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ROSE ANN DE VITO vs JOHN FALKNER, CHRISTOPHER FALKNER, AND SOUTHWEST FLORIDA WATER MANAGEMENT DISTRICT, 95-005763 (1995)
Division of Administrative Hearings, Florida Filed:Tampa, Florida Nov. 27, 1995 Number: 95-005763 Latest Update: Jun. 03, 1996

The Issue The issue in this case is whether the application of Respondents Falkner to transfer and modify a Water Use Permit should be approved.

Findings Of Fact The Southwest Florida Water Management District (District) is responsible for regulation and protection of water resources in the geographic area involved in this proceeding. Since 1994, John Falkner has owned the property in Hillsborough County which is the subject of this proceeding. The Falkner property is farmed by Christopher Falkner, the owner's brother. Prior to purchasing the land, the Falkners farmed the property, also known as the Rogers farm, through a lease arrangement with the previous owner. Rose Ann DeVito owns property to the south of the Falkner property. In the time since Ms. DeVito purchased the property, the elevation of Sumner Road has been raised and culverts were replaced. A fish farm was constructed in close proximity to her property. The result of this and other development has been to direct all the water flow from the surrounding area into the stream adjacent to the DeVito property. Drainage patterns in the area of Ms. DeVito's property have been altered since she first occupied the property. A ditch along Sumner Road which used to handle runoff from her property has been blocked by a neighbor's driveway. Maintenance on the ditch, allegedly a county responsibility, is described as poor. The ditch at the rear of Ms. DeVito's property handled water flow to Bullfrog Creek until the water flow became blocked, and the water diverted onto her property. The effect is that Ms. DeVito's property often contains a large amount of water. A substantial amount of sand is visible on her property, allegedly deposited by water flow. According to Ms. DeVito, both the county and the District have blamed the Falkner farm for the water-deposited sand. Charles and Diana Booth own property adjacent and to the south of the Falkner property. From 1992 to 1994, the Booths suffered from water running off the Falkner/Rogers farm and flooding the Booth property. A flood of the Booth property in the Fall of 1994 was not caused by irrigation but was related to a ten inch rainfall event at the Falkner farm. A ten inch rainfall exceeds a 25 year storm event and would likely result in widespread flooding. The Booths' pasture, top soil and driveway were eroded by the flooding. During the two years of flooding, Mr. Booth complained on several occasions about the flooding to the Falkners' foreman, "Cleo." The complaints were not relayed to Mr. Falkner. In October 1994, Mr. Booth reported the problem to the Southwest Florida Water Management District. Soon after the complaint was made, a representative of the District inspected the property and determined that a ditch needed maintenance. Shortly thereafter, the ditch was cleaned and a berm was installed to redirect runoff away from the Booth property. There has been no further flooding of the Booth property. In October 1995, Mr. Booth became concerned that a ditch was filling with sand and would not continue to handle the runoff. After voicing his concern, a water diverter was installed in the ditch and appears to have remedied the situation. At the time the Falkners began to lease the Rogers property, an existing water use permit, numbered 206938.01, had been issued and was valid for the farm. The Falkners have applied to transfer the existing water use permit from the previous property owner. The Falkners also seek to modify the permit, increasing the total quantities which can be pumped by transferring previously approved quantities from another permit the Falkners currently hold. All of the relevant wells are within the District's Most Impacted Area (MIA) of the Tampa Bay Water Use Caution Area. The District allows a permit holder within the MIA to increase withdrawals from a well by transferring the quantities from another permitted well within the MIA. The other Falkner farm (the "301 farm") from which the quantities would be transferred is located approximately one-half mile to the south of the Rogers farm and is within the MIA. The District reviewed the application and, on September 29, 1995, issued its Proposed Agency Action to Issue Water Use Permit No. 206938.03. The proposed permit includes special conditions requiring monthly pumping reports, water quality reports, adherence to District irrigation allotments (irrigation levels established by the AGMOD computer model) and crop reporting. In reviewing the application the District utilized the criteria set forth in Florida Administrative Code, and the Basis of Review, incorporated into the code by reference. In order to obtain a Water Use Permit, an applicant must demonstrate that the water use is reasonable and beneficial, is in the public interest, and will not interfere with any existing legal use of water. Additionally, the applicant must provide reasonable assurances that the water use: will not cause quantity or quality changes which adversely impact the water resources, including both surface and ground waters; will not adversely impact offsite land uses existing at the time of the application; will not cause water to go to waste; and will not otherwise be harmful to the water resources within the District. The uncontroverted evidence establishes that the water use is reasonable, beneficial and is in the public interest. The Falkners irrigate farmland to produce agricultural products. The production of food is in the public interest. The proposed use is reasonable and beneficial. Further, uncontradicted evidence and opinions of expert witnesses establish that the proposed use will not interfere with any existing legal use of water. The applicant must provide reasonable assurances that the water use will not cause quantity or quality changes which adversely impact the water resources, including both surface and ground waters. The evidence establishes that pumping from the Falkner wells will not adversely affect the quality of water within the aquifers from which the water is drawn. Mr. Booth asserted that he is having water quality problems, specifically with rust in his well. The Booth well is approximately 25 years old. There is no evidence that the rust is related to the Falkner pumping. The DeVito and Booth wells draw from the Intermediate aquifer. Review of the potentiometric surface map of the intermediate aquifer indicates that there is a water level variation of 17 feet between the rainy and dry seasons. The result of the variance can be "dry" wells. There are two wells on the Falkner/Rogers property relevant to this proceeding. The first (District ID number 1) is 770 feet deep, is cased to a depth of 160 feet, and opens to the Floridan aquifer. The second (District ID number 2) is 1100 feet deep, is cased to a depth of 140 feet, and opens to the Intermediate and the Floridan aquifers. A cased well does not withdraw water from the formations through which the casing is placed. For example, a well cased to a depth of 160 feet draws no water from the top of the casing (at approximately ground level) to the bottom of the casing at 160 feet. The Intermediate aquifer releases water at a much slower rate than the Floridan aquifer. Based on the type and location of the Falkner wells, the vast majority of the water pumped by the Falkners comes from the Floridan aquifer. Impacts on existing wells are calculated through computer modeling. The "MOD" flow model demonstrates impacts that will occur after 90 days of pumping at peak month levels with no recharge to the aquifer. The MOD flow model results in a conservative "worst case" projection. The MOD flow model calculation projects the drawdown at Falkner well number 1 to be approximately .9 feet. The MOD flow model calculation projects the drawdown at Falkner well number 2 to be approximately 1.4 feet. The MOD flow model calculation projects the drawdown at the Booth well to be approximately one-half foot. The impact on the DeVito well will not exceed that projected at the Booth well. District permitting criteria allow for projected MOD flow model drawdown impacts of less than five feet at existing wells. The impact possible after approval of this application falls well within the District's guidelines. The impact of pumping if the application at issue in this proceeding is approved will result in a maximum variation of one-half foot at the Booth well. The evidence fails to establish that any problems related to water quantity encountered by the Booths are related to agricultural pumping at the Falkner farms. The evidence also establishes that, based on the existing retention and drainage system, the proposed use will not adversely impact surrounding surface water bodies. A system of swales and ditches is utilized to retain the water on the farm property. The evidence fails to establish that runoff from the Falkner/Rogers farm will adversely impact surrounding surface waters if this application is approved. The applicant has provided reasonable assurances that the water use will not adversely impact offsite land uses existing at the time of the application. The evidence establishes that the runoff from the Falkner farm does not discharge directly to the stream at the rear of the DeVito property. Other agricultural property discharges into the stream adjacent to the DeVito property. There is a steady waterflow through the stream at all times, whether or not the Falkner pumps are operating. Ms. DeVito's property consists of Myakka soil, which has little capacity to absorb rainfall and generates large amounts of runoff. The altered drainage patterns in the area have resulted in substantial water on her property. The evidence in insufficient to establish that the Falkner farm pumping has resulted in flooding on Ms. DeVito's property. The evidence fails to establish that approval of the application at issue in this proceeding will cause adverse impact to the DeVito property or will result in water quality or quantity problems. The Booths are concerned that the existing drainage system will not be maintained and that increased pumping will result in their land being flooded again. The evidence fails to establish a substantial likelihood that the Falkner farm drainage system will not be maintained. The applicant has provided reasonable assurances that the water use will not cause water to go to waste. The Falkners use a semi-enclosed seep irrigation system at the Rogers farm. Irrigation is only used when necessary. Mushroom compost, humates, and plastic mulch retain moisture in the soil. A special condition of the permit requires the Falkners investigate the feasibility of tail water recovery and reuse. The applicant has provided reasonable assurances that the use will not otherwise be harmful to the water resources within the District. The permit application results in no increased withdrawal of water than is allowed under the existing permits for the Rogers and the "301" farms.

Recommendation Based on the foregoing, it is hereby RECOMMENDED that the Southwest Florida Water Management District enter a Final Order granting the Falkner application and issuing permit number 206938.03. DONE and ENTERED this 26th day of April, 1996 in Tallahassee, Florida. WILLIAM F. QUATTLEBAUM, 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 26th day of April, 1996. APPENDIX TO RECOMMENDED ORDER, CASES NO. 95-5763 and 95-5764 To comply with the requirements of Section 120.59(2), Florida Statutes, the following constitute rulings on proposed findings of facts submitted by the parties. Petitioners Booth The Petitioners Booth proposed findings of fact fail to comply with the requirements of Rule 60Q-2.031(3), Florida Administrative Code, which requires citations to the record of hearing. The proposed findings are rejected as irrelevant or not supported by the greater weight of the evidence except where they are consistent with the Findings of Fact set forth herein. Respondents The Respondents' joint proposed findings of fact are accepted as modified and incorporated in the Recommended Order except as follows: 15. Rejected, cumulative. 28-29. Rejected, subordinate. 33. Rejected, subordinate. COPIES FURNISHED: Rose Ann DeVito, pro se 11001 Sumner Road Wimauma, Florida 33598 Diana P. and Charles B. Booth, pro se 10812 Sumner Road Wimauma, Florida 33598 Patricia Petruff, Esquire Dye and Scott, P.A. 1111 Third Avenue West Bradenton, Florida 34206 Martin Hernandez, Esquire Southwest Florida Water Management District 2379 Broad Street Brooksville, Florida 34609-6899 Peter G. Hubbell, Executive Director Southwest Florida Water Management District 2379 Broad Street Brooksville, Florida 34609-6899

Florida Laws (1) 120.57 Florida Administrative Code (1) 40D-2.301
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FLORIDA KEYS CITIZENS COALITION vs DEPARTMENT OF TRANSPORTATION AND SOUTH FLORIDA WATER MANAGEMENT DISTRICT (940606-10 (MSSW) AND 940606-2-D (WRM)), 95-005525 (1995)
Division of Administrative Hearings, Florida Filed:Fort Lauderdale, Florida Nov. 17, 1995 Number: 95-005525 Latest Update: Dec. 29, 1997

The Issue Whether FDOT has provided reasonable assurances that the activities it proposes to conduct pursuant to proposed District SWM Permit Application No. 940606-10, WRM Permit Application No. 940606-2-D and modification to ROW Permit No. 2584 will comply with the relevant permit criteria set forth in Chapters 373 and 403, F.S., and applicable rules and criteria promulgated thereunder.

Findings Of Fact THE PARTIES Petitioner, 1000 Friends of Florida (1000 Friends), is a not-for-profit, tax exempt membership corporation, organized and existing under the laws of the State of Florida. The principal office of 1000 Friends is 926 East Park Avenue, Tallahassee, Florida 32314 and it also maintains an office at 3305 College Avenue, Ft. Lauderdale, Florida 33314. Petitioner, Florida Bay Initiative, Inc. (FBII), is an entity incorporated under the laws of Florida with its principal office located at 250 Australian Avenue South, Suite 500, West Palm Beach, Florida 33401. Petitioner, the Florida Keys Fishing Guides Association, is an association of sport fishing guides who live in the Florida Keys and is headquartered at 138 Royal Lane, Islamorada, Florida 33036. Petitioner, Michael Collins, is a private individual. His address is 138 Royal Lane, Islamorada, Florida 33036. Petitioner, Charles W. Causey, is a private individual. His address is Post Office Box 448, Islamorada, Florida 33036. Petitioner, the Florida Keys Concerned Citizens Coalition (FKCC), is a not-for-profit Florida corporation whose address is West Shore Drive, Big Pine Key, Florida 33043. Petitioner, AG Intus, Inc., filed a Notice of Voluntary Dismissal on August 9, 1996. DOAH Case 95-5524, the proceeding filed by Intus, was previously consolidated with the other cases to this proceeding. On August 12, 1996, the Intus case was severed from this proceeding and the Intus hearing cancelled. Respondent, the South Florida Water Management District (the District or SFWMD), is a public corporation in the State of Florida existing by virtue of Chapter 25270, Laws of Florida, 1949, and operating pursuant to Chapter 373, F.S., and Title 40E, F.A.C., as a multi-purpose water management district, with its principle office in West Palm Beach, Florida. Respondent, the Florida Department of Transportation (FDOT), is an agency of the State of Florida. Its District Six address is 1000 N.W. 111th Avenue, Miami, Florida 33172. Intervenor, Monroe County, is a political subdivision of the State of Florida. For the purposes of this proceeding the address for Monroe County is c/o Apgar and Pelham, 909 East Park Avenue, Tallahassee, Florida 32301. The District, FDOT and Monroe County did not object to the standing of the Petitioners at the formal hearing and represented that they will not object to the standing in the event of an appeal. Based on the representations of the Respondents, the Petitioners were not required to put on a case as to their standing. THE THREE PERMIT APPLICATIONS FDOT has applied to the District for a Wetland Resource Management (WRM) permit, a Surface Water Management (SWM) permit, and a Right of Way (ROW) occupancy permit. On June 6, 1994, the Applicant submitted applications for surface water management and wetland resource management permits for the purpose of widening and modifying this 20.4 mile stretch of U.S. 1. The surface water management permit application is identified as Application No. 940606-10. The wetland resource management permit application is identified as Application No. 940606-2-D. On October 24, 1995, the District issued Staff Reports on Permit Application No. 960606-10 and Permit Application No. 94060-2-D. These Staff Reports recommended issuance of the permits subject to general and special conditions as specified therein. An addendum to the staff report was issued November 3, 1995. On September 27, 1994, the Applicant submitted a request to modify its existing ROW Occupancy Permit to enable it to replace the bridge where U.S. 1 crosses the C-111 Canal. The land encompassed by the ROW occupancy permit challenged in this proceeding is located in Section 16 and 17, Township 59 South, Range 39 East, Dade County, Florida. A draft right-of-way occupancy permit with standard limiting and special conditions was produced as part of a package that went to the Governing Board and others. The proposed authorization for use of the ROW is for the following: REMOVAL OF EXISTING U.S. HIGHWAY 1 BRIDGE AND REPLACEMENT WITH A NEW FIXED BRIDGE. PROJECT INCLUDES CONSTRUCTION OF A NEW SERVICE/ACCESS ROAD, 2 DETENTION PONDS, 2 CATCH BASINS, 2-15" R.C.P. OUTFALLS, BOAT RAMP WITH LOADING DOCK, PARKING AREA, PEDESTRIAN GATE AT S-197, FENCING AND WILDLIFE CROSSING ALL WITHIN THE NORTH AND SOUTH RIGHT OF WAY OF C-111 (STATION 938+00 - 955+00). The draft right-of-way occupancy permit modification, identified as “SFWMD PERMIT NO. MOD 2548," should correctly be identified at “SFWMD PERMIT NO. MOD 2584.” The numbers “8” and “4” were inadvertently transposed. STIPULATIONS AS TO APPLICABLE LAW The parties have accurately set forth the applicable permitting criteria and the appropriate Basis of Review in their prehearing stipulation. CRITERIA FOR ROW PERMIT Rule 40E-6.301, Florida Administrative Code, provides, in pertinent part, as follows: In determining whether an occupancy permit should be issued, the District shall consider whether the proposed activity: interferes with the present or future construction, alteration, operation or maintenance of the works of the District; is consistent with the policy and objectives of Chapter 373 F.S., the legislative declaration of policy contained in Section 373.016, F.S. and the state water policy, Chapter 17-40, F.A.C.; has an actual or potential negative impact upon environmentally sensitive areas, which include: wetlands; endangered or threatened species habitat; aquatic preserves; outstanding Florida waters; federal, state and privately owned parks and wildlife management areas; designated areas of critical state concern; lands purchased by federal, state and local governments for the purpose of environmental protection, water resource protection and esthetics; and lands which contain native terrestrial plant species in significant amounts. Environmentally sensitive areas include areas on and off- site that are affected by activities which occur on, or are initiated from, the District’s works; degrades water quality within the receiving water body or fails to meet the provisions of Ch. 373, F.S., the state water policy, and Ch. 40E, F.A.C.; involves a discharge of wastewater from a new wastewater source or an increased discharge from an existing wastewater source; will discharge debris or aquatic weeds into District lands or works or cause erosion or shoaling within the works of the District; is supported by financial assurances, which will ensure that the proposed activity will be conducted in accordance with Chapter 373, F.S., and Chapter 40E-6, F.A.C.; presents an increased liability risk to the District; meets the general and specific criteria in the Basis of Review which is incorporated by reference in Rule 40E- 6.091, F.A.C.; interferes with actual or potential public use of the District’s works or public, recreational or other facilities not within the District’s works; is consistent with local zoning and other private land uses in the area; interferes with the quality or quantity of a public or private water supply; meets applicable criteria in Chapters 40E-61 and 40E-62, F.A.C.; ROW occupancy permits typically have standard limiting conditions which are incorporated as part of the permit. The permit may also have special limiting conditions. CRITERIA FOR PERMITTING THE SWM SYSTEM Rule 40E-4.301(1), Florida Administrative Code, contains the following criteria that, at the times pertinent to this proceeding, were used by SFWMD in determining whether to permit a surface water management system: In order to obtain or modify a permit under this chapter, an applicant must give reasonable assurances that the surface water system: provides adequate flood protection and drainage, without causing over- drainage, will not cause adverse water quality and quantity impacts on receiving waters and adjacent lands regulated pursuant to Chapter 373, F.S., will not cause discharges which result in any violations, in surface waters of the state, of the standards and criteria of chapter 17-302, F.A.C., will not cause adverse on-site or off-site impacts on surface and groundwater levels and flows, including impacts to sources of water supply and wetland hydrology, will not cause adverse environmental impacts, can be effectively operated and maintained, will not adversely affect public health and safety, is consistent with the State Water Policy, chapter 17-40, F.A.C., for a DRI with a signed Preliminary Development Agreement with the Florida Department of Community Affairs, pursuant to section 380.06(8), F.S., provides a surface water management system for that portion of the site approval for development which is able to operate separately from the surface water management system for the balance of the project site and still meet applicable District criteria. meets any applicable basin criteria in chapter 40E-41, F.A.C., will not otherwise be harmful to the water resources of the District, will not interfere with the legal rights of others as defined in subsection 17-40.401(8), F.A.C., is not against public policy, will meet general and specific criteria in the document described in subsection 40E-4.091(1)(a), F.A.C., (0) will meet criteria for isolated wetlands, which are found in Appendix 7 of the document described in rule 40E- 4.091(1)(a), F.A.C., (p) will meet the criteria for above ground impoundments, which are found in Appendix 6 of the document described in rule 40E-4.091(1)(a), F.A.C. The SFWMD has adopted certain procedures and criteria contained in a document, referred to as “Basis of Review for Surface Water Management Permit Applications Within The South Florida Water Management District” (BOR). Subsection 40E-4.091(1)(a), F.A.C. incorporates this document by reference into Chapter 40E-4, F.A.C. The BOR is a document that is “described in subsection 40E-4.091(1)(a), F.A.C.,” within the meaning of Rule 40E-4.301(1), F.A.C. The BOR establishes a rebuttable presumption that water quality criteria are met through specified volumetric retention and detention requirements. These performance based criteria are designed to be flexible. CRITERIA FOR THE WRM PERMIT In 1992 DEP entered into an Operating Agreement with the District, which delegated to the District responsibility for issuing wetland resource management (WRM) permits, which are required for dredge and fill activities in wetlands. Both DEP and the District implement the same wetland resource permit and MSSW permit rules. The District agrees with DEP's interpretation and application of the WRM permitting rules and non-rule policy, and applies the same when issuing such permits. Section 403.918, Florida Statutes (1991), provides the pertinent criteria that must be applied by the District in determining whether to grant or deny the WRM permit. That criteria requires the applicant to provide reasonable assurance that water quality standards will not be violated. In addition, for projects in OFW, the applicant must provide reasonable assurance that the project is clearly in the public interest. THE PUBLIC INTEREST TEST The District is required to balance the following criteria, found at Section 403.918(2)(a), Florida Statutes (1991), in determining whether a project is clearly within the public interest: Whether the project will adversely affect the public health, safety, or welfare or the property of others; Whether the project will adversely affect the conservation of fish and wildlife, including endangered species, or their habitats; Whether the project will adversely affect navigation or the flow of water or cause harmful erosion or shoaling; Whether the project will adversely affect the fishing or recreational values or marine productivity in the vicinity of the project; Whether the project will be of a temporary or permanent nature; Whether the project will adversely affect or will enhance significant historical and archaeological resources under the provisions of s.267.061; and The current condition and relative value of functions being performed by areas affected by the proposed activity. MITIGATION If the applicant is unable to otherwise meet the public interest test, the District shall, pursuant to Section 403.918(2)(b), Florida Statutes, “consider measures proposed by or acceptable to the applicant to mitigate adverse effects which may be caused by the project . . .” The District thereafter re-evaluates the project to determine whether the project, as mitigated, meets the public interest test. The criteria for mitigation is found in Chapters 373 and 403, Florida Statutes, Title 40 E (including the Basis of Review) and Rule 62-312, Florida Administrative Code. Rule 62-312.330, Florida Administrative Code, states the general criteria for evaluating mitigation proposals as follows: The goal of the mitigation proposal shall be to offset the expected adverse impact of the project that have resulted in the project being deemed unpermittable such that the resulting project with mitigation is not contrary to the public interest or, in the case of Outstanding Florida Waters, is clearly in the public interest. Each project must be separately evaluated to determine whether the proposed mitigation is sufficient. Rule 62-312.340, Florida Administrative Code, provides guidelines that are to be used in evaluating proposed mitigation projects. GENERAL DESCRIPTION OF THE PROJECT AREA FDOT proposes to widen a 20.4 mile portion of U.S. 1 in southern Dade County and northern Monroe County. Approximately seven miles of the project area is in Monroe County and approximately thirteen miles is in Dade County. The northern terminus of the project is the intersection of U.S. 1 and Card Sound Road, which is located in Dade County south of Florida City. The southern terminus of the project is the intersection of U.S. 1 and Abaco Road on Key Largo in Monroe County. The corridor of the proposed project passes through Sections 6, 7, 16, 18, 21, 27, 28, Township 59 South, Range 39 East; Sections 24, 25, 36, Township 58 South, Range 38 East; Sections 16, 19, 30, 31, Township 58 South, Range 39 East, Sections 16, 30, 31, Township 60 South, Range 40 East; Sections 25, 26, Township 60 South, Ranges 39 East, Dade and Monroe Counties, Florida. U.S. 1 is the main highway between northern Monroe County and southern Dade County. The only other road between Monroe County and Dade County is Card Sound Road. The Florida Keys is designated as an Area of Critical State Concern, pursuant to Section 380.0552, Florida Statutes. The Dade County portion of the road, north of the C- 111 canal, lies within typical Everglades habitat, which is classified as environmentally protected lands of Dade County. Most of the project corridor in Dade County is part of or adjacent to the Everglades National Park. Valuable wetlands exist throughout the project corridor. The following bodies of water will receive discharges if the surface water management system is permitted: C-111 Canal, Jewfish Creek, Lake Surprise, Blackwater Sound, Barnes Sound, Little Blackwater Sound, Long Sound, Manatee Bay, Sarge Lake, andManatee Creek. The receiving bodies of water are Outstanding Florida Waters (OFWs) or are connected to OFWs. THE EXISTING ROADWAY As it presently exists in the project area, U.S. 1 is a two lane undivided highway with two passing zones that are each one mile in length. Each travel lane on the existing facility is twelve feet wide. The existing shoulder on either side of the road consists of four feet of pavement and six feet of grassed area. FDOT Exhibit 7 accurately depicts the existing roadway typical section. Exotic vegetation, generally limited to the areas immediately adjacent to the highway, exist throughout the project corridor. These exotic species are present because FDOT has failed to properly maintain its right of way. A clear zone is an unobstructed area that includes the shoulder of the roadway and typically extends beyond the shoulder. The purpose of the clear zone is to provide a driver who has lost control of his or her vehicle a sufficient clear recovery area to regain control of the vehicle so that it can be maneuvered back onto the road. The clear zone for the existing road is inadequate to provide a safe recovery area. There is at present a two lane bridge over Manatee Creek, a two-lane bridge crossing the C-111 Canal, a bascule bridge, which is a drawbridge, over Jewfish Creek, and a two lane causeway through Lake Surprise. The two existing passing zones are located in Dade County. The first is south of U.S. 1’s intersection with the C-111 canal between mile markers 113-115. The second passing lane is approximately four miles south of the northern terminus of the project between mile markers 120-122. Each existing passing zone is undivided and consists of two northbound lanes and two southbound lanes, with each travel lane being twelve feet in width. The shoulders in the passing zones are the same as for the typical section. A surface water management (SWM) system is defined by Rule 40E-4.021(5), Florida Administrative Code , as being "the collection of devices, improvements or natural systems whereby surface waters are controlled, impounded, or obstructed.". There is no surface water management system presently associated with the road. The roadbed is elevated approximately five feet above mean sea level according to the National Geodetic Vertical Datum and was constructed on the old railroad bed of the Florida East Coast Railroad. No hydrologic culverts have been placed within the roadbed. Consequently, surface water flow between the eastern and western sides of the road north of the C-111 Canal has been cut off. C-109 AND C-111 CANALS In the 1960's, the C-109 and C-111 canals were constructed as part of an overall water management system in the area. As a result of the roadbed and the canals, water has been impounded on the western side of U.S. 1 at a level higher than on the eastern side. Due to cutoff of waterflow by the roadbed embankment, historic freshwater flow between the eastern and western sides of the project area has been restricted, which has resulted in an adverse impact on the Everglades ecosystem north of the C-111 Canal. The restricted water flow has resulted in less fresh water being available for shorter periods of time. Consequently, aquatic life has had reduced opportunities to develop. The restricted flow also has impeded the ability of aquatic life to reach freshwater areas during times of drought. On the east side of the road marine conditions have displaced what naturally should be freshwater conditions. PROJECT HISTORY While FDOT has been aware of traffic safety and hurricane evacuations concerns on the roadway for a long time, the current project originated in 1986 when Monroe County identified this project as a need in its 1986 Comprehensive Plan. Pursuant to agency practice, the proposed project was incorporated into FDOT's five year work program and a study was performed pursuant to FDOT’s Project Development and Environment (PD&E) Manual. FDOT's PD&E manual describes the process by which FDOT determines whether to construct or improve a road. The PD&E process includes an Environmental Impact Statement (EIS) to analyze existing conditions, assess the need for improvement, and develop alternatives. A Draft EIS is performed and circulated for comment to governmental agencies and the public. Based upon comments and further review a Final EIS is prepared. Metric Engineering ("Metric") began the PD&E study of the project in 1988 pursuant to a contract with FDOT. Metric identified seven factors which it concluded supported the need for the project. First, the improved corridor would improve the linkage between the four lane road at the northern terminus and the four lane road at the southern terminus. Second, the project would improve navigation by replacing the existing bascule bridge at Jewfish Creek. Third, the project would improve the level of service for the road. Fourth, the project would improve the safety of the road. Fifth, the project would improve the clearance time for hurricane evacuation. Sixth, the project was consistent with the long range transportation plans adopted by Monroe County. Seventh, the project would accommodate increased traffic, which can be expected with or without the project. Based on the needs evaluation, Metric performed a corridor analysis to determine the best way to get from Florida City to Key Largo, including improving only Card Sound Road, improving only U.S. 1, or improving a combination of the two. Metric concluded that the best resolution was to improve the project corridor. Metric also analyzed various alternatives in an effort to reduce the size of the typical section of the roadway in the U.S. 1 corridor and thereby minimize environmental impacts of the project. Because of concerns from Everglades National Park that no aspects of the project construction occur within its boundaries, FDOT agreed to conduct all construction east of FDOT's existing right of way line. The conclusions of the Metric studies were memorialized in a Final EIS and Final Engineering Report published in 1992. Conclusions regarding alternatives and project needs were then incorporated into the permit application and have continued to be updated. The 1992 version of the project was for a four lane roadway with four lane bridges throughout the project corridor. Subsequent to its June 6, 1994, permit applications to the District for a four lane roadway, FDOT went through an extensive process of providing the District with additional information in an effort to provide the District with the necessary reasonable assurance that the proposed project would comply with the permit criteria. The final series of modifications contained the three lane alternative, which will be described in detail below and is now the subject of this proceeding. The three lane proposal is a compromise that FDOT agreed to in an effort to minimize the direct, secondary, and cumulative impacts of the project. Monroe County passed Resolution No. 315-1995 on September 7, 1995, asking FDOT to build a three-lane road on a four-lane embankment. This resolution provided, in part, that “. . . Monroe County finds that the '3-lane alternative' as described in the Statement of Agency Commitments is the most viable proposal of those considered, because it balances the needs for a widened highway with safeguards designed to address secondary impacts.” The secondary impacts referred to in the resolution included concerns that two southbound lanes would result in more growth. The rationale behind the resolution was that more growth would result from two southbound lanes than from one southbound lane with the proposed passing zones. In response to the request of Monroe County and in response to a similar request made by the District, FDOT notified the District by letter dated September 5, 1996 of FDOT's decision to redesign the project to change the roadway from four to three lanes. FDOT HAS MINIMIZED THE IMPACTS OF THE PROJECT During the PD&E process prior to permit application FDOT studied project needs and alternative alignments, and conducted corridor analyses. FDOT originally considered a proposal that included approximately 250 acres of wetlands impacts. At the District's suggestion, FDOT revised its proposal prior to the permit application to reduce the wetland impacts and project footprint. The application submitted contained approximately 165 acres of impact. FDOT changed the typical section of the proposed roadway again after substantial interagency coordination in an effort to reduce wetlands impacts even further. FDOT agreed to reduce the footprint by changing the design of the median from 22 feet and a Jersey barrier (which is a minimum barrier) to 20 feet with a tri-beam rail barrier. The more substantial barrier was added because the median was narrowed. Additionally, instead of ten-foot paved shoulders on each side of the median, FDOT would use two-foot paved shoulders with sixteen feet of grass in the middle. These minimization efforts resulted in a wetland impacts decrease from 164 acres to 149.07 acres, the current impact of the project. Avoidance, or choosing alternate routes to avoid impacts to wetlands, was not a possible option because only wetlands and open waters exist between the northern and southern terminus of the project. FDOT explored all reasonable alternatives to the proposed project, including a two lane alternative proposed by a consultant for FBII. As discussed below, FDOT did not adopt the two-lane alternative, because the alternative did not address all of FDOT's identified needs for the project. FBII prepared a report with a two-lane alternative to the proposed project. FBII's original proposal included one 12-foot northbound lane with a 10-foot paved shoulder covered with thermoplastic rumble strips to deter vehicular use of the shoulder. In the southbound direction, FBII proposed a 12-foot travel lane with a 4-foot paved shoulder, essentially the same as currently exists. That proposal was analyzed by Metric Engineering on behalf of FDOT. FDOT rejected the FBII alternative for several reasons. First, though the 10-foot northbound shoulder theoretically may be used by cars during hurricane evacuation, removal of the rumble strips would be impractical due to lack of time to do so under threat of a hurricane, and due to the costs involved. It would be unrealistic to require people to otherwise drive over the rumble strips, without removal, because they are designed to prevent such access. Using the 10-foot shoulder during an evacuation would result in there being no shoulder area to remove accident vehicles from the roadway which would otherwise threaten to restrict the flow of traffic or cease it altogether. The reduced width of the shoulder lane below the standard 12-foot lane would also decrease the flow of evacuees. FBII's proposal for a two-lane fixed-height bridge at Jewfish Creek would not completely eliminate rear-end collisions at the bridge. The two-lane alternative proposed by FBII is not a signed and sealed cross section. The proposal by FBII does not include the area necessary for a SWM system or for clear zones. FBII did not do an analysis to determine whether its proposal complies with pertinent FDOT roadway and traffic design standards or with pertinent highway safety and improvement standards. The FBII proposal does not account for removal of the Lake Surprise causeway or construction related impacts from barge traffic. FBII did not do a wetlands survey to determine the impact of its two-lane proposal. At the Final Hearing, Petitioners presented for the first time a new proposal to use "flexible diverters" to pave a third northbound lane and to block that lane from travel traffic with poles. However, no research was conducted into the feasibility of such a proposal, nor was it adequately thought out. Such a use of "flexible diverters" is unprecedented in FDOT's history, is impractical to implement, and would violate FDOT's design standards contained in its Manual on Uniform Traffic Control Devices. Petitioners also presented for the first time at the Final Hearing a proposal to add an 8 to 10 foot paved northbound shoulder which could be converted to a travel lane with traffic control cones in the event of an evacuation. This plan is also not feasible, because the resulting lanes would not be wide enough to safely accommodate evacuating traffic, and because the contradiction between existing road striping and the placement of cones would likely cause accidents, which would halt evacuation. The proposals submitted by FBII do not sufficiently improve hurricane evacuation or traffic safety and, consequently, are not acceptable alternatives to the project. FDOT can do nothing else to minimize the impacts of the project and still address the needs for the project. Minimization of wetlands impacts was accomplished to the greatest extent possible. FDOT has proposed mitigation to offset the impacts that could not be avoided. THE PROPOSED PROJECT - IN GENERAL STIPULATION AS TO DESIGN AND CONSTRUCTION Petitioners stipulated that the design and construction specifications of the roadway proposed to be permitted in this case comply with all applicable design and construction standards for structural integrity, and adequately describe the three-lane divided roadway proposed to be constructed on a four-lane roadbed/embankment. PROPOSED LANES, SHOULDERS, AND MEDIAN FDOT proposes to widen the roadway in the project area to a three lane divided roadway with two northbound lanes and one southbound lane, plus three passing zones. The proposed project will be constructed on a four lane roadbed embankment. FDOT does not presently have plans to add the fourth lane to this roadway. FDOT Exhibit 8 contains an accurate description of the proposed typical section of the roadway. The typical section will consist of two twelve-foot northbound lanes with a six-foot paved shoulder and a four foot stabilized area adjacent to the paved shoulder; a twenty-foot median consisting of a two-foot paved shoulder, sixteen feet of grass and a tri-beam guardrail in the middle as a separator; and one twelve-foot southbound lane with an eight-foot paved shoulder. The proposed typical section also includes a storm water management system that will be described in more detail below. The proposed typical section includes a clear zone thirty feet in width, which is adequate. THE THREE PASSING ZONES The existing passing zone located in Dade County between mile markers 113 and 115 is one mile in length. FDOT proposes to alter this passing zone to 1.44 miles in length. The existing passing zone located in Dade County between mile markers 120 and 122 is also one mile in length. FDOT proposes to alter this passing zone to 2 miles in length. In addition, FDOT proposes to construct a 1.5 mile long passing zone between mile markers 110 and 112 in Monroe County. If permitted, the proposed project will include 2 passing zones in Dade County and 1 passing zone in Monroe County, for a total of 3 passing zones. The total length of the passing zones will equal 4.94 miles. ELEVATION There are no plans to change the elevation of the existing roadway. HYDROLOGIC CULVERTS The project contemplates the construction of 25 hydrologic culverts north of the C-111 Canal. These culverts will remain capped until further hydrological studies are completed and input from all concerned regulatory agencies can be obtained. It has not yet been determined how these culverts will be utilized to maximize the improvement to the ecosystem north of the C-111 Canal. WILDLIFE CROSSINGS INCLUDING THE C-111 BRIDGE The project contemplates the construction of three wildlife crossings north of the C-111 Canal in Dade County with fencing designed to funnel wildlife through the crossing. These crossing, sometimes referred to in the record as “panther crossings” are located between mile markers 118-119, 122-123, and 126-127 and will be constructed as overland bridges. In addition, the replacement bridge over the C-111 Canal (located between mile markers 116-117 in Dade County) is intended to serve as a wildlife crossing and will also employ fencing to funnel wildlife through the crossing. All four of these structures will be constructed as four-lane bridges, but will be striped for three lanes with rumble strips on the southbound fourth lane to discourage vehicular traffic in that lane. There will be an eight foot outside shoulder. FDOT proposes to construct 18 culverts south of the C-111 Canal for crossings by crocodiles, alligators, manatees, and other wildlife. These crossings will consist of 15 box culverts and 3 bridges. MANATEE CREEK BRIDGE The proposed bridge at Manatee Creek would be constructed as a four lane bridge, but would be striped for three lanes with rumble strips on the southbound fourth lane to discourage vehicular travel in that lane. There would be an eight foot outside shoulder. BRIDGING JEWFISH CREEK AND LAKE SURPRISE Jewfish Creek, which is part of the Intracoastal Waterway, and Lake Surprise would be bridged by a continuous structure. The Jewfish Creek bascule bridge would be replaced by a high-level four-lane fixed bridge. The Lake Surprise causeway would be replaced by a low-level four-lane bridge. The total distance for this bridging is approximately 2.35 miles. AREA OF PROJECT THAT WILL BE OPERATED WITH FOUR-LANES The three passing lanes (4.94 miles) and the bridge over Jewfish Creek and Lake Surprise (2.35 miles) would be operated with four lanes. Those areas total 7.29 miles of the 20.4 mile project corridor. Approximately 43 percent of the proposed roadway would have four lanes of pavement. Excluding the areas where the fourth lane will be blocked from travel with rumble strips, only 35 percent of the completed project will contain four travel lanes. This area consists of the three passing zones and the bridges over Jewfish Creek and Lake Surprise. THE PROPOSED SWM SYSTEM The proposed project would provide for a SWM system consisting of inlets, culverts, swales, berms and dry/wet retention areas. For the typical roadway section, runoff from the paved roadway surfaces will be directed to roadside swales designed to provide retention for 50 percent of 2.5 inches times the impervious area. The SWM system for the bridges will collect runoff in inlets and culverts and direct it to either swales or dry or wet retention ponds. The berms of the SWM system provide additional protection by restricting spills of pollutants, such as petroleum from overturned tankers or other vehicle accidents, from running into the surrounding waters. The berms and swales of the SWM are designed to catch pollutants and prevent their discharge into the surrounding waters. FDOT Exhibit 18 consists of four separate drainage reports submitted to the District in 1995 in connection with the project, one report for each section of the project. The reports accurately document the drainage calculations, the drainage design, the rationale behind the drainage design, and compliance of the design with the laws and regulations of the permitting agencies for the original four-lane proposal. On or about September 5, 1995, FDOT submitted revised drainage calculations to the District, determining the amount of stormwater treatment for the three-lane project. The revised calculations established that at least 95% percent of all stormwater runoff from the project would be captured in the proposed SWM system. Because the swale design was based on the originally proposed four-lane road, retention will be in excess of the required volume for most sections of the roadway. The required retention volume for this project is approximately 166 percent of what is required by the BOR. The surface and subsurface geology of the roadway consists of Miami oolite limestone overlain with Perrine maral. Underlying this is Thompson formation, anastasia and Key Largo limestone. Based on these constituencies, the swales proposed by the SWM system would be effective in rapidly removing heavy metals and phosphorous. The revised calculations established that approximately five percent of the project area will not have a SWM system. These areas will not have a SWM system because properly-sized retention systems in those areas can not be constructed without causing a disproportionate, adverse impact to surrounding wetlands. FDOT has provided reasonable assurances that the proposed SWM system’s total water quality treatment exceeds the District's permitting requirements and provides sufficient treatment to exceed the BOR requirements. The water discharged from the proposed system would be of higher quality than that currently discharged, which is not treated. FDOT has provided reasonable assurances that the proposed SWM system complies with the permitting criteria found in Rule 40E.301(1)(a)-(p), Florida Administrative Code. The following findings are made as to that criteria. Rule 40E-4.301(1)(a), F.A.C. The parties stipulated that Rule 40E-4.301(1)(a), F.A.C., pertaining to flood protection and the adequacy of drainage, is not at issue in this proceeding. Rule 40E-4.301(1)(b), F.A.C. The quality of water being discharged from the SWM system will be of substantially higher quality than the existing discharges. Consequently, it is concluded that the system will not cause adverse water quality impacts within the meaning of Rule 40E-4.301(1)(b), F.A.C. In addition, the evidence established that there will likely be less water discharged from the roadway if the project is constructed because of the amounts of water that will likely be retained in the swales that are a part of the SWM systems. Rule 40E-4.301(1)(c), F.A.C. Because the receiving bodies of water are designated Outstanding Florida Waters, the District is required to apply the DEP's most stringent water quality requirements -- the antidegredation requirements for discharge to OFWs, to this project. Those standards will be discussed in more detail below. The evidence established that the proposed project will not violate those requirements. Rule 40E-4.301(1)(d), F.A.C. Impacts to sources of water are not at issue. The District reviewed the potential effect of the SWM system upon on-site and off-site impacts to surface or groundwater levels and flows. The evidence supports the District's conclusion that no adverse impacts will be caused. Petitioners failed to present any evidence on groundwater levels and flows. Consequently, it is found that the criteria found at Rule 40E-4.301(1)(d), F.A.C., has been satisfied. The 25 hydrologic culverts north of C-111 have the potential to re-establish historic surface water flow in the area. They were sized, based on rainstorm events, to help equalize water levels from one side of the road to the other. The culverts are capable of transferring water from west to east to assist in the historic restoration of flows. In order to assure the proper usage of the culverts, they will remain gated until the District develops a management plan in conjunction with other agencies. The District will determine the maintenance entity. The FKAA water main runs beneath this section of the road. As a result, there is no other more hydrologically efficient alternative for the placement of the culverts. The culverts would also provide a means for overwash from storm events, over the U.S. 1 roadbed, to flow back to its point of origin, stabilizing the roadbed and allowing release of the accumulated salt water. Rule 40E-4.301(1)(e), F.A.C. In addition to providing for a net improvement in water quality, the project will offset any adverse impacts through mitigation and other environmental enhancements for which no mitigation credits are being assigned, as described below. Rule 40E-4.301(1)(f), F.A.C. FDOT has a history of adequate maintenance of SWM systems, and has provided reasonable assurance that it has the staff and budget to comply with District operation and maintenance requirements. FDOT will also be able to comply with the District's requirements to control exotic plants and other foliage along project corridor. Rule 40E-4.301(1)(g), F.A.C. The SWM system will not adversely affect public health and safety. The dispute as to the public interest test focused more on the WRM permitting requirements. Findings as to the public interest test are discussed in more detail below. Rule 40E-4.301(1)(h), F.A.C. The evidence established that the SFM system is consistent with State Water Policy. Rule 40E-4.301(1)(i), F.A.C. This project does not pertain to a DRI and, consequently, this criteria is not applicable. Rule 40E-4.301(1)(j), F.A.C. There are no basin criteria applicable to this project. Rule 40E-4.301(1)(k), F.A.C. The evidence established that the SWM system will not be harmful to the water resources of the District. While there will be adverse environmental impacts caused by the project, those adverse impacts have, as will be discussed in more detail below, adequately offset by mitigation. Rule 40E-4.301(1)(l), F.A.C. This issue was not at issue in this proceeding. Rule 40E-4.301(1)(m), F.A.C. As will be discussed in greater detail in a subsequent section of this Recommended Order, the project is not against public policy. For the reasons set forth in that subsequent section, it is found that the project is clearly in the public interest. Rule 40E-4.301(1)(n), F.A.C. Rule 40E-4.091(1)(a), F.A.C., constitutes the BOR. As discussed in detail above, the SWM system complies with the BOR. Rule 40E-4.301(1)(o), F.A.C. There are no isolated wetlands pertaining to this project. Rule 40E-4.301(1)(p), F.A.C. There are no above ground impoundments, as described in Appendix 6 of the BOR, pertaining to this project. WATER QUALITY - DISCHARGES INTO OFW Because the project will involve discharges into Outstanding Florida Waters, it was necessary for FDOT to establish that the discharges from the SFW system will not degrade those OFWs. The evidence established that FDOT's proposed project complies with and exceeds applicable water quality standards and permitting criteria. There will be no significant degradation of ambient water quality as a result of the project. It is expected that there will be a net improvement in ambient water quality resulting from the proposed project, as opposed to the continued degradation if nothing is done to treat stormwater runoff. In FDOT Exhibit 46, FDOT provided baseline water quality data in the form of STORET data for waters adjacent to the project area. STORET is a centralized repository and database for water quality data throughout Florida. It is Florida's principal source of water quality data. STORET contains the best scientific database on water quality in Florida. The STORET data set forth in FDOT Exhibit 46 provided sufficient evidence on ambient water quality for the waters adjacent to the proposed project. In addition to providing the water quality data in FDOT Exhibit 46, FDOT is required by Special Permit Condition 37 to submit appropriate water quality data in the surrounding waters prior to any construction activities. SFWMD Exhibits 5 and 6 contain amendments to Proposed Agency Action made after the beginning of the formal hearing. These amendments include a requirement that an appropriate water quality monitoring plan be submitted within 30 days of the permit issuance. FDOT has provided reasonable assurances that water quality standards will be met and that there will be appropriate water quality monitoring during construction. DIRECT IMPACTS OF THE PROJECT The proposed roadway design will result in the following direct impacts to wetlands adjacent to the roadway corridor: 1) the dredging of 11,028 cubic yards of material from 2.1 acres, 2) the placement of 1,689,553 cubic yards over 147.0 acres of wetlands, and 3) 6.9 acres of (potential) permanent impact due to shading and 4.1 acres (potential) of temporary impacts from the Jewfish Creek Bridge construction activities to seagrass habitat. In order to determine the project's direct impacts, the area surrounding the project was surveyed to determine the number of affected acres. This was done by using a computer aided design ("CAD") system, and by categorizing the various forms of wetlands and associated flora and fauna into the following communities: mangrove, emergent freshwater, open water, and tidal, consisting of seagrass and non-vegetated bottoms. Using these categories and the CAD system, every square foot of direct impacts were accounted for. The adverse direct wetland and surface water impacts of this project are as follows: 1) 27.83 acres Non- Vegetated Tidal Bottom; 2) 11.27 acres Seagrasses; 3) 46.85 acres Mangroves; 4) 42.35 acres Sawgrass/Cattail/Spikerush; 5) 14.31 acres Shrub Wetlands; and 6) 6.46 acres Open Fresh Water; totaling 149.07 acres. Though some wetlands to be impacted may be of lesser quality, FDOT stipulated that all wetlands to be directly impacted by the project should be considered to be high quality wetlands for the purpose of mitigating the impacts. The impacted wetlands are part of larger wetland systems. Petitioners assert that the District should have required studies as to impacts as to the larger wetland systems. The evidence established that the District appropriately considered the type and location of the wetlands involved so that additional study suggested by Petitioners was unnecessary. Petitioners also assert that impacts to isolated wetlands should have been studied. The evidence established that there will be no such impacts. SECONDARY AND CUMULATIVE IMPACTS RECOGNIZED BY SFWMD In addition to the direct impacts of the project, the District is required to analyze secondary and cumulative impacts. A project's secondary impacts are those that, though outside of the project footprint, are very closely linked and causally related to the project. This is a "but for" test. Secondary impacts are those impacts which, if not for the proposed project, would not occur. Both positive and negative secondary impacts are considered. When there are both positive and negative secondary impacts caused by a project, the permitting agency must consider the severity of the impacts and balance these together with the other factors in the public interest test to determine whether or not the project is clearly in the public interest. WRM statutes, and DEP rules and policies pertaining to those statutes do not regulate growth or traffic increases, per se. Only if such increases are very closely linked and causally related to the project will they be considered. The District identified several secondary impacts that would be temporary in nature since they would occur while the project is being constructed. One is the use of a barge facility, primarily at Jewfish Creek, where the anchoring of the barge may result in temporary impacts to seagrass during construction. This impact is addressed by a component of the seagrass mitigation at Boca Chica, discussed below. Another impact is turbidity associated with the dredge and fill and the barge activities. That issue is appropriately addressed by permit conditions, through the use of turbidity control screens and other techniques. The District also identified secondary impacts directly associated with the project footprint that would be permanent in nature. The removal of the exotic vegetation potentially opens up the areas adjacent to the road north of the C-111 canal to off-road vehicles or four-wheel driving and the potential impacts caused by those vehicles. That impact is appropriately addressed by fencing north of the C-111 canal. When a road is widened, animals have a greater distance to travel back and forth from one side of the road to the other. A wider road exposes such animals to greater risk of being hit by a motor vehicle while crossing the road. That impact is addressed in this project by the fencing, the wildlife crossings, and the wildlife box culverts. The crossings are designed for large mammals and some species, such as the Indigo snake, will likely not use these crossings. The wildlife crossings will not entirely mimic the crossing patterns of all wildlife that need to cross U.S. 1 and will result in some wildlife habitat fragmentation. The fencing that will be erected to funnel wildlife through the crossings will fragment the habitat of some species by altering wildlife crossing patterns and blocking access of some species to certain areas of habitat. The greater weight of the evidence established that any habitat fragmentation should, when compared to existing conditions, be minimal. The District appropriately evaluated the advantages and disadvantages of using wildlife crossing and hydrological culverts and appropriately concluded that there would be a net benefit to wildlife as a result of their construction. The District properly concluded that the culverts, bridges and fencing located south of the C-111 canal, construction of wildlife crossings and fencing north of the C- 111 canal, construction of the hydrologic culverts, and removal of the Lake Surprise Causeway are positive secondary benefits of the project. These benefits should be considered when applying the public interest test. THE FKAA PIPELINE RELOCATION The project requires the relocation of two segments of the existing pipe owned by the Florida Keys Aqueduct Authority (FKAA) around Jewfish Creek Bridge. The segments total approximately 1.5 miles. The District inspected the area where the pipeline will be relocated to assist in determining its impact. The pipeline relocation is a temporary disturbance during construction. It is a small linear facility, which will not generate pollution in and of itself. The pipeline relocation is not expected to result in a violation of State water quality standards. The FKAA is responsible for obtaining the necessary permits for the relocation. Direct impacts to wetlands will occur in a 4 to 5 foot wide strip along the length of the relocated aqueduct. The FKAA has submitted a permit application to the DEP for a permit to relocate the aqueduct. DEP believes that adequate mitigation can be achieved to make the project permittable. Once the FKAA submits an adequate mitigation plan, then relocation of the aqueduct will not be an adverse secondary impact caused by the U.S. 1 project. The permit for the subject project should contain a condition that the FKAA obtain a permit for the relocation of these two segments of its pipeline. THE C-111 BOAT RAMP There is an existing boat ramp designed for small boats to access District canals that is located on the north side of the C-111 canal. As a result of the proposed project, it will be relocated to the southern side of the project. This relocation is a relatively minor project requiring a cut in the canal bank and a fourteen-foot wide slab for the boat ramp. When the District considered the potential impacts associated with this relocation in conjunction with the impact of the proposed project, it was determined to be a relatively insignificant impact in terms of the project as a whole. Relocation of the boat ramp is not expected to result in a violation of state water quality standards. All direct, cumulative, and secondary impacts, whether positive or negative, should be considered in balancing the public interest test. ARE THERE ADDITIONAL SECONDARY AND CUMULATIVE IMPACTS Petitioners assert that there are additional cumulative and secondary impacts that the District failed to consider. Petitioners argue that the project cannot meet permitting criteria if those additional impacts are considered. The additional impacts pertain to additional development throughout Monroe County because of the “rate of growth ordinance” (ROGO), additional development along the project corridor, impacts to the coral reefs of the Keys, impacts to Key Deer, generalized impacts, and impacts from increased number of “day trippers." For the reasons discussed below, it is found that the District has considered all appropriate direct, secondary, and cumulative impacts of the project. The additional impacts that Petitioners assert should have been considered are not causally connected or directly linked to the project. THE RATE OF GROWTH ORDINANCE Monroe County adopted its Year 2010 Comprehensive Plan (the "Plan") to meet the requirements of Chapter 163, F.S. The Plan, adopted May 15, 1993, is unusual in that the County limits future growth based on a carrying capacity analysis of its hurricane evacuation clearance time. No other jurisdiction in Florida, and few others in the United States, have used a carrying capacity planning approach. To implement the carrying capacity limitation, Monroe County determined the total number of dwelling units that could be permitted while maintaining an acceptable hurricane evacuation clearance time of 24 hours. This number of dwelling units, less an allowance for vested development and development in municipalities, was the basis for a ROGO that was adopted by the County in 1992. The ROGO allocates the available units at a uniform annual rate of growth (currently, 255 units per year). The ROGO regulates all proposed new residential buildings, including hotels, motels, and other transient tourist accommodations as well as permanent residences. The number of building permits that Monroe County can issue is, at present, directly related to how rapidly the County can be evacuated in the event of a hurricane. The lower the clearance time, the greater the number of permits that can be issued. The Comprehensive Plan requires that the County be able to evacuate within a 24-hour period. As of March 7, 1995, the hurricane evacuation time for Monroe County was determined to be 21.25 hours.1 The project is expected to reduce by six or seven hours the modeled hurricane evacuation capacity for Monroe County, regardless of whether it consists of three or four lanes. This is because both the three lane and four lane plans provide for two northbound lanes. Because of the rate of growth provisions in county law, this reduction of clearance times results directly in an increase in the number of building permits that the county can issue annually. Under ROGO, Monroe County can, with this project, issue 255 permits each year through the year 2026. Without this project, Monroe County can issue 255 permits each year only through the year 2001. Alternatively, without this project, the county can issue 88 permits each year through the year 2010 if it chooses to issue permits over a longer period of time. Following extensive litigation before the Division of Administrative Hearings in an unrelated proceeding2, the Administration Commission entered a final order on December 12, 1995, that approved approximately 97 percent of the Plan. In addition, the Administration Commission has published a proposed rule to bring the remainder of the Plan into compliance and assure its financial feasibility. The central feature of the proposed rule is a five- year work program, with annual reviews by the Administration Commission. It is likely that the proposed rule will eventually result in the complete revision of the ROGO. The proposed rule provides that Monroe County's annual rate of growth be revised within five years, no later than December 31, 2001, "to establish a rate of growth and a set of development standards that ensure that any and all new development does not exceed the capacity of the county's environment and marine systems." A carrying capacity study will comprehensively assess water quality, habitat protection, and public facility issues to determine the capacity of the Keys to sustain further development. The proposed project is but one of many factors that will be considered in future rate of growth regulations. If the expected revisions occur, it would be speculative to predict what development would be allowed. While the studies are underway the rate of growth will remain at 255 units per year. The rate of growth will be reviewed annually, and may be reduced a minimum of 20% if the goals of the studies are not being met. The DCA has determined that Monroe County’s Comprehensive Plan and its land development regulations are sufficient to prevent or mitigate any potential adverse secondary impacts of the project caused by development. The DCA has consistently supported the proposed project, even in its earlier four-lane configuration, because it was consistent with Monroe County's 1986 Comprehensive Plan, and because the project would improve hurricane evacuation clearance times and improve water quality in the vicinity of the roadway. The 1986 plan supported widening of the roadway to four lanes based on projected travel demand. The DCA prefers the current, three-lane proposal to the earlier four-lane. On September 7, 1995, the Monroe County Commission adopted Resolution 315-1995 in support of the proposed project because "it balances the needs for a widened highway with safeguards designed to address secondary impacts." Lorenzo Aghemo, an expert in comprehensive planning, served as Monroe County Planning Director during the development of the Plan and ROGO. In Mr. Aghemo's opinion, the widening of the roadway to either three or four lanes would generate minimal growth pressure in Monroe County, particularly because the Plan limits the rate of growth. Because the Keys are designated by Section 380.0552, F.S., as an area of critical state concern, the DCA is charged with oversight of Monroe County's Comprehensive Plan, its LDRs, and all development that takes place in Monroe County. Additionally, the Administration Commission may amend Monroe County's plan or regulations by rule (See Section 380.0552(9), F.S.). There is virtually no action that Monroe County can take related to the use of land without review and approval of a state agency. The Administration Commission’s proposed rule demonstrates its intent to revise comprehensively Monroe County's ROGO within five years to ensure that future development does not exceed the capacity of the Keys' environmental resources. It also demonstrates the Administration Commission's intention to closely monitor growth and development in the Keys during the five-year study period. Some of the studies required by the proposed rule are already underway: 1) the DCA has entered into a contract with the ACOE to complete the environmental carrying capacity study; 2) the HRS study of advanced on-site waste water treatment systems is underway; 3) Monroe County is developing the required Marathon central sewer facilities plan; and 4) Monroe County and HRS have begun the cesspit identification and elimination process. Caution should be exercised in relying on this or on any other proposed rule. Likewise, caution should be exercised in relying on changes to ROGO that may or may not occur. It is likely that the present status of the law will be changed in the near future so that future development will be based on environmental carrying capacity as opposed to hurricane evacuation clearance times. However, for the purposes of this proceeding the District should accept the fact that the issuance of future building permits is closely linked and causally related to the project. Consequently, it is found that under the present status of the law, the issuance of additional building permits in Monroe County is closely linked or causally related to the project. MONROE COUNTY LDRS AND DCA OVERSIGHT Although Petitioners established that there is a causal relation between the project and the existing status of the law governing the number of building permits that can issued in the future, the evidence was insufficient to establish at a level above speculation that adverse environmental impacts will result because of the issuance of those building permits. The Monroe County Comprehensive Plan contains land development regulations that govern all development in Monroe County. These regulations are among the most stringent in the State and are designed to avoid or minimize adverse environmental impacts caused by development. All development orders in Monroe County are closely scrutinized by the Department of Community Affairs to ensure compliance with applicable permitting criteria. Those regulations and the DCA’s close scrutiny are intervening factors that break any causal relation between the project and the speculative adverse environmental impacts that the Petitioners assert will be caused by future issuance of building permits by Monroe County. Petitioners failed to establish that the impacts of future development are very closely linked or causally related to the project. Consequently, it is found that such impacts are not secondary or cumulative impacts of the project. DEVELOPMENT ALONG THE PROJECT CORRIDOR A major portion of the area next to the road has little or no development potential because it is either water, land in public ownership, or land slated for public ownership. The areas east of the road are mostly in private ownership, but are primarily submerged lands and mangrove areas. The Crocodile Lakes National Wildlife Refuge is federally owned and is managed by the U.S. Fish and Wildlife Service (USFWS). The Southern Glades lands, located immediately west of the project and Everglades National Park (ENP) in Dade County, have been acquired by the District and are managed by the Florida Game and Freshwater fish Commission (FGFWFC). The Model Lands Basin in Dade County is in private ownership but proposed for public acquisition in the future. The land adjoining the roadway in Dade County is designated as open area or environmentally sensitive. Almost half of the land along Monroe County's portion of the roadway is in public ownership. At least 90% of the land in private ownership is mangroves or wetlands that cannot be developed. The small area of uplands is currently being used by a resort marina which will not be allowed to develop further under the new comprehensive plan. There is very little potential for future development in the project area. The comprehensive plan designation for areas in Dade County are open space, and the ones in Monroe County have the conservation designation. The District's regulatory programs consider areas adjacent to the project as sensitive wetland habitats. Based on the District's regulatory authority and comprehensive plan designation for those lands, which would have to be obtained prior to obtaining a permit for development, it is very unlikely that those lands could be developed. Florida Rock and Sand Co. (FRS) has a permit to mine approximately 1,100 acres of wetlands. As part of its mitigation program, FRS will donate this land to the District once its mining and mitigation projects are complete. The FRS mitigation lands are preserved as a permit condition and will ultimately be transferred to the District. This land will not be developed. In addition, the District established that the U.S. 1 project and the FRS project do not constitute a cumulative impact that the District failed to consider. The evidence established that development along the project corridor will not be a secondary or cumulative impact of the project. IMPACTS ON CORAL REEF SYSTEM The evidence was insufficient to establish a close link or causal connection between the project and the coral reef system. As reflected elsewhere, it is found that there will be no degradation of ambient water quality as a result of the project. Therefore, there is no need to resolve the conflicting testimony as to the present status of the coral reef system. IMPACT ON KEY DEER There are no key deer in the project area. The nearest key deer habitat, Big Pine Key, is approximately 70 miles from the southern terminus of the project. The evidence is insufficient to establish that there is a very closely linked and causally related connection between the project and key deer mortality on Big Pine Key. GENERALIZED IMPACTS The Petitioners presented certain opinion testimony that the Keys cannot be developed in an environmentally sensitive manner because of potential adverse impacts of new development in Monroe County, or new boats operating in the waters of the Florida Keys. The credibility of that testimony need not be evaluated because the evidence was not sufficient to tie those generalized concerns into the specific regulatory criteria of the permitting agency. There was insufficient evidence to establish that those alleged impacts would be very closely linked or causally related to the proposed project. DAY TRIPPERS Induced demand is new travel that occurs solely because additional capacity is added to a highway. Petitioners' transportation experts, Michael Replogle and Robert Morris, testified that FDOT's traffic studies, and FDOT's projected rate of traffic growth of approximately 3 percent annually, are incorrect because the studies do not predict the amount of "induced demand" that would result from the proposed project. Petitioners assert that induced demand would generate an unknown number of people who drive to the Keys for the day from south Dade County, referred to as “day trippers,” will have an impact on the Keys that has not been evaluated. The assertion that this potential impact has not been analyzed is rejected as being contrary to the greater weight of the evidence. Induced demand is accounted for in Monroe County's Long Range Transportation Plan, which was never evaluated by Mr. Replogle or Mr. Morris. The Long Range Transportation Plan was prepared by an experienced traffic engineering consulting firm, Barton-Aschman, using an FDOT- approved traffic demand model, the FSUTMS model, that includes all traffic generators and attractors, and all travel on U.S. 1 on weekdays and weekends. The FSUTMS model does not restrict demand based on the existing road capacity. The model uses an "unrestrained assignment" that incorporates the total predicted trip generation on recreational facilities, hotels, and all other attractors. The Long Range Traffic Plan was used to develop the Monroe County Comprehensive Plan, which takes into consideration the projected increases in traffic and makes appropriate provisions for those increases. FDOT has provided reasonable assurances that it has properly projected the amount of traffic for the project corridor after the project is completed and that the projected increases have been appropriately addressed by Monroe County's Comprehensive Plan. MITIGATION - IN GENERAL For the reasons discussed above, it is found that there are no secondary or cumulative impacts that the District failed to consider. Petitioners also contend that the mitigation proposal is insufficient to offset the direct and secondary impacts recognized by the District. This is a large dredge and fill project that will permanently fill 149 acres of wetlands. The wetlands that will be adversely impacted by the project include OFWs that provide a great variety of functions and serve as habitat for fish and wildlife, including threatened and endangered species. The wetlands are unique and of high quality. Mitigation for direct, secondary and cumulative impacts was considered as part of the permit evaluation. In- kind mitigation is considered to be most effective, but out- of-kind mitigation may be offered by the applicant where it is impractical to conduct in-kind mitigation due to historic changes in the project area or sensitivity of the habitat type for which mitigation is offered. Such mitigation is also appropriate to address regional alteration of an ecosystem, such as the Everglades ecosystem alteration caused by the original roadway embankment. FDOT developed a conceptual mitigation plan that took into account project impacts on the freshwater, marine and estuarine components of the ecosystems involved, as well as the impacts on threatened and endangered species of wildlife which may be affected by the project. FDOT coordinated the plan's development with the National Parks Service, U.S. Fish and Wildlife Service, the Army Corps of Engineers, the National Marine Fisheries Service, the U.S. Environmental Protection Agency, the Dade County Department of Environmental Resources Management, the Florida Game and Fresh Water Fish Commission, and the Florida Department of Environmental Protection. The conceptual mitigation plan evolved as a result of project modifications and agency comments into what is now proposed as mitigation for the project. The current proposal is summarized in FDOT Exhibit 26, consisting of Attachment H to FDOT's SWM and WRM permit applications. The timing of their construction falls into two general categories: mitigation previously permitted and concurrent mitigation. UPFRONT MITIGATION Typically, mitigation is done concurrently with project construction rather than prior to permit issuance. Mitigation is often done afterwards because of construction timing constraints. Here, FDOT applied for and, in May 1994 received, permits to conduct mitigation prior to applying for the permits at issue, with the understanding that performance of these activities does not require the District to issue permits for the proposed projects. A total of 385.22 acres of mitigation has already been completed. The applicant received 203.02 mitigation credits from the District on May 12, 1994, for several mitigation projects that the applicant proposes to apply to the proposed U.S. 1 widening project provided it is approved. Table 2 of Attachment H to FDOT Exhibit 26 sets forth the four mitigation projects that constitutes the up- front portion of the mitigation for the project. This table sets forth the acres mitigated, the conversion factor for the mitigation, and the resulting mitigation credit awarded. The four mitigation activities already authorized are: enhancement of the wetland habitat in the Harrison Tract located adjacent to Barnes Sound within the Crocodile Lakes National Wildlife Refuge on the north end of Key Largo (70.37 acres credit for 252.6 acres of restoration); removal of the spoil mounds on the eastern bank of the C-111 canal east of U.S. 1 located on the District’s ROW (10.65 acres credit); the back filling of the C-109 canal levee located on the District ROW within the Southern Glades Save Our River project (112.7 acres credit); and the removal of the roadside spoil mounds on the west side of U.S. 1 located between C-111 and the Dade Work Camp Road within the District’s Southern Glades Save Our Rivers Project (9.30 acres credit). The mitigation projects pertaining to the roadside spoil removal along U.S. 1, the backfill of the C-109 Canal, and the removal of spoil along the C-111 Canal are similar projects because they each involve existing deep ditches cut through wetlands. When these deep ditches were cut, the spoil material from the ditch was deposited alongside the ditch. This resulted in areas that were previously Everglades wetlands becoming spoil, supporting the growth of exotic species and, for the most part, not exhibiting wetland functions. FDOT is proceeding with the backfilling the C-109 canal located between mile markers 122.5 and 117, and removal of the corresponding spoil mounds created during construction of the C-109 canal. In connection with this mitigation, marsh areas, tree islands and deep water aquatic refugia have been restored. In this area, there has been considerable attraction of wildlife subsequent to restoration, including otters, alligators, and turtles, which could not previously use the habitat because the canal was too deep. Upon completion waterflow between the east and the west will be restored, and the area will be restored to a wetland habitat from its current uplands habitat type. Backfilling of the C-109 canal is part of an interagency effort with the ACOE to restore as closely as possible to natural conditions the flow of water in the C-111 watershed area. C-111 mitigation includes removal of roadside spoil along the C-111 canal to restore the natural condition of the area. The mitigation was devised in coordination with the National Maine Fisheries Service (NMFS), which required mitigation for non-vegetated habitat types. Restoration also includes preserving some spoil areas as islands to maintain habitat for endangered species of plants. When the C-111 spoil mounds are scraped down, the fill will not fill the whole ditch. The ditch will, therefore, be a bit more valuable but will not be completely restored to its former elevation. FDOT will also remove roadside spoil along the west side of U.S. 1, upon which exotic species of plants had grown, and returning the area to its original grade. The Harrison Tract is a known habitat and nesting area for American crocodiles. Its wetlands functions were altered or eliminated by prior development of the land by its original owners. Restoration includes regrading the area to restore its original wetlands functions, including habitat for young and adult crocodiles. FDOT's mitigation of the Harrison Tract also includes restoration of tidal flushing to increase contributions of nutrients and food sources to the surrounding tidal bay system. Crocodiles have been observed using the restored areas. FDOT has installed additional nesting berm habitat, basking habitat and shallow lagoon habitat to promote juvenile crocodile development. The District established that the credit awarded for this mitigation and the conversion ratios utilized for determining this credit were consistent with agency practice and its pertinent rules. FDOT was given a 1:1 credit ratio for areas involving full restoration of wetlands. In other portions of the Harrison Tract mitigation involving restoration of flushing to existing wetlands, FDOT was given not full credit, but credit based on the severity of limitation of the existing wetland functions. Based on this evaluation, mitigation credits were given in a range of a 3:1 ratio for restoration of severely disrupted or non-existent wetlands to a 20:1 ration for restoration of higher quality but not fully functional wetlands. FDOT is being awarded 70 mitigation credits for the 252 acres in the Harrison Tract that are being restored or enhanced. CONCURRENT MITIGATION Based on the mitigation ratios developed by the District, additional mitigation credits were required. Consequently, the project contemplates mitigation that will be undertaken concurrently with the construction of the project in addition to the upfront mitigation. FDOT proposes to earn these additional credits by projects involving creation and/or restoration of emergent vegetation, mangrove and seagrass habitats. FDOT’s proposal to mitigate mangrove impacts with "out of kind" mitigation of emergent vegetation habitats was viewed by the District as being necessary and appropriate because there were no sufficiently large areas of mangrove habitat suitable for restoration. Table 7 of Attachment H to FDOT Exhibit 26 sets forth the four mitigation projects that constitutes the concurrent portion of the mitigation for the project. This table sets forth the acres mitigated, the conversion factor for the mitigation, and the resulting mitigation credit awarded. In addition, the table references certain credit for the placement of the hydrological culverts. As will be discussed later, that credit was withdrawn at the formal hearing. The four mitigation activities that will constitute the concurrent portion of the mitigation plan are: the removal of the Lake Surprise causeway (2.90 acres credit); the scrape down of the Jewfish Bridge approaches (0.67 acres credit); the restoration of the FGFWFC road (10.34 acres credit); and the Boca Chica project (27.17 acres credit) The Lake Surprise Causeway removal mitigation involves 5.26 acres of on-site seagrass restoration and 0.54 acres of unvegetated bottom mitigation through the excavation of 52,220 cubic yards of material. Lake Surprise historically was a shallow tidal lake supporting seagrasses before a causeway was built across the lake over the seagrasses. FDOT proposes to remove the causeway and restore the previous elevation, after which it is anticipated that seagrasses that grow on the east side of the causeway will fully recruit naturally to the excavated area. Removing the Lake Surprise Causeway will establish 5.26 acres of seagrass, for which FDOT received 2.63 acres of on-site mitigation credit based on a 2:1 ratio. Through natural recruitment after removal of the causeway, there is a high likelihood that the entire 5.26 acres will recolonize with seagrass. FDOT minimized the seagrass impacts to the greatest extent possible. The mitigation credit pertaining to Lake Surprise does not include credit for the removal of the causeway itself. This awarded credit is for the restoration of seagrass areas. The mitigation pertaining to the Jewfish Creek Bridge approaches proposes the scrape down of 1.33 acres of existing fill to allow the area to become recolonized with mangroves. Boca Chica is located in southern Monroe County over one hundred miles from the southern terminus of the project. This site was chosen by FDOT as a site for seagrass mitigation project after FDOT reviewed several other potential sites. Two other sites were rejected. The area around the C- 111 canal was rejected because the land proposed for use was in private ownership. Several defunct marinas in Port Bougainville were rejected due to poor conditions not conducive to seagrass growth. Boca Chica was finally chosen as the site because it was a large enough area with light and hydrological flow conditions conducive to seagrass growth. The evidence establishes that the Boca Chica site is the most viable for seagrass mitigation. The seagrasses to be impacted at Lake Surprise are healthy and productive turtle grass, manatee grass and cuban shoalgrass. Turtle grass is considered an extremely valuable “climax community” of seagrasses which hold sediments in place, cleanse water quality, and forms the base of the food chain. It is valuable to sea turtles, manatees and recreationally important fish and shellfish. The cuban shoalgrass that will colonize at Boca Chica is a pioneer colonizer species that grows in disturbed areas. It is not as valuable to the marine system as turtle grass. The Boca Chica seagrass mitigation permit condition proposed to offset impacts to 11.27 acres of seagrass. This will involve the removal of 306 cubic yards of sediment and hydraulically dredging approximately 1,175 cubic yards of spoil material. The proposed permit conditions state that FDOT shall provide future maintenance of the culvert areas to maintain adequate flushing. FDOT will plant 25.92 acres of seagrasses to mitigate for the remaining 8.64 acres of impacts, for a mitigation ratio of 3:1. In addition, 8.46 acres of seagrass will be planted to mitigate for the barren bottom area that will be affected, and 1.62 additional acres will be planted to compensate for any unexpected impacts to Boca Chica based on the necessary improvements. Overall, there will be of 36 acres of seagrass mitigation by FDOT, for which FDOT is receiving 27.17 acres credit. FDOT will also increase the water flow between the east and west lagoons of Boca Chica, and maintain the culverts connecting the two sides, in order to further promote growth of seagrass therein. FDOT is responsible for 80% survival of each acre of seagrass mitigation, as well as monitoring once a year for five years. Based on historical data obtained from Boca Chica during past mitigation efforts, there is a high likelihood that the entire 36 acres of mitigation will survive, and that the remaining 74 acres of the Boca Chica lagoons will experience natural recruitment of seagrass as a result of FDOT's efforts. The FGFWFC access area was built by excavating a ditch, and putting fill on the wetlands and creating a dirt road bed. After the C-109 canal is backfilled, the access road will no longer be needed. The mitigation project will excavate the existing road bed, back fill it into the ditch, thereby recreating the wetlands that were there previously. FDOT will receive 10.34 mitigation credits based on a 1:1 ratio of acres restored. EVALUATION OF MITIGATION There is no mitigation in this permit for any wetland impact beyond the direct loss of the specific 149 acres that will be dredged or filled. Mitigation was provided only for the direct, footprint impacts of the project. None of the up front mitigation involves the creation of wetlands, which entails converting areas that were not previously wetlands or open water and turning them into wetlands. It will likely take between 20 and 50 years for the mitigation areas to achieve full functional value required by the South Florida Water Management District mitigation permit. In the interim, there will be a net loss of wetland functional value. With time, the proposed mitigation has a high likelihood of success. Based on FDOT's past successes in mitigation of construction-related impacts, FDOT is able to comply with permit conditions relating to best management practices associated with the construction of bridges and pilings and turbidity screens around road construction, as well as restoration of seagrasses and mangroves. Petitioners assert that the District erred in determining the credit to be given for the up-front portion of the mitigation. While it is true that the SFWMD Rules do not mention "up-front" mitigation, the District has the authority to consider all aspects of a mitigation project in weighing its relative value. Consulting engineering inspectors have been retained by FDOT to insure that all permitting requirements are met during mitigation and construction, and that the technical special provisions for protection of threatened and endangered species are complied with by FDOT. The proposed permits contain appropriate conditions that require FDOT to monitor and maintain the mitigation areas. FDOT will be responsible in perpetuity for maintaining the tidal flushing connection at the Boca Chica mitigation site. Special permit condition 6 to the SWM and WRM staff reports require wetland and upland monitoring. If wetland and upland monitoring or other information demonstrate that additional adverse impacts have occurred due to this project, FDOT would be required to offset the loss of any additional wetland impacts. MITIGATION IS APPROPRIATE The evidence established that the mitigation projects were fairly and appropriately reviewed by SFWMD and that the mitigation credits were fairly and appropriately awarded. The evidence also established that there is appropriate mitigation for the direct, secondary, and cumulative impacts of this project. ACTIVITIES NOT RECEIVING MITIGATION CREDIT Mitigation credits for the 25 hydrologic culverts north of C-111 were originally included in the permit staff reports. Those mitigation credits were removed in an addendum to the staff reports, introduced as District's Exhibits 5 and 6. These credits were not necessary to offset project impacts. After the staff report was issued, they became a point of contention by the Petitioners because they will not be utilized until a management plan is developed. Since they were not necessary to meet mitigation requirements, the credits were removed from this project. These credits were never included in the mitigation ratios for these permit applications. The addendum removed the 9.6 credits initially contemplated for the culverts. No credit has been awarded for the relocation of threatened and endangered species of plants, such as Joewood and Bay Cedar by FDOT from the C-111, C-109 and roadside spoil mitigation areas. These species have been relocated to tree islands constructed by FDOT on the mitigation sites, or to other areas that would not be impacted by the project. FDOT also was not given mitigation credits for: (1) the wildlife crossings and the fencing that will funnel wildlife through these crossings; (2) installation of pipe culverts north of the C-111 canal and bridges and box culverts south of C-111; and which, in addition to providing a corridor for aquatic species, will increase the tidal flushing of the area; (3) the removal of the Lake Surprise Causeway, which will restore historical hydrological flow between the eastern and western sides of Lake Surprise; (4) FDOT's commitment to improve and maintain the flushing of the west lagoon culverts in Boca Chica (mitigation is in the east lagoon); and (5) FDOT's contribution of $300,000 to assist Monroe County in performing a carrying capacity study for the County. Additionally, FDOT will preserve the Jewfish Creek Bridge abutment, which will be preserved for local historical purposes. FDOT will prepare the Jewfish Creek Bridge pilings for an artificial reef at Long Key during construction. THE PUBLIC INTEREST TEST It is appropriate for the SWFMD to consider, in balancing the public interest test, to consider traffic safety and hurricane evacuation.3 Because of FDOT's expertise in those areas, it is appropriate for the permitting agency to give great weight to highway safety concerns, including hurricane evacuation, presented by FDOT. The application of the public interest test does not involve consideration of non-environmental factors other than those expressly set forth in the statutes such as navigation or preservation of historical or archaeological resources. Specifically, aesthetics, quality of life, the potential for a project to cause increased crime, and school overcrowding are not properly considered within any of the seven factors contained in Section 403.918(2)(a), Florida Statutes (1991). The District concluded that the project is clearly in the public interest based upon consideration and balancing of the following factors: hurricane evacuation improvements, public safety improvements, a SWM system where no SWM system currently exists; wildlife crossings and fencing north of the C-111 canal where no such crossings or fencing currently exist; wildlife box culverts to accommodate crocodiles, alligators, manatees and marine life where no such culverts currently exist; and hydrologic culverts, which have the potential to assist in the restoration of hydrologic flows, and the mitigation projects, both upfront and concurrent. SECTION 403.918(2)(a), FLORIDA STATUTES Section 403.918(2)(a), Florida Statutes, requires the permitting agency to determine “[w]hether the project will adversely affect the public health, safety, or welfare or the property of others." The property of others is not at issue. As discussed below, the evidence clearly established that the project will greatly enhance the safety of the road during normal operations and facilitate evacuation in the event of a hurricane. There will be clear benefits to the public safety as a result of this project. As part of the PD&E process, FDOT, through Metric, prepared "A Safety Evaluation" of the existing roadway. The safety analysis was based on FDOT accident statistics for the years 1983-1988, as well as engineering review of the conditions causing the accidents. Specifically, FDOT based their safety analysis on the following: 1) calculation of the abnormally high accident rate on the roadway based on the rate quality control formula set forth in the FDOT Highway Safety Improvement Guidelines, and approved by the Federal Highway Administration; 2) copies of the actual crash reports filed with the Florida Division of Highway Safety and Motor Vehicles, which provided detail greater than that generally available through FDOT's own accident data reports, and which formed the basis of the collision diagram in the Safety Evaluation (FDOT Exhibits 36; and 3) and its August 1996 update thereto (FDOT Exhibit 41), on-site evaluation and review of the roadway to determine geometrics of the roadway, locations of driveway accesses and side roadways and the degrees at which roadways intersected. Metric prepared an update of the Safety Evaluation for the years 1989-1994, to determine the continuing validity of the Safety Evaluation, as well as to review alternative proposals to the original proposed roadway configuration. In preparing the update, the recent accident data (FDOT Exhibit 37) and the underlying research in the Safety Evaluation were used by Metric Engineering in reaching its conclusions. The Safety Evaluation performed by Metric in 1989 established high accident rates on the roadway based on a detailed segmental analysis of the roadway. In August of 1996, the Safety Evaluation was updated by Metric, which update confirmed the findings of the Safety Evaluation, and further stated that accident frequency on the Monroe County portion of the roadway exceeded the state average accident rate and the abnormally high accident rate for the years 1990 through 1994 (notwithstanding the rear-end accidents occurring at Jewfish Creek). Fatal accidents on the Dade County portion exceed the state average on the same stretch by 37 percent for the same years. The most severe accidents occur on the Dade County portion. The Monroe County portion of the roadway exceeds the statewide average in the abnormally high accident rate four out of the last five years that FDOT studied. The Dade County portion does not exceed the accident frequency or the number of accidents, but the fatality rate in Dade County is much higher than the state average. Presently an abnormally high accident rate exists in three locations along the project corridor, two of which are in the vicinity of the Jewfish Creek bridge. The third location is north of the bridge on Cross Key. Replacing the Jewfish Creek Bridge with the fixed-height bridge proposed by FDOT will substantially increase the safety on the project corridor. The District considered this to be an important positive element in the public interest balancing test. The existing 2:1 slopes of the roadway make it difficult for drivers to recover from running off the roadway, resulting in a greater frequency of this type of accident. Moreover, the existing clear zone is not large enough to overcome the 2:1 slope to allow safe recovery of errant vehicles. As a result, catastrophic crashes occur rather than safe recoveries. Also, as with hurricane evacuation discussed in the following section, actual accidents on the roadway prevent traffic from accessing or leaving the Keys, and also prevent emergency vehicles from rapidly accessing the Keys and a crash site. This occurs because there is little or no shoulder or clear zone along the sides of the road to allow emergency vehicles to efficiently access an accident site, and in the event of a severe, head-on type collision, the roadway is blocked off. U.S. 1 through the project corridor is regarded as so unsafe for travel that Monroe County law enforcement officials call it "death alley." There are many head-on collisions due to the two-lane, no-median alignment. Law enforcement is difficult and dangerous along the roadway, because it has very few areas wide enough to allow law enforcement officials to detain driving violators. It is also very dangerous, for the same reasons, for a driver to pull off the roadway with a broken-down vehicle. High rates of speed and impaired drivers contribute to the accident rates along the project corridor. The efforts of law enforcement to control speeders and drunk drivers is impeded since it is practically impossible for enforcement officers to turn their vehicles around to pursue violators without running a high risk of causing an accident on their own. The project would significantly improve safety on the roadway by reversing the problems identified in the this section, as well as the previous sections of this Recommended Order. The project would virtually eliminate head-on collisions which largely contribute to serious injuries and fatalities along the roadway. The project would also help eliminate problems with emergency vehicle access to accident sites and restoration of service in the event of accidents, and would increase the roadway's level of service as discussed below. Improved level of service was an additional need considered by FDOT during the PD&E process. While the District did not consider the traffic level of service by itself to be weighted as part of the positive public interest criteria in this project, the impacts of resulting congestion are relevant to the public interest consideration of traffic safety as discussed in the foregoing sections. Lower quality level of service, as presently exists on the roadway through level of service F, adversely affects the safety of the roadway. When traffic levels rise, driver frustration increases leading to drivers passing in no-passing zones and potentially resulting in head-on collisions and high-severity accidents. Additionally, due to the narrow shoulders of the existing roadway, accident vehicles pose a threat to and impede normal traffic flow on the roadway. The Highway Capacity Manual set the standards for traffic engineering and is used in all fifty states. The manual classifies the existing roadway as a two-lane arterial rural road. Applying the standards for measuring level of service for two-lane rural roads set forth in the Highway Capacity Manual, FDOT determined that the existing level of service on the roadway is E, which is a very poor level of service that does not meet the established standard of level of service C required by the Highway Capacity Manual. Monroe County uses a speed based method of calculating level of service. Using that method, the level of service for U.S. 1 is at an acceptable level. The parties disagree as to which method of calculating the level of service is appropriate. That conflict is resolved by finding that the method used by FDOT is the appropriate method because of its wide acceptance and long-term use. Traffic volume in the area of the southern terminus of the project is growing at a rate average annual rate of 3.07 percent. In the present condition of the roadway, level of service will degrade to F, or forced-flow conditions, by the year 2006. Even with the improvements proposed by FDOT, the level of service in the northbound direction would improve to level of service B, but the level of service in the southbound direction would remain at level of service D or E due to the single southbound land configuration. Hurricanes pose a serious threat to the safety and welfare of residents and visitors of the Keys. Monroe County is the most vulnerable hurricane-prone area in the United States because it is surrounded by tropical waters, land elevation is low throughout the islands, and the evacuation routes are limited to U.S. 1, an extended route that starts in Key West and runs to the mainland, and Card Sound Road. The greatest potential for loss of life during a hurricane in the Keys is from storm surge. Storm surge is a dome of water near the center of a hurricane which is created by the winds on the water's surface. In a category 3, 4 or 5 storm, the entire land mass in the path of the storm will be inundated. Because of the wind and storm surge associated with hurricanes, the best response to a hurricane warning in the Keys is to evacuate people to the mainland away from the water and the storm surge threat. Accordingly, Monroe County orders a mandatory evacuation in a category 3, 4, or 5 hurricane, and no shelters are opened. There is little or no disagreement as to the vulnerability of the Keys to hurricanes or as to the danger posed by a hurricane. There is disagreement as to whether the proposed project is needed for improved hurricane evacuation. The conflicting evidence in this regard is resolved by the following findings, which are based on the more credible, substantial evidence. The existing road does not have sufficient hurricane evacuation capacity to meet the present and projected future needs of Monroe County residents and visitors. In current hurricane evacuations, the two northbound lanes on U.S. 1 between mile marker 90 and 106 are split at Key Largo. Sixty percent of the traffic is directed up the northbound lane of U.S. 1; forty percent of the traffic is diverted onto the northbound lane of Card Sound Road. One southbound lane of U.S. 1 and Card Sound Road must remain open for emergency vehicles to reach an accident or a disabled vehicle, or to bring emergency supplies into the Keys. Improving the roadway is critical to the success of Monroe County's hurricane evacuation plan. FDOT relied on hurricane evacuation and needs modeling performed by Monroe County and the ACOE to confirm the need for improvements. All of the models used indicated that the project corridor is the controlling roadway segment for improving hurricane evacuation of the Keys. Additionally, FDOT relied on the Lewis Report of January 15, 1993, a study commissioned by the Governor of Florida. Recommendation No. 17 of the Lewis report recommends that FDOT expedite the design and construction of the project, which is viewed as being critical for increasing the rate of emergency evacuation. Dr. Robert Sheets, former director of the National Hurricane Center, testified that the failure to make improvements to the roadway would be "unconscionable." Dr. Sheets and Billy Wagner, the Director of Emergency Management for Monroe County, presented very compelling and very persuasive testimony that this project is essential for hurricane evacuation purposes. The proposed project is the minimum transportation improvement that will achieve a significant improvement in evacuation safety and clearance time. With the present two- lane configuration and narrow shoulders, evacuating traffic would be halted completely by a vehicle breakdown or an accident blocking one lane. Replacement of the Jewfish Creek Bridge will also facilitate the hurricane evacuation need for the project. In addition to improving the rate of evacuation, the project will make an evacuation safer. Emergency personnel cannot reach accidents on the roadway during an evacuation because, in certain segments, no roadbed exists adjacent to the northbound lane. A second northbound lane and wider road shoulders would enable disabled vehicles to be serviced and removed from the highway. The proposed changes to the road would improve emergency vehicles' access to an accident scene. The elevation of the roadway at Lake Surprise is so low that it can be flooded easily by a storm. The proposed project would replace the existing muck bed of the roadway with more stable material. The existing roadway is subject to settling and washout during storm events, which reduce the safety of the roadway itself and reduce the evacuation capacity of the roadway. If washout occurs, moving equipment to the islands for recovery efforts following a hurricane will be difficult or impossible. The proposed project will prevent erosion and reduce the effects of storm surge and wave action on the road during a hurricane. When the project has been completed, three lanes of evacuating traffic, two lanes from U. S. 1 and a third from Card Sound Road, will converge at Florida City. Representatives of FDOT, the Monroe County Sheriff's Department, the Florida Department of Law Enforcement and Monroe County Emergency Management have planned to manage the northbound traffic when it reaches Florida City during an evacuation. Several feasible alternatives exist, but additional planning is needed to prevent a monumental bottleneck at the northern terminus of the project. While it is clear that this project will not resolve all problems that exist as to hurricane evacuation, it is also clear that this project is essential to improve hurricane evacuation. SECTION 403.918(2)(a)2, FLORIDA STATUTES Section 403.918(2)(a)2, Florida Statutes, requires the permitting agency to consider “[w]hether the project will adversely affect the conservation of fish and wildlife, including endangered species, or their habitats.” The District considered the effect of the direct loss of dredging and filling 149.07 acres of wetland. As set forth in previous sections, it is found that this loss will be offset by the mitigation. For use during construction of the project, FDOT will adhere to technical special provisions and special permit conditions 9 through 13 to protect manatees, crocodiles, alligators, indigo snakes, marine turtles, and valuable trees, palms and other wildlife, to minimize or preclude any impacts to those species. Additionally, any osprey nests around the Jewfish Creek Bridge area at the time of construction will be relocated by FDOT if necessary. As part of the development of the FEIS, as required by the Federal Highway Administration under the National Environmental Protection Act, FDOT obtained official letters of concurrence from the USFWS and NMFS that the project would cause no adverse impacts to endangered species under section 7 of the Endangered Species Act. That process also established the project's consistency with Florida Coastal Zone Management Program, as determined by the State Clearinghouse within the Office of the Governor, in coordination with DEP, the Department of National Resources and FGFWFC. The project also contains provisions to impact positively or enhance the conservation of fish and wildlife, including threatened or endangered species and their habitat, as described below. These were positive factors that further helped neutralize and offset the 149.07 acres of direct impacts. In addition, FDOT is required to evaluate the effectiveness of the fencing along the entire project corridor, discussed below, and report to the District on that effectiveness. If the District determines that the fencing could be more effective, it may require FDOT to implement those suggestions. South of the C-111 canal, construction of box culverts and bridges addresses impacts to the American crocodile, a listed endangered species. Problems were identified with placement of existing culverts, which did not provide enough clear space and which caused the crocodile to cross over the roadway rather than through the culvert. To address this problem, 15 larger box culverts and three bridges will be placed within the roadway. These provide the necessary clear space to allow the crocodile to safely pass under rather than over the road. The location of the box culverts was chosen by reviewing crocodile mortalities associated with road crossings. Placement of these box culverts and bridges will also improve the hydrological flow of water within the project area, provide a crossing area for manatees, and allow greater dispersal of the crocodile population throughout Florida Bay. Species expected to use these box culverts include aquatic and aquatic water dependent species in the area. They were primarily targeted for crocodiles, alligators, and manatees, but certain fishes, turtles, frogs and other species in the wetlands along the project corridor will utilize the culverts. The box culverts will have 100 feet of wingback fencing extending north and south of each culvert. The intent of the wingback fencing is to funnel wildlife into the box culverts. Intermittent or wingback fencing is appropriate south of the C-111 canal for two primary reasons. First, the animals which will be guided into the box culverts are aquatic dependent. The area south of the C-111 canal is primarily water, washed mangrove areas and tidal creeks. Crocodiles tend to move in tidal creeks. Second, it was not possible to ensure continuous fencing along all portions of the project south of the C-111 canal because there are existing businesses. It could not be assured that these businesses would keep a gate closed. The project originally proposed continuous fencing alongside the road where it abuts ENP. Continuous fencing was initially proposed because the initial application included a solid concrete barrier down the median of the road. If a crocodile did enter the road from the side with discontinuous fencing, after crossing one lane the crocodile would hit the barrier, but then easily find its way back to the area it came from. However, the project was later modified to include a tri-beam barrier because it lessens the footprint of the project and thereby lessens the wetland impact. Since the current application does not include a continuous barrier down the middle of the road, if a crocodile enters the road it would cross the tri-beam barrier, go across another lane of roadway before hitting a continuous fence. The animal would then run up and down that fence with nowhere to go except back across the road again. This would increase their exposure to a road kill. With the installation of bridges and culverts along the southern portions of the project corridor, there is no need for continuous fencing because aquatic wildlife, such as the American crocodile, will tend to follow the flow of water through the culverts rather than climb over the roadway. The FGFWFC and ENP oppose continuous fencing and prefer intermittent fencing south of C-111 canal since the project now includes a tri-beam barrier. Positive benefits also include construction of panther crossings at four locations north of the C-111 canal to account for impacts to the Florida panther, a listed endangered species, in the vicinity of the project, along with continuous fencing on both sides of the road north of the C- 111 canal. The crossings will be placed at locations that show historical use by wildlife, including areas at the Dade County Correctional Institute access roadway, the water control structure on the C-109 canal, and the berm of the C- 111 canal. The wildlife crossings are indicated by blue dots on FDOT's Exhibit 1. FDOT underwent years of extensive coordination with the environmental regulatory and resource agencies to design a project that would accommodate their ecosystem management plans. The location of the wildlife crossings was based upon radio telemetry data, collected from radio-collared panthers, and their typical corridor movement. The location was further chosen based on input from the USFWS and the FGFWFC. The continuous fencing north of the C-111 canal will prevent wildlife from crossing the road, and instead force them to use the wildlife crossings. The crossings were designed for panther use, the panthers being the shyest animal in the area. If panthers can be accommodated, then other threatened and endangered species and other wildlife are expected to use them. DOT studies of the effectiveness of wildlife crossings, with fencing, including crossings installed on Alligator Alley, establish that wildlife will use the crossings, both singly and in groups, and that the crossings substantially reduce, if not eliminate, automobile- related mortality of wildlife. Documented wildlife include panthers, wild turkeys, wading birds, alligators, deer, bobcats, black bears and raccoons. SECTION 403.918(2)(a)3, FLORIDA STATUES Section 403.918(2)(a)3, Florida Statutes, requires the permitting agency to consider “[w]hether the project will adversely affect navigation or the flow of water or cause harmful erosion or shoaling.” The replacement of the bascule bridge at Jewfish Creek with a 65-foot high fixed-height bridge will be a benefit to navigation. Because Jewfish Creek is part of the intracoastal waterway, the existing bridge has to be frequently raised or lowered to accommodate marine traffic. Because of the age of the existing structure, frequent breakdowns have been experienced. Marine traffic is stopped or delayed if the bridge cannot be raised or if there is a delay in raising the bridge. Vehicular traffic is stopped while the bridge is raised. Regarding the flow of water, the project incorporates wildlife box culverts and bridges, which will improve tidal flushing and the flow of water south of the C- 111 canal. The District considered this to be a positive consideration under the public interest test. The 25 hydrologic culverts north of the C-111 canal were also a positive factor in the test because the culverts provide future water management capability. Erosion and shoaling are neutral factors in the public interest test because the permit conditions contain a plan to control erosion and shoaling during construction and to provide for road stabilization after construction. In addition, there is a positive factor regarding shoaling in that the roadway area now has a lot of storm action, causing problems with erosion on the side of the road. The project provides for road stabilization, which is a neutral to positive factor in the public interest test. SECTION 403.918(2)(a)4, FLORIDA STATUTES Section 403.918(2)(a)4, Florida Statutes, requires the permitting agency to consider “[w]hether the project will adversely affect the fishing or recreational values or marine productivity of the project.” A positive factor pertaining to marine productivity is the box culverts and bridges south of C-111, which will allow marine species to travel beneath the road to access the water on both sides of the road. Removal of the causeway along Lake Surprise opens that water body back up to one contiguous system, which is also a positive factor. The seagrass mitigation addressed in previous sections will also improve marine productivity and provide habitat for fish. SECTION 403.918(2)(a)5, FLORIDA STATUTES Section 403.918(2)(a)5, Florida Statutes, requires the permitting agency to consider “[w]hether the project will be of a temporary or permanent nature.” The project is permanent, though some construction impacts are temporary in nature. Once temporary impacts have ended and the project is complete, the project will be a positive benefit, because of the construction of the SWM system, culverts, animal underpasses and other benefits as set forth above. SECTION 403.918(2)(a)6, FLORIDA STATUTES Section 403.918(2)(a)6, Florida Statutes, requires the permitting agency to consider “[w]hether the project will adversely affect or will enhance significant historical and archaeological resources under the provisions of s. 267.061.” This factor is not at issue. SECTION 403.918(2)(a)7, FLORIDA STATUTES Section 403.918(2)(a)7, Florida Statutes, requires the permitting agency to consider “[t]he current condition and relative value of functions being performed by areas affected by the proposed activity.” A percentage of wetlands immediately adjacent to the road are impacted by exotic vegetation. Areas further out are part of a significant wetland ecosystem and are considered high quality. This project contains an exotic control program within FDOT's right of way, which is a positive consideration in the public interest test. Wetlands are currently receiving untreated storm water, which runs off the road immediately into the adjacent wetlands and water bodies without treatment. The project will include a SWM system where none currently exists as is detailed in the previous sections. This is a positive factor in the public interest test. The direct impacts of the project on 149 acres of wetlands alongside the roadway is not as large or significant as the impact caused by placement of the original embankment and resulting cut off of the eastern and western portions of the Everglades north of the C-111 canal. Overall, the concurrent and upfront mitigation efforts of FDOT are of regional significance and benefit to Everglades ecosystem by helping to repair the damage caused by the original embankment. THE PROJECT IS CLEARLY IN THE PUBLIC INTEREST The District appropriately weighed all considerations in determining that the project is clearly in the public interest. The greater weight of the competent, credible evidence established that the project is clearly in the public interest. RIGHT OF WAY PERMIT APPLICATION The land encompassed by the ROW permit has been properly adopted as a "work" of the District, requiring District authorization via a ROW Permit Modification to FDOT. The District's real property interest in the C-111 ROW applicable to the ROW permit modification consists of both fee simple and easement interests. The evidence is clear that DOT's application for the permit modification was thoroughly reviewed by the District, consistent with the District's established ROW permit review process. The District presented uncontroverted evidence and expert testimony to establish by a preponderance of the evidence that issuance of the permit modification to FDOT is consistent with all applicable District statutes, rules and other criteria, including the District's conditions for issuance of ROW Permits set forth in Rule 40E-6.301, F.A.C. FBII offered no evidence or testimony to the contrary. FUTURE MODIFICATIONS Modifying the project at a later date to pave a second southbound lane would require a District ERP permit. The addition of impervious surface triggers the District's SWM jurisdiction in this regard. However, FDOT established that that it had no current plans for further widening. The permit conditions require secondary and cumulative impacts associated with the increased capacity be addressed in accordance with the rules and criteria in effect at the time of any application for future widening. In addition, the permits require that FDOT must comply with any more stringent water quality criteria in effect at the time of any future widening. MODIFICATIONS AT THE FINAL HEARING At the Final Hearing, the District issued an Addendum to Staff Report for each of the SWM and WRM permits. The amendments made non-substantive changes to the District's staff reports regarding fencing along the roadway, performance of a study of fencing on the roadway by FDOT, water quality sampling along the roadway, assignment of mitigation credits, and other technical changes in wording for purposes of clarification. The changes set forth in the District's Exhibits 5 and 6 do not create impacts to the environment beyond those addressed elsewhere herein.

Recommendation Based on the foregoing findings of fact and conclusions of law it is RECOMMENDED that the Governing Board of the South Florida Water Management District enter a Final Order that issues the three permits challenged in this proceeding (SWM Permit No. 940606-10, WRM Permit No. 9460606-2-D, and ROW Permit No. 2584) subject to the conditions contained in the staff reports on the SWM permit application and the WRM permit application and subject to the additional permit conditions reflected by District Exhibits 5 and 6 and by the Findings of Fact pertaining to the permit for the relocation of the FKAA pipe. DONE AND ENTERED this 11th day of April, 1997, in Tallahassee, Leon County, Florida. ___________________________________ CLAUDE B. ARRINGTON Administrative Law Judge Division of Administrative Hearings Hearings The DeSoto Building 1230 Apalachee Parkway Tallahassee, Florida 32399-3060 (904) 488-9675 SUNCOM 278-9675 Fax Filing (904) 921-6847 Filed with the Clerk of the Division of Administrative this 11th day of April, 1997.

Florida Laws (8) 120.5714.31203.02373.016373.046380.0552380.067.29
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CITY OF MIAMI AND DEPARTMENT OF ENVIRONMENTAL REGULATION vs. DEPARTMENT OF ENVIRONMENTAL REGULATION, 78-002183 (1978)
Division of Administrative Hearings, Florida Number: 78-002183 Latest Update: Oct. 04, 1979

Findings Of Fact In April, 1976, Petitioner City of Miami, Florida (hereinafter "City"), filed application with Respondent Department of Environmental Regulation (hereinafter DER), for a construction permit and water quality certification to fill submerged land which it owned in Biscayne Bay adjacent to the City's Bayfront Park. The proposed project, as finally developed, was described by DER as follows: The project would involve the filling of 2.06 acres of submerged land, owned by the City of Miami, in Biscayne Bay. A dock, varying in width from 15 to 45 feet, would be constructed adjacent to the bulkhead to provide temporary berthing space for 5 to 6 boats. Riprap would be placed waterward at the bulkhead and an artificial reef constructed next to the bulkhead/riprap. The stated purpose of the project by Petitioner in its letter of April 2, 1976, transmitting the application, was for the "redevelopment and eastward expansion of the present Bayfront Park." The application enclosed approval of the proposed project by the City Commission of the City of Miami and a biological assessment of the proposed construction by the Department of Natural Resources. (Exhibit 15) The project assessment by the Department of Natural Resources was set forth in a letter to the City, dated April 16, 1975, and was predicted upon an original proposal to fill some 6 acres of submerged land. The agency stated that the sparsely vegetated intertidal zone of the proposed fill area was of limited biological significance, but that filling open-water area would permanently remove it from the Biscayne Bay Aquatic Preserve, and that the cumulative effect of many such fill projects could have massive adverse biological effects on the preserve. It concluded that restoration of productive intertidal communities should be encouraged by the addition of sloping riprap along the face of the existing seawall. The Florida Game and Fresh Water Fish Commission contributed its views to the DER by a letter, dated July 14, 1976. It agreed that the area had limited biological productivity, but that filling it would result in permanent removal of open-water habitat from the preserve and set a precedent for similar projects. It therefore recommended that a permit not be issued. The Director of the Metropolitan Dade County Environmental Resources Management, by letter of July 12, 1978, also provided an evaluation of the application to DER. He and his staff found that the proposed construction represented the least amount of filling necessary to eliminate an existing shoreline configuration which served to trap a variety of floating debris, and would eliminate an aesthetically undesirable condition adjacent to the park by improving water circulation. It also stated that the low biological productivity of the area was due to the lack of a suitable habitat for the establishment of a viable benthic community, and that the proposed riprap and artificial reef should provide such a habitat and thus increase the productivity of the area. He stated that the proposed shoreline treatment would allow greater access to the Bay by the non-boating public and additional access to the park by boaters using the proposed dock area. Accordingly, that agency recommended approval of the permit subject to certain conditions as to the method of construction and the prevention of turbidity during the construction process. A further report of the Director, dated July 25, 1978, stated that an underwater survey of the proposed area showed a low diversity of benthic invertebrates and concluded that filling the area would not destroy a viable productive community, but would cover a sparsely populated, unproductive, barren mud bottom. (Exhibits 4-5, 12-13). The DER staff evaluation of the project, as contained in a report of Doctor Thomas L. Hart, agreed that the sparsely vegetated area which supported only small populations of various marine life would improve by the placement of riprap and an artificial reef by providing a habitat for a variety of invertebrates and protective cover for small fish. This report further found that filling the cove area would not destroy a productive marine community or produce a significant adverse water quality condition if proper techniques were used in the fill operation. Dr. Hart therefore concluded that the project met the requirements for a permit under Chapters 253 and 403, Florida Statutes. However, he concluded that the project would not qualify for an exemption under Section 258.165, Florida Statutes, the Biscayne Bay Aquatic Preserve Act. He found that placement of riprap for seawalls was required under that Act and any benefits derived from the construction of the artificial reef could not be used to justify filling the submerged land. He also stated in his report that elimination of the cove area to prevent the collection of debris was unnecessary since alternative means of removing the unsightly material could be developed. Dr. Hart therefore recommended that the permit application be denied. This recommendation was adopted by the DER in its Intent to Deny and Proposed Order of Denial issued to the City on October 27, 1978, which predicated its proposed denial on the inability of the City to demonstrate compliance with Section 258.165, Florida Statutes. (Exhibits 11, 17). The project will eliminate a cove created by the construction of Miamarina which is adjacent to the project area. The cove is bounded on its northern side by a 300 foot riprap revetment, on the western side by vertical sheet steel bulkhead fronting Bayfront Park, and on the eastern side by Biscayne Bay. A 1977 study of hydrodynamic factors affecting the area by an expert in oceanography and tide hydraulics showed that the cove was a "dead pocket" that, together with the adjacent riprap, collected floating debris in an eddy from lack of water circulation. He found that the debris, such as paper cups, old tires, and dead animals, and the like, was moved to the cove area by wind and that there was insufficient tidal action to flush it out of the area. He concluded that by redefining the shore to provide a straight line and extension of the outer bulkhead of the Miamarina to where it would meet the existing Bayfront Park bulkhead would provide maximum current velocity to move debris along the new bulkhead and eventually carry it into the Atlantic Ocean. He is of the opinion that any area of fill less than the 2.6 acres created by such a bulkhead would not sufficiently eliminate the existing problem of water circulation. Biological studies of the site by experts in the field show that it is a low area of biological productivity which is primarily attributable to turbidity of the waters and the silt-clay bottom which is anaerobic and receives stagnant material, thus providing degraded water quality and a poor habitat for the growth of plant and animal life. The proposed placement of riprap and the outside artificial reef below the low tide mark will provide places for attachment of marine organisms and an excellent refuge for a greatly increased variety of marine species. The marine organisms presently found in the area are much sparser than those in a normal area of the Bay. They are found mainly in the dredged mud bottom which is not considered to be a natural shoreline area. The collected debris at the site presents a serious maintenance problem for the City and engenders complaints from the public. Although greater than normal efforts are made to keep the area free of such litter, it is a continuing maintenance problem and detracts from the aesthetic value of the park and Biscayne Bay. (Testimony of Michel, Morrisey, Voss, Howard, Exhibits 1-3, 7-10, 14, 16). The proposed project is part of a comprehensive plan to enlarge and restore Bayfront Park to integrate its facilities in the environment, improve the appearance of the area, and increase use of the Bay. It is planned that an amphitheater, restaurant, and promenade will be constructed at the filled site sometime in the future. (Testimony of Ambruster) DER staff personnel who testified at the hearing agreed with the City's experts that the project site is not a natural condition and that conditions there are not conducive to the support of a large benthic population. They also agreed that the proposed construction has the potential for increasing biological productivity of the area. However, they were of the opinion that the project was unnecessary, would result in a loss of a portion of the Bay, and therefore was contrary to the intent of the Biscayne Bay Aquatic Preserve Act. (Testimony of Jones, McWilliams, Hart)

Recommendation That the application of the City of Miami, Florida for the requested permit be approved, subject to standard and customary conditions attached to the issuance of such a permit. DONE AND ORDERED in Tallahassee, Leon County, Florida, this day of 14th day of August, 1979. THOMAS C. OLDHAM Hearing Officer Division of Administrative Hearings 101 Collins Building 2009 Apalachee Parkway Tallahassee, Florida 32301 (904) 488-9675 COPIES FURNISHED: Randall E. Denker, Esq. Assistant General Counsel Department of Environmental Regulation 2600 Blair Stone Road Tallahassee, FL 32301 G. Miriam Maer, Esq. Assistant City Attorney City of Miami 174 East Flagleer Street Miami, FL 33131 Jacob Varn, Secretary Department of Environmental Regulation 2600 Blair Stone Road Tallahassee, FL 32301 ================================================================= AGENCY FINAL ORDER ================================================================= STATE OF FLORIDA DEPARTMENT OF ENVIRONMENTAL REGULATION CITY OF MIAMI, FLORIDA, Petitioner, vs. CASE NO. 78-2183 STATE OF FLORIDA, DEPARTMENT OF ENVIRONMENTAL REGULATION, ET AL., Respondent. / BY THE DEPARTMENT:

Florida Laws (4) 120.57253.03258.39258.40
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STANLEY DOMINICK, VINCE EASEVOLI, KATHERINE EASEVOLI, JOHN EASEVOLI, PAULA EASEVOLI, TOM HODGES, ELAINE HODGES, HANY HAROUN, CATHERINE HAROUN, MARTHA SCOTT, AND MARIANNE DELFINO vs LELAND EGLAND AND DEPARTMENT OF ENVIRONMENTAL PROTECTION, 01-001540 (2001)
Division of Administrative Hearings, Florida Filed:Tavernier, Florida Apr. 25, 2001 Number: 01-001540 Latest Update: Sep. 04, 2003

The Issue The issue in this case is whether Respondent, the Department of Environmental Protection (DEP), should grant the application of Respondent, Leland Egland, for an Environmental Resource Permit (ERP), Number 44-01700257-001-ES, to fill an illegally-dredged trench or channel in mangrove wetlands between Florida Bay and what was a land-locked lake, to restore preexisting conditions.

Findings Of Fact Since 1988, Applicant, Leland Egland, has resided in a home built on property he purchased in Buccaneer Point Estates in Key Largo, Florida, in 1986--namely, Lots 14 and 15, Block 2, plus the "southerly contiguous 50 feet." A 1975 plat of Buccaneer Point shows this "southerly contiguous 50 feet" as a channel between Florida Bay to the west and a lake or pond to the east; it also shows a 800-foot linear canal extending from the lake or pond to the north. Egland's Lot 14 borders Florida Bay to the west; his lot 15 borders the lake or pond to the east; the "southerly contiguous 50 feet" is between Egland's lots 14 and 15 and property farther south owned by another developer. See Finding 10, infra. Buccaneer Point lots in Blocks 1 (to the east) and 2 (to the west) surround the lake or pond and canal. The developer of Buccaneer Point applied to the Florida Department of Environmental Regulation (DER) in 1977 for a permit to dredge a channel, characterized as a flushing channel for the lake or pond, which was characterized as a tidal pond with replanted red mangroves. (There was no evidence as to the character of this pond before the 1977 permit application or if it even existed.) DER denied the permit application because the: proposal . . . to open a pond to Florida Bay . . . will connect an 800 linear foot dead-end canal. The pond and canal will act as a sink for marl and organic debris which will increase Biological Oxygen Demand and lower Dissolved Oxygen. The project is expected to result in substances which settle to form putrescent or otherwise objectionable sludge deposits and floating debris, oil scum, and other materials, in amounts sufficient to be deleterious. Based on the above, degradation of local water quality is expected. * * * Furthermore, your project will result in the following effects to such an extent as to be contrary to the public interest and the provisions of Chapter 253, Florida Statutes: Interference with the conservation of fish, marine life and wildlife, and other natural resources. Destruction of natural marine habitats, grass flats suitable as nursery or feeding grounds for marine life, including established marine soils suitable for producing plant growth of a type useful as nursery or feeding grounds for marine life. Reduction in the capability of habitat to support a well-balanced fish and wildlife population. Impairment of the management or feasibility of management of fish and wildlife resources. As a result, the proposed channel to Florida Bay was not dredged (although some of the lake side of the proposed channel apparently was dredged before the project was abandoned); the building lots surrounding the lake or pond (now known as South Lake) and canal were sold as waterfront lots on a land-locked lake without access to Florida Bay; and the "southerly contiguous 50 feet" was included with the conveyance to Egland, along with the Lots 14 and 15 of Block 2. The evidence was not clear as to the characteristics of the "southerly contiguous 50 feet" in 1977, or earlier. When Egland purchased his property in 1986, it was a mature mangrove slough with some tidal exchange between the lake and Florida Bay, especially during high tides and stormy weather. Some witnesses characterized the area of mangroves as a shallow creek in that general time frame (from about 1984 through 1988). According to Vince Easevoli, at least under certain conditions, a rowboat could be maneuvered between the lake and Florida Bay using a pole "like a gondola effect." But Egland testified to seeing Easevoli drag a shallow-draft boat through this area in this general time frame, and the greater weight of the evidence was that the mangrove slough was not regularly navigable channel at the time. During this general time frame (the mid-to-late 1980's) several Petitioners (namely, Stanley Dominick, John and Katherine Easevoli, and their son, Vince Easevoli) purchased property on South Lake. All but Vince built homes and resided there; Vince did not reside there until after Hurricane Andrew in 1992, but he sometimes stayed at the residence on his parents' property during this general time frame. In the early 1990's, the slough or creek became somewhat deeper, making it increasingly more easily passable by boat. Large storms such as Hurricane Andrew in 1992 and the "storm of the century" in 1993 may have contributed to these changes, but human intervention seems to have been primarily responsible. In 1994, Egland added a swimming pool south of the residence on his lots. During construction, some illegal filling took place. Several witnesses testified that the illegal fill occurred to the north of the creek, which was not affected. Vince Easevoli's lay interpretation of several surveys in evidence led him to maintain that illegal fill was placed in the mangrove slough and that the creek became narrower by approximately four feet and, eventually, deeper. But no surveyor testified to explain the surveys in evidence, which do not seem to clearly support Easevoli's position, and the greater weight of the evidence was that illegal fill was not added to the creek in Egland's "southerly contiguous 50 feet." At some point in time, hand tools were used to deepen the slough or creek and trim mangroves without a permit to enable a small boat to get through more easily. As boats were maneuvered through, the creek got deeper. Eventually, propeller-driven boats of increasing size were used to "prop- dredge" the creek even deeper. According to Petitioner, Tom Hodges, when he and his wife purchased their lot on the lake in 1994, it was possible to navigate the creek in a 22-foot Mako boat (at least under certain conditions), and their lot was sold to them as having limited access to Florida Bay. (There was evidence that access to Florida Bay could increase the price of these lots by a factor of three.) Petitioners Martha Scott and Marianne Delfino also purchased their property on the lake in 1994. Tom Hodges claimed to have seen manatees in the lake as early as 1994, but no other witnesses claimed sightings earlier than 1997, and the accuracy of this estimate is questionable. Even if manatees were in the lake during this time frame or earlier, it is possible that they used an access point other than the creek. At the southeast corner of South Lake in Buccaneer Point, there is a possible connection to a body of water farther south, which is part of a condominium development called Landings of Largo and leads still farther south to access to Florida Bay near a dock owned by Landings of Largo. While this connection is shallow, it may have been deep enough under certain conditions to allow manatees to pass through. Apparently not with manatees but rather with boaters from the lake in Buccaneer Point in mind, Landings of Largo has attempted to close this access point by placement of rebar; Landings of Largo also has placed rip-rap under its dock farther south to prevent boats from passing under the dock. However, there are gaps in the rip-rap, some possibly large enough for manatees to pass. In approximately 1995 or 1996, Egland observed Vince Easevoli and his father, John Easevoli, digging a trench through the mangrove slough with a shovel and cutting mangrove trees with a saw in Egland's "southerly contiguous 50 feet." Others were standing by, watching. Egland told them to stop and leave.6 These actions made the creek even deeper and more easily navigable by boat, which continued to further excavate the trench by such methods as "prop dredging." In 1997 Hany Haroun purchased property adjacent to South Lake where he lives with his wife, Christine. By this time, Florida Bay was easily accessible by boat from the lake, and Haroun paid $260,000 for the property. He estimated that his property would be worth about $150,000 less without boat access to Florida Bay. In approximately 1997, manatees began to appear in South Lake year round from time to time, especially in the winter months. In 1997, the Hodgeses saw one they thought may have been in distress and telephoned the Save Our Manatee Club and Dolphin Research for advice. Following the advice given, they used lettuce to coax the manatee over to their dock to check its condition and videotape the event. The manatee appeared healthy and eventually departed the lake. On subsequent visits, manatees have been seen and videotaped resting and cavorting with and without calves and possibly mating in the lake. Groups of as many as seven to eight manatees have been seen at one time in the lake. Tom Hodges, Vince Easevoli, and Hany Haroun testified that they have enjoyed watching manatees in the lake since 1997. It can be inferred from the evidence that Elaine Hodges also has enjoyed watching manatees in the lake. There was no evidence as to the extent to which other Petitioners enjoy watching manatees in the lake. In 1997, the ACOE began an investigation of the illegal dredging of Egland's "southerly contiguous 50 feet." According to Egland, he was in communication with ACOE; presumably, he told ACOE what he knew about the illegal dredging on his property. According to Egland, ACOE advised him to place posts in the dredged channel to keep boats out. When he did so, Tom Hodges removed the posts. Egland replaced the posts, and Hodges removed them again. When Egland told ACOE what was happening, ACOE asked him to try reinstalling the posts and screwing plywood to the posts to achieve a stronger, fence-like barrier. Hodges also removed these barriers, and Egland did not replace the posts or plywood barrier again. In 1998, ACOE mailed Egland a Cease and Desist Order accusing him of illegal dredging in his "southerly contiguous 50 feet" and demanding that he restore the mangrove slough to its previous conditions. Egland was angry at being blamed for the dredging and initially disputed ACOE's charges and demands. But ACOE and the United States Environmental Protection Agency (EPA), which accepted the role of lead federal enforcement agency on December 18, 1998, was seeking monetary civil penalties. In addition, Egland received legal advice that, if restoration were delayed, he could be sued for damages by someone purchasing property on the lake or canal in the meantime upon the mistaken belief that there was boat access to Florida Bay. For these reasons, Egland agreed to comply with the Cease and Desist Order. However, ACOE and EPA informed Egland that he might have to obtain a permit from DEP to fill the dredged channel in compliance with the Cease and Desist Order. On May 22, 2000, Egland applied to DEP for an ERP to restore a trench about 100 feet long varying from seven to ten feet in width that was illegally dredged on his property. He estimated that a total of 160 cubic yards of fill would be required, to be spread over approximately 900 square feet. He assured DEP that rip-rap would be used to contain the fill and that turbidity screens would be used during construction. During processing of Egland's application, DEP requested additional information, which Egland provided, and DEP's Environmental Manager, Edward Barham, visited the project site in October 2000. Based on all the evidence available to him at that point in time, Barham viewed Egland's proposed fill project as a simple restoration project to correct illegal dredging and return the mangrove slough to its preexisting condition. For that reason, Barham recommended that DEP process the application as a de minimis exemption and not charge a permit application fee. Subsequently, some Petitioners brought it to DEP's attention that manatees were accessing South Lake through the channel Egland wanted to fill. DEP saw no need to verify the accuracy of Petitioners' information or obtain additional information about the manatees use of the lake because DEP still viewed it as a restoration project. However, DEP decided that it would be necessary to include specific conditions in any ERP issued to Egland to ensure that no manatees would be trapped in the lake or otherwise injured as a result of filling the channel. Primarily due to the need for these conditions, and also because of anticipated opposition from Petitioners, DEP decided to charge Egland a permit application fee and not process the application as a de minimis exemption. DEP staff visited the mangrove slough on numerous occasions between October 2000, and final hearing and observed that the trench continued to get deeper over time as a result of continued prop-dredging and digging. In early August 2001, Tom Hodges observed a man walking back and forth with a wheel barrow between a storage shed on Egland's property and the channel. (Hodges was on his property across South Lake but use of binoculars enabled him to see this.) The next day, Hany Haroun discovered a poured- concrete slab forming a plug or dam in the channel on the lake side. Haroun reported his discovery to Tom Hodges, who investigated with his wife, who took photographs of the structure. At some point, the Hodgeses realized that a manatee was trapped in the lake. The manatee did not, and appeared unable to, use the other possible access point towards Landings of Largo to escape. See Finding 10, supra. The Hodgeses telephoned Barham at DEP to report the situation and complain. Tom Hodges then proceeded to break up the concrete, remove the resulting rubble, and place it on the path to the storage shed, freeing the manatee. The incident was reported in the newspaper the next day and prompted Petitioners to file their Motion to Dismiss and for Other Relief on August 9, 2001. See Preliminary Statement. The evidence was inconclusive as to who poured the concrete, or had it poured, and why. Egland testified that he was in Egypt on an extended trip at the time and denied any knowledge of the concrete plug until he saw the rubble on his property upon his return from Egypt. Egland testified that he saw no "aggregate" in the concrete, which would make it relatively easy to break up, and he suspected that Petitioners were responsible for pouring the concrete in order to publicly make false accusations against Egland. Petitioners denied Egland's accusation. Vince testified that the concrete contained rebar for strength. The evidence was inconclusive as to who was responsible for this incident. As pointed out by Petitioners, DEP did not investigate and does not know whether there is any freshwater upwelling in the lake, whether manatees have mated in the lake, or whether calves have been birthed in the lake. DEP also did not investigate and does not know whether South Lake is unlike other manatee habitat in the area. DEP did not investigate or obtain any information as to how many manatees use the lake, or what manatees use the lake for, in addition to the information provided by Petitioners. Carol Knox, an Environmental Specialist III with the Florida Fish and Wildlife Commission, testified as a manatee expert based on her knowledge of manatees and manatee habitat in the area, as well as the information known to DEP. It was her opinion that, regardless what South Lake might offer manatees in the way of habitat, closing the channel (with the specific conditions required by DEP to protect manatees during the filling itself) would have no adverse impact on manatees because it did not appear that manatees made use of the lake before the channel was dug in 1996 or 1997, and ample other manatee habitat of various kinds continued to be available in the area.7 Based on the testimony of Knox and Barham, and the totality of the evidence in this case, it is found that Egland provided reasonable assurance that his proposed restoration project will not harm or adversely affect manatees or their habitats. Petitioners also questioned Egland's assurances as to water quality. Vince Easevoli, Stanley Dominick, and Hany Haroun testified to their concerns that water quality in the lake will decline if the channel is closed. As Petitioners point out, DEP did not require Egland to provide any water quality measurements. This was because the proposal is reasonably expected to reverse the effects of the illegal dredging on water quality and to return both the water in the lake and canal and the water in Florida Bay to the quality that existed prior to the illegal dredging. Without requiring any water quality measurements, it is reasonably expected that the water quality in Florida Bay would not decline in any respect; to the contrary, if anything, Florida Bay's water quality would be expected to improve by reduction of contributions from the lake and canal. Conversely, water quality in the lake and canal would be expected to decline but not below what it was before the illegal dredging. Petitioners also question DEP's failure to require Egland to provide a survey or stake the area to be filled, so as to ensure against filling too much of the mangrove slough. But the proposed ERP contains a specific condition: "The final fill elevation of the fill shall be at the elevation of the substrate within the adjacent mangrove wetlands." Barham testified persuasively that this specific condition is adequate to provide reasonable assurance. Compliance can be ascertained by simply viewing the site after completion of the restoration project, and compliance can be enforced by requiring removal of excess fill as necessary. The proposed ERP also contains a general condition that the permit does not convey or create any property right, or any interest in real property, or authorize any entrances upon or activities on property which is not owned or controlled by Egland.

Recommendation Based upon the foregoing Findings of Fact and Conclusions of Law, it is RECOMMENDED that the Respondent, the Department of Environmental Protection, enter a final order granting the application of Leland Egland and issuing ERP Number 44- 01700257-001-ES. DONE AND ENTERED this 25th day of November, 2002, in Tallahassee, Leon County, Florida. ___________________________________ J. LAWRENCE JOHNSTON Administrative Law Judge Division of Administrative Hearings The DeSoto Building 1230 Apalachee Parkway Tallahassee, Florida 32399-3060 (850) 488-9675 SUNCOM 278-9675 Fax Filing (850) 921-6847 www.doah.state.fl.us Filed with the Clerk of the Division of Administrative Hearings this 25th day of November, 2002.

Florida Laws (9) 120.52120.5726.012267.061373.413373.414373.42140.011403.031
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THE CONSERVANCY, INC., AND FLORIDA AUDUBON SOCIETY vs. A. VERNON ALLEN BUILDER, INC., AND DEPARTMENT OF ENVIRONMENTAL REGULATION, 88-004760 (1988)
Division of Administrative Hearings, Florida Number: 88-004760 Latest Update: Jan. 05, 1993

Findings Of Fact The Hearing Officer's findings of fact in both the First Recommended Order and the Recommended Order As To Matters On Remand are accepted except as otherwise noted in either this Final Order After Remand or the First Final Order. The Florida Audubon has filed 80 pages of exceptions comprising 98 exceptions to findings of fact and 33 exceptions to conclusions of law. I have grouped these exceptions and ruled on them under the categories listed below. Scope of Remand and Hearing Officer's Preliminary Statement. Florida Audubon's Exceptions No. 1(A)-1(G), 2(A)-2(M), 3(A)-3(C), 4(A)- 4(B), 5(A)-5(C) and 9(A)(3) in whole or in part take exception to the Hearing Officer's preliminary statement of the background of the case and the scope of the issues on remand. My review of the record in this case leads me to conclude that the Hearing Officer's factual summary and statement of the issues on remand in her preliminary statement is an accurate and concise description of the background of this case and is based on matters of record and competent substantial evidence. Accordingly, I reject these exceptions. Furthermore, the Hearing Officer's preliminary statement comprises neither findings of fact nor conclusions of law. Therefore, a ruling on these exceptions is not actually required. 5/ Nature of the Proposed Development. Florida Audubon's Exceptions 8(A)-8(I) in whole or part take exception to the Hearing Officer's description in F.O.F. Nos. 1-9 of the nature of the proposed development. These exceptions do not assert that F.O.F. Nos. 1-9 are not supported in the record by competent substantial evidence. Rather, the gist of these exceptions is that the Hearing Officer overlooked or did not give proper weight to evidence that may suggest a contrary finding. It is well settled that where a Hearing Officer's finding of fact is supported in the record by competent, substantial evidence. I am not at liberty to reject or modify it. See e.g., Florida Dept. of Corrections v. Bradley, 510 So.2d 1122 (Fla. 1st DCA 1987); Heifetz v. Dept. of Business Regulation, 475 So.2d 1277, 1281 (Fla. 1st DCA 1985); Sections 120.57(1)(b)10., and 120.68(10), Florida Statutes. Nor may I reweigh the evidence considered by the Hearing Officer. Heifetz, supra. My review of the record shows that the Hearing Officer's F.O.F. Nos. 1-9 are supported in the record by competent, substantial evidence. The following summarizes F.O.F. Nos. 1-9 and the competent substantial evidence in the record which supports them. The proposed development on the island has been approved by the City of Naples and involves the refurbishment and expansion of existing Keewaydin Club facilities along with the construction of 42 single family homes within the city's jurisdictional boundaries. (F.O.F. No. 1: App. Remand Ex. 2). The Applicant is limited in its improvement of the Keewaydin Club facilities as follows: Construction must occur within the existing club property boundaries. A maintenance facility, firehouse, helipad and additional tennis courts are to be constructed. In addition, two buildings containing guest units and a building with 21 staff units can be built. Existing buildings can be remodeled to continue in their present functions and the clubhouse can be expanded by an additional 4,400 square feet. (F.O.F. No. 2: Stipulation of Respondents; DER Remand Ex. 2.). Marina expansion has been proposed by the Applicant, along with elevated walkways through jurisdictional wetlands, but are not essential to the proposed development. For purposes of consideration of secondary impacts the hearing on remand assumed that the marina expansion and walkways would be constructed so that the secondary impacts of the potential development could be considered during the current dredge and fill permit review. (F.O.F. No. 3: DER Remand Ex. 2; DER Remand Ex. A at 18-19). The 42 single family homes are planned for specific locations south of the club property. These homes will be on 15,000 square foot lots. It is anticipated that they will be landscaped with native vegetation and that residents will move around the island via golf carts on cart paths. (F.O.F. No. 4: App. Remand Ex. 2 at 1-1, 1-5, 1-16, 1-38, 2-7 to 2-9, and 5-2; App. Remand Ex. 11 at 6; Tr. at 413-15). Because the city has limited the planned development to the 42 residential units and the improvements to the club, both the Department of Natural Resources and South Florida Water Management District have approved permits specifically tailored to this development plan. (F.O.F. No. 5: App. Remand Exh. 2; App. Remand Ex. B at 6-10, App. Remand Ex. 11). The privately owned portion of the island cannot be developed further because of the city's approval conditions for this project. These two conditions are: (1) City Ordinance 89-5843 mandates all of the property in the land options involved with future development must be annexed into the city; and Once the property is annexed, the Applicant will give the city a conservation easement over 2,270 acres. This acreage is to be retained in its natural state and is expected to be maintained as suitable habitat for fish, plants and wildlife. (F.O.F. No. 6: App. Remand Ex. 2 at 1-3, 1-30; App. Remand Ex. 6; App. Remand Ex. 11; App. Remand Ex. A at 11-12). The City of Naples requires the developer to eliminate all septic tanks serving the Keewaydin Club as one if its conditions for approval of the current project. This has the potential to positively impact and improve current water quality on the island. (F.O.F. No. 7: Tr. at 317, 323-24; App. Remand Ex. D at 12; App. Remand Ex. F at 13 and 15; App. Remand Ex. 2). Specific measures have been proposed to minimize development impacts on the wildlife known to inhabit the island. Preservation of the osprey nest zone, upland gopher tortoise habitat, control of wheeled traffic on the beach, use of indirect lighting to avoid disorientation of baby atlantic loggerhead turtles as they hatch from nests, and trapping programs to control the raccoon population are prepared and ready for implementation. (F.O.F. No. 8: App. Remand Ex. 2; DER Remand Ex. A. at 22; DER Remand Ex. 2). The vast number of natural plant species on the island will be protected in designated areas. The preservation has been planned so representatives of species of interest will continue to thrive. (F.O.F. No. 9: App. Remand Ex. F at 16; DER Remand Ex. A at 22; DER Remand Ex. 2; App. Remand Ex. 2 at 1-25, 2-7, 2-16, and 2-17). Since the above findings of fact are supported in the record by competent substantial evidence, I can not disturb these findings of fact. I therefore reject the above noted exceptions. The MSSW Permit and Reasonable Assurance As To Water Quality. Florida Audubon's Exceptions No. 1(C)-1(F), 8(G)(3), 9(A), 9(I)(1)-(3) and 30(D) in whole or part take exception to the Hearing Officer's findings of fact and conclusions of law that the applicant has provided reasonable assurance that the project will not cause violations of water quality standards. (F.O.F. Nos. 10-20; Conclusion of Law No. 42). 6/ The gist of these exceptions is that the Department erred in relying on the assumption that in issuing its Management and Storage of Surface Water ("MSSW") permit, the South Florida Water Management District ("SFWMD") properly determined that the surface water management system for the island development provided reasonable assurance that the system would not result in violations of state water quality standards. There is competent substantial evidence in the record supporting the Hearing Officer's finding that the Department did not independently evaluate whether the development's surface water management system provided reasonable assurance that it would not violate state water quality standards. (F.O.F. No. 10; Dentzau, Tr. at 700-701, 712-13). It is therefore necessary to decide whether the Department properly relied on the MSSW permit for reasonable assurances that the surface water management system would not result in water quality violations, or whether the de novo hearing rendered the reliance moot in any event. Before the Department may issue a dredge and fill permit, it must determine that the applicant has provided reasonable assurances that the project, when considered with cumulative and secondary impacts, will not cause violations of water quality standards. Section 403.918(1), Florida Statutes. See also Conservancy v. A. Vernon Allen Builder, 580 So.2d 772 (Fla. 1st DCA 1991) and authorities cited therein. 7/ Where development is a secondary impact of a dredge and fill project, and the development will have a related surface water management system, the Department must also determine whether reasonable assurances have been provided that the surface water management system will not cause water quality violations. The first issue presented by this case is whether the Department may properly rely on a water management district's MSSW permit as the needed reasonable assurances, or whether the Department must "look behind" the water management district's MSSW permit and make a separate and independent evaluation of whether the necessary reasonable assurances have been provided. I note that in 1989 the Legislature enacted Ch. 89-279, Section 15, Laws of Florida, which created Section 373.418, Florida Statutes, providing in part that: It is the intent of the Legislature that stormwater management systems be regulated under this part [i.e., Part IV of Chapter 373] incorporating all of existing requirements contained in or adopted pursuant to Chapters 373 and 403. * * * (3) The department or governing boards may adopt such rules as are necessary to implement the provisions of this part. Such rules shall be consistent with state water policy and shall not allow harm to water resources or be contrary to the policy set forth in s. 373.016. The rules of SFWMD require that surface water management systems not cause violations of state water quality standards. Rule 40E-4.301(1)(c), Fla. Admin. Code. Also, State water policy requires that MSSW permits not cause violations of state water quality standards. Rule 17-40.420(3)(a), (b)1.a., Fla. Admin. Code. Although the Department is authorized to issue MSSW permits under section 373.418, it is the intent of Chapter 373 that Department powers be delegated to the water management districts to the greatest extent practicable. Section 373.016(3), Florida Statutes. The Legislature has ,thus established a scheme where strong preference is given to the regulation of surface water management systems by Water management districts through Chapter 373 MSSW permits. 8/ This scheme includes a mechanism in which the Department, the applicant, or a substantially affected person can petition the Land and Water Adjudicatory Commission for a determination of the validity of the permit. See Section 373.114, Florida Statutes. If the Department in the context of a Chapter 403 dredge and fill permit evaluation were to second guess and make an independent assessment of whether a surface water management system which had already received a water management district MSSW permit actually provided the necessary reasonable assurances, it could lead to a collateral attack on the validity of the MSSW permit and defeat the Legislative intent expressed in Sections 373.418 and 373.114, Florida Statutes. I therefore conclude that where an MSSW permit issuance by a water management district has become final, the Department may accept the MSSW permit as reasonable assurance that, as to the operation of the system within the scope of the dredge and fill permit, the surface water management system will not cause violations of state water quality standards. Of course, the Department will continue to make an independent determination of whether the remaining aspects of the project, taking into consideration cumulative and secondary impacts, provide the necessary reasonable assurances. I note that in this case the MSSW permit has not yet become final, as it is pending review before the Land and Water Adjudicatory Commission. 9/ A second issue raised is whether the de novo hearing rendered moot any question as to the propriety of the Department's reliance on the MSSW permit. I note that in the remand hearing in this case expert testimony was introduced to the effect that the development's management and storage of surface water system would not cause violations of state water quality standards. (App. Remand Ex. B, Prefiled Test. of Means at 6-12, 14-17.). Since this proceeding on remand is a de novo determination of the issues on remand, if there was any error by the Department in relying on the MSSW permit, it is moot because the Hearing Officer found that the necessary reasonable assurances were provided based on competent substantial evidence in the record. Since the Hearing Officer's finding that reasonable assurances have been provided is supported in the record by competent substantial evidence, I may not disturb it. Accordingly, the above noted exceptions are rejected. Reasonable Assurances As to Water Quality. Florida Audubon's Exceptions No. 1(C)-(F), 8(D)(2)-8(D)(3) , 8(E)(1), 8(F), 8(G)(1)-8(G)(3), 8(H) and 9(A)-9(K) in whole or in part take exception to the Hearing Officer's finding of fact that the Applicant has provided reasonable assurances that the proposed project, including the secondary impacts of the expected development, will not cause violations of water quality standards. (F.O.F. Nos. 10-20). Once again, Florida Audubon's exceptions do not assert the Hearing Officer's findings of fact are not supported in the record by competent substantial evidence, but essentially contend that the Hearing Officer did not give proper weight to what Florida Audubon contends is conflicting evidence. As I noted above, the standard which I must apply in ruling on exceptions to findings of fact is whether the Hearing Officer's findings of fact are supported in the record by competent substantial evidence. Florida Dept. of Corrections; Heifetz; supra. If I find any competent substantial evidence in the record to support a finding of fact I must accept the finding of fact even if there are contrary facts in the record and even if I would have weighed the facts differently. Heifetz, supra. 10/ As noted in Part III(3) above, the Department did not independently evaluate whether the design of the project's surface water management system provided reasonable assurance that the system would not violate state water quality standards. Rather, the Department relied on the issuance of the MSSW permit by the South Florida Water Management District. (F.O.F. No. 10; Dentzau, Tr. at 700-701, 712-713). Florida Audubon suggests that SFWMD did not in fact review the impact of the surface water management system on water quality, and that the Department's reliance on the MSSW permit precludes a finding that the Applicant has provided reasonable assurances that the project will not violate water quality standards. I disagree for the reasons stated in Part III(3) above. In particular, I note that the record on remand contains competent substantial evidence that the surface water management system will not result in violations of water quality standards. (App. Remand Ex. B, Prefiled Test. of Means at 6-12, 14-17). This proceeding on remand is a de novo determination of whether reasonable assurances have been provided that the project, taking into consideration the expected development of the island, will not result in violations of water quality standards. Therefore, regardless of whether the Department initially erred in relying on the MSSW permit, any error has been rendered moot by this de novo proceeding on remand in which the Applicant introduced competent substantial evidence that reasonable assurances have been provided that the stormwater management system will not cause violations of water quality standards. As to F.O.F. Nos. 11-20, the following summarizes the findings of fact and the competent substantial evidence in the record supporting them. In its review of the proposed development the Department identified several areas of potential adverse water quality impacts. Specifically, the Department investigated impacts from a potential marina expansion; the creation of all planned cart paths, proposed house pad construction, boardwalk and canoe launches, exempt docks, and beach renourishment. (F.O.F. No. 11: DER Remand Ex. 2; DER Remand Ex. A, Prefiled Test. of Dentzau at 7-9, 11-25; DER Remand Ex. B, Prefiled Test. of Llewellyn at 5-13). The marina expansion, boardwalks, and canoe launches will impact existing jurisdictional mangroves, thereby affecting water quality. If later permitted, however, the Applicant can reasonably minimize such impacts and offset them in a suitable fashion. (F.O.F. No. 12: DER Remand Ex. A, Prefiled Test. of Dentzau at 20-21; DER Remand Ex. 2). 11/ The primary impacts from exempt docks are minimized by the development plan. The secondary potential impacts are negligible. (F.O.F. No. 13: DER Remand Ex. A, Prefiled Test. of Dentzau at 20-21; DER Remand Ex. 2). The cart paths will not be paved. Urban runoff from these surfaces will have an insignificant quantity of pollutants that are accounted for in the surface water management system design. (F.O.F. No. 14: App. Remand Ex. F, Prefiled Test. of McWilliams at 14; Applicant's Remand Ex. B, Prefiled Test. of Means at 6-12, 16; Applicant's Remand Ex. D, Prefiled Test. of Missimer at 11). The secondary impacts from the house pad construction and the urban runoff from associated impervious surfaces are minimal. Nevertheless, they are accounted for in the surface water management system design. (F.O.F. No. 15: Applicant's Remand Ex. 2 at 1-16, 5-2; App. Remand Ex. B, Prefiled Test. of Means at 6-10; App. Remand Ex. D, Prefiled Test. of Missimer at 11-12; App. Remand Ex. F, Prefiled Test. of McWilliams at 13-14). The agreements entered into between the Applicant, the City of Naples, and the Department of Natural Resources prohibit any additional shore hardening. The beach management plan includes periodic beach renourishment. (F.O.F. No. 16: DER Remand Ex. A, Prefiled Test. of Dentzau at 16; App. Remand Ex. 11; App. Remand Ex. E at 10, Prefiled Test. of Stephen at 10; Tr. at 368-369). A review of the surface water management plan presented at the remand hearing reveals that the potential for adverse secondary impacts is significantly limited due to the low density and minimal infrastructure for the proposed development. The 42 new homes will be spread over 430 acres. A series of swales, collection ponds and surface water treatment areas have been designed to minimize the impacts of development on the surface water. The use of fertilizer or pesticides by residents will be strictly limited. (F.O.F. No. 17: App. Remand Ex. B, Prefiled Test. of Means at 6-10; App. Remand Ex. D, Prefiled Test. of Missimer at 11-12; App. Remand Ex. F, Prefiled Test. of McWilliams at 12-19; App. Remand Ex. 6). The surface water management system meets the Department's water quality standards. (F.O.F. No. 18: App. Remand Ex. B, Prefiled Test. of Means at 6-14; App. Remand Ex. 6; Tr. at 185-89, 197-215). Potable water is already conveyed to the island from the city. Once the septic tanks are removed, the overall affect of the planned development on ground water will be negligible. (F.O.F. No. 19: DER Remand Ex. 2; DER Remand Ex. A, Prefiled Test. of Dentzau at 16, 23-24). I conclude that the Hearing Officer's F.O.F. Nos. 10-20 are supported in the record by competent substantial evidence and therefore I will not disturb them. Accordingly, the above noted exceptions are rejected. Reasonable Assurances As to Public Interest Test. Florida Audubon's Exceptions No. 10(A)-10(O)(2) in whole or in part take exception to the Hearing Officer's findings of fact that reasonable assurances have been provided that the proposed project, taking into consideration the cumulative and secondary impacts, is not contrary to the public interest. (F.O.F. Nos. 21-34). As with the previous exceptions, Florida Audubon is essentially arguing that the Hearing Officer improperly weighed the evidence. My task is to determine whether the Hearing Officer's findings of fact are supported in the record by competent substantial evidence. If they are, I may not reject them. The following summarizes F.O.F. Nos. 22-33 and the competent substantial evidence in the record supporting them. All new construction is required to meet flood protection standards even though the owners will not be eligible for flood insurance. Home construction standards take into consideration many of the effects of hurricanes. (F.O.F. No. 22: App. Remand Ex. 2: App. Remand Ex. F at 15). The hurricane evacuation plan has been approved by the city and Collier County emergency management authorities. (F.O.F. No. 23: App. Remand Ex. 2 at Ib, 1-29; App. Remand Ex. A at 17-21). Public funds are protected as the proposed development is not dependent upon federal, state or local funding or insurance. The city has passed an ordinance that requires property owners to acknowledge that the city has no liability for rebuilding any damaged infrastructure or improvements. The monetary risk associated with the development will be borne by the developer and the residents. (F.O.F. No. 24: App. Remand Ex. 2 at 1-3 to 1-8). The 42 single family homes will be located within the island's Coastal Barrier Resources Act (CBRA) unit boundaries. The evidence adduced at hearing indicated that the CBRA designation will not be jeopardized by the proposed development. (F.O.F. No. 25: Tr. at 106-7; App. Remand Ex. A at 21-33; App. Remand Ex. 3; App. Remand Ex. 4; App. Remand Ex. E at 16). The proposed development will have negligible secondary impacts on fish and wildlife. The project protects or enhances various fish and wildlife habitats. All wetlands will be preserved. The beach dune system will be improved through removal of exotics and dune restoration. As a result, the interdependence of the estuarine area on the coastal barrier resource will not be adversely affected by the project. (F.O.F. No. 26: DER Remand Ex. A at 15- 16; App. Remand Ex. E at 19; App. Remand Ex. F at 10, 13-14, 15-16; Tr. at 414, 825-26, 829-30). Gopher tortoises will be relocated to an upland preserve on the same island. The removal of exotic plants, the introduction of native herbaceous plants and control of the raccoon population should positively effect the gopher tortoise population. (F.O.F. No. 27: DER Remand Ex. 2; DER Remand Ex. A at 21- 22; App. Remand Ex. F at 15-16; Tr. at 855-60). Indirect lighting and the reduction of raccoons should benefit the atlantic loggerhead turtle population. (F.O.F. No. 28: DER Remand Ex. 2; DER Remand Ex. A at 22; App. Remand Ex. 2). Threatened or endangered plant species on the site include golden leather fern, assorted orchids and bromeliads, golden polypody fern, shoestring fern and prickly pear cactus. Representatives of these species will be protected in preserve areas, according to conditions in the development plan approved by the city and conditions established in other permits. (F.O.F. No. 29: DER Remand Ex. 2; DER Remand Ex. A at 22; App. Remand Ex. F at 16). The proposed project preserves all identified habitats which contribute to marine productivity. Low density development and other limitations already placed on the project were designed to minimize the adverse impacts on fishing and marine productivity. Recreational values will be enhanced by the project because of the proposed canoe launches and habitat restoration. (F.O.F. No. 30: App. Remand Ex. F at 16). The development is permanent in nature. Design limitations on the project, existing permit conditions and the low density aspect of the development combine to assure that the project has limited adverse impacts. (F.O.F. No. 31: App. Remand Ex. 2; App. Remand Ex. F at 17-18; Tr. at 872-73). There will be no adverse impacts on historical or archaeological resources. The Caloosa Indian Midden located on the property is to be preserved undisturbed. The Keewaydin Club Lodge is a designated structure on the National Historical Register and will be maintained as a historical building. (F.O.F. No. 32: DER Remand Ex. 2; DER Remand Ex. A at 22; App. Remand Ex. A at 16-17). Except for the creation of 42 single home residencies for people willing to spend a million dollars for a home on an island with access only by boat or helicopter and all monetary risk for infrastructure and improvements damaged by any cause, the current condition of the island will not be changed significantly. All high quality resources and their functions have been preserved by project design. (F.O.F. No. 33: App. Remand Ex. F at 17-18; Tr. at 872-73). The above findings of fact which are supported in the record by competent substantial evidence support the Hearing Officer's F.O.F. No. 21 that the project will not adversely affect public health, safety or welfare or the property of others. Since the above noted findings of fact are supported in the record by competent substantial evidence, I shall not disturb them and the above noted exceptions are therefore rejected. However, as to the Hearing Officer's "finding" that the project is not contrary to the public interest, this is ultimately a conclusion of law for which I have the final authority and responsibility to determine. 1800 Atlantic Developers v. Depart. of Environmental Regulation, 552 So.2d 946 (Fla. 1st DCA 1989), rev. den., 562 So.2d 345 (Fla. 1990); Harloff v. City of Sarasota, 575 So.2d 1324 (Fla. 2d DCA 1991), rev. den. 583 So.2d 1035 (Fla. 1991). Although the factors found in the Hearing Officer's F.O.F. Nos. 26-30 help alleviate the adverse impacts of the project, when I balance the public interest criteria I conclude that the project would be contrary to the public interest without the mitigation offered by the preservation conservation easement to be placed over 2,270 acres. When I take the mitigation into consideration, I conclude that the project, taking into consideration the cumulative and secondary impacts, is not contrary to the public interest. Barrier Island -- Executive Order 81-105 and Designation Under The Federal Coastal Barrier Island Resources Act (CBRA). Florida Audubon's Exceptions No. 1(G), 3(A)-3(C), 5(A), 8(D)(1), 8(E)(1), 9(A)(3), 9(B)-9(D), 10(E)(1) (3), 10(J) 10(N)(3), 17 (A)-17(D), 21, 22, 24 and 25 in whole or in part take exception to the Hearing Officer's finding of fact that the federal Coastal Barrier Resources Act (CBRA) designation of Keewaydin Island will not be jeopardized by the proposed development (F.O.F. No. 25) and to the Hearing Officer's conclusion of law that the development is not prevented by Governor Graham's Executive Order No. 81-105. (C.O.L. No. 43). My review of the record shows that competent substantial evidence was admitted supporting the fact that Keewaydin Island's Coastal Barrier Resource System ("CBRS") unit designation does not prohibit the development of Keewaydin Island. It just precludes federal funds to facilitate such development. Therefore, that development would not jeopardize the CBRS unit designation. (App. Remand Ex. 3; App. Remand Ex. 4; App. Remand Ex. A at 21-23; App. Remand Ex. E at 16; Tr. at 106-107) Accordingly, I shall not disturb this finding of fact. Although I note that Executive Order No. 81-105 may have some weight in the balancing of the public interest criteria under Section 403.918(2), Florida Statutes, I concur with the Hearing Officer's conclusion of law that Executive Order No. 81-105 does not per se preclude the development of coastal barrier islands where government funds will not be used to create the infrastructure that promotes development on the barrier island. In view of the above, the above noted exceptions are rejected. Exceptions Lacking Particularity. Florida Audubon Exceptions No. 6 and 7 lack sufficient particularity. Rule 17-103.200(1), Fla. Admin. Code, provides in part: Exceptions shall state with particularity the basis for asserting that the Hearing Officer erred in making or omitting specific findings of fact, conclusions of law, or a recommendation ... The reason for the above requirement is clear. It is impossible for the parties to respond, or for me to rule, when the basis for a purported error is not clearly stated. Exceptions No. 6 and 7 fail to state how the Hearing Officer has erred in a finding of fact, conclusion of law, or recommendation. Such exceptions do not comply with Rule 17-103.200(1), Fla. Admin. Code, and therefore must be rejected. For this reason, I reject these exceptions. RULINGS ON EXCEPTIONS TO CONCLUSIONS OF LAW The Hearing Officer's conclusions of law in both the First Recommended Order and the Recommended Order As To Matters On Remand are accepted except as otherwise noted in either this Final Order After Remand or the First Final Order as modified by the court's opinion in Conservancy v. A. Vernon Allen, Builder, supra. Scope of Remand. Florida Audubon's Exceptions No. 11-14 in whole or in part take exception to the Hearing Officer's Conclusions of Law No. 36-39. The gist of these exceptions is that the Hearing Officer misconstrued the scope of the remand and consequently lacked jurisdiction. There is no merit in the contention that the Hearing Officer lacked jurisdiction. Jurisdiction was conferred by the court's mandate that the matter be remanded to the Division of Administrative Hearings for further proceedings consistent with the court's opinion. See Conservancy v. A. Vernon Allen Builder, 580 So.2d 772 (Fla. 1st DCA 1991). Nor do I agree that the Hearing Officer misconstrued the scope of remand. The opinion of First District Court of Appeal stated: In the instant case, we disagree with appellee that the contemplated development of 75 estate homes is speculative and is not closely linked or causally related to the proposed dredging and filling. We perceive there to be little difference between the Department's aforestated need to "consider what will be at the end of the bridge or road," and the necessity here to consider what will be at the end of the pipeline, especially when the evidence, proffered or admitted, suggests that the development enabled by the dredge and fill permit could have devastating environmental impacts. Such evidence would be highly relevant to the Department's consideration of whether the applicant has carried its burden of giving reasonable assurances under section 403.918 that water quality standards will not be violated and the project is not contrary to the public interest. Thus, the Department's consideration of the proposed development solely in relation to the design of the pipeline system itself neglected the necessity in this case to consider potential secondary impacts. Consequently, it was error for the Hearing Officer to exclude the evidence proffered by appellants for the reasons set forth in her recommended order. Accordingly, this cause must be reversed and remanded for further proceedings and re-evaluation of the proffered evidence in a manner consistent with this opinion. 12/ Conservancy v. A. Vernon Allen Builder, 580 So.2d at 779 (quoting McCormick v. City of Jacksonville, (12 FALR 980, 981 (DER Final Order, Jan. 22, 1990); footnote omitted). I conclude that the Hearing Officer properly construed the scope of remand to require the consideration of "the secondary impacts associated with the development of Key Island, which the Court determined were closely linked and causally related to the proposed permit." (R.O.R., C.O.L. No. 37) I also note that this administrative proceeding on remand is a de novo determination of the issue of the secondary impacts, and that Florida Audubon has fully participated and submitted testimony and evidence on the issue of the secondary impacts. I therefore conclude that the administrative hearing fully complied with the scope of remand, and accordingly reject the above noted exceptions. Reasonable Assurances As To Water Quality. Exceptions No. 14, 15(A)-15(C), 16, 18, 24 and 30(D) in whole or part take exception to the Hearing Officer's conclusions of law that reasonable assurances have been provided that the project and its cumulative and secondary impacts will not cause violations of water quality standards. (C.O.L. Nos. 40, 41, 42). Based on the Hearing Officer's findings of fact which I have accepted, I conclude that the project, taking into consideration cumulative and secondary impacts, provides reasonable assurance that water quality standards will not be violated. I therefore reject the above noted exceptions. Reasonable Assurances As To The Public Interest Test. Florida Audubon's Exceptions No. 15(A)-15(C), 16, 17, 18, and 21-24 take exception to the Hearing Officer's conclusions of law that reasonable assurance has been provided that the project together with its cumulative and secondary impacts are not contrary to the public interest. (C.O.L. No. 43) As I noted above, the determination of whether reasonable assurances have been provided as to the public interest test is ultimately a conclusion of law for which I have the final authority and responsibility to determine. 1800 Atlantic Developers v. Depart. of Environmental Regulation, 552 So.2d 946 (Fla. 1st DCA 1989), rev. den., 562 So.2d 345 (Fla. 1990). Based on the Hearing Officer's findings of fact which I have accepted, I conclude that the project, taking into consideration the cumulative and secondary impacts and the offered mitigation of the preservation conservation easement over 2,270 acres, has provided reasonable assurance that the project is not contrary to the public interest. Therefore the above noted exceptions are rejected. Barrier Island -- Executive Order 81-105 and Designation Under The Federal Coastal Barrier Island Resources Act (CBRA). Florida Audubon's Exceptions No. 17(A)-(D), 21, 22, 24 and 25 in whole or in part take exception to the Hearing Officer's conclusions of law that Executive Order No. 81-105 and the Federal Coastal Barrier Island Resource Act do not preclude the proposed development on Keewaydin Island. Based on the Hearing Officer's findings of fact which I have accepted, and for the reasons stated in Part III(6) above, I concur with the Hearing Officer's conclusions of law and reject the above noted exceptions. Evidentiary Issues Official Recognition of Hurricane Andrew and Amendment to Rule 28-21.003 Florida Audubon's Exceptions No. 25, 30(A)-30(C) do not take exception to any specific finding of fact or conclusion of law. Rule 17-103.200(1) requires rulings only to exceptions to findings of fact, conclusions of law or recommendations. Although lacking in specificity, these exceptions apparently assert that the Hearing Officer erred in an implied conclusion of law when she declined to take official recognition of (1) an amendment to Department of Natural Resources Rule 18-21.003 relating to leases or consent to uses of sovereign submerged lands incident to the development of undeveloped coastal barrier islands, and (2) the effects of Hurricane Andrew on Keewaydin Island. The Hearing Officer, relying on the authority of Collier Medical Center v. Department of Health and Rehabilitative Services, 462 So.2d 83, 86 (Fla. 1st DCA 1985), denied these motions on the ground that the evidentiary hearing had ended. I note that the decision to give official recognition, like judicial notice, lies in the discretion of the Hearing Officer. See ., Huff v. State, 495 So.2d 145, 151 (Fla. 1986)("It is upon the wisdom and discretion of the judges of our courts that the doctrine of judicial notice must rest."). Even assuming that the Hearing Officer's decision to deny official recognition is an implied conclusion of law to which an exception is appropriately made, I cannot say that I believe the Hearing Officer abused her discretion in declining to take the requested official recognition. Florida Audubon has suggested no competent substantial evidence in the record which would be a basis for determining whether the amended Rule 18-21.003 would be applicable to the proposed development on Keewaydin Island. Furthermore, even if the rule was applicable to Keewaydin Island, the effect of the rule would be relevant to the necessary permit, easement or consent to use from the Board of Trustees of the Internal Improvement Trust Fund. The Department's permit does not remove the applicant's need for a Board of Trustees permit over sovereign submerged lands. 13/ As to the request for official recognition of Hurricane Andrew, it cannot be said that it is generally known and not subject to dispute how Hurricane Andrew would have effected Keewaydin Island if the proposed project has been in place. Therefore official recognition of Hurricane Andrew is neither appropriate nor material for the purposes sought by Florida Audubon. Accordingly, I conclude that the Hearing Officer did not abuse her discretion in denying official recognition. I therefore reject the above noted exceptions. Official Recognition of Facts In the MSSW Permit Proceeding Before SFWMD. Florida Audubon's Exception No. 27, although lacking in specificity, appears to be taking exception to the Hearing Officer's implicit denial of taking official recognition of facts in the administrative proceedings of another case, i.e., the MSSW permit proceedings before the SFWMD. Apparently Florida Audubon is contending that the Hearing Officer erred in not taking official recognition of Florida Audubon's assertion that the SFWMD did not consider impacts on water quality when it issued the MSSW permit. As I noted in my discussion in Parts III(3) and III(4) above, the Department may properly rely on the issuance of an MSSW permit as reasonable assurance that the surface water management system will not cause violations of water quality standards. Regardless of whether the SFWMD properly considered water quality impacts when it issued the MSSW permit, in this case the issue is moot because a de novo proceeding was held where the record contains competent substantial evidence that the surface water management system provides reasonable assurance that the system will not cause violations of water quality standards. This exception is therefore rejected. Miscellaneous Exceptions. Exception 13 takes exception to the Hearing Officer's C.O.L. No. 38 describing the nature of the proffers made in the previous hearing. Since the hearing on remand was a de novo hearing on the issue of secondary impacts of the island development in which Florida Audubon presented all of its evidence related to the issue, I find no error that is relevant or material to this proceeding. Exception 13 is therefore rejected. Exception 14 takes exception to the Hearing Officer's C.O.L. No. 39 holding that the Department acted in good faith in its pre-hearing review of the information regarding the development. Once again, since the hearing was a de novo proceeding to establish the secondary impacts of the development I find no relevant or material error. Exception 14 is therefore rejected. Exceptions No. 19(A)-19(C) take exception to the Hearing Officer's C.O.L. No. 45, which concluded that the Department witnesses who disagreed with the proposed project did not apply the tests set forth in the statutes as did the Department witnesses who actually made the initial determination of whether the permit should issue. This exception also looses sight of the fact that this remand proceeding is a de novo determination of the facts. Florida Audubon presented witnesses who opposed the permit, and the Applicant presented witnesses and evidence in favor of the permit. The Department presented witnesses as to the Department's initial determination of the matter. I find no error and reject the exception. Exceptions 20(A) to 20(C) taking exception to the Hearing Officer's recommendations. These exceptions essentially are attacks on the Hearing Officer's findings of fact and conclusions of law as to reasonable assurances. The exceptions are denied for the same reasons stated in Parts III(3), (4) and (5) and IV(2) and (3). Exceptions 28 and 29 take exception to the Hearing Officer's acceptance of proposed findings of fact in the proposed recommended orders of the Applicant and the Department. These exceptions are redundant and are rejected for the same reasons stated in Parts III and IV(1)-(5) above.

Recommendation Based upon the foregoing, it is RECOMMENDED: That a Final Order be entered approving Respondent Builders' dredge and fill permit in DER File No. 111486645 filed August 31, 1988, subject to the following modifications: Specific condition number 6 should be amended to read: 6. Dredging shall be done by mechanical means (no hydraulic dredging) as there does not appear to be an appropriate area for discharge retention available. No dredging shall be allowed during the weeks of July 1st through September 30th of any year. If rock is encountered during the dredging activity along the proposed pipeline corridor, the rock is to be punctured by mechanical means. DONE and ENTERED this 7th day of December, 1989, in Tallahassee, Leon County, Florida. VERONICA E. DONNELLY Hearing Officer Division of Administrative Hearings The DeSoto Building 1230 Apalachee Parkway Tallahassee, Florida 32399-1550 (904)488-9675 Filed with the Clerk of the Division of Administrative Hearings this 7th day of December, 1989. APPENDIX TO RECOMMENDED ORDER Rulings on the proposed findings of fact filed by Petitioners are addressed as follows: Accept that John Remington holds the option on the property. See HO #1. Reject the rest of paragraph 1 as contrary to fact. See HO #6. Accept the description of the project locale. See HO #7. The rest is rejected as irrelevant. Outside scope of hearing. Accepted. See HO #7. Accepted. See HO #7. Rejected. Irrelevant. Outside scope of hearing. Rejected. Irrelevant. Outside scope of hearing. Rejected. Irrelevant. Outside scope of hearing. Accepted. Accepted. Rejected. Argumentative. Rejected. Improper summary. Irrelevant. Accepted. See Ho #2. Accepted. See Preliminary Matters. Rejected. Improper summary. Rejected. Immaterial. Accepted. Rejejcted. Improper summary. Accepted. Rejected. Immaterial. Rejected. Legal argument. Rejected. Beyond the reasonable assurances standards. Accepted as a reasonable possibility. See HO #11. Accept the first sentence. See HO #11. The rest is rejected as argumentative. Accept as a fact summary. The assumption portion is rejected as argumentative. Rejected. Premature analysis of future sewer treatment plant permit. Accept first sentence. The rest is rejected as argumentative and beyond scope of hearing. Accepted. Accepted to the point that such information could be known, based upon the methods used to form the opinion. Rejected. Argumentative. Respondent Builders' proposed findings of fact are addressed as follows: Accepted. See HO #4. Accepted. See HO #4. Accepted. See HO #2. Accepted. Accepted. See HO #7. Accepted. See HO #10. Accepted. See HO #7 and #9. Accepted. See HO #11. Accepted. See HO #8. Accepted. See HO #21. Rejected, except that there is no evidence of scour activity. There was insufficient evidence for the conclusion that the pass is very stable. Accepted. See HO #7. Accepted. See HO #4. Accepted. See HO #13. Accepted. See HO #21. Accepted. Rejected. Premature in this proceeding. Accepted. See HO #16 and #17. Accepted that reasonable assurances provided. See HO #11 and #16. Accepted. See HO #33. Accepted. See HO #13 through #16. Accepted. See HO #16 and #17. Accepted. Rejected. Repetitive. Accepted. See HO #31. Accepted. See HO #18. Rejected. Contrary to fact. See HO #21 and #29. Accepted. See HO #23-#25. Rejected. Contrary to fact. See HO #21, #22 and #29. Accepted. See HO #30. Accepted. Accepted. Respondent DER's proposed findings of fact are addressed as follows: Accepted. See HO #4 and HO #7. Accepted. See HO #5. Rejected. Contrary to fact. See HO #4. Accepted. See HO #4. Accepted. See HO #15. Accepted. See HO #16. Rejected. Contrary to fact. See HO #8. Accepted. Rejected. Conclusionary. See HO #21 and #29. Accepted. See HO #9. Accepted. See HO #10. Accepted. See HO #23. Accepted. Rejected. Contrary to fact. See HO #22. Accepted. See HO #22. Accepted. See HO #16. Accepted. Accepted. Accepted. See HO #13. Rejected. Speculative. Accepted. See HO #16. Accepted. Rejected. Speculative. Accepted. See HO #17. Accepted. See HO #5. Accepted. See HO #6. Rejected. Outside of scope of hearing. COPIES FURNISHED: Joseph Z. Fleming, Esquire 620 Ingraham Building 25 Southeast Second Avenue Miami, Florida 33131 Terry E. Lewis, Esquire Kevin S. Hennessy, Esquire MESSER VICKERS CAPARELLO FRENCH AND MADSEN Suite 301 2000 Palm Beach Lakes Boulevard West Palm Beach, Florida 33409 Richard Grosso, Esquire Assistant General Counsel Department of Environmental Regulation 2600 Blairstone Road Tallahassee, Florida 32399-2400 Daniel H. Thompson, Esquire General Counsel Department of Environmental Regulation 2600 Blairstone Road Tallahassee, Florida 32399-2400 Dale H. Twachtmann, Secretary Department of Environmental Regulation 2600 Blairstone Road Tallahassee, Florida 32399-2400 =================================================================

Florida Laws (7) 120.52120.57120.68373.016373.114373.418403.087 Florida Administrative Code (2) 18-21.00340E-4.301
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ENPOWER, INC., FOR ITSELF AND FOR FLORIDA SEAWATER DESALINATION COMPANY (NOT INC.) vs TAMPA BAY WATER, A REGIONAL WATER SUPPLY AUTHORITY, 99-003398BID (1999)
Division of Administrative Hearings, Florida Filed:Clearwater, Florida Aug. 10, 1999 Number: 99-003398BID Latest Update: Jun. 17, 2004

The Issue This is a procurement protest. The ultimate issue is whether the Respondent’s award of the "Agreement for the Construction and Operation of a Seawater Desalination Plant and Water Purchase Agreement" ("WPA") to Intervenor, S & W Water, LLC ("S&W") on July 19, 1999, is contrary to Tampa Bay Water's (TBW’s) governing statutes, its rules or policies, or the proposal specifications, or is clearly erroneous, contrary to competition, arbitrary, or capricious. Additional issues presented for decision are: (1) whether Petitioner has standing to maintain this protest; and (2) whether, by participating in the procurement process, Petitioner has waived or is estopped from claiming irregularities arising out of that process.

Recommendation Based on the foregoing Findings of Fact and Conclusions of Law, it is recommended that TBW enter a Final Order denying Petitioner's Formal Protest. Jurisdiction is reserved for consideration of S&W's request for a determination of improper purpose under Section 120.595(1), Florida Statutes, if such request is made by motion within 10 days from the issuance of this Recommended Order. DONE AND ENTERED this 25th day of October, 1999, in Tallahassee, Leon County, Florida. J. LAWRENCE JOHNSTON Administrative Law Judge Division of Administrative Hearings The DeSoto Building 1230 Apalachee Parkway Tallahassee, Florida 32399-3060 (850) 488-9675 SUNCOM 278-9675 Fax Filing (850) 921-6847 www.doah.state.fl.us Filed with the Clerk of the Division of Administrative Hearings this 25th day of October, 1999. COPIES FURNISHED: Charles W. Pittman, Esquire 400 North Tampa Street Suite 1040 Tampa, Florida 33602 Richard A. Harrison, Esquire John W. Wilcox, Esquire Allen, Dell, Frank & Trinkle, P.A. Post Office Box 2111 Barnett Plaza, Suite 1240 101 E. Kennedy Boulevard Tampa, Florida 33601-2111 Donald D. Conn, General Counsel Tampa Bay Water 2535 Landmark Drive Suite 211 Clearwater, Florida 33761-3950 John H. Rains, III, Esquire Annis, Mitchell, Cockey, Edwards & Roehn, P.A. Post Office Box 3433 One Tampa City Center, Suite 2100 Tampa, Florida 33601

Florida Laws (7) 120.57120.595163.01287.012287.057373.069620.8307 Florida Administrative Code (1) 49B-3.004
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