The Issue The issue is whether to approve an application by Respondents, Palm Beach County (County) and The David Minkin Florida Realty Trust, Richard Thall, Robert Thall, Peter L. Briger, Paul H. Briger, and The Lester Family Investments, LP (The Briger Group), for a conceptual Environmental Resource Permit (ERP) authorizing a surface water management system to serve a mixed-use development in the City of Palm Beach Gardens known as Scripps Florida Phase II/Briger (Scripps project).
Findings Of Fact Based on the evidence presented by the parties, the following findings of fact are made: The Parties Petitioner Tsolkas resides at 822 North C Street, Lake Worth, Florida, which is approximately 16.8 miles (in a straight line) south-southeast of the project site and approximately one mile west of the Intracoastal Waterway (ICW). Among others, he expressed concerns in this case about the potential extinction of species and the impact of the proposed site on the ICW. However, other than a general interest in environmental issues, he presented no evidence to demonstrate how he is affected by the issuance of the permit. Petitioner Minaya resides at 901 North Federal Highway, Apartment A, Lake Worth, Florida, and approximately the same distance from the project site and ICW. He has the same concerns as Petitioner Tsolkas but presented no evidence to demonstrate how the project will affect his substantial interests. The County is a chartered county and a political subdivision of the state. It owns approximately 70.0 acres of the site on which the Scripps project will be located and the 193.92-acre off-site mitigation area for the project at the Pine Glades Natural Area (Pine Glades). It is a co-applicant for an ERP. The Briger Group is a co-applicant for the modified ERP and owns 611.69 acres of the project site. The original permit that is being modified was issued as conceptual approval on January 19, 1978. The District is a public corporation in the State, having been created by special act in 1949 and operating pursuant to Chapter 373, Florida Statutes. The Application On April 27, 2009, the applicants submitted an application to modify a conceptual ERP, Application No. 090427- 7, for a surface water management system to serve 681.89 acres of mixed-use development in the City of Palm Beach Gardens (City). The original permit was also issued as a conceptual approval in 1978 and has been modified conceptually on a number of occasions, most recently in 2001. The application includes 193.92 acres of off-site mitigation at Pine Glades in the northern part of the County and additional off-site mitigation through the purchase of mitigation credits at the Loxahatchee Mitigation Bank in the southern part of the County. "Conceptual approval" means "an [ERP], issued by the District Governing Board, which approves a conceptual master plan for a surface water management system or a mitigation bank." Fla. Admin. Code R. 40E-4.021(5). It constitutes final agency action and is "binding to the extent that adequate data has been made available for review by the applicant during the review process." Id. After conceptual approval is obtained, the applicants must then file an application for an ERP to construct and operate the surface water management system. Therefore, no construction will be authorized by this permit. On April 16, 2010, the District issued a Staff Report recommending approval of the requested ERP. A Revised Staff Report making minor changes and clarifications to the original proposed agency action was issued on May 4, 2010. The Project and the Site The proposed project that will be served by the surface water management system is a multi-use development on a 681-acre tract located south of Donald Ross Road and north of Hood Road in the City. The site is divided by Interstate 95 (I-95) into two wedge-shaped parcels known as the western and eastern parcels. The Florida Turnpike adjoins the western side of the western parcel. With the exception of the highways, the site is surrounded by residential development including two projects located just east of the site: Legends at the Gardens (on the northern side) and San Michele (on the southern side). A portion of the site located east of I-95 is mostly undeveloped and vegetated. However, approximately 60 acres located at the southeast corner of the site include an existing horse farm with improved and unimproved pastures. The central and southern portions of this parcel contain a number of ditches that were created prior to the 1950s. The portion of the site west of I-95 is undeveloped and vegetated, but it also includes a few mobile homes on approximately 2 acres at the southern end of the site. The upland habitats are disturbed and degraded and primarily include pine flatwoods, mixed hardwood-pine forest, hardwood hammock, and dry prairie, some of which are infested with Brazilian pepper, Australian pine, and Japanese climbing fern. There are also around 86 acres of state jurisdictional wetlands and other surface waters. Finally, the southwestern portion of the parcel located west of I-95 contains a prehistoric/archaeological site which is proposed for preservation. The County owns 70 acres of the property on the eastern parcel, while The Briger Group owns the remaining acreage. The project is anticipated to house the Scripps Research Institute, as well as ancillary institutional, commercial, and residential uses. The project received development of regional impact approval from the City on April 1, 2010, and is subject to a master plan that identifies land use districts, such as a biotech district, a town center district, residential districts, and a neighborhood-serving commercial district. The 70 acres owned by the County will be used to house the second phase of the Scripps Research Institute. It is unknown at this time whether the Scripps facility will house administrative offices, laboratory space, or some other use. The build-out schedule for the project is twenty years. Before construction can commence, the applicants will be required to obtain zoning and site plan approval from the City, authorization from both the Northern Palm Beach County Improvement District (Improvement District) and the Seacoast Utility Authority, and a permit from the County Health Department. Also, the applicants will be required to receive a construction-related modification to the ERP from the District. The Surface Water Management System In 2001, the District issued a permit to the Improvement District for conceptual approval of a surface water management system for flood protection within a 4,059.9-acre area known as Unit 2, which includes the area of the proposed project. See Respondents' Exhibit 57. Drainage from the project site is presently covered by this permit. The Improvement District's system was designed, constructed, and is being operated and maintained for stormwater treatment. The waters in that system are not considered waters of the State. The proposed project will discharge into the Improvement District's system, which is upstream of a permitted man-made control structure on the property designed to retain or detain stormwater runoff in order to provide treatment and attenuation of the stormwater. The proposed system is primarily a wet detention system consisting of three large basins: A1, B1E(East), and B1W(West). The system has been designed to provide water quality and storm water attenuation prior to overflowing to the Improvement District's Unit 2 master system. As shown in the conceptual plans, Basin B1W is located on the west side of I-95 and has a control elevation of 13.5 feet National Geodetic Vertical Datum (NGVD). Mostly residential development is anticipated in this basin with a small supporting commercial development. An existing 60-inch culvert located under I-95 will continue to connect the two wetland areas, identified as W1 and W2, that are located on both the west and east sides of I- 95, respectively. Basin B1E is located in the southeastern portion of the site and will be controlled at 13.0 feet NGVD. Anticipated development in this area will be mostly residential neighborhoods as well. Exhibit 2 of the Staff Report reflects that runoff from the out-parcels and the northern half of Hood Road will be directed into the proposed project area. Pervious and impervious assumptions were made for future Hood Road improvements and are listed in the land use table. See Respondents' Exhibit 43 at p. 3 of 26. Basin B1E will overflow into the Unit 2 master system via a control structure and outfall pipe which discharges to a wet pond located within the adjacent San Michele development to the east. Industrial and commercial development is planned in Basin A1, which is the northeastern basin. The lakes will be controlled at elevation 13.0 feet NGVD. Runoff from this basin will be directed eastward into the Improvement District's Unit 2 master system via a control structure and pipe connection into the lake within the Legends of the Gardens development to the east. The applicants submitted site grading assumptions and pervious/impervious percentages as well as stormwater modeling to demonstrate compliance with the existing master system for the overall Improvement District's Unit 2 master system. In addition, the system for this basin has been designed to accommodate inflows from approximately 50 acres of I-95 right- of-way through an existing control structure which was permitted as part of the I-95 widening project. The proposed project includes direct impacts to a total of 78.47 acres of on-site wetlands. Wetland mitigation to offset the adverse impacts includes enhancement of 7.50 acres of on-site wetlands; the purchase of 13.70 freshwater herbaceous credits at the Loxahatchee Mitigation Bank; off-site wetland and upland restoration and enhancement of 163.41 acres of wetlands; and preservation of 30.51 acres of other surface waters, or a total of 193.92 acres, at Pine Glades. The ERP Permitting Criteria In order to obtain an ERP, an applicant must satisfy the conditions for issuance set forth in Rules 40E-4.301 and 40E-4.302. Additionally, the District has adopted BOR provisions that implement the relevant portions of the rules. The conditions for issuance primarily focus on water quantity, water quality, and environmental criteria and form the basis of the District's ERP permitting program. The first step in the District's environmental review is to identify wetlands and other surface waters. On March 5, 2009, the District issued a formal determination of wetlands delineating 34 wetland areas and 4 jurisdictional surface water ditches. This determination was not timely challenged and therefore represents final agency action. That determination was used in this permit application. Water Quantity Criteria Rule 40E-4.301(1)(a) requires an applicant to provide reasonable assurances that the propose activity will not cause adverse affects to water quantity, while Rule 40E-4.301(1)(b) requires reasonable assurances that the proposed activity will not cause adverse flooding to on-site or off-site property. The BOR provides a method to calculate allowable discharge rates. The evidence is that the proposed discharge is well within the standards imposed by the rules governing water quantity impacts. There will be no on-site or off-site flooding as a consequence of the proposed project. Rule 40E-4.301(1)(c) requires reasonable assurance that there will be no adverse impacts to existing surface water storage and conveyance capabilities. The evidence supports a finding that the proposed discharge will not cause any adverse impacts. Also, the system is capable of being developed and of functioning as proposed, as required by Rule 40E-4.301(1)(i). Petitioners contended that the project poses a threat of over-draining, which will significantly affect the region directly and cumulatively. However, the project does not pose a risk of over-draining because the control elevation of the project will be maintained at a level consistent with surrounding properties and the proposed drainage rate is less than the allowable rate under the rules. Water Quality Rule 40E-4.301(1)(e) sets forth the requirements relating to water quality. Also, BOR Section 5 contains the design criteria that a project must follow regarding off-site discharges to provide reasonable assurances to satisfy the above rule. Water quality treatment will be provided in a proposed wet detention system which utilizes stormwater ponds. The evidence shows that the ponds are larger than required, thereby providing water quality treatment in excess of what is required by the BOR. All water quality standards will be met. Hazardous Waste Management Plan Petitioners contend that no hazardous waste management plan was submitted to the District. However, a plan is not required now because it would need to address the specific uses for the property, which have not yet been designated. Special Condition 31 of the permit requires that such a plan be submitted at the time an application for construction approval is filed with the District. When this is submitted, it will be reviewed to determine if there are reasonable assurances that hazardous materials, if any, will not enter the proposed project's surface water management system. Elimination and Reduction Under BOR Section 4.2.1, after the District identifies the wetlands and other surface waters, the next step is to consider elimination and reduction of impacts. However, BOR Section 4.2.1.2(b) provides that an applicant is not required to demonstrate elimination and reduction impacts when: the applicant proposes mitigation that implements all or part of a plan that provides greater ecological value and that provides greater long term ecological value than the area of wetland or other surface water to be adversely affected. In considering this provision, the District concluded, consistent with the evidence, that the quality of the wetlands which will be adversely affected by this application is low, and the mitigation proposed will provide greater long-term ecological value than the wetlands impacted. This is because the mitigation at both Pine Glades and the Loxahatchee Mitigation Bank have regional ecological value, and these sites will provide greater long-term ecological value than the impacted wetlands. Secondary Impacts Rule 40E-4.301(1)(f) requires reasonable assurance that the project will not cause adverse secondary impacts to water resources. BOR Section 4.2.7 sets forth the requirements for on-site wetlands that will be preserved and enhanced. Under that section, secondary impacts to the habitat of wetlands associated with adjacent upland activities will not be considered adverse if buffers, with a minimum width of 15 feet and an average width of 25 feet, are provided abutting the wetlands. In this case, the single wetland area being preserved is buffered in accordance with those requirements. Applicants have satisfied the requirements of the rule. Mitigation If impacts to wetlands and other surface waters will occur, then mitigation may be offered to offset the impacts to functions identified in BOR Sections 4.2 through 4.2.9. To assess the impacts and the value of mitigation, the applicants used the statewide Uniform Mitigation Assessment Method and the Wetland Rapid Assessment Procedure. Those results are found in Appendix 1 of the application and in Responses to Requests for Additional Information submitted in August 2009 and January 2010. Page 13 of the Staff Report describes the mitigation. The District also performed its own independent analysis of both the impact and mitigation. That analysis demonstrated that sufficient mitigation is available in the options identified to offset the impacts. In fact, there was a net functional gain to the environment. In order to offset 50.76 acres of wetland impacts, the applicants will provide restoration and enhancement of 139.6 acres of wetlands and 23.81 acres of uplands, and preservation of 30.51 acres of other surface waters, or a total of 193.92 acres, at Pine Glades. Mitigation at this location offsets those impacts and is appropriate because it will provide more functional gain than the amount of functional loss for the same habitat types that are being impacted. Because Pine Glades is within the same drainage basin as the impacts, and the mitigation offsets the impacts, the District is not required to consider cumulative impacts. See § 373.414(8), Fla. Stat.; Fla. Admin. Code R. 40E-4.302(1)(b). Petitioners suggested that because Pine Glades is already owned by the County and intended to be restored, by allowing the applicants to receive mitigation credit for the restoration amounts to "double dipping." However, the evidence shows that the 193 acres proposed as mitigation in the permit is site-specific; no one has ever received mitigation credit for it in the past and no one will be able to receive mitigation credit for it in the future; and The Briger Group paid $86,250.00 per functional unit to reimburse the County for the cost of the land. Mitigation credit for restoration at Pine Glades is appropriate. As compensation for impacts to a total of 26.14 acres of freshwater marsh wetlands, the applicants will mitigate off- site by purchasing 13.70 freshwater herbaceous credits at the Loxahatchee Mitigation Bank. This bank is of regional ecological significance. Mitigation at this bank offsets the impacts and is appropriate because it will offset the impacts to freshwater marsh wetlands. Drainage basins are established by District rule in BOR Figure 4.4-1. While Petitioners contended that BOR Figure 4.4-1 does not accurately identify the geographic boundaries of the South Indian River Basin, which is being used here, the District is required to follow its own rules when reviewing an ERP application. Therefore, the use of Figure 4.4-1 was appropriate to determine whether the project is located within or outside of that drainage basin. Because the Loxahatchee Mitigation Bank is not located within the same basin as the proposed impacts, it was necessary for the District to consider cumulative impacts which will be mitigated at that bank. See § 373.414(8), Fla. Stat. This means that the applicants are required to give reasonable assurances that the impacts proposed for mitigation at Loxahatchee Mitigation Bank would not result in unacceptable cumulative impacts if the regulatory precedent set by the permit were applied to all properties within the basin that have the same type of habitat as that being impacted by the project and that have potential for development. The project will be located in the South Indian River Basin. The District's cumulative impact analysis for that basin supports a finding that there is very limited potential for future wetland loss in the basin and reasonable assurances have been given that there will be no adverse cumulative impacts. See Respondents' Exhibit 60. Species Rule 40E-4.301(1)(d) requires an applicant to demonstrate that the activities will not adversely impact the value of functions provided to fish and wildlife and listed species by wetlands and other surface waters. This evaluation is limited to wetland-dependent species. Upland species fall outside of the District's jurisdiction. Contrary to Petitioners' assertion, the hand fern is not a wetland-dependent species. Also, the District must rely on State-listed species, and not lists prepared by federal agencies. The evidence shows that the potential for utilization of this site by wetland-dependent species is minimal, and this site does not contain preferred habitat for nesting or denning of wetland dependent listed species. Although the site does not contain preferred habitat, the habitat value currently existing on this site will be replaced with mitigation at Pine Glades and the Loxahatchee Mitigation Bank. Public Interest Test In order to obtain a conceptual approval ERP, an applicant must provide reasonable assurances that the system located in, on, or over wetlands or other surface waters will not be contrary to the public interest and will not be inconsistent with the objectives of the District. See Fla. Admin. Code R. 40E-4.302(1)(a)1.-7.; § 373.414(1), Fla. Stat. The evidence establishes that reasonable assurances were provided to demonstrate that the proposed activities will not adversely affect the public health, safety, or the welfare or property of others; that they will not adversely affect the conservation of fish and wildlife, including endangered or threatened species or their habitat; that there are no issues related to navigability or the flow of water, erosion or shoaling; that the property does not currently provide fishing, recreational values, or marine productivity and is not open to the public; that the activity will be permanent; that there is an archeological site on the property which the applicants will preserve; that the mitigation will more than fully offset the impacts; and that the value of the functions currently being performed will not be adversely affected. Petitioners offered no evidence or analysis to rebut the expert testimony offered by Respondents. After balancing all seven factors, the evidence supports a finding that the activities will not be contrary to the public interest. Florida Coastal Management Program Petitioners contend that the project is inconsistent with the Florida Coastal Management Program (FCMA), which is administered by the Department of Environmental Protection (DEP). They also assert that the District is required to coordinate its review of the application with that agency and that it failed to do so. However, the issuance of the ERP (after a demonstration that all permitting criteria have been satisfied) constitutes certification that the project is consistent with the FCMA and no coordination with DEP is necessary. Other Criteria Any other criteria not discussed herein were either satisfied by the applicants or are not relevant to the project. Petitioners' Evidence Other than very limited cross-examination of some of Respondents' witnesses, Petitioner Minaya did not present any evidence to support his allegations. Other than cross-examination of Respondents' witnesses, Petitioner Tsolkas, a lay person, testified that his standing was based on general concerns that the project would drive species (such as the hand fern) into extinction, that it would pollute waters, including the ICW, and that it would destroy habitat for other species. No competent or persuasive evidence to support these contentions was presented. Other issues raised by Mr. Tsolkas were matters beyond the District's jurisdiction and are not considered in the permitting process.
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 No. 090427-7 with the conditions contained in the Amended Staff Report. DONE AND ENTERED this 30th day of November, 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 30th day of November, 2010.
Findings Of Fact The Petitioner is the owner of Lot 28, Hidden Bay Subdivision, Martin County, Florida. On July 19, 1990, Petitioner filed an application with the Respondent for a dredge and fill permit to construct on the wetland portion of his lot a single family dwelling on stilts, a garage, and a connecting driveway to an existing roadway. The application also seeks a permit to retain a roadway that was constructed on the property before the Respondent asserted jurisdiction over the property. The existing roadway is 25 feet wide and 510 feet long and remained in existence at the time of the formal hearing. The connecting driveway on the wetlands portion of the property would require 40 cubic yards of fill. The following, taken from the Notice of Permit Denial entered by Respondent, accurately describes the proposed project: The proposed project will entail the temporary placement of 500 cubit yards of clean fill in order to set piles for a proposed stilt house. Additional fill (40 cubic yards) is proposed for a driveway to access a proposed garage. Riprap is proposed along the east slope of the driveway and along the northwest slope under the proposed stilt house. In addition, 186 cubic yards of the existing unauthorized fill road is proposed to remain. Total acreage to be impacted by this project is .092 acres. Petitioner's lot fronts Bessey Creek and is located in Section 1, Township 38 South, Range 40 East, in Palm City. Petitioner's lot is located approximately 2,200 feet south of the C-23 Canal on Bessey Creek. Bessey Creek is designated a Class III water. Bessey Creek combines with other tributaries and ultimately discharges into the North Fork of the St. Lucie River, which is designated an Outstanding Florida Water. Petitioner's lot consists of 1.82 acres. Respondent has asserted jurisdiction over approximately 1.3 acres of Petitioner's lot on the grounds that it is a fresh water wetland. Petitioner does not challenge Respondent's asserted jurisdiction in this proceeding. The Respondent has jurisdiction over dredge and fill activities conducted on the portion of Petitioner's lot that is at issue in this proceeding. This project is not exempt from permitting procedures. A dredge and fill permit is required for the proposed construction. Prior to applying for this permit, Petitioner contacted James McElheny, a landscape architect, who assisted Petitioner in drawing up the plans for the house, the driveway, and the garage that Petitioner desired to construct on the property. Without being aware that a permit from the Respondent would be required, Petitioner constructed a driveway on a portion of his property that was within the permitting jurisdiction of Respondent. This driveway extended to the landward end of a boardwalk that terminated as a dock in Bessey Creek. After Petitioner became aware of the need for a permit, he removed the filled driveway to a point that Martin County and Respondent agreed was appropriate. A portion of the driveway remained on property within the permitting jurisdiction of the Respondent at the time of the formal hearing. The plan prepared by Mr. McElheny also depicted this existing, unauthorized roadway. Petitioner's application seeks, in part, a permit to retain this driveway. On June 10, 1991, Respondent issued its Notice of Permit Denial based on the Respondent's conclusion that the Petitioner had failed to provide the required assurances in Sections 403.918(1) and (2), Florida Statutes. The Notice of Permit Denial provided, in pertinent part, as follows: The Department hereby denies the permit for the following reasons: This project is expected to have both short and long term impacts to biological resources and water quality. The total acreage to be impacted by this project is .092 acres. In addition, the applicant has not provided reasonable assurance that the project is not contrary to the public interest pursuant to Section 403.918(2), Florida Statutes. Pursuant to 403.919, F.S. which gives the Department the authority to examine secondary impacts, the Department has concerns about additional wetland resource and water quality impacts that may result from this project. Floodplain areas are essential to the river system and provide important functions for the environment. The floodplain serves as a buffer system in high tide and storm events. It also serves as a source of detrital input which supports the freshwater and estuarine food chains. In addition, these areas act to improve water quality by stabilizing sediment and filtering upland runoff. Long-term effects of the proposed project would include a decrease in the productivity of the system, as well as a decrease in the filtering and stabilizing capabilities of the system. Water quality degradation is also expected to occur with upland runoff from pesticides, fertilizers, sewerage and petroleum products. Floodplain wetlands also provide a habitat for a wide variety of reptiles, amphibians, birds, crustaceans and mammals. This would eliminate this wetland habitat. This project is expected to be in violation of the following Florida Statutes and Florida Administrative Code Rules: 403.918 Criteria for granting or denying permits 17-312.080 Standards for Issuance or Denial of Permit 17-312.300(3) Mitigation Intent 17-302.560 Criteria: Class III waters The Department has determined that the following changes to the project make the project permittable. Modify the project to reduce or eliminate adverse environmental impact by: Removing the unauthorized fill road from water of the state. Relocate the proposed house to utilize as much upland area on the property as possible. Relocate the garage and access driveway to an upland area [and] eliminate or modify the garage and access road to reduce impacts. Section 403.918, Florida Statutes, provides the following permitting criteria pertinent to this proceeding: A permit may not be issued . . . unless the applicant provides the department with reasonable assurance that water quality standards will not be violated. . . . A permit may not be issued . . . unless the applicant provides the department with reasonable assurance that the project is not contrary to the public interest. . . . (a) In determining whether the project will adversely affect the public health, safety, or welfare or the property of others . . . the department shall consider and balance the following criteria: Whether the project will adversely affect the public health, safety, or welfare or the property of others. Whether the project will adversely affect the conservation of fish and wildlife, including endangered species, or their habitat; Whether the project will adversely affect navigation or the flow of water or cause harmful erosion or shoaling; Whether the project will adversely affect the fishing or recreational values or marine productivity in the vicinity of the project; Whether the project will be of a temporary or permanent nature; Whether the project will adversely affect or will enhance significant historical and archaeological resources under the provisions of s. 267.061; and The current condition and relative value of functions being performed by areas affected by the proposed activity. The Respondent is entitled to consider the cumulative impact of the proposed project pursuant to Section 403.919, Florida Statutes, which provides as follows: The department, in deciding whether to grant or deny a permit for an activity which will affect waters, shall consider: The impact of the project for which the permit is sought. The impact of projects which are existing or under construction or for which permits or jurisdictional determinations have been sought. The impact of projects which are under review, approved, or vested pursuant to s. 380.06, or other projects which may reasonably be expected to be located within the jurisdictional extent of waters, based upon land use restrictions and regulations. The residence that Petitioner proposes to build on the wetland portion of the property will be constructed on pilings so that the underside of the house will be 12 feet above the ground. There will be a total of 12 pilings, with each piling being 10 inches square. The "footprint" of the house will be 1,654 square feet. If the project is permitted, best management practice will require that a silt screen be erected around the construction site during construction to prevent silt runoff. The proposed site for the house is located in a natural clearing that would require minimal clearing. If the project is to be permitted in this wetland, the site selected by Petitioner is the best site with the least impact on the wetland. Petitioner would be required to remove up to two laurel oaks and seven red maple trees. These are relatively small trees, and both species are common. Petitioner would also be required to remove shrub of no particular unique value. Petitioner proposes to mitigate the removal of the trees by replanting on the property trees that were removed in a 2-1 ratio, so that 6 laurel oaks and 14 red maples would be replanted. Petitioner also proposes to revegetate the area beneath the residence, with the exception of the area required by the pilings. There are invasive, exotic plants on the property, such as Brazilian pepper, that would be removed by Petitioner and replaced by native plants. Ms. Jacqueline Kelly, the environmental specialist who reviewed this project for Respondent, visited the property approximately four times for a total of eight hours. Ms. Kelly is of the opinion that no dredge and fill activity should be permitted on jurisdictional wetlands. Ms. Kelly testified that she observed several species of birds while she was on the property, including a wood stork, a great blue heron, a little blue heron, a tricolored heron, an osprey, bluejays, woodpeckers, and grackles. The wood stork is an endangered species and the little blue heron, the tricolored heron, and the osprey are species of special concern. These birds do not nest on the subject property, and they were not observed in the area of the wetland on which the proposed construction would occur. There was no testimony upon which it can be concluded that the proposed construction will stop these species from coming on to the property. Because of the slope of the terrain, the upland portion of the Petitioner's property drains away from the wetland while the portion on which the proposed construction would occur drains toward the wetland. At the formal hearing, Petitioner suggested that any concerns as to drainage from the roof of the proposed residence could be discharged onto the upland portion of the lot by gutters. In his post-hearing submittal, Petitioner proposes that a condition of the permit be that "[a] roof drainage system be installed that allows the roof to drain to the upland portion of the project." The permitting requirement contained in Section 403.918(6), Florida Statutes, pertaining to historical or archaeological resources was not at issue in this proceeding. Ms. Kelly concluded that Petitioner has not provided reasonable assurances required by Section 403.918(2), Florida Statutes, as to each of the remaining permitting criteria. The rationale given by Ms. Kelly for her conclusions is not persuasive. The greater weight of the evidence is that all reasonable assurances required by Section 403.918(2), Florida Statutes, that were at issue in this proceeding have been provided as it pertains to the construction of the residence. The existing roadway was filled using shell rock which has stabilized. The mere existence of the roadway on the wetland property was not shown to violate any permitting criteria since this roadway does not violate water quality standards and is not contrary to the public interest. Petitioner did not, however, provide reasonable assurances that the utilization of this existing roadway as either a driveway or a parking area would not violate water quality standards as required by and within the meaning of Section 403.918(1), Florida Statutes, or that such use would not be contrary to the public interest or that those parts of the project would not be contrary to the public interest as required by and within the meaning of Section 403.918(2), Florida Statutes. Petitioner did not provide reasonable assurances that the construction of the garage or the extension of the driveway on these wetlands would not violate water quality standards as required by and within the meaning of Section 403.918(1), Florida Statutes, or that those parts of the project would not be contrary to the public interest as required by and within the meaning of Section 403.918(2), Florida Statutes. John Meyer was of the opinion that the project should be denied because of the possible precedent that the permitting of this project may establish for other owners of wetland properties. There was no factual or legal basis established for this opinion. The permitting of this project has no value as a precedent for other projects. There was no evidence that there were other permit applications pending for other projects in wetlands, and Mr. Meyer could only recall one or two such applications ever having been filed. The greater weight of the evidence establishes that speculative cumulative impacts of this project does not prohibit the permit pursuant to the provisions of Section 409.919(3), Florida Statutes.
Recommendation Based on the foregoing Findings of Fact and Conclusions of Law, it is RECOMMENDED that Respondent enter a Final Order which permits Petitioner to construct the residence on stilts with the following conditions: That silt screens be erected during the actual construction to prevent silt runoff from the construction from reaching Bessey Creek. That a roof drainage system be installed that allows the roof to drain to the upland portion of the project. That Petitioner be required to mitigate for the removal of laurel oaks and red maple by replanting on the property two laurel oaks for each laurel oak removed and by replanting on the property two red maples for each red maple removed. That Petitioner be required to revegetate with native plants the area under the house except for the areas required for the stilts. IT IS FURTHER RECOMMENDED that Respondent deny a permit to construct a garage or extend the existing roadway. IT IS FURTHER RECOMMENDED that Respondent permit Petitioner to retain the existing roadway on the condition that the roadway not be utilized as either a driveway or as a parking area for motor vehicles. DONE AND ENTERED this 12th day of January 1994 in Tallahassee, Leon County, Florida. CLAUDE B. ARRINGTON Hearing Officer Division of Administrative Hearings The DeSoto Building 1230 Apalachee Parkway Tallahassee, Florida 32399-1550 (904) 488-9675 Filed with the Clerk of the Division of Administrative Hearings this 12th day of January 1994.
The Issue The issue is whether the applicant for an Environmental Resource Permit ("ERP"), the City of Deltona ("City" or "Applicant"), has provided reasonable assurance that the system proposed complies with the water quantity, environmental, and water quality criteria of the St. Johns River Water Management District's ("District") ERP regulations set forth in Florida Administrative Code Chapter 40C-4, and the Applicant's Handbook: Management and Storage of Surface Waters (2005).
Findings Of Fact The District is a special taxing district created by Chapter 373, Florida Statutes, charged with the duty to prevent harm to the water resources of the District, and to administer and enforce Chapter 373, Florida Statutes, and the rules promulgated thereunder. The City of Deltona is a municipal government established under the provisions of Chapter 165, Florida Statutes. The Lake Theresa Basin is comprised primarily of a system of interconnected lakes extending from Lake Macy in the City of Lake Helen to the Butler Chain of Lakes (Lake Butler and Lake Doyle). The Lake Theresa Basin is land-locked and does not have a natural outfall to Lake Monroe and the St. Johns River. In 2003, after an extended period of above-normal rainfall in the Deltona area, the lakes within the land-locked Lake Theresa Basin staged to extremely high elevations that resulted in standing water in residential yards, and rendered some septic systems inoperable. Lake levels within the Lake Theresa Basin continued to rise and were in danger of rising above the finished floor elevations of some residences within the basin. On March 25, 2003, the District issued an Emergency Order (F.O.R. No. 2003-38) authorizing the construction and short-term operation of the Lake Doyle and Lake Bethel Emergency Overflow Interconnection. Since wetland and surface water impacts would occur, the Emergency Order required the City of Deltona to obtain an ERP for the system. The project area is 4.1 acres, and the system consists of a variable water structure on the west shore of Lake Doyle connected to a series of pipes, swales, water control structures, and wetland systems which outfall to a finger canal of Lake Bethel, with ultimate discharge to Lake Monroe and the St. Johns River. The first segment of the system extends downstream from the weir structure on the west shore of Lake Doyle via a pipe entrenched in the upland berm of the Sheryl Drive right-of-way. The pipe passes under Doyle Road and through xeric pine-oak uplands to the northeast shore of a large (approximately 15 acres) deepwater marsh. Water flows south through the deepwater marsh where it outfalls through four pipes at Ledford Drive. Two of the four pipes are overflow structures, controlled by canal gates. The pipes at Ledford Drive discharge into a ditch and into a large (greater than 20 acres) shallow bay swamp. The south end of the bay swamp is defined (and somewhat impounded) by a 19th Century railroad grade. Water flows through the bay swamp where it outfalls through five pipes at the railroad grade. Three of the five pipes are overflow structures, controlled by channel boards. The pipes at the railroad grade discharge to a 1500-foot long finger canal that was dug some time during the period 1940-1972 from the north central shore of Lake Bethel. The overflow interconnection system has three locations whereby the system can be shut down: 1) Lake Doyle--a control weir, controlled by three sluice gates; 2) Ledford Drive--two thirty-inch reinforced concrete pipes, controlled by canal gates; and 3) railroad grade--three thirty-inch reinforced concrete pipes, controlled by channel boards (collectively referred to as "Overflow Structures"). The Overflow Structures are designed to carry the discharge of water from Lake Doyle to Lake Bethel. With the Overflow Structures closed the system returns to pre-construction characteristics, meaning there will be no increase or decrease in the quantity or quality of water throughout the path of the system as a result of the project. An unequivocal condition of the permit is that the system would operate with all of the Overflow Structures closed. As an added assurance, the City proposes to place a brick and mortar plug in the Lake Doyle weir structure outfall pipe to prevent any discharge from the weir. The City has submitted to the District preliminary plans for a future phase in which the system would be modified for the purpose of alleviating high water levels within the Lake Theresa Basin when the water level in Lake Doyle rises above an elevation of 24.5 feet. The District shall require a separate permit application to be submitted for such future plans. Petitioner, Barbara Ash, has lived on Lake Theresa for 19 years. Ms. Ash lives upstream from the area of the weir that will be plugged in accordance with the ERP. She does not trust either the City of Deltona to comply with or the District to enforce the conditions of the ERP applied for by the City. Petitioner, Barbara Ash, also served as the qualified representative for Petitioners, Francell Frei, Bernard J. and Virginia Patterson, and Ted and Carol Sullivan. Ms. Ash represented that Ms. Frei has lived on Lake Theresa for 12 years, and both the Pattersons and the Sullivans live on Lake Louise, which is within the area of concern in this proceeding. Petitioner, Diana Bauer, has lived on Lake Theresa since February 2004. She fears that the lake will become too dry if the system is allowed to flow. She also believes the wildlife will be adversely affected if the water levels are too low since many species need a swampy or wet environment to thrive. She fears her property value will decrease as a result of the approval of the ERP. She also does not trust either the City to comply with or the District to enforce the conditions of the ERP. Petitioner, Howard Ehmer, lives two to three hundred yards down Lake Theresa from Ms. Bauer. He is concerned about the lake bed being too dry and attracting people on all terrain vehicles who enjoy driving around the lake bottom. He is concerned about his property value decreasing if the lake bed is dry. Further, when the lake level is too low, people cannot enjoy water skiing, boating, and fishing on Lake Theresa. Petitioner, Phillip Lott, a Florida native, has also owned and lived on property abutting Lake Theresa since 1995. Mr. Lott has a Ph.D. in plant ecology, and M.P.A. in coastal zone studies, an M.B.A. in international business, and a B.S. in environmental resource management and planning. Mr. Lott has been well acquainted with the water levels on Lake Theresa for many years. Based upon his personal observations of the lake systems in the Deltona area over the years, Mr. Lott has seen levels fluctuate greatly based upon periods of heavy and light rainfall. Mr. Lott is concerned that the District will permit the City to open the weir to let water flow through the system and cause flooding in some areas and low water levels in other areas. He fears that the District will allow the water to flow and upset the environmental balance, but he admits that this ERP application is for a closed system that will not allow the water to flow as he fears. Mr. Lott similarly does not trust the City to comply with and the District to enforce the conditions of the ERP. Petitioners, James E. and Alicia M. Peake, who were represented by Steven L. Spratt at hearing as their qualified representative, live on Lake Louise, which is interconnected with the Lake Theresa basin. The Peakes are concerned that if the level of Lake Louise drops below 21 feet, nine inches, they will not be able to use the boat launch ramps on the lake. Petitioner, Steven L. Spratt, also lives on Lake Louise, and is concerned about the water levels becoming so low that he cannot use the boat launch on the lake. He has lived on the lake since 2000, and remembers when the water level was extremely low. He fears that approval of the ERP in this case will result in low levels of water once again. Petitioner, Gloria Benoit, has live on Lake Theresa for two years. She also enjoys watching recreational activities on the lake, and feels that approval of the ERP will devalue her lakefront property. Ms. Benoit appeared at the first day of the hearing, but offered no testimony on her behalf. J. Christy Wilson, Esquire, appeared prior to the final hearing as counsel of record for Petitioners, Steven E. Larimer, Kathleen Larimer, and Helen Rose Farrow. Neither Ms. Wilson nor any of the three Petitioners she represented appeared at any time during the hearing, filed any pleadings seeking to excuse themselves from appearing at the final hearing, or offered any evidence, testimony, pre- or post- hearing submittals. Petitioner, Gary Jensen, did not appear at hearing, did not file any pleadings or papers seeking to be excused from appearing at the final hearing, and did not offer any evidence, testimony, pre- or post-hearing submittals. Both the City and the District recognize that areas downstream from the project site, such as Stone Island and Sanford, have experienced flooding in the past in time of high amounts of rainfall. The system proposed by the City for this ERP will operate with the overflow structures closed and a brick and mortar plug in the outfall pipe to prevent water flow from Lake Doyle to Lake Bethel. So long as the overflow structures are closed, the system will mimic pre-construction flow patterns, with no increase in volume flowing downstream. The District has considered the environment in its proposed approval of the ERP. The area abutting the project is little urbanized and provides good aquatic and emergent marsh habitat. With the exception of the western shore area of the deepwater marsh ("west marsh area"), the bay swamp and remaining deepwater marsh area have good ecological value. In the 1940's, the west marsh area was incorporated into the drainage system of a poultry farm that occupied the site. This area apparently suffered increased nutrient influxes and sedimentation that contributed to a proliferation of floating mats of aquatic plants and organic debris. These tussocks reduced the deepwater marsh's open water and diminished the historical marsh habitat. Water under the tussocks is typically anoxic owing to total shading by tussocks and reduced water circulation. Thick, soft, anaerobic muck has accumulated under the matted vegetation. Exotic shrubs (primrose willow Ludwigia peruvania) and other plants (cattails Typha spp.) dominate the tussocks. The construction of the project, from the 2003 Emergency Order, resulted in adverse impacts to 1.3 acres of wetlands having moderately high- to high ecological value and 0.2 acres of other surface waters. The 0.2 acre impact to other surface waters was to the lake bottom and the shoreline of Lake Doyle where the weir structure was installed. The 0.3 acres of wetland impacts occurred at the upper end of the deepwater marsh where the pipe was installed. The largest wetland impact (1.0 acre) was to the bay swamp. The bay swamp is a shallow body dominated by low hummocks and pools connected inefficiently by shallow braided channels and one acre is filled with a 1-2 foot layer of sediment following swamp channelization. Disturbance plants (e.g., primrose willow, Ludwigia peruvania, and elderberry Sambucus Canadensis) now colonize the sediment plume. Pursuant to the District's elimination and reduction criteria, the applicant must implement practicable design modifications, which would reduce or eliminate adverse impacts to wetlands and other surface waters. A proposed modification, which is not technically capable of being done, is not economically viable, or which adversely affects public safety through endangerment of lives or property is not considered "practicable." The City reduced and/or eliminated the impacts to the lake bottom and shoreline of Lake Doyle and deepwater marsh, to the extent practicable. The impacts were the minimum necessary to install the weir structure and pipe for the system; the weir structure and pipe were carefully installed on the edges of the wetland and surface water systems, resulting in a minimum amount of grading and disturbance. To compensate for the loss of 1.3 acres of wetlands and 0.2 acres of other surface waters, the City proposes to preserve a total of 27.5 acres of wetlands, bay swamp, marsh, and contiguous uplands. Included in this 27.5 acres are 6.4 acres of the west marsh, which are to be restored. The parties stipulated that the mitigation plan would adequately compensate for losses of ecological function (e.g. wildlife habitat and biodiversity, etc.) resulting from the project. Water quality is a concern for the District. Lake Monroe is included on the Florida Department of Environmental Protection's verified list of impaired water bodies for nitrogen, phosphorous, and dissolved oxygen. Water quality data for Lake Monroe indicate the lake has experienced high levels of nitrogen and phosphorous and low levels of dissolved oxygen. Prior to construction of the project, there was no natural outfall from the Lake Theresa Basin to Lake Monroe and therefore no contribution from this basin to nitrogen and phosphorous loadings to Lake Monroe. Lake Colby, Three Island Lakes (a/k/a Lake Sixma), and the Savannah are surface waters within the Lake Theresa Basin for which minimum levels have been adopted pursuant to Florida Administrative Code Chapter 40C-8. The system will operate with the overflow structures closed and a brick and mortar plug in the outfall pipe to prevent water flow from Lake Doyle to Lake Bethel, resulting in no outfall from the Theresa Basin to Lake Monroe. Minimum flows established for surface waters within the Lake Theresa Basin will not be adversely impacted. Under the first part of the secondary impact test, the City must provide reasonable assurance that the secondary impacts from construction, alteration, and intended or reasonable expected use of the project will not adversely affect the functions of adjacent wetlands or surface waters. The system is designed as a low intensity project. As proposed, little activity and maintenance are expected in the project site area. The reasonably expected use of the system will not cause adverse impacts to the functions of the wetlands and other surface waters. None of the wetland areas adjacent to uplands are used by listed species for nesting or denning. In its pre-construction state, the project area did not cause or contribute to state water quality violations. Under the second part of the secondary impact test, the City must provide reasonable assurance that the construction, alteration, and intended or reasonably expected uses of the system will not adversely affect the ecological value of the uplands to aquatic or wetland dependent species for enabling existing nesting or denning by these species. There are no listed threatened or endangered species within the project site area. Under the third part of the secondary impact test, and as part of the public interest test, the District must consider any other relevant activities that are closely linked and causally related to any proposed dredging or filling which will cause impacts to significant historical and archaeological resources. When making this determination, the District is required, by rule, to consult with the Division of Historical Resources. The Division of Historical Resources indicated that no historical or archaeological resources are likely present on the site. No impacts to significant historical and archaeological resources are expected. Under the fourth part of the secondary impact test, the City must demonstrate that certain additional activities and future phases of a project will not result in adverse impacts to the functions of wetlands or water quality violations. The City has submitted to the District preliminary plans for a future phase in which the system would be modified for the purpose of alleviating high water levels within the Lake Theresa Basin when the level in Lake Doyle rises above an elevation of 24.5 feet. Based upon the plans and calculations submitted, the proposed future phase, without additional measures, could result in minor increases in the loadings of nitrogen and phosphorous to Lake Monroe. Lake Monroe is included on the Florida Department of Environmental Protection's verified list of impaired water bodies due to water quality data indicating the lake has experienced high levels of nitrogen and phosphorous, and low levels of dissolved oxygen. Under this potential future phase, there would be an outfall from the Lake Theresa Basin to Lake Monroe. To address the impact on water quality of this potential future phase, the City has submitted a loading reduction plan for nitrogen, phosphorous, and dissolved oxygen. The plan includes compensating treatment to fully offset the potential increased nutrient loadings to Lake Monroe. Specifically, the loading reduction plan includes: Construction and operation of compensating treatment systems to fully offset anticipated increased nutrient loadings to Lake Monroe. Weekly water quality monitoring of the discharge from Lake Doyle for total phosphorous and total nitrogen. A requirement that the overflow structure be closed if the total phosphorous level reaches 0.18 mg/l or higher or the total nitrogen level reaches 1.2 mg/l or higher in any given week and will remain closed until levels fall below those limits. The implementation of these water quality mitigation measures will result in a net improvement of the water quality in Lake Monroe for nitrogen, phosphorous, or dissolved oxygen. The future phase was conceptually evaluated by the District for impacts to wetland functions. The future phase as proposed could result in adverse impacts to wetland functions. Operation of the system with the overflow structures open could impact the bay swamp and deepwater marsh. The City has demonstrated that any adverse impacts could be offset through mitigation. Based upon the information provided by the City and general engineering principles, the system is capable of functioning as proposed. The City of Deltona will be responsible for the operation, maintenance, and repair of the surface waster management system. A local government is an acceptable operation and maintenance entity under District rules. The public interest test has seven criteria. The public interest test requires the District to evaluate only those parts of the project actually located in, on, or over surface waters or wetlands, to determine whether a factor is positive, neutral, or negative, and then to balance these factors against each other. The seven factors are as follows: the public health, safety, or welfare of others; conservation of fish and wildlife and their habitats; fishing, recreational value, and marine productivity; temporary or permanent nature; 5) navigation, water flow, erosion, and shoaling; 6) the current condition and relative value of functions; and 7) historical and archaeological resources. There are no identified environmental hazards or improvements to public health and safety. The District does not consider impacts to property values. To offset any adverse impacts to fish and wildlife and their habitats, the City has proposed mitigation. The areas of the project in, on, or over wetlands do not provide recreational opportunities. Construction and operation of the project located in, on, or over wetlands will be permanent in nature. Construction and operation of the project located in, on, or over wetlands will not cause shoaling, and does not provide navigational opportunities. The mitigation will offset the relative value of functions performed by areas affected by the proposed project. No historical or archaeological resources are likely on the site of the project. The mitigation of the project is located within the same drainage basin as the project and offsets the adverse impacts. The project is not expected to cause unacceptable cumulative impacts.
Recommendation Based upon the Findings of Fact and Conclusions of Law, it is RECOMMENDED that a Final Order be entered granting the City of Deltona's application for an environmental resource permit with the conditions set forth in the Technical Staff Report, and dismissing the Petitions for Formal Administrative Hearing filed by Gary Jensen in Case No. 04-2405, and by Steven E. Larimer, Kathleen Larimer, and Helen Rose Farrow in Case No. 04-3048. DONE AND ENTERED this 27th day of May, 2005, in Tallahassee, Leon County, Florida. S ROBERT S. COHEN Administrative Law Judge Division of Administrative Hearings The DeSoto Building 1230 Apalachee Parkway Tallahassee, Florida 32399-3060 (850) 488-9675 SUNCOM 278-9675 Fax Filing (850) 921-6847 www.doah.state.fl.us Filed with the Clerk of the Division of Administrative Hearings this 27th day of May, 2005. COPIES FURNISHED: George Trovato, Esquire City of Deltona 2345 Providence Boulevard Deltona, Florida 32725 Diana E. Bauer 1324 Tartan Avenue Deltona, Florida 32738 Barbara Ash, Qualified Representative 943 South Dean Circle Deltona, Florida 32738-6801 Phillip Lott 948 North Watt Circle Deltona, Florida Howard Ehmer Nina Ehmer 32738-7919 1081 Anza Court Deltona, Florida 32738 Francell Frei 1080 Peak Circle Deltona, Florida 32738 Bernard T. Patterson Virginia T. Patterson 2518 Sheffield Drive Deltona, Florida 32738 Kealey A. West, Esquire St. Johns River Water Management District 4049 Reid Street Palatka, Florida 32177 J. Christy Wilson, Esquire Wilson, Garber & Small, P.A. 437 North Magnolia Avenue Orlando, Florida 32801 Gloria Benoit 1300 Tartan Avenue Deltona, Florida 32738 Gary Jensen 1298 Tartan Avenue Deltona, Florida 32738 James E. Peake Alicia M. Peake 2442 Weatherford Drive Deltona, Florida 32738 Steven L. Spratt 2492 Weatherford Drive Deltona, Florida 32738 Ted Sullivan 1489 Timbercrest Drive Deltona, Florida 32738 Kirby Green, Executive Director St. Johns River Water Management District 4049 Reid Street Palatka, Florida 32177
The Issue The issue in this case is whether Seacoast Utility Authority's challenge to the South Florida Water Management District's proposed issuance of a water use permit to PGA National Golf Club and Sports Center, Ltd. in a critical water supply area should be upheld. As discussed below, the parties have stipulated that, in deciding to issue the permit, the South Florida Water Management District has not evaluated or considered whether the use of reclaimed water was either economically, environmentally or technically infeasible.
Findings Of Fact Based upon the evidence adduced at the hearing and the entire record in this proceeding, the following findings of fact are made: Seacoast is a publicly owned water and sewer utility which operates a wastewater treatment facility in Palm Beach County, Florida. Seacoast's service area is bounded on the south by Riviera Beach and on the north by the Town of Jupiter. Seacoast operates four treatment plants: two water plants and two wastewater plants. Seacoast's regional wastewater facility currently generates approximately six (6) million gallons per day ("MGD") of reclaimed water and is permitted by the Florida Department of Environmental Protection ("DEP") as an eight (8) MGD wastewater treatment plant. As discussed in more detail in the Conclusions of Law below, the Florida Legislature and DEP have sought to encourage the reuse of reclaimed water. This policy is one of the many sometimes competing goals that are supposed to be taken into account in the water use permitting process. Until a few years ago, the treated effluent from one of Seacoast's wastewater plants was directly discharged to nearby surfacewater. During the last four years, Seacoast installed a pumping station and five miles worth of transmission lines to deliver all of its treated effluent to its regional wastewater facility. Seacoast claims that these efforts were prompted by its interpretation of changing regulations and a perceived regulatory preference for reuse of water.1 Although Seacoast claims that there has been a change in regulatory emphasis in favor of reuse of reclaimed water, Seacoast is not under a mandate from any court or agency to sell or utilize any specific amount of reclaimed water. It does appear that a deep injection well used by Seacoast for disposal of wastewater is not or was not operating as designed. Seacoast was apparently obligated to construct reclaimed water facilities at its wastewater treatment plant as part of its permit from DEP for the injection well. There was no requirement that the reclaimed water be sold or otherwise utilized. The intended primary disposal for Seacoast's reclaimed water is reuse.2 Seacoast's wastewater treatment plant provides irrigation quality reclaimed water. Seacoast tries to sell the reclaimed water for irrigation use in an effort to recoup the costs incurred in constructing the facilities necessary to reclaim the water. Backup disposal is achieved through injection down a 3300 feet deep injection well into the boulder zone. Once the reclaimed water is injected down the well, it is unavailable for reuse. The evidence suggests that there are other possible utilizations available for Seacoast's reclaimed water including sale to another utility and/or backup recharge to preserve wetlands during periods of high pumpage. For example, Seacoast is apparently in the process of applying for the necessary permits to utilize a portion of its reclaimed water to prevent harm to wetlands adjacent to its Hood Road Well Field by constructing an hydraulic barrier. At all times pertinent to this proceeding, only approximately 1.2 MGD of the reclaimed water generated by Seacoast was being reused. The remaining approximately 5 MGD was disposed of through the injection well. PGA owns and operates three (3) golf courses in Palm Beach County within Seacoast's service area. PGA's golf courses are located within an area that has been designated by the District as a Critical Water Supply Problem Area. Critical Water Supply Problems Areas are geographical regions where the available water supply due to the potential for saltwater intrusion, wetland impacts, or impacts to existing legal uses, is predicted not to meet water demands that are projected during the next 20 years. See, Chapter 40E-23, Florida Administrative Code. The use of reclaimed water is not mandated in such areas. However, the District's Rules seek to insure the optimal utilization of alternative sources of water in such areas to minimize the potential harm to water resources. It is not clear from the evidence presented in this case when PGA first obtained the Permit from the District for golf course irrigation. The Permit allows PGA to use the groundwater table as the source of water for its irrigation. Before its expiration, PGA timely sought renewal of the Permit. On April 12, 1994, the District staff recommended renewal of PGA's Permit. The staff recommendation would allow PGA to continue using the groundwater table as the source of its water. The recommendation did not contain a requirement for PGA to use any reclaimed water as part of its golf course irrigation system. Seacoast became aware of PGA's application to renew its Permit through a routine review of all water use permit applications made to the District by "potential reclaimed water users in [its] service area." Seacoast filed a Petition for Formal Administrative Hearing challenging the District staff's recommendation to renew PGA's Permit. In its Petition, Seacoast alleged that its substantial interests would be affected by the renewal of the Permit because Seacoast's ability to achieve the State of Florida's goals of conservation and environmental protection depends upon PGA, and other similar country clubs, being required to consume reclaimed water. Seacoast contends that the staff recommendation immediately eliminates a major potential consumer of Seacoast's reclaimed water which purportedly impairs Seacoast's ability to meet state objectives for reuse of reclaimed water and results in the undesirable continued disposal of reclaimed water via deep well injection. In connection with its challenge to the proposed renewal of PGA's Permit, Seacoast has stipulated that PGA's proposed withdrawals from the groundwater table would not cause harm to the water resources of the District. Seacoast also admits that it has never evaluated whether it would be environmentally injured by PGA's withdrawals from the groundwater table and/or whether the proposed use by PGA is wasteful. The District does not currently have any goals for the utilization of reclaimed water on a regional basis. Instead, the District oversight of the utilization of reclaimed water is done on a permit by permit basis. As a general policy, the District will not accept a water use permit application in an area of critical water shortage unless a reuse feasibility determination is included. The District's rules do not currently contain any guidelines as to how the determination of feasibility is to be made, nor are there any criteria for reviewing an applicant's determination of feasibility. As discussed below, the District does not even consider the applicant's reuse feasibility determination unless the proposed withdrawal is projected to result in harm to the resources of the District. Even when harm to a resource is projected, the District accepts an applicant's feasibility determination regarding the use of reclaimed water without question or analysis. For the other consumptive use criteria set forth in Rule 40E-2.301, the District independently evaluates the applicant's conclusions to confirm that they are reasonable. In other words, the District treats reclaimed water as an alternative source of water in the event that an applicant's proposed water use is projected to cause harm to the water resources of the District. If no harm is expected to occur to water resources as a result of a proposed use, the District does not review the applicant's determination of whether or not to use reclaimed water. If harm is projected, the applicant is required to look at alternatives like water conservation or utilization of water sources other than those proposed (such as reclaimed water). The applicant is free to select any alternative that mitigates the harm. Thus, even in a Critical Water Supply Area, an applicant can mitigate concerns about harm to the resource without utilizing reclaimed water. In sum, under the District's current procedures, the use of reclaimed water is never required. It is simply one alternative an applicant can utilize to offset or mitigate projected harm to water resources (such as saltwater intrusion, contamination, wetland drawdowns or existing legal use impacts) from a proposed withdrawal. Even when the District staff concludes that an applicant's proposed use will result in harm to water resources, the staff does not critically review the applicant's determination of whether the use of reclaimed water is economically, environmentally, or technically infeasible. With respect to PGA's Permit, the District staff concluded that no harm to the resource was predicted as a result of PGA's proposed use. Thus, PGA's determination not to use reclaimed water was not evaluated or even considered. The District explains that its implementation of the permitting program is based upon its interpretation that its primary responsibility is to prevent harm to water resources. The District points out that there are a number of factors to be considered in utilizing reclaimed water. These factors include, but are not limited to, the cost of the reclaimed water, the cost of retrofitting an irrigation system, the long-term availability of the reclaimed supply and the availability of a back-up supply.
Recommendation Based upon the foregoing Findings of Fact and Conclusions of Law, it is RECOMMENDED that the South Florida Water Management District enter a Final Order dismissing the Petition filed by Seacoast challenging the renewal of Permit Number 50-00617-W to PGA for golf course irrigation. DONE AND ENTERED in Tallahassee, Leon County, Florida, this 6th day of February 1995. J. STEPHEN MENTON Hearing Officer Division of Administrative Hearings The DeSoto Building 1230 Apalachee Parkway Tallahassee, Florida 32399-1550 (904) 488-9675 Filed with the Clerk of the Division of Administrative Hearings this 6th day of February 1995.
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 The issue is whether the Southwest Florida Water Management District's (District's) proposed construction of a temporary floating weed barrier across the mouth of the canal exiting to the southwest side of Lake Hancock in Polk County, Florida, is exempt from regulatory review under Section 373.406(6), Florida Statutes.
Findings Of Fact Based upon all of the evidence, the following findings of fact are determined: Background This proceeding involves a request by the District for authorization to construct a temporary floating weed barrier across the mouth of the canal exiting the southwest side of the Lake in Polk County, Florida (County). After reviewing the request, and based on its determination that the project would "have only minimal or insignificant individual or cumulative adverse impacts on the water resources of the State," on September 27, 2002, the Department concluded that the project qualified for an exemption from regulatory review under Section 373.406(6), Florida Statutes. The Department also authorized the District to use state-owned submerged lands, if applicable, for the construction of the project, and it found that the project was in compliance with the SPGP program and thus required no further permitting from the United States Army Corps of Engineers (Corps of Engineers). Even if the Department had not considered the project to be exempt, it concluded that it had sufficient information and assurances from the District to grant a Noticed General Environmental Resource Permit (ERP) authorizing the requested activity. On December 2, 2002, Petitioner, Bruce Lahey, who has resided and owned property on the southwest side of the Lake for 15 years and regularly uses the Lake for fishing and recreational purposes, filed a Petition for Administrative Hearing (Petition) challenging the proposed agency action. In his Petition, as later clarified and narrowed in the parties' Joint Pre-Hearing Stipulation, Mr. Lahey contends that a weed barrier is no longer necessary since there has not been a weed problem in the Lake since late 2002; that the placement of a weed barrier will make access to and from the Lake more difficult and create a safety hazard; and that in the event a problem arises again, the more desirable options for removing the weeds are "a 'cookie-cutter,' mechanical harvester, or the spraying of [the] tussocks," rather than erecting a barrier. Finally, Mr. Lahey contends that as a matter of law, Section 369.20, Florida Statutes, bars the construction of a barrier. He has not challenged the Department's authorization for the District to use state-owned submerged lands or its determination that the project complies with the SPGP program, and therefore those aspects of the proposed agency action are not in issue. Respondents do not dispute that Mr. Lahey has standing to bring this action. The Lake and Control Structure The Lake is an approximately 4,500-acre Class III waterbody located east of Highway 98 and Highland City, southeast of Lakeland, and just northeast of the City of Bartow (Bartow). It receives drainage from a significant portion of the County, including three streams and runoff from a surrounding 131-square mile watershed. Waters discharge from the Lake to Saddle Creek (the canal), which exits at the southwest end of the Lake and runs in a southerly direction for around a mile and a half until it merges with the Peace Creek, where the two then become the Peace River. At the confluence of the canal and Peace Creek, the waters flow through a broad, flat floodplain. Water moves slowly through this area, which can affect the ability of the Lake to discharge, especially during flood conditions. Like the Lake and canal, the Peace Creek also has a significant contributing basin. The canal contains a District-owned and operated water control structure known as Water Control Structure P-11 (the control structure) consisting of two twenty-foot radial arm gates that are raised when necessary to manage the water levels on the Lake and prevent the flooding of lakefront property. The control structure is approximately 3,000 feet or so south of the Lake and is the only control structure regulating water levels for the Lake. The gates are designed to discharge at a flow level of 1,100 cubic feet per second (cfs). The invert elevation of the control structure is 91.7 feet and the crest elevation is 98.7 feet. Flows from the Lake will exceed 1,100 cfs when the water levels are higher than the crest elevation of the structure. At this point, water flows over the structure’s weirs and flood control is no longer provided. The maximum desirable water elevation level for the Lake is 98.5 feet above mean sea level (msl). Typically, the District begins to operate, or open, the control structure when the Lake's water elevation reaches 98.25 feet msl. A water level of 99.0 feet msl is considered minimum flood level (or high guidance level). The low management water elevation (low guidance level) is 96.0 feet msl. These established water levels have been maintained at the Lake since approximately 1981. The District seeks to hold the water level of the Lake close to the maximum desirable level, and typically tries to hold the water level at 98.25 feet msl, which is slightly below the maximum desirable level of 98.5 feet msl, to allow storage of water and some response time. The control structure is intended primarily to be a water conservation structure that regulates the Lake's water levels to benefit the water resources, to include the Lake and the Peace River. In managing the Lake's levels, the District balances conservation of the water resource and public safety/flooding concerns. The Lake's water level elevations are monitored through the District’s Supervisory Control and Data Acquisition System (SCADA), which measures the water level and transmits hourly data to the District offices via satellite. SCADA monitors are located immediately upstream and downstream of the control structure. Since the tussock blockage events in the summer and fall of 2002, described more fully below, the District has installed an additional SCADA monitor on the north end of the Lake so that water levels in the Lake and canal can be compared. The Lake does not have direct public access or a public boat ramp and is not easily accessible. In addition, in the canal, there is only one unimproved location upstream from the control structure where boats can be placed in the water and gain access to the Lake. That portion of the canal which lies between the Lake and the control structure has not always been open to boat access. In the 1980’s, a floating weed barrier extended across the canal approximately 1,000 feet upstream from the current control structure, which blocked the canal and boat access. This floating weed barrier was installed primarily to address problems with water hyacinths that would float down the canal and interfere with the control structure. This floating barrier gave way sometime in the 1990’s. An earlier control structure also used to exist in this area, which blocked canal access. Navigation of the canal is limited due to the existence of the control structure and a number of other blockages further downstream, including a low bridge where old Highway 17 crosses the canal. Thus, boats coming from the Lake cannot navigate down the canal any further than the control structure, or slightly more than one-half mile, without taking the boat out of the water. Between 1999 and 2001, the District experienced one of the most severe droughts on record. During this time, the Lake went dry except for some isolated pools of water. Because of these conditions, a significant amount of wetland or aquatic vegetation began to grow on the exposed bottom of the Lake. The Lake historically did not support much plant growth, due to its eutrophic condition, poor water quality, and gelatinous mucky lake bottom. The types of vegetation currently existing in the Lake include cattails, pickerelweed, duck potato, and primrose willow. Following the return of summer rains and El Nino conditions in 2002, the Lake rebounded to within normal water levels. Because of the return of water in the Lake, the buoyant pressure of the water combined with the flaccid nature of the mucky lake bottom caused significant portions of vegetation to become uprooted, which formed an extensive amount of tussocks. Tussocks are floating mats of uprooted aquatic vegetation. They contain plant and organic material accumulated around the plant roots, can range from a few feet across to one hundred feet across or larger, and can reach a height of more than four feet. Once tussocks form, they move about the Lake by wind and water currents. The amount of vegetation currently existing in the Lake exceeds historic levels. At the present time, the District estimates that approximately 2,000 acres of the Lake are covered with tussocks, and that due to the flaccid nature of the lake bottom, the tussocks are susceptible to becoming uprooted through fluctuating water levels, wind, and wave action. Therefore, there is a strong potential that much of the currently rooted vegetation will form tussocks. Tussocks first impacted the District’s ability to operate the control structure in July 2002. During this event, the canal became partially filled with tussocks. Because the blockage occurred during the rainy and hurricane seasons, the District undertook efforts to clear the canal of tussocks. District staff used mechanical equipment commonly called a cookie cutter to break up the tussocks and flush them downstream through the control structure. During this tussock event, the Lake's water levels rose briefly above the maximum desirable level of 98.5 feet msl and then fell back to within normal elevations. In late August 2002, approximately three weeks after the first tussock blockage event, a number of homeowners on the Lake, including Petitioner's wife, contacted District staff to advise that the water level of the Lake was rising and flooding their yards. A rise in water levels did not register on the District’s water level monitoring SCADA system. Visual observation of the Lake did reveal, however, that there was a significant difference between the water levels being experienced on the Lake and the water levels reported at the control structure via the SCADA system. During this tussock event, masses of tussocks had completely filled the 3,000-foot length of the canal all the way to the control structure and were jamming against the control structure gates. Tussocks had also formed a vegetation dam approximately 900 to 1,400 feet north of the control structure where they compacted and became lodged on the bottom of the canal, significantly impeding the flow of water. During this event, flows out of the Lake were significantly diminished to a fraction of what they should have been. The tussock dam caused the Lake's level to rise above the minimum flood elevation of 99.0 feet and flood Petitioner's yard. There was an approximately one to one and one-half foot difference in the water levels in the Lake and in the canal. In response to this disparity, the District installed a third water level elevation monitor at the northern end of the Lake, so that it can monitor any differences in water elevations between the Lake and the canal and be alerted in the event that a blockage occurs in the canal. To eliminate the tussock blockage and restore flow through the control structure, the District had to employ mechanical means to break up and remove the tussocks. At the control structure, a trac-hoe was initially used in an attempt to force tussocks through the control structure, as tussocks would not flow through the structure unassisted. A cookie cutter was also employed, but it became sucked into the control structure and was damaged and had to be removed with a crane and repaired. The cookie cutter proved ineffectual in addressing the tussock blockage problem. If the canal were to again become clogged with tussocks, any resulting blockage of flow from the Lake would cause water levels to rise, which would endanger public safety and welfare. Prior to the tussock blockages experienced in the summer and fall of 2002, problems with tussocks had never been experienced at the Lake. The magnitude of the tussock formation on the Lake is unique and has not been experienced elsewhere in the District. In 2002, the Department expended over $46,000.00 in contracting for mechanical equipment and for spraying herbicide on tussocks to respond to the tussock buildup on the Lake. Since their formation after the summer of 2002, tussocks have blocked Petitioner's access to his dock on several occasions, thereby preventing him from being able to take his boat out into the Lake or to return to the dock once out on the Lake. The potential for similar blockages to occur remains, regardless of whether a floating weed barrier is erected as proposed. The direction of the winds is a major factor in determining where and how many tussocks will stack up in front of anyone’s property along the Lake. Access to the canal could become blocked with tussocks at any time, depending upon how the wind blows. Breaking up tussock blockages and flushing tussocks through the control structure does not eliminate water resource problems for the District. Tussocks that are pushed through the control structure cause downstream problems requiring the District to expend resources to push the tussocks through and under low downstream bridges crossing the canal, as well as break up tussock blockages that form in downstream waters. In January 2003, tussocks again accumulated at the control structure in such volume as to require assistance in flushing through the control structure. As a result of the large volume of tussocks pushed through the control structure, a tussock blockage occurred at a downstream bridge crossing, for which the District had to use mechanical equipment to restore flow. During March 2003, tussocks flushed through the control structure created a jam downstream on the Peace River. The tussocks were jammed up in a bend in the river and were blocking navigational access to the river. An El Nino weather cycle is currently being experienced. Water levels, including the Lake's water level, are already at their maximum and the ground is saturated. Localized flooding events have occurred. A very active summer rainy season is anticipated, which will mean significant flood control operations for the District. As the summer season approaches, the District must keep the control structure open and operational, which requires that the canal be kept open and flowing. A floating weed barrier at the entrance to the canal would keep tussocks from clogging the canal and prevent problems affecting operation of the control structure, downstream tussock blockages, and possible flooding. The Project To address the problem of tussocks entering the canal and causing blockages or possible flooding, on September 11, 2002, the District applied to the Department for a Noticed General ERP under Rule 62-341.475(1)(a), Florida Administrative Code, to authorize the construction of a floating weed barrier at the entrance to the canal. On September 27, 2002, the Department issued its notice of intent to authorize the requested activity. The proposed barrier will be constructed in two sections arranged at approximately 90-degree angles to each other, with a twenty-foot opening between the sections to allow boat access to the canal. A schematic drawing of the barriers is found in District Exhibit 5 received in evidence. As originally proposed, the barrier would consist of a total of sixteen nine-inch diameter pilings driven twenty-one feet apart, with twenty-foot sections of floating foam-filled polyvinyl chloride pipe (pvc) connected to the pilings. Pilings will be marked with reflective tape and five of the pilings will have three-foot diamond-shaped reflective danger signs reading "DANGER PILE/FLOAT BARRIER" placed on their upstream and downstream sides. The pilings are twenty-five feet in length and will extend above the Lake's water level approximately twelve to fourteen feet. Since the District's submittal of the application and the Department's authorization notice, the District has located commercially manufactured floating booms, called "Tuffbooms," that, if authorized, will be installed in lieu of the foam-filled pvc pipes. Use of these booms reduces the number of pilings needed from sixteen to eight, and their bright orange color is more visible than pvc piping. All other aspects of the proposed activity remain the same. The change in material to be used in the construction of the proposed floating barrier does not present any water quality issues, nor does it affect the Department's determination that the proposed activity will have minimal or insignificant adverse impacts on the water resources. The staggered layout of the proposed floating weed barrier is intended to keep tussocks in the Lake, where they can remain subject to the winds, while providing boat access to the canal in such a manner that is more difficult for tussocks to enter the canal. The Department's Exemption Process The Department's Tampa District Office routinely approves around 800 projects each year under various exemptions authorized by statute or rule. One type of exemption is found in Section 373.406(6), Florida Statutes, referred to as the de minimus exemption, which allows the Department to exempt from regulation those activities that are determined will have only minimal or insignificant individual or cumulative adverse impacts on the water resources of the District. The Department is authorized to make this determination on a case-by-case basis. In determining whether an activity qualifies for a de minimus exemption from permitting, the Department looks for parallels to other specific statutory or rule exemptions and analyzes the proposed activity similarly in terms of its scope, construction methods, potential to create water quality impacts or impediments to navigation, and other factors, because these recognized exemptions are also deemed to have minimal or insignificant impacts to the water resources. There is no specific exemption for a floating weed barrier as proposed by the District, but the Department considers this type of project to be similar in scope and potential impacts to other specific activities that have been determined to have minimal or insignificant adverse impacts to the water resources, such as docks and other piling-supported structures, navigational aids, and buoy systems. In assessing whether a project is appropriate for the de minimus exemption, the Department also looks to the criteria for Noticed General ERPs for guidance in determining whether a proposed project will have minimal or insignificant adverse individual or cumulative impacts upon the water resources. Under Section 373.406(5), Florida Statutes, the Department may by rule establish general permits for activities that have, either singularly or cumulatively, minimal environmental impact. Chapter 62-341, Florida Administrative Code, sets forth the Noticed General ERPs established by the Department. Department Rule 62-341.475(1)(a), Florida Administrative Code (as does District Rule 40D-400.475(1)(a), Florida Administrative Code), allows noticed general permits for piling supported structures of less than 1,000 square feet over wetlands or other surface waters, which are not designated Outstanding Florida Waters. To qualify for a noticed general permit for such activity, an applicant must provide reasonable assurance that the proposed structure: Does not significantly impede navigation and does not entail the construction of a structure for the launching or mooring of a boat when navigational access to the structure does not currently exist; Does not cause a violation of state water quality standards; Does not impede the conveyance of a stream, river or other watercourse in a manner that would increase off-site flooding; Does not adversely impact aquatic or wetland dependent listed species; Does not cause the drainage of wetlands; and Is not located in, on or over a coral community, macro-marine algae or submerged grassbed community. Will the Project Impact Water Resources? The District’s proposed floating weed barrier will involve less than 7.1 square feet of impact to the water resources, which is significantly less impact in square footage to the water resources than is allowed by Rule 62- 341.475(1)(a), Florida Administrative Code, or occurs with other specified exempt projects. Best management practices will be used in the erection of the pilings and in the construction of the barriers. Pilings will be jetted into the lake bottom without need for any dredging or lake bottom removal. Installation of a floating weed barrier will not result in any significant detriment to existing conditions in the Lake or the canal. Installation of the proposed floating weed barrier will benefit the public interest and the water resources by allowing unimpeded operation of the control structure without risk of tussocks causing blockages and flooding. Installation of the proposed floating weed barrier will not have significant adverse impacts on fishing, boating, or recreational use of the Lake or canal. A blockage of the canal entrance by tussocks, or a tussock jam anywhere on the Lake, could occur under present conditions, and similar blockages have already occurred. The potential for tussocks to block the opening between the sections of the floating weed barrier is considered remote and of temporary duration, due to the potential for shifting winds. The District’s proposed floating weed barrier is a reasonable means of addressing the continuing potential for tussocks to interfere with operation of the control structure. Use of mechanical equipment such as a cookie cutter or harvester would not be an effective or economical means of addressing tussock blockages in the canal or preventing their occurrence and possible interference with operation of the control structure. Pushing tussocks through the control structure would not be an effective means of addressing the potential for tussocks to cause blockages and possible flooding. Merely pushing the material through the control structure moves the potential blockage problem downstream and does not alleviate the potential for tussocks to cause adverse impacts to the water resources of the District. Spraying tussocks with herbicides would not be an effective means of addressing tussock blockages due to the fact that, once treated, tussocks can take weeks to die and fall to the lake bottom. Floating tussocks are and will continue to be treated with herbicide sprays when found in the Lake to reduce the amount of tussocks. However, once tussocks enter the canal, spraying serves little benefit in preventing tussocks from causing blockages or other problems. Tussocks originate in the Lake and not in the canal. Tussocks in the Lake have had and likely will continue to have an impact on boating and recreational use of the Lake and canal, as evidenced by tussock blockages to Petitioner's dock. By confining the tussocks to the Lake, the potential for tussocks to impact boating and recreational use of the Lake will remain the same as current conditions, but the potential for tussocks to affect operation of the control structure and contribute to Lake flooding will be eliminated. Petitioner contends that the proposed floating weed barrier will impede navigation, either by itself or as a result of tussocks piling up in front of the barrier. The proposed barrier will be marked and visible through reflective tape and signage. The barrier does not create a navigational hazard and is not a significant impediment to access to the canal. Constructed in two sections, the barrier provides an opening that allows boat access to the canal. As noted above, the likelihood of tussocks piling up at the barrier and blocking the opening between the barrier sections is considered remote and temporary. Based upon the information provided by the District, the proposed floating weed barrier will not significantly impede navigation; will not cause a violation of state water quality standards; will not impede the conveyance of a stream, river, or other water course in a manner that would increase off-site flooding; will not adversely impact aquatic or wetland dependent listed species; and will not cause the drainage of wetlands. There is no evidence that the proposed activity is located in, on, or over a coral community, macro-marine algae, or submerged grassbed community or that it entails the construction of a structure for the launching or mooring of a boat for which navigational access does not currently exist. The proposed activity would have only minimal or insignificant individual or cumulative adverse impacts on the water resources of the District. As an activity that has minimal or insignificant adverse impacts on the water resources of the District, either individually or cumulatively, the District’s project qualifies for an exemption pursuant to Section 373.406(6), Florida Statutes, as well as a Noticed General ERP under Rule 62- 341.475(1)(a), Florida Administrative Code. The Department's exemption determination authorized the District’s floating weed barrier for one year, presumably so that the effectiveness of the barriers can be evaluated during that period of time. If they are effective, an extension or renewal of the authorization will be sought. If the tussocks problem becomes less acute, or the barriers do not achieve the desired purpose, they will be taken down. In contrast, Noticed General ERPs authorize a particular activity for five years. Other Contentions by Petitioner Petitioner has also contended that the proposed activity may violate a condition of the District's Corps of Engineers general permit by interfering with general navigation. As found earlier, however, the more credible evidence indicates otherwise. Moreover, it is presumed that this issue was considered by the Corps of Engineers prior to its approval of the project. In any event, that matter should be raised with the Corps of Engineers, and not with the Department. Finally, Mr. Lahey contends that since at least late 2002, the Lake has been free of a tussocks problem and therefore barriers are no longer needed. As noted above, however, blockages have occurred at the control structure and in the Peace River as recently as January and March 2003, and such blockages were the direct result of tussocks which originated in the Lake. Given the likelihood of a very active summer rainy season, it is essential that the canal be kept open so that the District can properly manage and control the water resources.
Recommendation Based on the foregoing Findings of Fact and Conclusions of Law, it is RECOMMENDED that the Department of Environmental Protection issue a final order determining that the Southwest Florida Water Management District's proposed project qualifies for an exemption under Section 373.406(6), Florida Statutes; that authorization to use state-owned lands be given; and that the project is in compliance with the State Programmatic General Permit program. DONE AND ENTERED this _____ day of May, 2003, in Tallahassee, Leon County, Florida. ___________________________________ DONALD R. ALEXANDER 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 _____ day of May, 2003. COPIES FURNISHED: Kathy C. Carter, Agency Clerk Department of Environmental Protection 3900 Commonwealth Boulevard Mail Station 35 Tallahassee, Florida 32399-3000 Bruce Lahey 5280 Waterwood Drive Bartow, Florida 33830-9766 Martha A. Moore, Esquire Southwest Florida Water Management District 2379 Broad Street Brooksville, Florida 34604-6899 Doreen Jane Irwin, Esquire Department of Environmental Protection 3900 Commonwealth Boulevard Mail Station 35 Tallahassee, Florida 32399-3000 Teri L. Donaldson, General Counsel Department of Environmental Protection 3900 Commonwealth Boulevard Mail Station 35 Tallahassee, Florida 32399-3000
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
Findings Of Fact The City of Boynton Beach, Florida, filed application number 24859 with the South Florida Water Management District (formerly the Central and Southern Florida Flood Control District) for an annual allocation of 3.89 billion gallons (10.7 mgd) for a public water supply system for its service area of 18,351 acres for a period of ten years. The application was dated February 26, 1976. A supplemental engineering report was submitted on April 26, 1977, and a water withdrawal management plan on August 18, 1977. The delay in completing the documentation for the application was due to the applicant's completion of a test well program and hydrogeological evaluation of the aquifer capability of the 34 acre tract known as the "Jarvis Property," the proposed site of eight future wells. (Composite Exhibit 1) The existing raw water supply system for Boynton Beach consists of four separate well fields, comprising a total of 14 wells with a total rated capacity of 9700 gpm. Wells 1 through 5 were built during the period 1946-1958. Wells 6 through 11 were built from 1961-1973, and wells 12 through 14 were completed in 1976. The application seeks approval for eight additional wells, numbers 16 through 22 to be located on the "Jarvis Tract." It is proposed that wells numbers 15 and 16 be built immediately upon approval of the application and that the remaining six new wells be constructed at a rate of two per year through 1982, subject to demand. The city presently operates a water treatment plant with a treatment capacity of 8 mgd and is expanding that facility to a capacity of 16 mgd. It is anticipated that this expansion and the new well field will meet projected water demands in the service area through 1987. (Testimony of Swan, Composite Exhibit 1, Exhibit 2) The Applicant's present wells tap the shallow aquifer overlying the Hawthorne formation. These wells range in depths from 54 to 115 feet below ground surface. The planned wells will reach 180 to 230 foot depths. The shallow aquifer is largely recharged by local precipitation and a surface canal system. There are two major canals located near the Applicant's well fields in distances ranging from directly adjacent to approximately one mile. Canal E-4 is located on the western boundary of the proposed Jarvis well field which would provide direct recharge in the area. Withdrawal of water from wells number 1-5 had to be curtailed due to a landward movement of the freshwater/saltwater interface. The wells at present are used for emergency standby purposes only. After wells number 12-14 were put into operation, it was discovered that the withdrawals affected residential shallow irrigation wells nearby. Three of the residents have filed objections to the application for this reason. This problem will be resolved by the development of the Jarvis well field which will allow curtailment of pumpage from wells numbers 12-14. Well number 14 presently is not in operation due to an unknown polluted condition. The curtailment of use of wells 1-5 will aid in controlling any salt water intrusion. A U.S. Geological Survey saltwater monitoring well in the area indicates that there has not been any net landward movement of the saltwater/freshwater interface in the shallow aquifer since 1973. The Applicant's water withdrawal management plan which will substantially reduce the pumpage from wells 6-14 will also reduce the threat of saltwater intrusion by maintaining the aquifer water levels in the area at a higher elevation. (Exhibits 2-4, 6, Testimony of Gresh, Higgins, Kiebler) The City of Boynton Beach currently has a population of 51,000 and it is projected that by 1987 the population will reach 71,000 which is the maximum limit of its water treatment facilities. The city plans to build a new treatment plant and well field in the western portion of the area when the capacity of the current and proposed well fields are reached. It would be uneconomic to place the currently proposed well field in that area due to the requirement of building a raw water line for a distance of approximately four miles. (Composite Exhibit 1, Testimony of Cessna) The South Florida Water Management District staff recommends that the application be approved in its entirety for a period of ten years, subject to 18 special conditions which are acceptable to the Applicant. The district staff concluded that sufficient water is available in the Applicant's area to support the 1987 level of withdrawals and that the proposed consumption rate reflects a reasonable use of water. The staff further found that there would be a minimal impact on existing users in the area and that westward lateral intrusion of saltwater from the coastline will be reduced. (Exhibit 2-3, Testimony of Higgins)
Recommendation That the application be approved and that a water use permit be issued to the Applicant pursuant to application number 24859 for a ten year allocation of 3.8 billion gallons, subject to the special conditions recommended by the South Florida Water Management District staff. DONE and ENTERED this 21st day of February, 1978, in Tallahassee, Florida. COPIES FURNISHED: Gene Moore, Esquire City Attorney City of Boynton Beach Post Office Box 310 Boynton Beach, Florida 33425 THOMAS C. OLDHAM Hearing Officer Division of Administrative Hearings Room 530, Carlton Building Tallahassee, Florida 32304 (904) 488-9675 Steve Walker, Esquire 3301 Gun Club Road Post Office Box 3858 West Palm Beach, Florida 33402
The Issue Whether a consumptive use permit for the quantities of water requested in the application should be granted.
Findings Of Fact Application 7500137 seeks an average daily withdrawal of 2.4 million gallons of water with maximum daily withdrawal not more than 2.88 million gallons from an existing well in order to process phosphate and reclaim land. This is an existing use for mining operations located southwest of Lakeland, Florida, on land consisting of 1531 acres. Notice was published in a newspaper of general circulation, to wit: The Lakeland Ledger, on November 11 & 18, 1975, pursuant to Section 373.146, Florida Statutes. The application and affidavit of publication were admitted into evidence without objection as Composite Exhibit 1, together with correspondence from James R. Brown, Vice President, Dagus Engineers, Inc., dated November 19, 1975 to the Southwest Florida Water Management District. No objections were received by the Water Management District as to the application. Mr. George Szell, hydrologist of the Water Management District testified that the application met the conditions for a consumptive use permit as set forth in Chapter 16J-2.11, Florida Administrative Code, except that the quantity of water requested to be withdrawn is 41.06 per cent over the maximum average daily withdrawal permitted under the water crop theory as set forth in Section 16J-2.11(3), F.A.C. However, the Water Management District witness recommended waiver of that provision since the mining operations will be concluded in several years and thereafter the water table and hydrologic conditions will return to normal. The Water District staff recommended approval of the application with the condition that a meter be installed on the well and that the applicant be required to take monthly readings thereof and submit quarterly reports of the readings to the District. The applicant's representative agreed to these conditions at the hearing.
Recommendation It is recommended that Application No. 7500137 submitted by Poseidon Mines, Inc., for a consumptive water use permit be granted on the condition that a meter be installed on the applicant's well and that monthly readings be taken and submitted quarterly by the applicant to the Southwest Florida Water Management District. It is further recommended that the Board of Governors of the Southwest Florida Water Management District, pursuant to Rule 16J-2.11(5), for good cause, grant an exception to the provisions of Rule 16J-2.11(3), as being consistent with the public interest. DONE and ENTERED this 19th day of January, 1976, in Tallahassee, Florida. THOMAS C. OLDHAM Division of Administrative Hearings Room 530, Carlton Building Tallahassee, Florida 32304 (904) 488-9675 COPIES FURNISHED: J.T. Ahern, Staff Attorney Southwest Florida Water Management District P.O. Box 457 Brooksville, Florida 33512 Poseidon Mines, Inc. P.O. Box 5172 Bartow, Florida
