C., including any anti-degradation provisions of paragraphs 62-4.242(1)(a) and (b), subsections 62-4.242(2) and (3), and rule 62-302.300, F.A.C., and any special standards for Outstanding Florida Waters and Outstanding National Resource Waters set forth in subsections 62-4.242(2) and (3), F.A.C., will be violated; will not cause adverse secondary impacts to the water resources; 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 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; These disputed criteria are discussed separately below. Surface Water Storage and Conveyance Rule 40E-4.301(1)(c) requires that an applicant provide reasonable assurances that a proposed activity will not cause adverse impacts to existing surface water storage and conveyance capabilities. Through unrefuted evidence, this requirement was shown to be satisfied. The evidence also establishes that the surface water in and around the Project will actually improve if the Project is constructed as permitted. Further, it will create improved and upgraded surface water management and treatment in areas that now lack features such as swales, retention/detention ponds, curbs and gutters, and improve the overall surface water storage and conveyance capabilities of the Project and surrounding areas. In its current pre-development condition, flooding has occurred in certain areas adjacent to and within the Project area due to poor conveyance, low storage volume, and high tailwater conditions that result from high tides. The Project will remedy historic flooding issues in the Old Palm City area which lies adjacent to a portion of the Project alignment. Surface water runoff will be captured, controlled, and treated by a system of swales, weirs, and retention/detention facilities for pretreatment prior to discharging into the South Fork of the St. Lucie River. Reasonable assurances have been given that existing surface water storage and conveyance capabilities will not be adversely affected. Value of Functions to Fish, Wildlife, and Species Rule 40E-4.301(1)(d) requires that an applicant provide reasonable assurances that a proposed activity will not adversely impact the value of functions provided to fish and wildlife and listed species by wetlands and other surface waters. BOR Section 4.2.2 further implements this provision. For the following reasons, the rule and BOR have been satisfied. The evidence shows that the existing functions to fish and wildlife were assessed and analyzed by a number of federal and state fish and wildlife agencies. There were extensive review and site inspections by the District, DOT, United States Fish and Wildlife Service, United States Army Corps of Engineers, and National Marine Fisheries Commission to assess the existence of, and potential impact on, fish and wildlife that may result from the Project. These studies revealed that while portions of the South Fork of the St. Lucie River provide potential habitat for aquatic or wetland-dependent or threatened species of special concern, no nesting or roosting areas within the vicinity of the Project were observed. The evidence further supports a finding that "other surface waters" over and under the Project will not receive unacceptable impacts due to their current condition, the detrimental influences of Lake Okeechobee discharges, and tidal impacts. Many of the wetlands to be impacted by the Project were shown to have been impacted by historic activities, and they provide diminished functions to fish and wildlife. The wetland functions were assessed through the Uniform Mitigation Assessment Methodology (UMAM). The UMAM is a standardized procedure for assessing the functions provided by wetlands and other surface waters, the amount that those functions would be reduced by a proposed project, and the amount of mitigation necessary to offset that loss. Detailed UMAM assessments were prepared by the Applicants and the District. They demonstrate that while certain functional units will be lost, they will be fully offset by the proposed mitigation. No credible evidence to the contrary was presented. Water Quality of Receiving Waters Rule 40E-4.301(1)(e) requires an applicant to provide reasonable assurances that a project will not adversely affect the quality of receiving waters such that State water quality standards will be violated. BOR Section 4.2.4 implements this rule and requires that "reasonable assurances regarding water quality must be provided for both the short term and long term, addressing the proposed construction, . . . [and] operation of the system." The receiving water body is the South Fork of the St. Lucie River, which is designated as an impaired water body. The evidence establishes that the Applicants will avoid and minimize potential short-term impacts to water quality by using silt screens and turbidity barriers, and implementing other best management practices to contain turbidity during construction of the Project. They will also use a temporary trestle rather than barges in the shallow portions of the South Fork to avoid stirring up bottom sediments. Finally, a turbidity monitoring plan will be implemented during construction and dewatering activities for all in-water work. All of these construction techniques will minimize potential impacts during construction. The evidence further establishes that water quality standards will not be violated as a result of the Project. In fact, in some cases water quality will be enhanced due to the installation and maintenance of new or upgraded surface water management features in areas where they do not exist or have fallen into disrepair. Over the long term, the Project is expected to have a beneficial effect on water quality. By improving existing surface water management and adding new surface water treatment features, the Project will provide net improvement to water quality. Wetland Delineation and Impacts The Project includes unavoidable impacts to wetlands and other surface waters. A total of 18.53 acres of wetlands and other surface waters within the Project site will be impacted by the Project, including 3.83 acres of wetlands that will be directly impacted and 14.7 acres of wetlands and other surface waters that will be secondarily impacted. The delineated wetlands are depicted in the Staff Report as wetlands 2a, 19a, 19b, 22, 25-29, 30a, 30b, and 30c, with each having a detailed UMAM assessment of its values and condition. (Impacts to wetland 25 are not included in this Project because they were accounted for in a separate permit proceeding.) Using a conservative assessment and set of assumptions, the District determined that, with the exception of wetlands 19a, 19b, 22, and 27, all wetlands would be impacted by the Project. However, the wetlands that would be impacted suffer from varying historical adverse impacts that have compromised the functions and values they provide to fish, wildlife, and species. This is due to their proximity to urban development, vegetative connectivity, size, historic impacts, altered hydroperiod, and invasive plant species. Likewise, even though the wetlands to be impacted on Kiplinger Island provide certain resting and feeding functions for birds, the value of these functions is comparatively lower than other wetlands due to the presence of invasive species and lack of management. The preponderance of the evidence supports a finding that the Applicants provided reasonable assurances that the Project will not cause adverse impacts to fish, wildlife, or listed species. See Fla. Admin. Code R. 40E-4.301(1)(d). Secondary Impacts Rule 40E-4.301(1)(f) and BOR Sections 4.1.1(f) and 4.2.7. require a demonstration that the proposed activities will not cause adverse secondary impacts to the water resources, both from a wetlands and water quality standpoint. Secondary impacts are those that occur outside the footprint of the project, but which are very closely linked and causally related to the activity to be permitted. De minimis or remotely-related secondary impacts, however, are not considered unacceptable. See § 4.2.7.(a). There will be secondary impacts to 6.83 acres of freshwater wetlands and 7.87 acres of mangroves, or a total of 14.7 acres. To address these secondary impacts, the Applicants have established extensive secondary impact zones and buffers along the Project alignment, which were based in part on District experience with other road projects and another nearby proposed bridge project in an area where a State Preserve is located. While Petitioners' expert contended that a 250-foot buffer on both sides of the roadway's 200-foot right-of-way was insufficient to address secondary impacts to birds (who the expert opines may fly into the bridge or moving vehicles), the greater weight of evidence shows that bird mortality can be avoided and mitigated through various measures incorporated into the Project. Further, the bird mortality studies used by the expert involved significantly different projects and designs, and in some cases involved projects outside the United States with different species concerned. Engineering and Scientific Principles Rule 40E-301(1)(i) requires that an applicant give reasonable assurance that a project "be capable, based on generally accepted engineering and scientific principles, of being performed and of functioning as proposed." Unrefuted evidence establishes that the proposed system will function and be maintained as proposed. Financial, Legal and Administrative Capability Rule 40E-4.301(1)(j) requires that an applicant give reasonable assurance that it has the financial, legal, and administrative capability to ensure that the activity will be undertaken in accordance with the terms of the permit. The evidence supports a finding that Applicants have complied with this requirement. Elimination and Reduction of Impacts Before establishing a mitigation plan, Rule 40E- 4.301(3) requires that an applicant implement practicable design modifications to eliminate and reduce wetland and other surface water impacts. In this case, there are unavoidable, temporary wetland impacts associated with the construction of the Project, as well as unavoidable wetland impacts for direct (project footprint), secondary, and cumulative impacts of the Project. The record shows that the Applicants have undertaken extensive efforts to eliminate and reduce wetland and other surface water impacts of the Project. For example, DOT examined and assessed several innovative construction techniques and bridge designs to eliminate and avoid wetland impacts. To eliminate and reduce temporary impacts occurring during construction, DOT has reduced the effect of scour on the pier foundation and reduced the depth of the footing to minimize the amount of excavation on the mangrove island. Also, during construction, the contractor is prohibited from using the 200- foot right-of-way on the mangrove island for staging or stockpiling of construction materials or equipment. The majority of the bridge width has been reduced to eliminate and avoid impacts. Also, the Project's alignment was adjusted to the north to avoid impacts to a tidal creek. Reasonable assurances have been given that all practicable design and project alternatives to the construction and placement of the Project were assessed with no practicable alternatives. Public Interest Test Besides complying with the requirements of Rule 40E- 4.301, an applicant must also address the seven factors in Rule 40E-4.302(1)(a)1.-7., which comprise the so-called "public interest" test. See also § 373.414(1)(a), Fla. Stat. In interpreting the seven factors, the District balances the potential positive and negative effects of a project to determine if it meets the public interest criteria. Because Petitioners agree that factors 3 and 6 of the rule are not at issue, only the remaining five factors will be considered. For the following reasons, the Project is positive when the criteria are weighed and balanced, and therefore the Project is not contrary to the public interest. Public Health, Safety, and Welfare The Applicants have provided reasonable assurance that the Project will not affect public health, safety, and welfare. Specifically, it will benefit the health, safety, and welfare of the citizens by improving traffic conditions and congestion, emergency and hurricane evacuation, and access to medical facilities. In terms of safety, navigation markers are included as part of the Project for safe boating by the public. See Fla. Admin. Code R. 40E-4.302(1)(a)1. Conservation of Fish and Wildlife The activity will not adversely affect the conservation of fish and wildlife, including endangered or threatened species, or their habitats. The mitigation projects will offset any impacts to fish and wildlife, improve the abundance and diversity of fish and wildlife on Kiplinger Island, create mangrove habitat, and add to the marine productivity in the area by enhancing water quality. See Fla. Admin. Code R. 40E-302(1)(a)2. Fishing or Recreational Values The Project has features that allow for pedestrian and bicycle utilization and observation areas which should enhance recreational values. The Old Palm Bridge, approximately one mile north of the Project, has had no adverse impact on the fishing recreation along the South Fork of the St. Lucie River. Navigation will not be affected due to the height and design of the new bridge. Finally, the bridge is expected to be a destination for boating, kayaking, fishing, and bird watching. See Fla. Admin. Code R. 40E-4.302(1)(a)4. Whether the Activity is of a Permanent Nature The parties have stipulated that the Project is permanent in nature. No future activities or future phases of the project are contemplated. Temporary and permanent impacts are all being fully mitigated. See Fla. Admin. Code R. 40E- 4.302(1)(a)5. Values of Functions Being Performed in Affected Areas Due to historic impacts to the areas affected by the Project, the current condition is degraded and the relative value of functions is minimal. Although Kiplinger Island will have temporary impacts, that island is subject to exotic species and has no recreational use or access by boaters or members of the public. The Applicants propose mitigation which will improve and enhance these wetland functions and values in the areas. See Fla. Admin. Code R. 40E-4.302(1)(a)7. Summary The evidence supports a finding that the Project is positive as to whether it will affect the public health, safety, welfare, or property of others; that the Project is neutral with respect to navigation, erosion and shoaling, and water flow, as well as to historical and archaeological concerns; and that the Project is positive as to conservation of fish, wildlife, recreational values, marine productivity, permanency, and current values and functions. When weighed and balanced, the Project is not contrary to the public interest. Cumulative Impacts Rule 40E-4.302(1)(b) requires that an applicant give reasonable assurance that a project will not cause unacceptable cumulative impacts upon wetlands and other surface waters as set forth in BOR Sections 4.28 through 4.2.8.2. Cumulative impacts are the summation of unmitigated wetland impacts within a drainage basin. An analysis is geographically based upon the drainage basins described in BOR Figure 4.4.1. Petitioners' contention that Figure 4.4.1 is inaccurate or not representative of the basin in which the Project is located has been rejected. In this case, the North St. Lucie Basin was used. To assess and quantify any potential unacceptable cumulative impacts in the basin, and supplement the analyses performed by the Applicants, the District prepared a Basin Map that depicted all the existing and permitted wetland impacts as well as those wetlands under some form of public ownership and/or subject to conservation restrictions or easements. The District's analysis found that the wetlands to be mitigated were of poor quality and provided minimal wildlife and water quality functions. Cumulative impacts from the Project to wetlands within the basin resulted in approximately a four percent loss basin-wide. This is an acceptable adverse cumulative impact. Therefore, the Project will not result in unacceptable cumulative impacts. Mitigation Adverse impacts to wetlands caused by a proposed activity must be offset by mitigation measures. See § 4.3. These may include on-site mitigation, off-site mitigation, off- site regional mitigation, or the purchase of mitigation credits from mitigation banks. The proposed mitigation must offset direct, secondary, and cumulative impacts to the values and functions of the wetlands impacted by the proposed activity. The ability to provide on-site mitigation for a DOT linear transportation project such as a bridge is limited and in this case consists of the creation of mangrove and other wetlands between the realigned St. Lucie Shores Boulevard and the west shore of the St. Lucie River, north and south of the proposed bridge crossing. BOR Section 4.3.1.2 specifically recognizes this limitation and allows off-site mitigation for linear projects that cannot effectively implement on-site mitigation requirements due to right-of-way constraints. Off-site mitigation will offset the majority of the wetland impacts. Because no single on-site or off-site location within the basin was available to provide mitigation necessary to offset all of the Project's impacts, DOT proposed off-site mitigation at two established and functioning mitigation areas known as Dupuis State Reserve (Dupuis), which is managed by the County and for which DOT has available mitigation credits, and the County's Estuarine Mitigation Site, a/k/a Florida Oceanographic Society (FOS) located on Hutchinson Island. Dupuis is outside the North St. Lucie Basin and was selected to offset direct and secondary impacts to freshwater wetlands. That site meets the ERP criteria in using it for this project. The FOS is within the North St. Lucie Basin and was selected to offset direct and secondary impacts to estuarine wetlands. Like Dupuis, this site also meets the ERP criteria for the project. The preponderance of the evidence establishes that the on-site and off-site mitigation projects fully offset any and all project impacts, and in most instances before the impacts will actually occur. Sovereign Submerged Lands and Heightened Public Concern Chapter 18-21 applies to requests for authorization to use sovereign submerged lands. The management policies, standards, and criteria used to determine whether to approve or deny a request are found in Rule 18-21.004. For purposes of granting a public easement to the Applicants, the District determined that the Project is not contrary to the public interest and that all requirements of the rule were satisfied. This determination was not disputed. The only issue raised by Petitioners concerning the use of submerged lands is whether the application should have been treated as one of "heightened public concern." See Fla. Admin. Code R. 18-21.0051(5). If a project falls within the purview of that rule, the Board of Trustees of the Internal Improvement Trust Fund (Board), rather than the District, must review and approve the application to use submerged lands. Review by the Board is appropriate whenever a proposed activity is reasonably expected to result in a heightened public concern because of its potential effect on the environment, natural resources, or controversial nature or location. Id. In accordance with established protocol, the ERP application was sent by the District to DEP's review panel in Tallahassee (acting as the Board's staff) to determine whether the Project required review by the Board. The panel concluded that the Project did not rise to the level of heightened public concern. Evidence by Petitioners that "many people" attended meetings and workshops concerning the Project over the last 20 years or so is insufficient to trigger the rule. Significantly, except for general project objections lodged by Petitioners and Audubon of Martin County, which did not include an objection to an easement, no adjacent property owner or other member of the public voiced objections to the construction of a new bridge. Revised Staff Report On October 20, 2010, the District issued a Revised Staff Report that merely corrected administrative errors or information that had been previously submitted to the District. Contrary to Petitioners' assertion, it did not constitute a material change to the earlier agency action either individually or cumulatively. Therefore, it was properly considered in this proceeding. Letter Modifications The Letter Modifications were used as a mechanism to capture minor alterations made to previously issued permits for Kanner Highway and Indian Street. Neither Letter Modification is significant in terms of water quality, water quantity, or environmental impacts. Both were issued in accordance with District rules and should be approved.
Recommendation Based on the foregoing Findings of Fact and Conclusions of Law, it is RECOMMENDED that the South Florida Water Management District enter a final order granting Application Nos. 091021-8, 100316-7, and 100316-6. DONE AND ENTERED this 28th day of December, 2010, in Tallahassee, Leon County, Florida. S D. R. ALEXANDER Administrative Law Judge Division of Administrative Hearings The DeSoto Building 1230 Apalachee Parkway Tallahassee, Florida 32399-3060 (850) 488-9675 Fax Filing (850) 921-6847 www.doah.state.fl.us Filed with the Clerk of the Division of Administrative Hearings this 28th day of December, 2010. COPIES FURNISHED: Carol Ann Wehle, Executive Director South Florida Water Management District 3301 Gun Club Road West Palm Beach, Florida 33406-3007 Jeffrey W. Appel, Esquire Ray Quinney and Nebeker, P.C. 36 South State Street, Suite 1400 Salt Lake City, Florida 84111-1401 Bruce R. Conroy, Esquire Department of Transportation 605 Suwannee Street Mail Station 58 Tallahassee, Florida 32399-0458 David A. Acton, Esquire Senior Assistant County Attorney Martin County Administrative Center 2401 Southeast Monterey Road Stuart, Florida 34996-3397 John J. Fumero, Esquire Rose, Sundstrom & Bentley, P.A. 950 Peninsula Corporate Circle Suite 2020 Boca Raton, Florida 33487-1389 Keith L. Williams, Esquire South Florida Water Management District 3301 Gun Club Road Mail Stop 1410 West Palm Beach, Florida 33406-3007
