The Issue Whether proposed Water Use Permits Nos. 20012236.000 (the Potable Water Permit) and 20012239.000 (the Irrigation Permit) and proposed Environmental Resource Permit No. 43020198.001 (the ERP) should be issued by the Respondent, Southwest Florida Water Management District (the District).
Findings Of Fact The Parties The individual Petitioners, Farnsworth, Roop, and Varnum are all Florida citizens and residents of Sumter County. None of the individual Petitioners offered any evidence relating to direct impacts that the ERP would have on their property. With respect to the Potable Water and Irrigation Permits, anecdotal testimony was presented by Petitioners and Wing and Weir relating to well failures and sinkholes in the area. Two Petitioners, Roop and Varnum, live in close proximity to the property encompassed by the three permits. Petitioner Farnsworth’s property is approximately three and a half miles from the project boundary. Wing and Weir live approximately four and a half to five and 18 miles from the project site, respectively. SCAID is a Florida not-for-profit corporation that has approximately 130 members. Farnsworth, the president of SCAID, identified only Roop and Varnum as members who will be directly affected by the activities to be authorized by the permits. The District is the administrative agency charged with the responsibility to conserve, protect, manage, and control water resources within its boundaries. The Utility and the Authority are limited liability companies, of which the Villages Inc. is the managing partner. The Villages Inc. is a Florida corporation. The Utility, which will serve as a provider of potable water, is regulated by the Public Service Commission, while the Authority which will provide irrigation water, is not. The Villages Inc., Development The Villages Inc. is a phased, mixed use, retirement community, which is located at the intersecting borders of Lake, Marion, and Sumter Counties. Development has been on going since at least 1983, with a current planning horizon of the year 2019. Currently, there are 15,362 constructed dwelling units in the built-out portion of the Villages Inc. that are located in Lake County and the extreme northeast corner of Sumter County. The portion located in Marion County is 60 percent complete, with 750 homes completed and another 600 under construction. Approximately another 22,000 residences are planned for development in Sumter County by the year 2012, with an additional 10,200 by the year 2019. However, the Potable Water and Irrigation Permits are only for a six-year duration, and the ERP has a duration of only six years. None of the permits authorize development activities beyond that time frame. Generally speaking, the three permits at issue include an area owned by the Villages Inc. that lies in northeast Sumter County South of County Road 466 and North of County Road 466A. However, it is not projected that this entire area will be built-out during the terms of three proposed permits. Area Hydrology and Topography In the area of the Villages Inc., there is a layer of approximately five to ten feet of sand at the land surface, which is underlain by ten to 70 feet of a clayey sand. Both of these constitute the surficial aquifer and are extremely leaky, allowing water to percolate easily through to a lower layer. Except in the vicinity of Lake Miona, there is no water in the surficial aquifer except after rainfall events. The clayey sand layer is underlain by the Upper Floridan, a limestone unit. The top of this limestone layer ("the top of the rock") occurs at fluctuating depths of between 30 and 70 feet. At approximately 350 to 400 feet below the land surface, there begins a transition to a denser unit that serves as a confining layer between the Upper Floridan production zone and the Lower Floridan production zone. This confining layer, which was confirmed by drilling at three locations in the Villages Inc. is approximately 150 feet thick in the area of the Villages Inc. Another transition, this time to a less dense formation, begins at approximately 550 to 600 feet, which is considered the top of the Lower Floridan production zone. While testing conducted on the project site indicated almost no leakage between the Upper and Lower Floridan production zones, it is generally known by experts that there is some exchange of water between the two layers. Both the Upper and the Lower Floridan contain water that meets potable water standards and both are considered water production zones. The water quality of the two zones is not significantly different. The project area is prone to karst activity, that is, the formation of sinkholes. Sinkholes are formed as a result of the collapse of the overburden above subsurface cavities which have been formed through a very gradual dissolution of limestone, thus resulting in a "sink" at the land surface. Surface water bodies in the area include Lake Miona, Black Lake, Cherry Lake, and Dry Prairie, as well as several other small wetlands. The Potable Water and Irrigation Permits The potable water permit is for the withdrawal from the Upper Floridan Aquifer of 1.164 million gallons of water per day (MGD), on an annual average, for potable use in residences and both commercial and recreational establishments. It also limits the maximum withdrawal during peak months to 2.909 MGD. The Irrigation Permit is for the withdrawal from the Lower Floridan Aquifer of 2.850 MGD, on an annual average, for use in irrigation. The peak month usage rate permissible under the proposed permit would be 9.090 MGD. Water withdrawal under the Irrigation Permit will be used for the irrigation of residential lawns, common areas, commercial landscaping, and golf courses. Modeling of Drawdowns In assessing the impacts of proposed water withdrawals from an aquifer, District personnel considered effects on the aquifers and on-surface water features in the area. Computer- generated models of the predicted effects of the Potable Water and Irrigation Permits withdrawals provided one of the principal bases for this assessment. The primary geologist assigned to review the permit applications reviewed two of the models submitted by the Utility and the Authority (jointly the WUP Applicants) and ran one personal model of her own in order to predict the effects of the proposed withdrawals on the aquifers, as well as on any wetlands and other surface water bodies. In particular, the models predict both the vertical and horizontal extent to which the withdrawals may lower the level of water within the aquifers and in-surface waters under various conditions. One of the models submitted by the WUP Applicants predicted drawdowns during a 90-day period of no rainfall while the other predicted the impacts of the withdrawals over the life of the permits, considered cumulatively with the effects of withdrawals from the already-existing Villages' development in Sumter, Marion, and Lake Counties. The District’s geologist modeled the impacts of the withdrawals over the life of the permits and included the cumulative effects of all of the current Villages' withdrawals in Sumter County. All of these models included the combined effects of both the proposed Potable Water and the Irrigation Permits. Based upon these models, it is concluded that there will be no significant drawdowns as a result of the withdrawals authorized by the proposed water use permits. Specifically, the only predicted drawdown in the surficial aquifer (0.25 feet of drawdown) is in an area where there are no natural surface water features. Drawdown in the Upper Floridan is predicted at between 0.1 and 0.2 feet, while the drawdown in the Lower Floridan is predicted at a maximum of 1.5 feet. These minor drawdowns are not expected to cause any adverse impacts. Transmissivity is the rate at which water moves horizontally through the aquifer. In areas with high transmissivity, the results of water withdrawals from an aquifer will generally be low in magnitude, but broad in lateral extent. Water withdrawals from areas of low transmissivity will result in cones of depression that are more limited in lateral extent, but steeper vertically. The use of too high a transmissivity rate in a model, would overpredict the horizontal distance of the drawdowns caused by withdrawals, but would underpredict the vertical drawdown in the immediate vicinity of the withdrawal. Conversely, use of too low a transmissivity would over-predict the effects in the immediate vicinity of the withdrawal but underpredict the lateral extent of the drawdown. The WUP Applicants’ models used a transmissivity value for the Lower Floridan Aquifer of 100,000 feet squared per day ("ft.2/d'). The WUP Applicants’ consultant derived the transmissivity values from a regional model prepared by the University of Florida. The regional model uses a transmissivity value for the entire region of 200,000 ft.2/d for the Lower Floridan. While that transmissivity is appropriate for assessing large-scale impacts, on a more localized level, the transmissivity of the aquifer may be lower. Therefore, the WUP Applicants’ consultant met with District representatives and agreed to use a value half that used in the University of Florida model. A similar approach was used for the transmissivity value used in modeling effects in the Upper Floridan. Notably, specific transmissivity values recorded in four wells in the Villages Inc. area were not used because two of these wells were only cased to a depth of just over 250 feet, with an open hole below that to a depth of 590 feet. Thus, the transmissivity measured in these wells reflect conditions in the confining layer at the immediate location of the wells - not the transmissivity of the Lower Floridan production zone. Further, site-specific information on transmissivity, measured during pump tests at individual wells, does not correlate well to the transmissivity of the aquifer, even at short distances from the well. Transmissivities measured at individual wells are used to determine the depth at which the pump should be set in the well, not to determine the transmissivity of the aquifer. Thus, the use of transmissivities derived from the regional model, but adjusted to be conservative, is entirely appropriate. Moreover, using a transmissivity in her modeling of the project impacts of 27,000 ft.2/d for the Lower Floridan Aquifer, the district geologist’s model predicted no adverse impacts. Leakance is the measure of the resistance of movement vertically through confining units of the aquifer. The leakance value used by the District for the confining layer between the Upper and Lower Floridan was taken from the University of Florida model. Tests conducted on the site actually measured even lower leakance values. Thus, the evidence establishes that the leakance value used in the WUP Applicants’ and the District’s modeling for the Floridan confining layer was reasonable and appropriate. Competent, substantial evidence also establishes that the leakance value used for Lake Miona was reasonable. The WUP Applicants submitted to the District substantial data, gathered over several years, reflecting the balance of water flowing into Lake Miona and the lake’s levels in relation to the potentiometric surface. This documentation verified the leakance value used for Lake Miona in the modeling. Finally, the District modeling used appropriate boundary condition parameters. The District modeling used what is known as the "constant head" boundary and assumes the existence of water generated off-site at the boundaries. Such a boundary simulates the discharge of the aquifer at a certain level. The use of constant head boundaries is an accepted practice. The modeling conducted on behalf of the District and the Applicants provides a reasonable assurances that the Potable Water and Irrigation Permits will not cause adverse water quality or quantity changes to surface or groundwater resources, will not cause adverse environmental impacts to natural resources, and will not cause pollution of the aquifer. Furthermore, because the predicted drawdowns are so insignificant, reasonable assurances have been provided that the withdrawals will not adversely impact existing off-site land uses or existing legal withdrawals. The modeling also provides reasonable assurances that the withdrawals will not be harmful to the water resources of the District. Moreover, monitoring requirements included in the proposed Potable Water and Irrigation Permits provide additional reasonable assurance that – should the withdrawal effects exceed those predicted by the modeling – such effects are identified and necessary steps are taken to mitigate for any potential impacts. The District has reserved the right to modify or revoke all or portions of the water use permits under certain circumstances. Specifically, the proposed Potable Water Permit requires a monitoring plan that includes the following pertinent provisions: There shall be no less than three control wetland and ten onsite wetland monitoring sites; A baseline monitoring report, outlining the current wetland conditions; * * * A statement indicating that an analysis of the water level records for area lakes, including Miona Lake, Black Lake, Cherry Lake, Lake Deaton and Lake Griffin, will be included in the annual report; A statement indicating that an analysis of the spring flow records for Gum Spring, Silver Spring, and Fenney Spring, will be included in the annual report; * * * Wildlife analyses for potentially impacted wetlands, lakes, and adjacent property owner uses or wells, including methods to determine success of the mitigation; A mitigation plan for potentially impacted wetlands, lakes, and adjacent property owner uses or wells, including methods and thresholds to determine success of the mitigation; An annual report of an analysis of the monitoring data . . . . Similar provisions are included in the proposed irrigation permit. The WUP Applicants, in conjunction with the District, have developed sites and methodologies for this monitoring. Reasonable Demand The water to be withdrawn under the proposed Potable Water Permit will serve 10,783 people. This total results from the simple multiplication of the number of residences to be built during the next six years (5,675) by the average number of residents per household (1.9). Those numbers are based upon historical absorption rates within the Villages Inc. development since 1983, an absorption rate that doubles approximately every five years. The Utility proposed a per capita use rate of 108 gallons per day for potable use only. District personnel independently verified that per capita rate, based upon current usage in the existing portions of the Villages Inc. and determined that the rate was reasonable. Based upon the population projections and the per capita rate, the District determined that there is a reasonable demand for the withdrawal of the amount of water, for potable purposes, that is reflected in the Potable Water Permit. The Utility has provided reasonable assurance regarding the Utility’s satisfaction of this permitting criterion. As to the irrigation permit, the Villages Inc. plans, within the next six years, to complete the construction of 1,911 acres of property that will require irrigation. The amount of water originally requested by the Authority for irrigation withdrawals was reduced during the course of the application process at the request of the District. The District determined the reasonable amount of irrigation water needed through the application of AGMOD, a computer model that predicts the irrigation needs of various vegetative covers. Since the Authority intends to utilize treated wastewater effluent as another source of irrigation water, the District reduced the amount of water that it would permit to be withdrawn from the Lower Floridan for irrigation. The District, thus, determined that the Authority would need 1.59 MGD annual average for recreational and aesthetic area irrigation and 1.26 MGD annual average for residential lawn irrigation, for a total of 2.85 MGD. The Villages Inc. also plans to accumulate stormwater in lined ponds for irrigation use. However, unlike its treatment of wastewater effluent, the District did not deduct accumulated stormwater from the amount of water deemed necessary for irrigation. This approach was adopted due to the inability to predict short-term rainfall amounts. The uncontroverted evidence of record establishes reasonable assurances that there is a reasonable demand for the amount of water to be withdrawn under the proposed irrigation permit. Conservation and Reuse Measures Both the Utility and the Authority applications included proposed measures for the conservation and reuse of water. The conservation plan submitted in conjunction with the irrigation permit application provides for control valves to regulate both the pressure and timing of irrigation by residential users; contractual restrictions on water use by commercial users; xeriscaping; and an irrigation control system for golf course irrigation that is designed to maximize the efficient use of water. In addition, in the proposed permits, the District requires the Utility and the Authority to expand upon these conservation measures through such measures as educational efforts, inclined block rate structures, and annual reporting to assess the success of conservation measures. The Authority also committed to reduce its dependence on groundwater withdrawals through the reuse of wastewater effluent, both from the on-site wastewater treatment facility and through contract with the City of Wildwood. Reasonable assurances have been provided that conservation measures have been incorporated and that, to the maximum extent practicable, reuse measures have been incorporated. Use of Lowest Available Quality of Water In addition to the reuse of treated wastewater effluent, the Authority intends to minimize its dependence on groundwater withdrawals for irrigation use through the reuse of stormwater accumulated in lined ponds. Thirty-one of the lined stormwater retention ponds to be constructed by the Villages Inc. are designed as a component of the irrigation system on-site. Ponds will be grouped with the individual ponds within each group linked through underground piping. There will be an electronically controlled valve in the stormwater pond at the end of the pipe that will be used to draw out water for irrigation purposes. These lined stormwater ponds serve several purposes. However, the design feature that is pertinent to the reuse of stormwater for irrigation is the inclusion of additional storage capacity below the top of the pond liner. No groundwater will be withdrawn for irrigation purposes unless the level of stormwater in these lined ponds drops below a designed minimum irrigation level. Groundwater pumped into these ponds will then be pumped out for irrigation. Thus, the use of groundwater for irrigation is minimized. The Authority has met its burden of proving that it will use the lowest quality of water available. With respect to the potable permit, the evidence establishes that there are only minor differences between the water quality in the Upper Floridan and Lower Floridan in this area. The Upper Floridan is a reasonable source for potable supply in this area. Thus, reasonable assurances have been provided by the Utility that it will utilize the lowest water quality that it has the ability to use for potable purposes. Waste of Water In regard to concerns that the design of the Villages Inc.'s stormwater/irrigation system will result in wasteful losses of water due to evaporation from the surface of the lined ponds, it must be noted that there are no artesian wells relating to this project and nothing in the record to suggest that the groundwater withdrawals by either the Utility or the Authority will cause excess water to run into the surface water system. Additionally, the evidence establishes that, to the extent groundwater will be withdrawn from the Lower Floridan and pumped into lined stormwater ponds, such augmentation is not for an aesthetic purpose. Instead, the groundwater added to those ponds will be utilized as an integral part of the irrigation system and will be limited in quantity to the amount necessary for immediate irrigation needs. Finally, the water to be withdrawn will be put to beneficial potable and irrigation uses, rather than wasteful purposes. Under current regulation, water lost from lined stormwater ponds through evaporation is not considered as waste. Thus, the Authority and the Utility have provided reasonable assurances that their withdrawals of groundwater will not result in waste. The ERP The stormwater management system proposed by the Villages Inc. will eventually serve 5,016 acres on which residential, commercial, golf course, and other recreational development will ultimately be constructed. However, the proposed permit currently at issue is preliminary in nature and will only authorize the construction of stormwater ponds, earthworks relating to the construction of compensating flood storage, and wetland mitigation. Water Quality Impacts The stormwater management system will include eight shallow treatment ponds that will be adjacent to Lake Miona and Black Lake and 45 lined retention ponds. Thirty-one of these lined ponds will serve as part of the irrigation system for a portion of the Villages Inc.'s development. All of these ponds provide water quality treatment. The unlined ponds will retain the first one inch of stormwater and then overflow into the lakes. The ponds provide water quality treatment of such water before it is discharged into the lakes. The water quality treatment provided by these ponds provides reasonable assurances that the project will not adversely impact the water quality of receiving waters. While they do not discharge directly to surface receiving waters, the lined retention ponds do provide protection against adverse water quality impacts on groundwater. There will be some percolation from these ponds, from the sides at heights above the top of the liner. However, the liners will prevent the discharge of pollutants through the highly permeable surface strata into the groundwater. The Villages Inc. designed the system in this manner in response to concerns voiced by the Department of Environmental Protection during the DRI process regarding potential pollutant loading of the aquifer at the retention pond sites. Furthermore, by distributing the accumulated stormwater - through the irrigation system - over a wider expanse of vegetated land surface, a greater degree of water quality treatment will be achieved than if the stormwater were simply permitted to percolate directly through the pond bottom. There is no reasonable expectation that pollutants will be discharged into the aquifer from the lined ponds. If dry ponds were used, there would be an accumulation of pollutants in the pond bottom. These measures provide reasonable assurances that there will be no adverse impact on the quality of receiving waters. Water Quantity Impacts With regard to the use of lined retention ponds, as part of the Villages Inc.’s stormwater system and the impact of such ponds on water quantity, the evaporative losses from lined ponds as opposed to unlined ponds is a differential of approximately one (1) inch of net recharge. The acreage of the lined ponds - even measured at the very top of the pond banks - is only 445 acres. That differential, in terms of a gross water balance, is not significant, in view of the other benefits provided by the lined ponds. As part of the project, wetlands will be created and expanded and other water bodies will be created. After rainfalls, these unlined ponds will be filled with water and will lose as much water through evaporation as would any other water body. The design proposed by the Villages Inc., however, will distribute the accumulated stormwater across the project site through the irrigation of vegetated areas. The documentation submitted by the Villages Inc. establishes that the ERP will not cause adverse water quantity impacts. The Villages Inc. has carried its burden as to this permitting criterion. Flooding, Surface Water Conveyance, and Storage Impacts Parts of the project are located in areas designated by the Federal Emergency Management Administration (FEMA) as 100-year flood zones. Specifically, these areas are located along Lake Miona, Black Lake, between Black Lake and Cherry Lake, and at some locations south of Black Lake. Under the District’s rules, compensation must be provided for any loss of flood zone in filled areas by the excavation of other areas. The District has determined, based upon the documentation provided with the Villages Inc.’s application, work on the site will encroach on 871.37 acre feet of the FEMA 100-year flood zone. However, 1,051.70 acre feet of compensating flood zone is being created. The Villages Inc. proposes to mitigate for the loss of flood zone primarily in the areas of Dry Prairie and Cherry Lake. At present, Cherry Lake is the location of a peat mining operation authorized by DEP permit. Mining has occurred at that site since the early 1980s. The flood zone mitigation proposed by the Villages Inc. provides reasonable assurance that it will sufficiently compensate for any loss of flood basin storage. The Villages Inc.'s project provides reasonable assurance that it will neither adversely affect surface water storage or conveyance capabilities, surface or groundwater levels or surface water flows nor cause adverse flooding. Each of the 45 retention ponds to be constructed on-site will include sufficient capacity, above the top of the pond liner, to hold a 100-year/24-hour storm event. This includes stormwater drainage from off-site. In addition, these ponds are designed to have an extra one foot of freeboard above that needed for the 100-year/24-hour storm, thus providing approximately an additional 100 acres of flood storage beyond that which will be lost through construction on-site. Furthermore, the Villages Inc. has proposed an emergency flood plan. In the event of a severe flood event, excess water will be pumped from Dry Prairie, Cherry Lake, and Lake Miona and delivered to the retention ponds and to certain golf course fairways located such that habitable living spaces would not be endangered. Environmental Impacts and Mitigation There are 601 acres of wetlands and surface waters of various kinds in the Villages Inc.’s project area. Forty-one acres of wetlands will be impacted by the work that is authorized under the ERP. Each of these impacted wetlands, along with the extent of the impact, is listed in the ERP. The impacts include both fill and excavation and all will be permanent. When assessing wetland impacts and proposed mitigation for those impacts, the District seeks to ensure that the activities proposed will not result in a net loss of wetland functionality. The object is to ensure that the end result will function at least as well as did the wetlands in their pre-impact condition. Functional value is judged, at least in part, by the long term viability of the wetland. While small, isolated wetlands are not completely without value, large wetland ecosystems – which are less susceptible to surrounding development – generally have greater long-term habitat value. The District’s policy is that an applicant need not provide any mitigation for the loss of habitat in wetlands of less than 0.5 acre, except under certain limited circumstances, including where the wetland is utilized by threatened or endangered species. Some wetlands that will be impacted by the Villages Inc.’s project are of high functional value and some are not as good. The Villages Inc. proposes a variety of types of mitigation for the wetlands impacts that will result from its project, all of which are summarized in the ERP. In all, 331.55 acres of mitigation are proposed by the Villages Inc. First, the District proposes to create new wetlands. Approximately 11 acres of this new wetland will consist of a marsh, which is to be created east of Cherry Lake. Second, it proposes to undertake substantial enhancement of Dry Prairie, a 126-acre wetland. Currently – and since at least the early nineties – Dry Prairie received discharge water from the peat mining operation at Cherry Lake. Without intervention, when the mining operations stop, Dry Prairie would naturally become drier than it has been for several years and would lose some of the habitat function that it has been providing. The Villages Inc.’s proposed enhancement is designed to match the current hydroperiods of Dry Prairie, thus ensuring its continued habitat value. Third, the Villages Inc. has proposed to enhance upland buffers around wetlands and surface waters by planting natural vegetation, thus providing a natural barrier. Placement of these buffers in conservation easements does not provide the Villages Inc. with mitigation credit, since a 25-foot buffer is required anyway. However, the District determined that the enhancement of these areas provided functional value to the wetlands and surface waters that would not be served by the easements alone. Fourth, the Villages Inc. will place a conservation easement over certain areas, including a 1500-foot radius preserve required by the Fish and Wildlife Conservation Commission (FWCC) around an identified eagles’ nest. These areas will also be used for the relocation of gopher tortoises and, if any are subsequently located, of gopher frogs. While the Villages Inc. is also performing some enhancement of this area, it will receive no mitigation credit for such enhancement – which was required to meet FWCC requirements. However, since the conservation easement will remain in effect in perpetuity, regardless of whether the eagles continue to use the nest, the easement ensures the continued, viability of the area’s wetlands and provides threatened and endangered species habitat. In order to provide additional assurances that these mitigation efforts will be successful, the District has included a condition in the proposed permit establishing wetland mitigation success criteria for the various types of proposed mitigation. If these success criteria are not achieved, additional mitigation must be provided. With the above described mitigation, the activities authorized under the ERP will not adversely impact the functional value of wetlands and other surface waters to fish or wildlife. The Villages Inc. has met its burden of providing reasonable assurances relating to this permit criterion. Capability of Performing Effectively The Villages Inc. has also provided reasonable assurances that the stormwater management system proposed is capable of functioning as designed. The retention ponds proposed are generally of a standard-type design and will not require complicated maintenance procedures. In its assessment of the functional capability of the system, the District did not concern itself with the amount of stormwater that the system might contribute for irrigation purposes. Rather, it focused its consideration on the stormwater management functions of the system. The question of the effectiveness of the system for irrigation purposes is not relevant to the determination of whether the Villages Inc. has met the criteria for permit issuance. Consequently, the record establishes that the documentation provided by the Villages Inc. contains reasonable assurances that the stormwater system will function effectively and as proposed. Operation Entity The Villages Inc. has created Community Development District No. 5 (CDD No. 5), which will serve as the entity responsible for the construction and maintenance of the stormwater system. CDD No. 5 will finance the construction through special revenue assessment bonds and will finance maintenance through the annual assessments. Similar community development districts were established to be responsible for earlier phases of the Villages Inc. The ERP includes a specific condition that, prior to any wetlands impacts, the Villages Inc. will either have to provide the District with documentation of the creation of a community development district or present the District with a performance bond in the amount of $1,698,696.00. Since the undisputed testimony at hearing was that CDD No. 5 has, in fact, now been created, there are reasonable assurances of financial responsibility. Secondary and Cumulative Impacts The Villages Inc.’s application also provides accurate and reliable information sufficient to establish that there are reasonable assurances that the proposed stormwater system will not cause unacceptable cumulative impacts upon wetlands or other surface waters or adverse secondary impacts to water resources. The system is designed in a manner that will meet water treatment criteria and there will be no secondary water quality impacts. Further, the use of buffers will prevent secondary impacts to wetlands and wetland habitats and there will be no secondary impacts to archeological or historical resources. In this instance, the stormwater system proposed by the Villages Inc. will function in a manner that replaces any water quantity or water quality functions lost by construction of the system. In its assessment of the possible cumulative impacts of the system, the District considered areas beyond the bounds of the current project, including the area to the south that is currently being reviewed under the DRI process as a substantial deviation. The District’s environmental scientist, Leonard Bartos, also reviewed that portion of the substantial deviation north of County Road 466A, in order to determine the types of wetlands present there. Furthermore, the District is one of the review agencies that comments on DRI and substantial deviation applications. When such an application is received by the District’s planning division, it is routed to the regulatory division for review. The District includes its knowledge of the DRIs in its determination that there are no cumulative impacts. Reasonable assurances have been provided as to these permitting criteria. Public Interest Balancing Test Because the proposed stormwater system will be located in, on, and over certain wetlands, the Villages Inc. must provide reasonable assurances that the system will not be contrary to the public interest. This assessment of this permitting criteria requires that the District balance seven factors. While the effects of the proposed activity will be permanent, the Villages Inc. has provided reasonable assurances that it will not have an adverse impact on the public health, safety, or welfare; on fishing or recreational values; on the flow of water; on environmental resources, including fish and wildlife and surface water resources; or on off-site properties. Furthermore, the District has carefully assessed the current functions being provided by the affected wetland areas. With respect to historical or archeological resources, the Villages Inc. has received letters from the Florida Department of State, Division of Historical Resources, stating that there are no significant historical or archeological resources on the project site that is the subject of this permit proceeding. Thus, the evidence establishes reasonable assurances that the Villages Inc.'s stormwater system will not be contrary to the public interest. Additionally, the District and Applicant presented uncontroverted evidence that the proposed project will not adversely impact a work of the District, and that there are no applicable special basin or geographic area criteria.
Recommendation Based on the foregoing findings of fact and conclusions of law, it is: RECOMMENDED that a final order be entered issuing Water Use Permit Nos. 20012236.000 and 20012239.000 and Environmental Resource Permit No. 43020198.001, in accordance with the District’s proposed agency action. DONE AND ENTERED this 24th day of June, 2002, in Tallahassee, Leon County, Florida. DON W. DAVIS 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 24th day of June, 2002.
The Issue Whether the applicants own the property in question? Whether the project would comply with the criteria of the South Florida Water Management District contained in Basis of Review for Surface Water Management Systems, specifically Sections 3.1.3 and 3.2? Whether flood protection would be inadequate or septic tanks unsuitable or whether the public health and safety would be compromised or the ultimate purchasers be deprived of usage of the property due to inundation in violation of Chapter 373, Florida Statutes (1981), or Rule 40E-4.301(1), Florida Administrative Code?
Findings Of Fact Ms. Williamson and Messrs. Leggett and Collins hold in fee simple a triangular 117.24-acre parcel in Okeechobee County as tenants in common under a warranty deed executed in their favor by one W. C. Sherman. They propose to develop the property as a trailer park (complete with airstrip) large enough to accommodate 109 trailers. To this end, soil would be dug up from the center of the property and used to raise the elevation of the surrounding land above the 100-year floodplain. (T. 47) The applicants have a dredging permit from the Department of Environmental Regulation authorizing them to excavate 629,889 cubic yards. They are proposing to dig to a depth of 76 feet below ground. This would create an 18-acre body of water ("Poe's Lake") which would overflow a V-notched weir into a county canal. The county canal would take the water to C- 38, one of the large canals to which the Kissimmee River has been relegated, at a point about 18 miles upstream from Lake Okeechobee. Runoff would wash over residential lots and roadways; the site would be graded to assure drainage into Poe's Lake. The minimum road crest elevation would be 30 feet NGVD ("[a]round twenty-nine feet" T.52), as compared to the control elevation for surface waters of 28.5 feet NGVD. WATER QUALITY The developers plan septic tanks for wastewater treatment. At the close of all the evidence, counsel for the applicants stated that sanitary sewers could be installed instead. Respondents' Proposed Recommended Order, p. With all the housing units in use, at least 10,900 gallons of effluent would seep into the ground from the tanks daily. There would be some evapotranspiration, but all the chemicals dissolved in the effluent would eventually end up in the groundwater. During the dry season, septic tank effluent would cause mounding of the groundwater and some groundwater movement toward, and eventual seepage into, Poe's Lake. The eventual result would be eutrophication and the growth of algae or macrophytes on the surface of Poe's Lake. This would cause dissolved oxygen violations in Poe's Lake. Discharges from the lake would inevitably occur, aggravating the situation in C-38, which already experiences dissolved oxygen levels below 5.0 milligrams per liter in the rainy summer months. Some fraction of the nutrients in the effluent from the septic tanks would ultimately reach Lake Okeechobee itself. The sheer depth of the excavation would create another water quality problem. Under the anaerobic conditions that would obtain at the bottom of Poe's Lake, bacteria acting on naturally occurring sulfates would produce hydrogen sulfide, ammonia and various other reduced organic nitrogen compounds. These substances are toxic to human beings and would, in some indeterminate quantity, enter the groundwater from Poe's Lake. This would affect the taste and perhaps the potability of water from any well nearby. It would be "possible to design a better system where there would be nutrient removal and a greatly reduced probability of violation of the dissolved oxygen criterion and obviation of the potential for ground water contamination." (T. 200) Installation of a baffle on the weir would serve to prevent buoyant debris from entering surface waters of the state. BASIS OF REVIEW Official recognition was taken of the "Basis of Review for Surface Water Management Permit Applications Within the South Florid Water Management District," parts of which all parties agree pertain in the present proceedings. Among the criteria stated in this document are: 3.1.3 Waste and Wastewater Service - Potable water and wastewater facilities must be identified. The Applicant for a Surface Water Management Permit must provide information on how these services are to be provided. If wastewater disposal is accomplished on-site, additional information will normally be requested regarding separation of waste and storm systems. 3.2.1.4 Flood protection - Building floors shall be above the 100 year flood elevations, as determined from the most appropriate information, including Federal Flood Insurance Rate Maps. Both tidal flooding and the 100 year, 3 day storm event shall be considered in determining elevations. b. Commercial and industrial projects to be subdivided for sale are required to have installed by the permittee, as a minimum, the required water quality system for one inch of runoff detention or one half inch of runoff retention from the total developed site. State standards - Projects shall be designed so that discharges will meet State water quality standards, as set forth in Chapter 17-3, Retention/detention criteria - Retention and/or detention in the overall system, including swales, lakes, canals, greenways, etc., shall be provided for one of the three following criteria or equivalent combinations thereof . . . Wet detention volume shall be provided for the first inch of runoff from the developed project, or the total runoff from a 3-year, 1-hour rainfall event, whichever is greater. Dry detention volume shall be provided equal to 75 percent of the above amounts computed for wet detention. Retention volume shall be provided equal to 50 percent of the above amounts computed for wet detention. 3.2.4.1 Discharge structures should include gratings for safety and maintenance purposes. The use of trash collection screens is desirable. Discharge structures shall include a "baffle" system to encourage discharge from the center of the water column rather than the top or bottom. 3.2.4.4.2 b. Control elevations should be no higher than 2 feet below the minimum road centerline elevation in the area served by the control device in order to protect the road subgrade. Simply detaining runoff before discharging it offsite will not insure that the water quality standards set forth in Chapter 17-3 will be met. Whether the standards are met depends on, among other things, the composition of the runoff. FWF'S INTEREST Among the purposes of the FWF, as stated in its charter, Shall be to further advance the cause of conservation in environmental protection, to perpetuate and conserve fish and wildlife, oil, water, clean air, other resources of the State and so manage the use of all natural resources, that this generation and posterity will receive the maximum benefit from the same. (T. 248-9) Four or five thousand Floridians belong to FWF. FWF members "make use" (T. 250) of the waters of Lake Okeechobee, the Kissimmee River and specifically of the waters in C-38. PROPOSED FINDINGS CONSIDERED The applicants and FWF filed post hearing memoranda and proposed recommended orders including proposed findings of fact which have been considered in preparation of the foregoing findings of fact. They have been adopted, in substance, for the most part. To the extent they have been rejected, they have been deemed unsupported by the weight of the evidence, immaterial, cumulative or subordinate.
Recommendation Upon consideration of the foregoing, it is RECOMMENDED: That SFWMD deny the pending application for surface water management permit. DONE and ENTERED this 29th day of November, 1983, in Tallahassee, Florida. ROBERT T. BENTON II, Hearing Officer Division of Administrative Hearings The Oakland Building 2009 Apalachee Parkway Tallahassee, Florida 32301 (904) 488-9675 Filed with the Clerk of the Division of Administrative Hearings this 29th day of November, 1983. COPIES FURNISHED: Dennis J. Powers, Esquire Gunster, Yoakley, Criser & Stewart 400 South County Road Palm Beach 33480 Terrell K. Arline, Esquire 325-C Clematis Street West Palm Beach, Florida 33401 Irene Kennedy Quincey, Esquire 3301 Gun Club Road West Palm Beach, Florida 33406 Charles P. Houston, Esquire 324 Datura Street, Suite 106 West Palm Beach, Florida 33401
The Issue Whether the Mosquito Ditch Exemption of Section 373.4211(25), Florida Statutes, applies so as to exclude Petitioners' property adjacent to Miguel Bay in Manatee County from the permitting authority of the Department of Environmental Protection? If not, whether Petitioners are entitled to an Environmental Resources Permit from the Department?
Findings Of Fact The Property Not far from the southern terminus of the Sunshine Skyway Bridge spanning the waters where Tampa Bay and the Gulf of Mexico meet is a subdivision known as San Miguel Estates. On the western shore of Terra Ceia Island in Manatee County, it takes its name from an adjacent body of water: Miguel Bay. Miguel Bay is classified by rule of the Department of Environmental Protection as Class II surface waters meaning it has been designated usable for "Shellfish Propagation or Harvesting," Rule 62.302-400(1), Florida Administrative Code. The classification is the highest available to surface waters which are not fresh. As a part of the Terra Ceia Aquatic Preserve, Miguel Bay also enjoys the status of an Outstanding Florida Water, so designated by the Environmental Regulation Commission to confirm its worthiness to receive special protection because of natural attributes. See Rules 62- 302.200(17) and 62-302.700(9)(h)39., Florida Administrative Code. The bay surrounds the subdivision together with two bayous, Custer to the northwest and Tillette to the southeast. The mouth of Tillette Bayou is formed by Boots Point, also a part of Terra Ceia Island and the subdivision jutting into the bay directly north of the point. The bay surrounds or washes onto the shores of a number of keys: Sister, Skeet, Ed's, and Rattlesnake. Through the middle of the subdivision runs a county- maintained road: Miguel Bay Drive. It provides access to a cul- de-sac containing seven lots. Lots 2, 6, 7, and 8 are fully improved with residential structures, boat docks and elevated walkways. Lots 3 and 4 are undeveloped. An application for a permit to construct a house on Lot 3 was denied in the early part of this decade. It is uncertain whether Lot 4 is permitted for a residential structure but an application for a permit to construct a boardwalk on the property is pending. The lot owned by the petitioner and his wife, also undeveloped, is Lot 5. Consisting of approximately 5.5 acres on the south side of Miguel Bay Drive, Lot 5 is within the geographical jurisdiction of the Southwest Florida Water Management District. It contains wetlands contiguous to the bay. The wetlands have suffered various disruptions over the years. In addition, to mosquito ditches dug more than 30 years ago, a dike was built around the same time to prevent the gulf tide from flowing onto the property. Furthermore, part of the property was cleared at one time as part of an agricultural venture. On its northern side, adjacent to Miguel Bay Drive, is the property’s approximate 0.9 acres of uplands. On the opposite side of the lot, where the wetlands meet the bay, the Petitioners plan a boat basin. A section of the proposed boat channel serving the basin, where it connects to the bay, is located within the Outstanding Florida Waters boundary of the bay. The boat basin will be part of a residential project planned by Mr. and Mrs. McGinnis. In addition to an access drive and the boat basin and channel, the Petitioners plan to build a house in the middle of the lot. In the mid-1960’s, Lot 5 was ditched for mosquito control. The mosquito control ditches transect the property along two lines running roughly east-west: one, just to the south of the uplands, not too far from the road; the other, just to the north of the dike and a mean high-water line approximated by Mr. and Mrs. McGinnis’ engineer, John Benson. Valuable Mangroves Mangroves cover the bulk of the property south of the uplands. Most are normal-sized. For example, “[a]ll the mangroves up . . . at the mosquito ditch going toward the . . . street [are] huge, . . . 10, 15, 20 feet.” (Tr. 41.) The mangroves closer to San Miguel Bay, too, are normal-sized. But in a basin in the center of the property there is an acre or so of “stunted mangroves that [are] only . . . three to four feet tall." (Tr. 39.) "And that [is] very unusual . . . there [is] obviously something wrong with them.” (Tr. 40-41.) The problem for the stunted mangroves is stress in their root zone due to "anoxia in the soil, that is, lack of oxygen." (Tr. 318). The anoxia is most likely a function of location: the stunted mangroves are in a basin surrounded by the mosquito ditches. The normal-sized mangroves are not experiencing anoxia because they are better irrigated. Those alongside or in the mosquito ditches are irrigated by the water which collects in the ditches while those in the southernmost part of the property are irrigated by tidal froth from the bay. Although the property has been ditched, diked and bermed (and may have even been tilled at one time for agricultural purposes after it was cleared), the mangroves on the property serve a valuable ecological function, particularly to the bay. The height of the mangroves does not alter their ecological value because the value is largely in their root system. The entire root system of the mangroves covering over four-fifths of the property serves as a filtration base for water running off the uplands. It provides, moreover, critical habitat for commercially important species such as redfish and snook. Building a residence in the middle of this mangrove swamp, even were it to disrupt only the stunted mangroves, would cause adverse ecological impact. The adverse impact would fall heavily on the bay because it needs the natural flushing action allowed by the uninterrupted tangle of mangroves covering more than four acres of the five and one-half acre plot. At the same time, wildlife enjoy orderly habitat in the mangroves on the property. The presence of a residence and the alterations to the property, particularly the loss of well over an acre of a mangrove root-system caused by dredging and filling to support the residence, would render the remaining mangrove wetlands on the property much less supportive of the wildlife inhabiting it now and the wildlife that would otherwise inhabit it in the future. The Parties Petitioners moved to Florida from Illinois in 1991. Mel McGinnis is a double above-the-knee amputee who walks with the aid of prosthetic devices. Pamela McGinnis is a licensed real estate broker. Mr. and Mrs. McGinnis live in Palmetto where Mrs. McGinnis conducts her real estate business. The Department of Environmental Protection is the state administrative agency with permitting authority under Part IV of the Florida Water Resources Act of 1972, Chapter 373, Florida Statutes and Chapters 62-330, 62-341 and 62-343, Florida Administrative Code, as well as Section 404 of the federal Clean Water Act (33 U.S.C. 1344). Pursuant to operating agreements executed between the Department and the Southwest Florida Water Management District (SWFWMD) via the authority of Chapter 62-113, Florida Administrative Code, the Department is responsible in this case for reviewing the permit application of the Petitioners. Manasota-88, Inc., filed a petition to intervene which was granted subject to proof of standing at hearing. No proof of standing was offered, however; Manasota-88's status as an Intervenor has been rescinded and it has been dismissed as a party to the proceeding. See Paragraphs 78 - 81, below in the Conclusions of Law section of this order. Acquisition of the Property In 1993, Mel and Pamela McGinnis purchased Lot 5 in San Miguel Estates. They were attracted to the lot because of the more than 500 feet of waterfront it enjoyed on Miguel Bay. The seller of the property was the federal government. The sale was arranged through the United States Marshall’s office as part of a forfeiture proceeding. The property had been seized by federal authorities because of the illegal involvement in drug activity of its owner at the time of the seizure. Prior to a decision to make the purchase, Mr. and Mrs. McGinnis were concerned about clear title because of the property's shadowy history. They researched the matter at the county offices. Their concerns were allayed when they found no liens and discovered the property was part of a platted subdivision. They inquired whether there would be water or sewer services provided by local government. The county reported plans to put water lines in soon, a promise made good in 1994. In testimony, Mrs. McGinnis summed up the results of the pre- purchase investigation: “We really didn’t perceive [there] to be a problem.” (Tr. 22.) Plans to Develop and an Application for an ERP In 1995, the McGinnises began planning the construction of the residential structure and boat dock on Lot 5. Accompanied by their engineer, John Benson, they met on the site in August of 1995 with Ken Huntington, an environmental manager in the Environmental Resources Permitting Section of the Department. Before the meeting, the McGinnises believed the mosquito ditches to be creeks. After John Benson corrected the misimpression, Mr. Huntington indicated there was a possibility the property might qualify for a mosquito ditch exemption from environmental resource permitting. Mr. Huntington did not make a commitment, however, at this early stage of the case's development that the Department would determine the exemption applied. In fact, the Department insisted that an application for an Environmental Resources Permit be filed before a decision could be made on the exemption. Mr. and Mrs. McGinnis, on October 5, 1995, applied for the Environmental Resource Permit. The application sought authority to dredge and fill in waters of the state for the purpose of constructing a single-family residence, driveway, swimming pool and boat channel and basin. It showed the construction to have impact upon approximately 1.61 acres of wetlands. About 1.39 acres of the affected area would be cleared and filled for the construction of the home, pool, and driveway. The remainder of the area under impact (about .22 acres) would be excavated for the construction of the boat basin and channel. Two months later, in December of 1995, Mr. and Mrs. McGinnis submitted additional application materials. The submission consisted of several parts: a written statement from Larry Rhodes, the Mosquito Control Director for Manatee County from 1961-94; a proposed work order of the mosquito control district from 1966; information from their engineers; and, aerial photographs from 1960 and 1965. These materials were intended to support the assertion that Lot 5 was eligible for a mosquito control exemption from Environmental Resource Permitting. Preliminary DEP Action On April 1, 1996, a Preliminary Evaluation Letter was sent to Petitioners by the Department. The letter stated that based on site inspection, "it appears that the project cannot be recommended for approval." Petitioners' Exhibit 1-h. Cautioning that the preliminary evaluation did not represent final agency action, the letter went on to provide modifications which would reduce or compensate for the project's negative impacts. Among them, was "relocation of the proposed structure to a more landward location." Id. The letter was not preliminary in one way. It explained the Department’s final position that the project site did not qualify for the mosquito ditch exemption: As indicated in previous Department correspondence of January 19, 1996, the Department does not believe that the project meets the . . . exemption. Pursuant to 40D- 4.051(14), Florida Administrative Code, the subject exemption applies only to 'lands that have become surface waters or wetlands solely because of a mosquito control program, and which lands were neither wetlands nor other surface waters before such activities . . .' Historical aerial photographs do not support that the parcel was not previously wetlands. Id., at pg. 2. Ten days later, Mr. and Mrs. McGinnis, through their attorneys, requested a one-week extension to submit revised plans "which attempt[] to reduce the impacts in response to the issues . . . raised [by the April 1 correspondence]." Petitioners' Exhibit 1-i. In a letter dated April 17, 1996, Mr. McGinnis submitted the revised plans in the form of proposals designed by Benson Engineering and CCI Environmental Services. As a prelude to the proposed modifications it had designed, Benson Engineering wrote, We have spent considerable effort to reduce the negative impacts with out (sic) placing the development in the unacceptable upland. The location of the residence has been chosen due to the nature of the stressed mangroves. This area (approximately 1.6 acres) is characterized in a report by H. Clayton Roberson, Environmental Scientist with CCI Environmental Services, Inc. dated 29 January, 1996. The majority of the mangroves to be impacted are less than 3 feet in height, with atypical stunted growth. The current proposal reduces the impacts to only 45% of the stressed area, and only 24% impact to the total site. This 24% development ratio is also being mitigated with enhanced water circulation to the entire site, . . . Petitioners' Exhibit 1-j. In the cover letter submitting the proposed modifications, Mr. McGinnis' frustration at this point with the process was evident. At least two of the items in the letter demonstrate its depth: Property was purchased by us from the government with no disclosure by anyone or any recorded documentation that would have given us even a hint that building our home would become such a nightmare. This property is in a long established recorded subdivision, and all adjacent property owners are either built, under construction or permitted to build. Our property as submitted to you under the revised design is compatible with the surrounding neighborhood. Placement of any dwelling on the road will have a major negative impact on this parcel. I cannot stress enough the negative economic impact that would be incurred by this action. Petitioners' Exhibit 1-j. Denial On May 1, 1996, the Department issued its Notice of Denial. The notice contained five parts: I. Description of the Proposed Activity; II. Authority for Review; III. Reasons for Denial; IV. Proposed Changes; and V. Rights of Affected Parties. Part III of the notice (Reasons for Denial) cited a June 1995 site inspection. It included a description of the site: 5.5 acres, the majority of which, according to a 1952 Soil Conservation Service survey, is Tidal Swamp, and according to a 1983 Soil Survey is classified as Wulfert-Kesson Association soils. The site had been found during the inspection to be dominated by mangroves, red, black and white. Other vegetation associated with wetlands had been observed "within the subject system at the time of inspection" (Petitioners' Exhibit 1-k) as well as Marsh periwinkle, Fiddler crabs, tricolered heron, greenback heron, and snowy egret. The project was found, moreover, to result in 1.61 acres of impact to a mangrove community with wetlands in a Class II waterbody directly contiguous to an aquatic preserve. After detailing the value and significance of mangroves to habitat and water quality functions and the applicant's failure to provide reasonable assurance that the construction and operation of the activity, considering direct, secondary and cumulative impacts, would comply with the provisions of Part IV of Chapter 373 and the rules adopted thereunder, Part III of the notice recited two primary bases for the denial. First, the immediate and long-term impacts of the activity were expected to cause violations of water quality standards. Second, the project was found to be contrary to the public interest for those portions of the activity located in, on or over wetlands or other surface waters. With regard to water quality, the Department found the project did not meet standards applicable to biological integrity, transparency, and turbidity. The project was expected, furthermore, to cause: adverse water quality impacts to receiving waters and adjacent lands; adverse impacts to the value of functions provided fish, wildlife and listed species by wetlands and other surface waters; and adverse secondary impacts to water resources. With regard to the public interest test for those portions of the activity located in, on or over wetlands or other surface waters, the Department expected the project to adversely affect the conservation of fish and wildlife, including endangered or threatened species and their habitats; adversely affect navigation or the flow of water or cause harmful erosion or shoaling; adversely affect the fishing or recreational value or marine productivity in the vicinity of the project, among other adverse impacts; and fail to meet standards imposed by law. Despite the existence in the Department's opinion of numerous substantial bases for denial, the Department offered hope to Petitioners that they might yet be able to build a residential structure on Lot 5. The first of changes to the project listed in the notice that might "enable the Department to grant a permit," Petitioners' Exhibit 1-k, was for Petitioners to "[r]elocate the proposed residence to a landward location-in proximity to the existing road which would result in a significantly minimized wetland impacts." Id. Other modifications included submission of an acceptable mitigation plan and addressing cumulative impacts, perhaps by way of granting a conservation easement. In response, the McGinnises modified their proposal. But the modifications did not include moving the residence into the uplands at the northern end of the property. The Department considered the changes to the proposal but the changes did not, in the Department's view, make the project permittable. (See Tr. 155). Environmental Dispute Resolution On May 15, 1996, a few weeks from the issuance of the Department's Notice of Denial, Mel and Pamela McGinnis filed a Request for Relief under the Florida Land Use and Environmental Resolution Act, Section 70.51, et seq., Florida Statutes. The Department filed a response to the request and parties participated in a hearing and mediation in accordance with the Act. A hearing was held on September 18 and 19, 1996, before Special Master Raymond M. McLarney who referred to the event as the "first Special Master Proceeding in Property Rights with the FDEP and a landowner." Petitioners' No. 4, Special Master Summary Report, Ex. 1a, p. 1. 36. Paragraph 4 of the Report Summary, bearing the heading, "Special Master's Initial Observation," states: Following completion of the hearings . . ., the Special Master concluded and communicated to the parties that the FDEP's Notice of Denial unreasonably and/or unfairly burdens use of the McGinnises['] real property. The Special Master's initial observation and conclusion was provided to the parties to serve as an indication of sufficient hardship to support modification, variances or special exceptions to applicable statutes, rules, regulations or ordinances of FDEP as applicable to the subject property, all as authorized by Section 70.51(25) of the Florida Statutes. The Special Master encouraged the parties to mediate their differences and attempt to seek a mutually- acceptable solution through the process of mediation. The parties agreed. Id., at 4. The Special Master's Report Summary reports that the result of the mediation was that "the McGinnises and FDEP reached a mutually-acceptable solution evidenced by an [attached] agreement . . . incorporated herein. The . . . solution . . . was initialed/signed on each page by authorized representatives of the parties and was accomplished in accordance with Section 70.51(19)(c) of the Act." Id., at 5. The “Initial Observation” section of the Report Summary appears to contain what would have been the Special Master’s Recommendation (that is, the conclusion that the Department’s actions “unfairly burdened the Petitioners’ use of the property”) had the Special Master not thought that the Department and the McGinnises had reached a mediated agreement. Whatever the appropriate characterization of this section of the report, the Department treated it as a recommendation. It did so when it declared the Special Master’s Report Summary null and void several months after receiving it. Null and Void On January 29, 1997, the Department received the Special Master's Report Summary. By order dated March 14, 1997, the Department rejected its "recommendations." Petitioners' Exhibit 4, Order, p. 1. Under an overarching declaration that the report summary was null and void (amounting to a declaration that the entire proceeding was null and void) the order detailed essentially four bases for the rejection: a. the hearing that led to it was not open to the public as required by the Act; the report was not timely submitted; c. the proceeding had not satisfied other requirements of the Act besides public openness and therefore was inadequate; and d. the report incorrectly concluded that the Department and the McGinnises had reached a mutually-acceptable solution. Allegations of the Petition In the body of the petition which initiated this case, Petitioners refer to the Special Master proceeding as one which led to a mediated agreement. They also make reference to the Department’s rejection of the Special Master’s recommendation. See Petition, paragraph 11, p. 3. But although they seek “[s]uch other relief as may be just and appropriate under the circumstances [of the case],” Petition, paragraph 12.c., p. 5, they do not plead in the petition that the rejection was either wrong as matter of law or action for which they specifically seek relief. Instead of challenging the Department’s rejection of a recommendation by the Special Master or the Department’s declaration that his Report Summary was null and void, the petition challenges only two decisions of the department. One is the Notice of Denial determining the Petitioners not entitled to an Environmental Resource Permit. The other is the decision that the project is not exempt from permitting because of effects caused by the mosquito control ditches. The Days of Mosquito Ditching Long before the Legislature enacted the Florida Land Use and Environmental Dispute Resolution Act to address unreasonable burdens placed on land owners by governmental regulation, local governments were confronted by issues less abstruse. The Manatee County Commission, for example, was striving to eradicate mosquito infestation along its coastline. One of the tools the county used in its efforts was ditching. Mosquito ditches were installed in uplands and fresh waters throughout Manatee County but they were excavated mainly in the salt marshes along the county’s coastline because "the biggest [mosquito] problem in Florida is coastal mosquitoes." (Tr. 105). Larry Rhodes, presently a resident of Terra Ceia and a long-time resident of the area, was the Director of Manatee County Mosquito Control at the time the mosquito ditches were dug across the McGinnis property. His tenure as director ended in 1994. It spanned a period of more than 33 years, having begun in 1961. Shortly after the commencement of Mr. Rhodes’ tenure, but prior to some of the canal construction by the developers of nearby Terra Ceia Estates, the McGinnis property was cleared almost entirely. Except for a small wet area of black mangroves, the property had been dominated by wax myrtle, guava and Brazilian Pepper, an invasive exotic in the process of pushing out the other dominant species. The clearing by the developers of Terra Ceia Estates, personally observed by Mr. Rhodes, was done at the time of installation of a system of canals. Around the canals a waterward dike was placed in order to keep the tides from Miguel Bay from inundating the property. The clearing shows up in an aerial photograph taken in 1965. Soon after the aerial was taken and developed, the mosquito ditches were excavated. Approved by the State Board of Health in 1966, the ditches were dug through the McGinnis property during that year or the next, when the mosquito ditch system in the area of San Miguel Estates was completed in 1967. As the result of the ditching, with the exception of the spoil banks where Brazilian Pepper took over, mangroves proliferated over the formerly-cleared land. Red mangroves grew "up [in] all the ditches and then black and white mangroves in other areas." (Tr.122). Maps, Aerial Photographs, and Soil Surveys The status of the property as cleared thirty-odd years ago and the subsequent generation of mangroves produced in the intervening years over most of the property, including alongside and in the mosquito ditches, did not mean necessarily that the cleared area had not been wetlands prior to the clearing activity. The Department, therefore, confronted with the Petitioners’ claim of a mosquito control exemption, set out to investigate. The investigation was necessary because entitlement to the exemption turns on whether the nature of the property as wetlands after the clearing was due solely to the excavation of the ditches. The investigation consisted of reviewing aerial photographs, maps and soil surveys and later required resort to expert opinion from outside the department. After an initial review conducted by Ken Huntington and Rose Poyner, another Department staff member, the Department contacted GIS analyst Robert P. Evans of the Southwest Florida Water Management District. As a GIS analyst, Mr. Evans’ primary functions (conducted for more than 25 years for the district) are GIS mapping and interpretation of aerial photographs. Mr. Evans reviewed a series of aerial photographs beginning with 1940 black and white photographs and ending with infrared photos from 1990. A 1940 Natural Resource Conservation Service (NRCS) photograph showed that the site of the McGinnis' proposed project consisted of mangroves that year. A copy of a 1951 NRCS aerial photo showed mangroves on the site as did a copy of a 1957 aerial photo. After review of the photos, Mr. Evans was of the opinion that the site of the proposed project was wetlands and had been so historically, that is, before the ditches approved and excavated in the mid-sixties. Rick Cantrell, the Administrator of the Wetlands Evaluation and Delineation Section of the Department, the "Administrator [of wetlands delineation] for the whole Department in the whole State of Florida," (Tr. 306), and an expert in aerial photo interpretation for purposes of wetlands delineation, also reviewed aerial photos of the site. Mr. Cantrell reached the opinion that the property had been historical wetlands, just as had Mr. Evans. In the meantime, Mr. Evans was hard at work seeking independent confirmation of his opinion. First, he reviewed United States geological surveys of the site. The 1969 revision of the 1964 edition of the Palmetto USGS Quad map of the area, based on an aerial photograph taken in 1951, shows the McGinnis project site was wetlands prior to the ditching. Not content to rely on the authoritative evidence of aerials and official federal geological survey maps, Mr. Evans sought out another source: soil surveys. These, too, confirmed the historic existence of wetlands on the site. Favored with Mr. Evans’ opinion, the Department contacted Juan Vega, a soil scientist, and asked him to use his expertise in both soil survey review and site testing to assist the inquiry. Mr. Vega agreed to look into the issues. He examined two soil surveys: a survey of Manatee County soils issued in December of 1958 by the United States Department of Agriculture's Soil Conservation Service in cooperation with a Florida Agricultural Experiment Station (Respondent's Exhibit 8) and a subsequent Soil Survey of Manatee County conducted by the federal Soil Conservation Service in cooperation with the University of Florida and other state entities (Petitioner's No. 9). The second survey, "done in '79 or '80," (Tr. 286) was a recorrelation of the first. The first survey shows the site to be tidal swamp as is all of Lot 5 with the exception of the less than one acre of uplands on the property's northern border. Vegetation in tidal swamps is usually mangroves in abundance. As one would expect from their denomination, tidal swamps are influenced by salt water tides, contain tidal soils and are generally wet. The 1979-80 survey indicated that the soil found on the site is Wulfert-Kesson Association. This soil is characterized by an accumulation of organic materials and ore black minerals on the surface, a process known as gleying. Gleying is caused by saltwater inundation and tidal effects and therefore, of course, is indicative of the presence of hydric soils in a wet area. The soil surveys led Mr. Vega to conclude that the site of the project was composed of historic wetlands. Field Testing The Department's interest in having Mr. Vega conduct soil testing on the site of the project was not fruitful. Access to the site was denied. In lieu of on-site testing, therefore, Mr. Vega conducted soil analysis nearby, a few hundred feet to the east of the proposed site. In March of 1996, he dug several holes, one near the road and others adjacent to the mangrove area of Lot 5. The soil near the road was Bradenton, "pretty much natural native soil." (Tr. 289). The soil from the other areas, buried under approximately two feet of fill, was Wulfert and Kesson, both hydric soils. There was also present a layer of muck, that is, decomposed organic material. It indicated that the soil had not been converted from uplands to wetlands but rather that the soil had been wetlands historically. The field testing conducted by Mr. Vega on the adjacent site confirmed his opinion that the site of the proposed McGinnis project was wetlands and had been so historically. Historic Wetlands The evidence on the issue of the property's status is summarized as follows: United States Geographical Survey maps indicate the area of Lot 5 in San Miguel Estates to be historic wetlands; federal soil surveys confirmed by nearby soil testing and conducted with the cooperation of the State of Florida indicate the presence of hydric soils on the lot; and aerial photographs show that mangroves existed on the site both before the clearing in the sixties and after the mosquito ditches were excavated in 1966-67. Although the proposed site contains mangroves stunted and suffering from the stress of anoxia today, and there are mangroves in and alongside the mosquito ditches dug as part of a governmental program in the 1960s which grew after the land had been cleared, Lot 5 in San Miguel Estates, with the exception of the approximate .9 of an acre alongside the road at the north end of the property, is comprised of wetlands that existed prior to the mosquito ditching activity. In short, Lot 5 is comprised of historic wetlands. The Permit Application Sovereign submerged lands would be affected by the project, a project permanent in nature. "[D]irect impact would be the excavation of the access channel from the boat basin to the water. So that last [scoop] of dirt, if you will, or piece of land separating the basin from Miguel Bay, that cut would be into the bottom of Miguel Bay, [an Outstanding Florida Water and part of the Terra Ceia Aquatic Preserve]." (Tr. 156). The proposed project would cause adverse impact to the quality of the receiving waters. The filtration function of the mangrove forest would be diminished and the boat basin would cut into the bottom of the bay within the aquatic preserve. Petitioners offered no evidence that water quality standards listed in Chapter 62-302, Florida Administrative Code, including those for biological integrity, transparency and turbidity would be met, all concerns listed by the Department in its Notice of Denial as a basis for its action on the permit application. Nor did Petitioners demonstrate that the dredging of the boat access channel in Miguel Bay would not violate ambient water quality standards, another basis for the Department's notice of denial. Any mitigation offered by Petitioners for the impacts of fill associated with construction of the access road and fill pad for the house were not adequate. "That fill will eliminate over half an acre . . . of mangroves and wetlands that are crucial to the eco system (sic) in Miguel Bay." (Tr. 157). In addition to the filtration these lost mangroves would have provided, "mangrove wetlands are vital for habitat, for fish and wildlife services." Id. Petitioners have not provided reasonable assurance that the boat basin would not create water quality violations, including dissolved oxygen concentrations falling below standards. Petitioners have not provided reasonable assurance that the proposed activity will not cause adverse secondary impacts that result from construction activities on the site. Secondary impacts include the establishment of nuisance species in disturbed areas. The property contains sufficient uplands upon which to construct the residential structure or at least enough of it to greatly minimize impact to wetlands. Siting a dock on the bay would obviate the need for the boat basin and channel. An associated boardwalk would eliminate the need to dredge wetlands populated by mangroves. Utilizing a dock and a boardwalk would save almost a quarter of an acre of wetlands from dredging. Mr. McGinnis' status as a double above-the-knee amputee may certainly be expected to create special needs, but other than to mention his disability, Petitioners made no showing that such a modification was not practicable in light of his condition. The proposed project would also present cumulative impacts to wetlands and other surface waters. There is significant development already in San Miguel Estates and there are other applications for development pending: for example, a permit application for construction of a boardwalk through wetlands submitted for the adjacent Lot 4. In sum, the project will have adverse water quality impacts, impacts to sovereignty submerged lands, secondary impacts, and cumulative impacts. Ways proposed by the Department of dramatically minimizing, reducing or preventing these impacts have not been accepted by Mr. and Mrs. McGinnis.
Recommendation Based on the foregoing findings of fact and conclusions of law, it is RECOMMENDED: That the Department of Environmental Regulation enter a final order denying both the mosquito ditch exemption and the Environmental Resource Permit applied for by Petitioners, Mel and Pamela McGinnis, for the project in DEP Permit File No. 412783533. DONE AND ENTERED this 17th day of April, 1998, in Tallahassee, Leon County, Florida. DAVID M. MALONEY Administrative Law Judge Division of Administrative Hearings The DeSoto Building 1230 Apalachee Parkway Tallahassee, Florida 32399-3060 (850) 488-9675 SUNCOM 278-9675 Fax Filing (850) 921-6847 Filed with the Clerk of the Division of Administrative Hearings this 17th day of April, 1998. COPIES FURNISHED: Frank E. Matthews, Esquire Kimberly A. Grippa, Esquire Hopping, Green, Sams and Smith, P.A. Post Office Box 6526 Tallahassee, Florida 32314-6526 Douglas H. MacLaughlin, Esquire T. Andrew Zodrow, Esquire Department of Environmental Protection Mail Station 35 3900 Commonwealth Boulevard Tallahassee, Florida 32399-3000 Thomas W. Reese, Esquire 2951 61st Avenue, South St. Petersburg, Florida 33712 Kathy Carter, Agency Clerk Department of Environmental Protection Mail Station 35 3900 Commonwealth Boulevard Tallahassee, Florida 32399-3000 Perry Odom, General Counsel Department of Environmental Protection Mail Station 35 3900 Commonwealth Boulevard Tallahassee, Florida 32399-3000
The Issue Petitioners challenge the South Florida Water Management District’s (the District) proposed action to issue Individual Environmental Resource Permit (ERP) 50-06558-P to authorize conceptual approval of a surface water management (SWM) system to serve 1,919 acres of a phased, multiple-use development referred to as the Palm Beach County Biotechnolgy Research Park (BRP) and to authorize construction and operation of Phase 1A of that proposed project. The ultimate issue is whether the Applicants provided reasonable assurances that the proposed activities will not be harmful to the water resources of the District; will not be inconsistent with the overall objectives of the District; and will comply with the water quantity, environmental, and water quality criteria of the District’s ERP regulations, which are set forth in Part IV of Chapter 373, Florida Statutes, Florida Administrative Code Chapter 40E-4, et. seq.; and the Basis of Review for Environmental Resource Permit Applications Within the South Florida Water Management District – September 2003 (BOR).1
Findings Of Fact THE PARTIES The Florida Wildlife Federation, Audubon Society of the Everglades, and Jupiter Farms Environmental Council, Inc. (d/b/a Loxahatchee River Coalition) are not-for-profit corporations in existence prior to 2003 with more than 25 members in Palm Beach County. Palm Beach County Environmental Coalition was formed in 1997 and is a private, county-wide, non-profit citizen’s organization. Ms. Ketter, Mr. Bell, Ms. Larson, and Mr. Christensen are individuals affected by the proposed BRP. The Respondents stipulated that the parties who remained Petitioners after Mr. Silver’s withdrawal as a Petitioner have standing to bring this proceeding. The District, a public corporation existing by virtue of Chapter 25270, Laws of Florida, 1949, operates pursuant to Chapter 373, Florida Statutes, and Title 40E, Florida Administrative Code, as a multipurpose water management district with its principal office in West Palm Beach, Florida. The County is a duly-constituted governmental entity. THE PROJECT SITE AND ADJACENT LANDS The site of the project is generally referred to as the Mecca Farms, which is a contiguous tract of 1,919 acres of land. At present, the Mecca Farms is used for farming and mining operations. There presently exists a permitted, SWM system on the Mecca Farms that was first permitted in 1979, and has been modified from time to time since then. The existing SWM system includes 73 acres of ditches and a 272-acre above-ground impoundment area. The Mecca Farms site is located within the C-18 Basin. There are no jurisdictional wetlands or delineated surface waters on the Mecca Farms. The following, which is taken from the Staff Report (SFWMD Ex. 1), accurately describes the project site and its adjacent lands: The project site consists of 1,919 acres presently supporting an active orange grove with approximately 73 acres of associated drainage and irrigation ditches/canals and a 30-acre active sand mining operation. The ditches/canals are presently maintained at an elevation of approximately 17 feet NGVD.[3] These ditches/canals provide drainage conveyance to a 272-acre above- ground impoundment located in the northeast corner of the site utilizing four (4) 22,000 gpm pumps. The above-ground impoundment discharges to the west leg of the C-18 Canal via gravity discharge. Project site ditches and canals also connect directly to the C-18 Canal through an 18,000 gpm pump. An additional 224-acre agricultural area east of the 1,919 acres of orange groves is connected to and drains into the canal/ditch system on the project site. This adjacent area was leased from the adjacent land owner by the grove owner for use as row crops and was connected to the grove canal/ditch system for better control of drainage and irrigation. The area is no longer used for row crops. There is also a small area on the site that contains caretaker housing and an equipment maintenance building for the orange groves. These facilities were originally permitted in 1979 under Surface Water Management Permit No. 50-00689-S and subsequent modifications. The citrus grove and primary drainage facilities have been in existence since the 1960s. The Hungryland Slough is located north of the project site, separated from the project site by the C-18 Canal. This area is comprised primarily of publicly-owned natural areas, including an area referred to as Unit 11, which is owned in the majority by Palm Beach County. To the west is the J.W. Corbett Wildlife Management Area (CWMA) owned and managed by the Florida Fish and Wildlife Conservation Commission (FFWCC). To the east, a large area of low-intensity agricultural land exists under the ownership of Charles Vavrus and within the City of Palm Beach Gardens. These lands contain extensive wetlands that are adjacent to the Loxahatchee Slough to the east. The Acreage, a low-density residential area, is located directly to the south of the project site. The only access to the site at this time is an unpaved extension of Seminole Pratt-Whitney Road (SPW), connecting the site at its southwestern corner to the Acreage. THE PROPOSED PROJECT The subject application is for conceptual approval of the SWM system for the BRP and for construction and operation of Phase 1A of the project. All of the proposed Phase 1A construction will occur on the Mecca Farms site. The following, taken from the Staff Report, accurately describes the proposed project: The [BRP] is a phased multiple use development planned for approximately 1,919 acres and will consist of land uses related to science and technology, biotechnology, biomedical, and other related research and development industries and manufacturing. Additionally, proposed support and complementary land uses include educational, institutional, residential, commercial, and recreational facilities, along with utilities and a large created natural area. THE PROPOSED SWM SYSTEM The proposed SWM system will consist of several interconnected lakes that will provide wet detention for storm water runoff from the property site and from 39 acres of off- site flows from SPW Road and a proposed Florida Power and Light (FPL) Substation. The lakes will collect, store, and treat the runoff. The storm water will pass through the lakes, through a 247-acre area referred to as the “Natural Area” (which will be created as part of the mitigation plan), and discharged to the C-18 Canal. To provide additional water quality treatment, these lakes will include planted littoral zones and the southern lake will include a filter marsh. The Natural Area will, in subsequent construction phases, be constructed on the western boundary of the Mecca site with discharge to the C-18 canal, which is adjacent to the northern boundary of the Mecca Farms. The southern boundary of the Natural Area will be the north boundary of the lake that is to be constructed on the southern end of the property. This is the area that is available for use as a flow-way (which will be discussed in greater detail in a subsequent section of this Recommended Order). The Natural Area will be a wetland type system that will move water slowly through that system providing additional storage and water quality benefits prior to discharging through a gravity control structure into the C-18 Canal. The C-18 Canal discharges to either the Northwest or Southwest Fork of the Loxahatchee River, depending on how structures are operated downstream. Discharges travel in the C-18 Canal for approximately nine miles before reaching the Loxahatchee River. The existing SWM system for the Mecca Farms currently discharges to the C-18 Canal, as will the proposed SWM system. The proposed project will not discharge to the CWMA or the Hungryland Slough. The Grassy Waters Preserve and the Loxahatchee Slough are several miles from the project site and will not be affected by the project’s proposed activities. The following, which is taken from the Staff Report, accurately describes the proposed SWM system. The proposed conceptual surface water management system which will serve the 1,919-acre site will consist of site grading, storm water inlets and culverts which will direct all runoff to a series of interconnected lakes for water quality treatment and attenuation of the peak runoff rate. Pumps will control the runoff rate from the developed site into the adjacent onsite BRP natural area. The BRP natural area will discharge into the C-18 canal via a gravity control structure. The system has been designed to accommodate 39 acres of off-site flows from SPW [Road] and a proposed Florida Power and Light (FPL) Substation. The existing control elevation of the citrus grove is 17.0’ NGVD. The proposed control elevations are 18.0’ NGVD for the developed area and 19.0’ NGVD for the natural area. The control elevations are being raised to provide a “step down” of water elevations from wetlands to the north, west and east of the site (20.5’ to 21.0’) to lower elevations to the south (17.0’). PHASE 1A CONSTRUCTION The following, which is taken from the Staff Report, accurately describes the proposed Phase 1A construction: The Phase 1A construction activities will allow the applicant to proceed with lake excavation, clearing and site grading of 536 acres in the southern portion of the site. No permanent buildings or parking areas are proposed at this time. Stormwater from Phase 1A and the remainder of the site, to remain in agricultural use, will be treated in the Phase 1A lakes and then pumped into the existing impoundment for additional water quality treatment and attenuation prior to discharging to the west leg of the C-18 Canal via the existing weir structures. The existing 18,000 gpm pump that connects the on-site ditches and canals directly to the C-18 Canal will remain, but will only be used if the impoundment is full. (See Special Condition No. 21). Approval of Phase 1A authorizes the use of the existing, previously permitted surface water management facilities, therefore, the previous permit no. 50-00689-S is superceded by this permit. The 224 acre agricultural area east of the existing grove that is connected to the grove canal/ditch system will be severed as part of Phase 1A. The pipe connecting this area will be removed and portions of the berm around this area will be regraded so the area will sheetflow into the adjacent pasture land’s canal/ditch system as it did previously [sic] to being connected to the grove system. Of the 536 acres involved in the Phase 1A construction, 87 acres will become lake bottom and 449 acres will remain pervious area, subject only to grading. CONCEPTUAL APPROVAL Pertinent to this proceeding, Florida Administrative Code Rule 40E-4.021(5) defines the term “conceptual approval” to mean an ERP issued by the District which approves a conceptual master plan for a surface water management system or a mitigation bank. Florida Administrative Code Rule 40E-4.305, pertains to conceptual approvals and provides, in relevant part, as follows: Conceptual approvals constitute final District action and are binding to the extent that adequate data has been submitted for review by the applicant during the review process. A conceptual approval does not authorize construction, alteration, operation, maintenance, removal, or abandonment of a surface water management system or the establishment and operation of a mitigation bank. * * * For phased projects, the approval process must begin with an application for a conceptual approval which shall be the first permit issued for the project. An application for construction authorization of the first phase(s) may also be included as a part of the initial application. As the permittee desires to construct additional phases, new applications shall be processed as individual or standard general environmental resource permit applications pursuant to the conceptual approval. The conceptual approval, individual and standard general permits shall be modified in accordance with conditions contained in Chapters 40E-4 and 40E-40, F.A.C. Issuance of a conceptual approval permit pursuant to Chapter 40E-4, F.A.C., shall not relieve the applicant of any requirements for obtaining a permit to construct, alter, operate, maintain, remove, or abandon a surface water management system or establish or operate a mitigation bank, nor shall the conceptual approval permit applicant be relieved of the District’s informational requirements or the need to meet the standards of issuance of permits pursuant to Chapters 40E-4 or 40E-40, F.A.C. . . . PERMITTING CRITERIA In order to obtain an ERP, an applicant must satisfy the conditions for issuance set forth in Florida Administrative Code Rules 40E-4.301 and 40E-4.302. The conditions for issuance focus on water quantity criteria, environmental criteria, and water quality criteria. Florida Administrative Code Rule 40E-4.301 contains the following permitting conditions applicable to this proceeding: In order to obtain a standard general, individual, or conceptual approval permit ... an applicant must provide reasonable assurance that the construction, alteration, operation, maintenance, removal, or abandonment of a surface water management system: will not cause adverse water quantity impacts to receiving waters and adjacent lands; will not cause adverse flooding to on-site or off-site property; will not cause adverse impacts to existing surface water storage and conveyance capabilities; will not adversely impact the value of functions provided to fish and wildlife and listed species by wetlands and other surface waters; will not adversely affect the quality of receiving waters ...; will not cause adverse secondary impacts to the water resources; will not adversely impact the maintenance of surface or ground water levels or surface water flows ...; will not cause adverse impacts to a work of the District ...; will be capable, based on generally accepted engineering and scientific principles, of being performed and of functioning as proposed; will be conducted by an entity with the sufficient financial, legal and administrative capability to ensure that the activity will be undertaken in accordance with the terms and conditions of the permit, if issued; and will comply with any applicable special basin or geographic area criteria established in Chapter 40E-41 F.A.C. Florida Administrative Code Rule 40E-4.302 provides the following Additional Conditions for Issuance of Permits applicable to this proceeding: In addition to the conditions set forth in section 40E-4.301, F.A.C., in order to obtain a standard general, individual, or conceptual approval permit under this chapter or Chapter 40E-40, F.A.C., an applicant must provide reasonable assurance that the construction, alteration, operation, maintenance, removal, and abandonment of a system: Located in, on, or over wetlands or other surface waters will not be contrary to the public interest, or if such an activity significantly degrades or is within an Outstanding Florida Water, that the activity will be clearly in the public interest, as determined by balancing the following criteria as set forth in subsections 4.2.3 through 4.2.3.7 of the Basis of Review for Environmental Resource Permit Applications Within the South Florida Water Management District: Whether the activity will adversely affect the public health, safety or welfare or the property of others; Whether the activity will adversely affect the conservation of fish and wildlife, including endangered or threatened species, or their habitats; Whether the activity will adversely affect navigation or the flow of water or cause harmful erosion or shoaling; Whether the activity will adversely affect the fishing or recreational values or marine productivity in the vicinity of the activity; Whether the activity will be of a temporary or permanent nature; Whether the activity will adversely affect or will enhance significant historical and archaeological resources under the provisions of Section 267.061, F.S.; and The current condition and relative value of functions being performed by areas affected by the proposed activity. Will not cause unacceptable cumulative impacts upon wetlands and other surface waters as set forth in subsections 4.2.8 through 4.2.8.2 of the Basis of Review. . . . THE BASIS OF REVIEW The District has adopted the BOR and incorporated it by reference by Florida Administrative Code Rule 40E- 4.091(1)(a). The standards and criteria found in the BOR are used to determine whether an applicant has given reasonable assurances that the conditions for issuance of an ERP have been satisfied. Section 1.3 of the BOR provides, in part, as follows: . . . Compliance with the criteria established herein [the BOR] constitutes a presumption that the project proposal is in conformance with the conditions for issuance set forth in Rules 40E-4.301 and 40E-4.302, F.A.C. WATER QUANTITY The term “control elevation” describes the level of freshwater water bodies established by a SWM system. The existing SWM system has a control elevation of 17’ NGVD. The control elevation for the proposed lake system will be raised to 18’ NGVD, and the control elevation for the proposed Natural Area will be raised to 19’ NGVD. Raising the control elevations will permit more treatment of storm water prior to discharge and will permit a more controlled discharge. In addition, raising the control elevation will lessen seepage onto the project site from adjacent wetlands. The Applicants provided reasonable assurances that the proposed project will not cause adverse water quantity impacts to receiving waters and adjacent lands, thereby satisfying the criteria set forth in Florida Administrative Code Rule 40E- 4.301(a). The Applicants provided reasonable assurances that the proposed project will not cause adverse flooding to on-site or off-site property, thereby satisfying the criteria set forth in Florida Administrative Code Rule 40E-4.301(b). The Applicants provided reasonable assurances that the proposed project will not cause adverse impacts to existing surface water storage and conveyance capabilities, thereby satisfying the criteria set forth in Florida Administrative Code Rule 40E-4.301(c). VALUE OF FUNCTIONS OF WETLANDS AND SURFACE WATERS Florida Administrative Code Rule 40E-4.301(d), requires the Applicants to establish that “. . . the construction, alteration, operation, maintenance, removal, or abandonment of a surface water management system . . .” “. . . will not adversely impact the value of functions provided to fish and wildlife and listed species by wetlands and other surface waters.” The District established that the term “value of functions,” as used in the rule, refers to habitat and life support functions. Because there are no wetlands or delineated surface waters on the Mecca Farms site, there are no direct adverse impacts to the functions that wetlands provide to fish and wildlife. The Applicants have provided reasonable assurances to demonstrate that the value of functions provided to fish and wildlife and listed species by wetlands and other surface waters will not be adversely affected. The existing project site does not contain nesting areas for wetland-dependent endangered or threatened wildlife species or species of special concern. The potential for use of the existing project site for nesting by such species is minimal. The existing project site does contain habitat for the American Alligator and foraging habitat for wading birds and birds of prey. The primary foraging habitat on the existing site is around the perimeter of the existing 272-acre impoundment area in the northeast portion of the site. The existing impoundment will be replaced by on-site storm water treatment lakes and the BRP Natural Area that will have shallow banks planted with wetland plant species common to the area. Wildlife is opportunistic; and wading birds commonly feed in areas where there is water, wetland vegetation and wetland plants. The end result will be that the proposed project will have more and better foraging habitat acreage than the existing site. The Natural Area will provide a wetland buffer between the developed area and CWMA that will prevent any adverse impacts both to the wetlands and other surface waters in CWMA and to the value of the functions those wetlands and other surface waters provide to fish, wildlife, and listed species. The Natural Area will provide a wetland buffer between the developed area and Unit 11 that will prevent any adverse impacts both to the wetlands and other surface waters in Unit 11 and to the value of the functions those wetlands and other surface waters provide to fish, wildlife, and listed species. There was no competent evidence that the proposed project would impact the ability of the Florida Fish and Wildlife Conservation Commission to manage the CWMA through control burns or otherwise, thereby adversely affecting the diversity or abundance of fish and wildlife (including endangered species and their habitats). Petitioners attempted to raise the issue of mosquito control in their Petitions and at the Final Hearing. The allegations pertaining to mosquito control were struck by the District and Special Condition Number 26 was added before the Petitions were referred to DOAH. Petitioners made no attempt to amend their Petitions and have not challenged Special Condition 26. The Addendum to Staff Report (SFWMD Ex. 2) contains the following Special Condition Number 26: “Upon submittal of an application for construction of any buildings, the permittee shall submit a mosquito control plan for review and approval by District Staff.” Since there will be no buildings containing people or other facilities which would encourage the use of mosquito spraying, it is appropriate for the mosquito control condition to apply to only future phases of construction. There was no competent evidence of impacts attributable to pesticides associated with the application for the SWM system or for Phase 1A construction and operation that would adversely affect the diversity or abundance of fish and wildlife including endangered species and their habitats. The Applicants have satisfied the criteria set forth in Florida Administrative Code Rule 40E-4.301(d). WATER QUALITY The primary concern during Phase 1A construction will be erosion control. Best Management Practices (“BMPs”) are operational and design elements used to either eliminate or reduce the amount of pollutants at the source so they do not get into a SWM system or move downstream. To contain erosion in Phase 1A, the Applicants will use the following BMPs: Silt screens and turbidity barriers within existing ditches and around the perimeter of property. Planned construction sequencing to reduce movement and stock piling of material; Slope stabilization and seeding or sodding of graded areas; and Containment of construction materials with berms. All erosion and turbidity control measures will remain in place until the completion of the on-site construction and approval by the District’s post-permit compliance staff. The Applicants provided reasonable assurances that the proposed Phase 1A construction activities will not adversely impact the quality of receiving waters and that those activities will not violate State water quality standards. Section 5.2.1, BOR, requires that a SWM system provide wet detention for the first one inch of runoff. The proposed SWM system will provide wet detention for one and one-half inches of runoff. The Applicants provided reasonable assurances to demonstrate that the technical criteria in the BOR will be met. Under Section 1.3 of the BOR, compliance with the criteria in the BOR constitutes a presumption that the Proposed Project is in conformance with the conditions for issuance. This presumption was not rebutted by the Petitioners. The lake system will include planted littoral zones to provide additional uptake of pollutants. A filter marsh is also included in the southern lake. All of the storm water runoff from the lakes will pass through the filter marsh, which will be planted with wetland plants. The filter marsh will provide additional polishing of pollutants, uptake, and filtering through the plants. The discharge will then go into the BRP, which will provide the discharge additional uptake and filtering. BMPs utilized during the Operations and Maintenance phase will include regular maintenance inspections and cleaning of the SWM system, street-sweeping, litter control programs, roadway maintenance inspections and repair schedule, municipal waste collection, pollution prevention education programs, pesticides, herbicides and fertilizer storage, and application training and education. The littoral zones, filter marsh, BRP natural area, and BMPs were not included in the water quality calculations and are over and above rule requirements. The Applicants provided reasonable assurances to demonstrate that the proposed project will not adversely affect the quality of receiving waters. Therefore, Rule 40E- 4.301(1)(e), F.A.C., will be satisfied and water quality standards will not be violated. HAZARDOUS SUBSTANCES Pursuant to Section 5.5.5 of the BOR, commercial or industrial zoned projects shall provide at least one-half inch of dry detention or retention pretreatment as part of the required retention/detention, unless reasonable assurances can be offered that hazardous materials will not enter the project's SWM system. The Addendum to Staff Report reflects the following Special Condition 25 pertaining to hazardous materials: Upon submittal of an application for construction of commercial or industrial uses the permittee shall submit a plan that provides reasonable assurances that hazardous materials will not enter the surface water management system pursuant to the requirements of section 5.2.2(a) of the Basis of Review. Applicable permitting criteria does not require the Applicants to present a hazardous substances plan at this point because no facilities that will contain hazardous materials are part of the Phase 1A construction. SECONDARY IMPACTS Florida Administrative Code Rule 40E-4.301(1)(f) and Section 4.1.1(f) of the BOR, require an applicant to provide reasonable assurances that the proposed activities will not cause adverse secondary impacts to the water resources. A secondary impact is an indirect effect of a project resulting in adverse effects to wetlands or other surface waters. The District considers those adverse effects that would not occur "but for" the activities that are closely linked and causally related to the activity under review. This standard is discussed further in the Conclusions of Law section of this Recommended Order. The County’s Exhibit 3 is a secondary impact analysis identifying the secondary impacts that may potentially result from the proposed project. These impacts are: 1) the widening of SPW Road; 2) the construction of an FPL substation; 3) the extension of PGA Boulevard; and 4) the potential relocation of a runway at North County Airport. The secondary impact analysis performed pursuant to the Uniform Mitigation Assessment Method (UMAM) contained in Florida Administrative Code Chapter 62-345 reflects that up to 153.3 acres of wetlands may be partially or completely impacted by these secondary impacts, resulting in approximately 71.21 units of functional loss. Where future activities are expected to directly impact wetlands, secondary impacts were assessed based on the loss of all current functional value within the direct footprint of that activity. Additionally, an assessment was conducted to determine the degree of partial functional loss where impacts beyond the footprint of these activities are anticipated. SPW Road is an existing dirt road which is in the County's five-year road plan to widen as a four-lane paved road. Because the widening of the existing dirt road to a four-lane paved road is part of the five-year road plan, the impacts of that widening are not attributable to the subject project. However, as part of the proposed project, it is proposed to widen SPW Road to a six-lane paved road. The additional impacts associated with the widening from four to six lanes will be caused by, and are linked to, the proposed project. These impacts amount to approximately 2.2 acres. The FPL substation, which is proposed to service the proposed project, may result in 1.6 acres of potential direct impacts to wetlands. In addition, 1.0 acre of potential indirect secondary impacts may occur to wetlands that are not going to be dredged and filled. Those indirect secondary impacts may have some adverse impact on the functional value to those wetlands for wildlife utilization. The extension of PGA Boulevard to the Mecca Farms site has the potential to result in 45.6 acres of direct impacts to wetlands and 56.6 acres of indirect secondary wetland impacts which will not be dredged or filled, but will be in close proximity to the road. The secondary impact assessment for PGA Boulevard assumed the incorporation of wildlife crossings to minimize habitat fragmentation. If the airport runway needs to be shifted, potential direct wetland impacts to an additional 22.7 acres may occur. Indirect impacts to 23.6 acres of wetlands in close proximity could also occur. Runway relocation may or may not be necessary due to the PGA Boulevard extension; however, the analysis assumed the need for the relocation. Each of the projects listed above as potential secondary impacts will require a separate construction and operation permit from the District. The issuance of this permit does not in any way guarantee the issuance of permits for any of these identified potential secondary impacts. MITIGATION PLAN The Applicants provided a conceptual mitigation plan using UMAM to demonstrate how potential secondary impacts could be offset. Mitigation options have the potential to provide more than twice the functional gain than the functional loss from the identified secondary impacts. The conceptual mitigation options include: 194 acres of the land that had been acquired for future mitigation needs in Unit 11. 227 acres of the BRP natural area. 32.6 acres in the southern lake wetland along with proposed upland habitat. Sufficient mitigation is available in these options to offset the potential secondary impacts. The mitigation for the four potential secondary impacts is not required to be implemented now because the impacts are not occurring now. Section 4.2.7 of the BOR requires that the District consider those future impacts now and that a conceptual mitigation plan be provided to demonstrate and provide reasonable assurances that those impacts, in fact, can be offset in the future. The Governor and Cabinet sitting as the Board of Trustees considered and approved a request for public easement of approximately 30 acres to use a portion of CWMA for SPW Road, an FPL substation, and the land area that may be needed by District in the future for the connection to the flow-way. As consideration in exchange for the public easement over 30 acres, the County will transfer fee simple title of 60 acres to the State. This public easement also provides a benefit for CERP as it includes the small portion that the District is going to need for its future CERP project to connect to the flow-way on the proposed project site. The Applicants provided reasonable assurances that mitigation will offset secondary impacts to wetlands and other surface waters. UNIDENTIFIED SECONDARY IMPACTS Testimony at the final hearing raised a question as to whether there is nesting or roosting by listed wading bird species in adjacent off-site wetlands outside the eastern boundary of the project site. Evidence was inconclusive on nesting or roosting in these areas. Because the status of adjacent listed wading bird nesting or roosting is uncertain, the District suggested in its Proposed Recommended Order that a special condition requiring a wildlife survey prior to construction near the eastern project boundary be added to the permit as follows: Prior to application for construction within 1000 feet of the eastern boundary of the above-ground impoundment, the applicant shall conduct a wildlife survey to identify any nesting or roosting areas in the adjoining off-site wetlands utilized by listed species of wading birds. If such nesting or roosting areas are found the permittee shall, if determined necessary by the District, incorporate additional buffers or other appropriate measures to ensure protection of these wetland functions. The District represented in its Proposed Recommended Order that the County has no objection to adding the foregoing condition. CUMULATIVE IMPACTS Pursuant to Section 373.414(8), Florida Statutes, the District is required to consider cumulative impacts upon wetlands and other surface waters delineated in Section 373.421(1), Florida Statutes, within the same drainage basin. Cumulative impacts are the summation of unmitigated wetland impacts within a drainage basin. The cumulative impact analysis is geographically based upon the drainage basins described in Figure 4.2.8-1 of the BOR. Cumulative impacts are unacceptable when they would result in unacceptable adverse impacts to the functions of wetlands and surface waters within a drainage basin. There are no wetlands or other surface waters delineated pursuant to Section 373.421(1), Florida Statutes, on the Mecca Farms site. Therefore, no cumulative impacts are created by the direct impacts of the project. Cumulative impacts may be created by a project's secondary impacts. If a wetland impact has been appropriately mitigated on-site within the drainage basin, there is no residual impact, and therefore no cumulative impact. The PGA Boulevard extension, a portion of the SPW Road widening, and the airport runway relocation are located within the C-18 Basin. The proposed mitigation options are all located in the C-18 Basin and will offset those impacts. Those potential secondary impacts are considered to meet the cumulative impact requirements of Section 373.414(8), Florida Statutes. The Applicants provided reasonable assurances that the proposed project will not result in cumulative impacts to the C-18 Basin. The FPL substation is located within the L-8 Drainage Basin. The majority of the SPW Road expansion is located within the C-18 Basin, but a portion is located on the basin line between the C-18 Basin and the L-8 Basin. Because the mitigation for the L-8 impacts are proposed in a different basin, the Applicants were required to conduct a cumulative impact analysis for the L-8 Basin impacts. Based on the Florida Land Use Cover Classification System, there are 43,457 acres of freshwater wetlands within the L-8 Basin. Approximately 41,000 acres of the wetlands in L-8 Basin are in public ownership. This total constitutes approximately 95 percent of all the wetlands in the L-8 Basin. Public ownership of these wetlands provide a high level of assurance that these lands will be protected in perpetuity. The Respondents established that proposed mitigation can fully offset the potential impacts from the SPW Road expansion and the FPL substation and the approximately four acres of impacted wetlands in the L-8 Basin. The Applicants provided reasonable assurances that there are no unacceptable adverse cumulative impacts on the L-8 Basin.4 GROUND WATER FLOWS, SURFACE WATER FLOWS, AND MINIMUM FLOWS AND LEVELS Florida Administrative Code Rule 40E-4.301(1)(g) requires an applicant to provide reasonable assurances that the proposed activity will not adversely impact the maintenance of surface or ground water levels or surface water flows established pursuant to Section 373.042, Florida Statutes. The term "maintenance of surface and groundwater levels or surface water flows" in Florida Administrative Code Rule 40E-4.301(1)(g) means that a project will not adversely impact the maintenance of surface water flows that contribute to meeting the minimum flow for the water body. An adverse impact to the maintenance of surface or groundwater levels or surface water flows may occur when a project discharging to a water body with a designated minimum flow level is proposed to be diverted. An analysis was done to compare the peak discharge rate from the existing SWM system on the Mecca Farms site with the projected peak discharge rate from the proposed SWM system. The analysis showed that the peak discharge rate under the proposed system will be less than that of the existing system. That result was expected since the proposed system will have higher control elevations, which, as noted above, will provide better treatment and permit a better control of the discharge into the C-18 Canal. Under the existing SWM system, storm event water in a dry period is frequently stored in the existing impoundment for future irrigation purposes. Under the proposed SWM system such storm event water will be discharged downstream, which will benefit those downstream areas during dry periods. The proposed system will also provide better control over pulse discharges during heavy storm events. The Applicants provided reasonable assurances that the proposed activities will not adversely impact the maintenance of surface or ground levels or surface water flows as required by Florida Administrative Code Rule 40E-4.301(1)(g). THE DISTRICT’S OBJECTIVES Sections 373.414 and 373.416, Florida Statutes, require an applicant to provide reasonable assurances that a regulated activity will not be harmful to the water resources and will not be inconsistent with the overall objectives of the District. Congress initially authorized the Central and Southern Florida (“C&SF”) Project in 1948. Thereafter extensive work was undertaken pertaining to flood control; water supply for municipal, industrial, and agricultural uses; prevention of saltwater intrusion; and protection of fish and wildlife. The work included construction of a primary system of 1000 miles each of levees and canals, 150 water-control structures, and 16 major pump stations. Unintended consequences of the C&SF Project have included the irreversible loss of vast areas of wetlands, including half of the original Everglades; the alteration in the water storage, timing, and flow capacities of natural drainage systems; and the degradation of water quality and habitat due to over-drainage or extreme fluctuations in the timing and delivery of fresh water into the coastal wetlands and estuaries. In 1992, Congress authorized the C&SF Project Comprehensive Review Study, which is generally referred to as the “Restudy.” The objective of the Restudy was to reexamine the C&SF Project to determine the feasibility of modifying the project to restore the South Florida ecosystem and provide for the other water-related needs of the region, such as water supply and flood protection. In April 1999, the U.S. Army Corps of Engineers issued the Central and Southern Florida Project Comprehensive Review Study Final Integrated Feasibility Report and Programmatic Environmental Impact Statement (“Restudy Report”). The Restudy Report recommends a comprehensive plan for the restoration, protection, and preservation of the water resources of Central and South Florida. The resulting plan is known as CERP. The North Palm Beach County Part I project, which includes restoration of the Northwest Fork of the Loxahatchee River (“NWFLR”), is a component of CERP. The successful completion of CERP and the successful restoration of the NWFLR are high-priority objectives of the District. The Loxahatchee River is an important feature of the South Florida ecosystem, nationally and internationally unique, and an important natural and economic resource. Rules pertaining to MFL for the NWFLR and for the recovery of the NWFLR are found at Florida Administrative Code Rule 40E-8.011; 40E-8.221(4); and 40E-8.421. Recovery goals, which are not presently being met, have been established; and strategies to meet those goals have been identified. The Mecca Farms site is located within the boundaries of the CERP North Palm Beach County Part I project and has the potential to affect CERP and the restoration of the NWFLR. Projects that potentially would affect or would be within or adjacent to a CERP project are evaluated on a case-by- case basis to determine whether a proposed project would not be inconsistent with CERP and other District objectives. There was a dispute between Respondents and Petitioners as to whether the proposed project was inconsistent with the District’s objectives, including CERP and its goals pertaining to the restoration of the NWFLR. Petitioners contend that the District has insufficient evidence that the Mecca Farms will not be needed for the construction of a reservoir. That contention is rejected. The greater weight of the credible evidence established that sufficient storage is available at a superior site known as the Palm Beach Aggregates (PBA) site in the L-8 Basin, which is a unique geological site that will provide in-ground storage of water.5 Water from the PBA storage site can be conveyed to the NWFLR to increase dry season flows. Water can be stored at the PBA site in the wet season to prevent potentially damaging high flows. The L-8 Basin, which is adjacent to the C-18 Basin, receives more water during the wet season than it uses. This means that at present a significant amount of water must be discharged to tide (lost) during the wet season to provide for flood protection in this area. As envisioned, the water currently lost to tide could be stored at the PBA site for use during the dry season. By combining the water storage in the L-8 Basin with connective flow-ways to the C-18 Canal, water demands within the C-18 Basin, including the NWFLR, can also be met by the PBA storage site.6 An increase in freshwater flows to the NWFLR will further the District’s restoration goals for the NWFLR. Storage at PBA has regional benefits for other significant natural areas because it will provide additional flows to the Loxahatchee Slough and Grassy Waters Preserve. Those additional flows will further the District’s CERP goals. Since October of 2003, County staff and the District’s ERP staff have coordinated review of the subject project with the District’s CERP Planning and Federal Projects Division and other District staff working on projects in this region. The County asked the District to determine if the Mecca Farms’ site could in some way accommodate CERP objectives, and three alternatives were considered: 1) no action; 2) a reservoir; and 3) a flow-way. As opposed to a reservoir, the more valuable and the more practical, use of the Mecca Farms site would be as part of the system to convey the stored water to the areas that would most benefit from its discharge. The proposed flow-way in the BRP Natural Area would be an integral part of that conveyance system and would provide the District with greater flexibility in managing and directing the discharge of the water stored at the PBA site. Prior to the development of the flow-way concept as part of the proposed development, CERP identified a single route to take water from PBA to the NWFLR. The flow-way will provide an additional route from PBA to the NWFLR. That additional route will provide the District with greater operational flexibility. The flow-way will complement the L-8 Basin flow- way and help reduce peak flows to the NWFLR and the Estuary. The flow-way also provides a potential route allowing excess water to be brought back from the C-18 Basin to the PBA site for storage. There are no other potential routes that allow water to be directed from the C-18 Basin in the wet season to the PBA site. The flow-way provides a feature that was not part of the CERP original plan and is therefore an unanticipated benefit for CERP. The Applicants provided reasonable assurances that the proposed project is not inconsistent with the District’s objectives.7
Recommendation Based on the foregoing findings of fact and conclusions of Law, it is RECOMMENDED that the District issue the subject ERP for the conceptual approval of the SWM system for the BRP and the Phase 1A construction and operation subject to the general and special conditions set forth in the Staff Report and the Amended Staff Report. It is further RECOMMENDED that the District add the following special condition: Prior to application for construction within 1000 feet of the eastern boundary of the above-ground impoundment, the applicants shall conduct a wildlife survey to identify any nesting or roosting areas in the adjoining off-site wetlands utilized by listed species of wading birds. If such nesting or roosting areas are found the permittee shall, if determined necessary by the District, incorporate additional buffers or other appropriate measures to ensure protection of these wetland functions. DONE AND ENTERED this 3rd day of December, 2004, in Tallahassee, Leon County, Florida. S CLAUDE B. ARRINGTON Administrative Law Judge Division of Administrative Hearings The DeSoto Building 1230 Apalachee Parkway Tallahassee, Florida 32399-3060 (850) 488-9675 SUNCOM 278-9675 Fax Filing (850) 921-6847 www.doah.state.fl.us Filed with the Clerk of the Division of Administrative Hearings this 3rd day of December, 2004.
The Issue The issue is whether to approve an application by Respondents, Palm Beach County (County) and The David Minkin Florida Realty Trust, Richard Thall, Robert Thall, Peter L. Briger, Paul H. Briger, and The Lester Family Investments, LP (The Briger Group), for a conceptual Environmental Resource Permit (ERP) authorizing a surface water management system to serve a mixed-use development in the City of Palm Beach Gardens known as Scripps Florida Phase II/Briger (Scripps project).
Findings Of Fact Based on the evidence presented by the parties, the following findings of fact are made: The Parties Petitioner Tsolkas resides at 822 North C Street, Lake Worth, Florida, which is approximately 16.8 miles (in a straight line) south-southeast of the project site and approximately one mile west of the Intracoastal Waterway (ICW). Among others, he expressed concerns in this case about the potential extinction of species and the impact of the proposed site on the ICW. However, other than a general interest in environmental issues, he presented no evidence to demonstrate how he is affected by the issuance of the permit. Petitioner Minaya resides at 901 North Federal Highway, Apartment A, Lake Worth, Florida, and approximately the same distance from the project site and ICW. He has the same concerns as Petitioner Tsolkas but presented no evidence to demonstrate how the project will affect his substantial interests. The County is a chartered county and a political subdivision of the state. It owns approximately 70.0 acres of the site on which the Scripps project will be located and the 193.92-acre off-site mitigation area for the project at the Pine Glades Natural Area (Pine Glades). It is a co-applicant for an ERP. The Briger Group is a co-applicant for the modified ERP and owns 611.69 acres of the project site. The original permit that is being modified was issued as conceptual approval on January 19, 1978. The District is a public corporation in the State, having been created by special act in 1949 and operating pursuant to Chapter 373, Florida Statutes. The Application On April 27, 2009, the applicants submitted an application to modify a conceptual ERP, Application No. 090427- 7, for a surface water management system to serve 681.89 acres of mixed-use development in the City of Palm Beach Gardens (City). The original permit was also issued as a conceptual approval in 1978 and has been modified conceptually on a number of occasions, most recently in 2001. The application includes 193.92 acres of off-site mitigation at Pine Glades in the northern part of the County and additional off-site mitigation through the purchase of mitigation credits at the Loxahatchee Mitigation Bank in the southern part of the County. "Conceptual approval" means "an [ERP], issued by the District Governing Board, which approves a conceptual master plan for a surface water management system or a mitigation bank." Fla. Admin. Code R. 40E-4.021(5). It constitutes final agency action and is "binding to the extent that adequate data has been made available for review by the applicant during the review process." Id. After conceptual approval is obtained, the applicants must then file an application for an ERP to construct and operate the surface water management system. Therefore, no construction will be authorized by this permit. On April 16, 2010, the District issued a Staff Report recommending approval of the requested ERP. A Revised Staff Report making minor changes and clarifications to the original proposed agency action was issued on May 4, 2010. The Project and the Site The proposed project that will be served by the surface water management system is a multi-use development on a 681-acre tract located south of Donald Ross Road and north of Hood Road in the City. The site is divided by Interstate 95 (I-95) into two wedge-shaped parcels known as the western and eastern parcels. The Florida Turnpike adjoins the western side of the western parcel. With the exception of the highways, the site is surrounded by residential development including two projects located just east of the site: Legends at the Gardens (on the northern side) and San Michele (on the southern side). A portion of the site located east of I-95 is mostly undeveloped and vegetated. However, approximately 60 acres located at the southeast corner of the site include an existing horse farm with improved and unimproved pastures. The central and southern portions of this parcel contain a number of ditches that were created prior to the 1950s. The portion of the site west of I-95 is undeveloped and vegetated, but it also includes a few mobile homes on approximately 2 acres at the southern end of the site. The upland habitats are disturbed and degraded and primarily include pine flatwoods, mixed hardwood-pine forest, hardwood hammock, and dry prairie, some of which are infested with Brazilian pepper, Australian pine, and Japanese climbing fern. There are also around 86 acres of state jurisdictional wetlands and other surface waters. Finally, the southwestern portion of the parcel located west of I-95 contains a prehistoric/archaeological site which is proposed for preservation. The County owns 70 acres of the property on the eastern parcel, while The Briger Group owns the remaining acreage. The project is anticipated to house the Scripps Research Institute, as well as ancillary institutional, commercial, and residential uses. The project received development of regional impact approval from the City on April 1, 2010, and is subject to a master plan that identifies land use districts, such as a biotech district, a town center district, residential districts, and a neighborhood-serving commercial district. The 70 acres owned by the County will be used to house the second phase of the Scripps Research Institute. It is unknown at this time whether the Scripps facility will house administrative offices, laboratory space, or some other use. The build-out schedule for the project is twenty years. Before construction can commence, the applicants will be required to obtain zoning and site plan approval from the City, authorization from both the Northern Palm Beach County Improvement District (Improvement District) and the Seacoast Utility Authority, and a permit from the County Health Department. Also, the applicants will be required to receive a construction-related modification to the ERP from the District. The Surface Water Management System In 2001, the District issued a permit to the Improvement District for conceptual approval of a surface water management system for flood protection within a 4,059.9-acre area known as Unit 2, which includes the area of the proposed project. See Respondents' Exhibit 57. Drainage from the project site is presently covered by this permit. The Improvement District's system was designed, constructed, and is being operated and maintained for stormwater treatment. The waters in that system are not considered waters of the State. The proposed project will discharge into the Improvement District's system, which is upstream of a permitted man-made control structure on the property designed to retain or detain stormwater runoff in order to provide treatment and attenuation of the stormwater. The proposed system is primarily a wet detention system consisting of three large basins: A1, B1E(East), and B1W(West). The system has been designed to provide water quality and storm water attenuation prior to overflowing to the Improvement District's Unit 2 master system. As shown in the conceptual plans, Basin B1W is located on the west side of I-95 and has a control elevation of 13.5 feet National Geodetic Vertical Datum (NGVD). Mostly residential development is anticipated in this basin with a small supporting commercial development. An existing 60-inch culvert located under I-95 will continue to connect the two wetland areas, identified as W1 and W2, that are located on both the west and east sides of I- 95, respectively. Basin B1E is located in the southeastern portion of the site and will be controlled at 13.0 feet NGVD. Anticipated development in this area will be mostly residential neighborhoods as well. Exhibit 2 of the Staff Report reflects that runoff from the out-parcels and the northern half of Hood Road will be directed into the proposed project area. Pervious and impervious assumptions were made for future Hood Road improvements and are listed in the land use table. See Respondents' Exhibit 43 at p. 3 of 26. Basin B1E will overflow into the Unit 2 master system via a control structure and outfall pipe which discharges to a wet pond located within the adjacent San Michele development to the east. Industrial and commercial development is planned in Basin A1, which is the northeastern basin. The lakes will be controlled at elevation 13.0 feet NGVD. Runoff from this basin will be directed eastward into the Improvement District's Unit 2 master system via a control structure and pipe connection into the lake within the Legends of the Gardens development to the east. The applicants submitted site grading assumptions and pervious/impervious percentages as well as stormwater modeling to demonstrate compliance with the existing master system for the overall Improvement District's Unit 2 master system. In addition, the system for this basin has been designed to accommodate inflows from approximately 50 acres of I-95 right- of-way through an existing control structure which was permitted as part of the I-95 widening project. The proposed project includes direct impacts to a total of 78.47 acres of on-site wetlands. Wetland mitigation to offset the adverse impacts includes enhancement of 7.50 acres of on-site wetlands; the purchase of 13.70 freshwater herbaceous credits at the Loxahatchee Mitigation Bank; off-site wetland and upland restoration and enhancement of 163.41 acres of wetlands; and preservation of 30.51 acres of other surface waters, or a total of 193.92 acres, at Pine Glades. The ERP Permitting Criteria In order to obtain an ERP, an applicant must satisfy the conditions for issuance set forth in Rules 40E-4.301 and 40E-4.302. Additionally, the District has adopted BOR provisions that implement the relevant portions of the rules. The conditions for issuance primarily focus on water quantity, water quality, and environmental criteria and form the basis of the District's ERP permitting program. The first step in the District's environmental review is to identify wetlands and other surface waters. On March 5, 2009, the District issued a formal determination of wetlands delineating 34 wetland areas and 4 jurisdictional surface water ditches. This determination was not timely challenged and therefore represents final agency action. That determination was used in this permit application. Water Quantity Criteria Rule 40E-4.301(1)(a) requires an applicant to provide reasonable assurances that the propose activity will not cause adverse affects to water quantity, while Rule 40E-4.301(1)(b) requires reasonable assurances that the proposed activity will not cause adverse flooding to on-site or off-site property. The BOR provides a method to calculate allowable discharge rates. The evidence is that the proposed discharge is well within the standards imposed by the rules governing water quantity impacts. There will be no on-site or off-site flooding as a consequence of the proposed project. Rule 40E-4.301(1)(c) requires reasonable assurance that there will be no adverse impacts to existing surface water storage and conveyance capabilities. The evidence supports a finding that the proposed discharge will not cause any adverse impacts. Also, the system is capable of being developed and of functioning as proposed, as required by Rule 40E-4.301(1)(i). Petitioners contended that the project poses a threat of over-draining, which will significantly affect the region directly and cumulatively. However, the project does not pose a risk of over-draining because the control elevation of the project will be maintained at a level consistent with surrounding properties and the proposed drainage rate is less than the allowable rate under the rules. Water Quality Rule 40E-4.301(1)(e) sets forth the requirements relating to water quality. Also, BOR Section 5 contains the design criteria that a project must follow regarding off-site discharges to provide reasonable assurances to satisfy the above rule. Water quality treatment will be provided in a proposed wet detention system which utilizes stormwater ponds. The evidence shows that the ponds are larger than required, thereby providing water quality treatment in excess of what is required by the BOR. All water quality standards will be met. Hazardous Waste Management Plan Petitioners contend that no hazardous waste management plan was submitted to the District. However, a plan is not required now because it would need to address the specific uses for the property, which have not yet been designated. Special Condition 31 of the permit requires that such a plan be submitted at the time an application for construction approval is filed with the District. When this is submitted, it will be reviewed to determine if there are reasonable assurances that hazardous materials, if any, will not enter the proposed project's surface water management system. Elimination and Reduction Under BOR Section 4.2.1, after the District identifies the wetlands and other surface waters, the next step is to consider elimination and reduction of impacts. However, BOR Section 4.2.1.2(b) provides that an applicant is not required to demonstrate elimination and reduction impacts when: the applicant proposes mitigation that implements all or part of a plan that provides greater ecological value and that provides greater long term ecological value than the area of wetland or other surface water to be adversely affected. In considering this provision, the District concluded, consistent with the evidence, that the quality of the wetlands which will be adversely affected by this application is low, and the mitigation proposed will provide greater long-term ecological value than the wetlands impacted. This is because the mitigation at both Pine Glades and the Loxahatchee Mitigation Bank have regional ecological value, and these sites will provide greater long-term ecological value than the impacted wetlands. Secondary Impacts Rule 40E-4.301(1)(f) requires reasonable assurance that the project will not cause adverse secondary impacts to water resources. BOR Section 4.2.7 sets forth the requirements for on-site wetlands that will be preserved and enhanced. Under that section, secondary impacts to the habitat of wetlands associated with adjacent upland activities will not be considered adverse if buffers, with a minimum width of 15 feet and an average width of 25 feet, are provided abutting the wetlands. In this case, the single wetland area being preserved is buffered in accordance with those requirements. Applicants have satisfied the requirements of the rule. Mitigation If impacts to wetlands and other surface waters will occur, then mitigation may be offered to offset the impacts to functions identified in BOR Sections 4.2 through 4.2.9. To assess the impacts and the value of mitigation, the applicants used the statewide Uniform Mitigation Assessment Method and the Wetland Rapid Assessment Procedure. Those results are found in Appendix 1 of the application and in Responses to Requests for Additional Information submitted in August 2009 and January 2010. Page 13 of the Staff Report describes the mitigation. The District also performed its own independent analysis of both the impact and mitigation. That analysis demonstrated that sufficient mitigation is available in the options identified to offset the impacts. In fact, there was a net functional gain to the environment. In order to offset 50.76 acres of wetland impacts, the applicants will provide restoration and enhancement of 139.6 acres of wetlands and 23.81 acres of uplands, and preservation of 30.51 acres of other surface waters, or a total of 193.92 acres, at Pine Glades. Mitigation at this location offsets those impacts and is appropriate because it will provide more functional gain than the amount of functional loss for the same habitat types that are being impacted. Because Pine Glades is within the same drainage basin as the impacts, and the mitigation offsets the impacts, the District is not required to consider cumulative impacts. See § 373.414(8), Fla. Stat.; Fla. Admin. Code R. 40E-4.302(1)(b). Petitioners suggested that because Pine Glades is already owned by the County and intended to be restored, by allowing the applicants to receive mitigation credit for the restoration amounts to "double dipping." However, the evidence shows that the 193 acres proposed as mitigation in the permit is site-specific; no one has ever received mitigation credit for it in the past and no one will be able to receive mitigation credit for it in the future; and The Briger Group paid $86,250.00 per functional unit to reimburse the County for the cost of the land. Mitigation credit for restoration at Pine Glades is appropriate. As compensation for impacts to a total of 26.14 acres of freshwater marsh wetlands, the applicants will mitigate off- site by purchasing 13.70 freshwater herbaceous credits at the Loxahatchee Mitigation Bank. This bank is of regional ecological significance. Mitigation at this bank offsets the impacts and is appropriate because it will offset the impacts to freshwater marsh wetlands. Drainage basins are established by District rule in BOR Figure 4.4-1. While Petitioners contended that BOR Figure 4.4-1 does not accurately identify the geographic boundaries of the South Indian River Basin, which is being used here, the District is required to follow its own rules when reviewing an ERP application. Therefore, the use of Figure 4.4-1 was appropriate to determine whether the project is located within or outside of that drainage basin. Because the Loxahatchee Mitigation Bank is not located within the same basin as the proposed impacts, it was necessary for the District to consider cumulative impacts which will be mitigated at that bank. See § 373.414(8), Fla. Stat. This means that the applicants are required to give reasonable assurances that the impacts proposed for mitigation at Loxahatchee Mitigation Bank would not result in unacceptable cumulative impacts if the regulatory precedent set by the permit were applied to all properties within the basin that have the same type of habitat as that being impacted by the project and that have potential for development. The project will be located in the South Indian River Basin. The District's cumulative impact analysis for that basin supports a finding that there is very limited potential for future wetland loss in the basin and reasonable assurances have been given that there will be no adverse cumulative impacts. See Respondents' Exhibit 60. Species Rule 40E-4.301(1)(d) requires an applicant to demonstrate that the activities will not adversely impact the value of functions provided to fish and wildlife and listed species by wetlands and other surface waters. This evaluation is limited to wetland-dependent species. Upland species fall outside of the District's jurisdiction. Contrary to Petitioners' assertion, the hand fern is not a wetland-dependent species. Also, the District must rely on State-listed species, and not lists prepared by federal agencies. The evidence shows that the potential for utilization of this site by wetland-dependent species is minimal, and this site does not contain preferred habitat for nesting or denning of wetland dependent listed species. Although the site does not contain preferred habitat, the habitat value currently existing on this site will be replaced with mitigation at Pine Glades and the Loxahatchee Mitigation Bank. Public Interest Test In order to obtain a conceptual approval ERP, an applicant must provide reasonable assurances that the system located in, on, or over wetlands or other surface waters will not be contrary to the public interest and will not be inconsistent with the objectives of the District. See Fla. Admin. Code R. 40E-4.302(1)(a)1.-7.; § 373.414(1), Fla. Stat. The evidence establishes that reasonable assurances were provided to demonstrate that the proposed activities will not adversely affect the public health, safety, or the welfare or property of others; that they will not adversely affect the conservation of fish and wildlife, including endangered or threatened species or their habitat; that there are no issues related to navigability or the flow of water, erosion or shoaling; that the property does not currently provide fishing, recreational values, or marine productivity and is not open to the public; that the activity will be permanent; that there is an archeological site on the property which the applicants will preserve; that the mitigation will more than fully offset the impacts; and that the value of the functions currently being performed will not be adversely affected. Petitioners offered no evidence or analysis to rebut the expert testimony offered by Respondents. After balancing all seven factors, the evidence supports a finding that the activities will not be contrary to the public interest. Florida Coastal Management Program Petitioners contend that the project is inconsistent with the Florida Coastal Management Program (FCMA), which is administered by the Department of Environmental Protection (DEP). They also assert that the District is required to coordinate its review of the application with that agency and that it failed to do so. However, the issuance of the ERP (after a demonstration that all permitting criteria have been satisfied) constitutes certification that the project is consistent with the FCMA and no coordination with DEP is necessary. Other Criteria Any other criteria not discussed herein were either satisfied by the applicants or are not relevant to the project. Petitioners' Evidence Other than very limited cross-examination of some of Respondents' witnesses, Petitioner Minaya did not present any evidence to support his allegations. Other than cross-examination of Respondents' witnesses, Petitioner Tsolkas, a lay person, testified that his standing was based on general concerns that the project would drive species (such as the hand fern) into extinction, that it would pollute waters, including the ICW, and that it would destroy habitat for other species. No competent or persuasive evidence to support these contentions was presented. Other issues raised by Mr. Tsolkas were matters beyond the District's jurisdiction and are not considered in the permitting process.
Recommendation Based on the foregoing Findings of Fact and Conclusions of Law, it is RECOMMENDED that the South Florida Water Management District enter a final order granting Application No. 090427-7 with the conditions contained in the Amended Staff Report. DONE AND ENTERED this 30th day of November, 2010, in Tallahassee, Leon County, Florida. S D. R. ALEXANDER Administrative Law Judge Division of Administrative Hearings The DeSoto Building 1230 Apalachee Parkway Tallahassee, Florida 32399-3060 (850) 488-9675 Fax Filing (850) 921-6847 www.doah.state.fl.us Filed with the Clerk of the Division of Administrative Hearings this 30th day of November, 2010.
The Issue Whether Petitioner Ross has standing to challenge the issuance of the WUP? Whether the District should approve the Application and enter a final order that issues the WUP?
Findings Of Fact The Parties Petitioner Ross Petitioner Ross is a resident of Pinellas County, (referred to by him at hearing as "the most urbanized county in the State of Florida"). Besides residing there, Petitioner Ross operates a farm on his property in the County. The City's experts reasonably projected and mapped a 0.5 foot drawdown contour surrounding the well field that is the subject of this proceeding. The contour defines "the cone of depression" associated with the well field. See Tr. 136. Mr. Ross' property is outside the cone of depression, to its south and west. The overall groundwater gradient in the area of the well field is from the east to the west. The water pumped from the well field does not pull water from the west because the pumping withdrawal will not reduce the potentiometric surface gradient enough to reverse the current gradient. Mr. Ross' property and the well on his property are "way outside," tr. 138, the well field and the 0.5 drawdown contour surrounding the well field. Based on the amount of drawdown reasonably projected by the well field, the effect on Mr. Ross' property could not be measured because it would be so slight. If the water in his well were to rise after the WUP is implemented, it would be impossible to tell whether the water rose "because the pump's turned off or because it rained the day before." Tr. 163. The District The District is the administrative agency charged with the responsibility to conserve, protect, manage, and control the water resources within its geographic boundaries. The District administers and enforces chapter 373, and the rules promulgated pursuant thereto. Among those rules are those that relate to the consumptive use of water found in chapter 40D-2. The City The City of Tarpon Springs is the applicant for the WUP that is the subject of this proceeding. The City's application seeks to modify an existing permit. The Existing Permit The City has an existing Water Use Permit (the "Existing Permit") from the District. Originally granted in 1976, it allows for withdrawal of fresh groundwater for public supply. The Existing Permit was last renewed in October of 2005 for a ten-year period. It expires in October of 2015. Under the Existing Permit, the withdrawal capacity is 1.38 million gallons per day annual average and allows for seven production wells. The Application and its Modification The City submitted the Application in July, 2008. The Application at that time was for 25 wells in a brackish water well field for a proposed brackish groundwater reverse osmosis plant that the City plans to build. The City's intent originally was to apply for a permit separate from the Existing Permit.1/ In September of 2009, however, the City requested that the Application be considered a modification of the Existing Permit. In honoring the request, the District changed the number assigned to the Application to "20000742.010."2/ The Application was also modified with regard to the number of production wells in the brackish well field. The number was reduced from 25 to 22, "due to land acquisition efforts indicating that the maximum number of wells . . . required for the project would be 22." Tr. 54. The Application contains an introduction that summarized the City's water supply system and its water supply plans, a completed Individual Water Use Permit Application form, a completed Public Supply Supplemental form, and an Impact Analysis Report (the "Report"). The Report states that the ground-water flow model "MODFLOW"3/ was used to perform the impact analysis. Assessment of average annual and peak month withdrawal impacts in the Upper Floridan and surficial aquifers used the SWFWMD District Wide Regulation Model Version 2 ("DWRM2"). One of the enhancements the DWRM2 offers over earlier model versions is "integrated focused telescopic mesh refinement (FTMR) which allows the model grid user to refine the model grid spacing to focus on specific areas within the District."4/ The Report included the FTMR model grid, total drawdown scenarios in the Upper Floridan Aquifer and the surficial aquifer, and a peak month drawdown scenario. The Application also included a summary of the regional hydro-geology, a summary of the City's wastewater system, a description of the City's potable water supply, an historical operating protocol and a proposed well field management plan for the City's new brackish water well field, a service area and well field location aerial, a table showing the general hydrostratigraphy in northern Pinellas County, a summary of seasonal fluctuations which addressed the conditions for issuance of a permit as set forth in rule 40D-2.381, a summary of the City's reclaimed water system, well location maps, wetland maps, Water Use Permit maps and schedules, the City's well field protection ordinance, maps pertaining to the proposed service areas, a water conservation letter, and water conservation information. The 22 new production wells in the brackish water well field will provide enough water once treated at the proposed reverse osmosis membrane treatment plant to enable the City to supply the anticipated potable water demand for all of the City's customers through the year 2015. Installation of the additional production wells will increase the annual average quantity of groundwater pumpage to 4,200,000 gallons per day ("gpd") and the peak month quantity to 6,300,000 gpd. Review of the Application by the District led to four requests by the District for additional information. The City responded to each. The responses included a well construction and aquifer testing program report, a Water Quality/Water Level Well Impact Mitigation Plan, a Water Quality Action Plan, a revised Water Quality/Water Level Well Impact Mitigation Plan, a revised Water Quality Action Plan and a second revision of the Water Quality Action Plan, a second Water Quality/Water Level Well Impact Mitigation Plan, a proposed Environmental Monitoring Plan, a third revised Water Quality Action Plan, a third revised Water Quality/Water Level Well Impact Mitigation plan, and the final Environmental Monitoring Plan. Draft Water Use Permit On October 8, 2010, the District gave notice of its intent to issue a permit that would modify the City's Existing Permit for public supply use. Attached to the notice is a Draft WUP. The modification includes the development of a brackish water well field with 22 additional production wells to allow the City to self-supply the anticipated potable water demand in 2015 for a customer base of approximately 34,259 persons. The annual average quantity authorized by the WUP is 4,200,000 gpd and the permitted peak month quantity increases to 6,300,000 gpd.5/ Special conditions of the Draft WUP require the City to maintain meters on existing and proposed withdrawal points; record and report monthly meter readings; confirm meter accuracy every five years; monitor and report the water quality and aquifer water levels; maintain an adjusted per capita rate of 150 gpd or less; conduct and report water audits; submit annual reports of residential water use, reclaimed water supplied, per capita water use rates, and well field operations; investigate withdrawal-related well complaints; conduct a well field inventory prior to the activation of the proposed production wells; comply with the environmental monitoring plan; set water quality concentration limits prior to the activation of the proposed production wells; and submit an Annual Water Quality Report and an annual Well Field Report. Criteria in Rule for Issuance of WUPs The District utilizes rule 40D-2.381 (the "Rule") in its review of water use permit applications. The Rule opens with the following: In order to obtain a Water Use Permit, an Applicant must demonstrate that the water use is reasonable and beneficial, is consistent with the public interest, and will not interfere with any existing legal use of water . . . Rule 40D-2.381(1), Tab 1 of the Binder Containing the Matters Officially Recognized, pp. 7-8. The Rule requires that the applicant make the required demonstrations through the provision of "reasonable assurances, on both an individual and a cumulative basis that the water use," id., will meet 14 conditions listed in subsections (a) through (n).6/ Condition (a) Condition (a) requires that the City demonstrate that the water use is necessary to fulfill a certain reasonable demand. To meet this condition, the City provided a population estimate through the end of the permit term and also provided a per capita rate that the City had used in the last five years. Calculations set forth in a table prepared at the request of the City show the population projections and projected water demands over a period from 2008 through 2030. These calculations provide reasonable assurances that the proposed water use meets Condition (a). Condition (b) Condition (b) requires that the City must demonstrate that the water use will not cause quantity or quality changes that adversely affect the water resources, including both surface water and groundwater. The City provided a groundwater model showing the anticipated groundwater drawdowns within the Upper Floridan and surficial aquifers. The City also completed a study on the wells within the sections of the actual proposed well field. Based upon the modeling, the drawdowns are not large enough to cause any impacts to quantity or quality of the water in the area. The City has a Water Quality/Water Level Well Impact Mitigation Plan, should there be any complaints of impact, to correct any problems after implementation of the WUP. The well field is designed with 22 supply wells. All 22 wells need not be operated at the same time to meet the water demand. Wells beyond those needed by demand have been designed into the well field so that there can be rotational capacity. Pumping at lower rates from among the 22 wells on a rotational basis is a management tool for protecting the resource and minimizing the effects of the withdrawals. The City's monitoring program provides for the collection of water levels from a large number of wells either on a monthly or quarterly basis to assess water level fluctuations in the Upper Floridan and surficial aquifers. The City also has numerous wells that will sample for chloride sulfates, total dissolved solids (TDS) and other water quality constituents on a monthly and quarterly basis to ensure that the conditions of issuance continue to be met. The City will submit groundwater pumping data on a monthly basis from all the production wells so that the District can determine that the City is indeed adhering to the quantities reflected in the WUP. Groundwater in the Upper Floridan Aquifer flows in a westward direction towards the Gulf of Mexico. The location of the proposed wells is in an urban land use area near the Gulf Coast. The wells will capture brackish groundwater that would otherwise flow westward into the Gulf. Brackish groundwater from the City's service area is the lowest quality water available for public supply in the area. The City plans to construct a reverse osmosis facility to utilize available brackish groundwater. The brackish groundwater pumped from the well field is an alternative supply source. Isolated from the regional system, it will be used for public supply in the service area. The high number of low-capacity wells will provide rotational ability for the City to manage the quantity and quality of the water resource in the area of the well field. Maximum drawdown within the well field area due to the average annual withdrawal is approximately 3 feet, with an additional 1.5 feet during peak month withdrawal. This amount of drawdown is not likely to impact other wells in the area. Condition (c) Condition (c) requires the City to demonstrate that water use will comply with the provisions of 4.2 of the WUP Basis of Review, incorporated by reference in rule 40D-2.091, regarding adverse impacts to wetlands, lakes, streams, estuaries, fish and wildlife or other natural resources. The Anclote River and associated wetlands are tidally influenced and will not be adversely impacted by the proposed withdrawal. Other wetlands in the well field area examined by a District biologist identified several isolated wetlands of concern. Isolated wetlands are generally more sensitive to withdrawal of groundwater than wetlands connected to larger basins. Initially, the City's proposed drawdowns were deemed to be unacceptable to the District because of the impact to the isolated wetlands of concern. As a first step, the City reduced the quantities of water to be withdrawn. Subsequently, an extensive Wetland Monitoring Plan was developed that included a mitigation plan if adverse impacts did occur to wetlands. Storm-water runoff will be the primary factor controlling the functions of the wetland areas. Mitigation measures, should any adverse impact become too great, include reduction of well field pumping, augmentation with well water, potable water and other feasible sources, and the purchase of mitigation credits. Condition (d) Condition (d) requires the City to demonstrate that the water use will not interfere with a reservation of water as set forth in rule 40D-2.302. The groundwater modeling that the City provided the District indicates that there are no adverse impacts to the minimum flows and levels ("MFLs") in the Anclote River or the water level at the Tarpon Road Deep Well. There are, therefore, no impacts to reservations of water. Condition (e) Condition (e) requires the City to demonstrate that the water use will comply with the provisions of 4.3 of the WUP Basis of Review,7/ regarding MFLs. The closest MFL site is the Upper Floridan Aquifer monitoring well called Tarpon Road Deep, located approximately 2.4 miles southeast of the well field. The impact analysis model results show that at the annual average withdrawal rate of 4.20 million gallons per day ("mgd") approximately 0.1 feet of drawdown at this MFL site is currently projected to occur, assuming static pumping conditions in all other regional groundwater withdrawals. This amount of drawdown will not cause the water level at the Tarpon Road Deep Well to fall below its minimum level. The District is in the process of setting an MFL for the Anclote River. Based on the operation of the new well field and the City's continued operation of their freshwater discharge to the Anclote River from their reclaimed water facility, there will be no impact to the Anclote River. Condition (f) Condition (f) requires the City to demonstrate that the water use will utilize the lowest water quality the City has the ability to use, provided that its use does not interfere with the recovery of a water body to its established MFL and it is not a source that is either currently or projected to be adversely impacted. The City is using brackish water, the lowest water quality available to be used for public supply. The City will be treating it at a reverse osmosis water treatment plant. Water of this quality is not available for others to use without special treatment. Based upon the modeling provided by the City, there are no anticipated impacts to MFLs or any other water body resources. Condition (g) Condition (g) requires the City to demonstrate that the water use will comply with section 4.5 of the WUP Basis of Review,8/ regarding saline intrusion. Groundwater in the Upper Floridan Aquifer in the area of the well field is brackish. The well field's design allowing well rotation minimizes changes in water quality during operation. The amount of drawdown and the fact that water levels will remain above sea level suggests that saline water intrusion will not occur. The reported potentiometric surface in the area of the well is approximately five feet NGVD while the land surface is roughly five feet higher at approximately ten feet NGVD. The City's monitoring and mitigation programs will address adverse impacts from saline intrusion should they occur. Condition (h) Condition (h) requires the City to demonstrate that the water use will not cause the pollution of the aquifer. Soil and groundwater contamination is documented at the Stauffer Management Company site located approximately 3,000 feet west of the well field. The drawdown from the well field is calculated to be about one foot at the Stauffer site. That level of drawdown will not induce migration of contaminants because the upward head differential from the Upper Floridan Aquifer to the surficial aquifer will be altered and the Stauffer site is down gradient of the well field. Testimony from Mr. Wiley established that the aquifers should not be contaminated by the City's withdrawals despite the presence of the Stauffer site: [T]here is a known source of contamination approximately 3,000 feet from the new well field to the west, Stauffer Chemical Company. With the small amount of drawdown that's caused in the Upper Floridan aquifer and the surficial aquifer, there's no potential for the withdrawals to cause pollution of the aquifer. Tr. 254-55. Mr. Wiley's opinion was reached primarily based on the use of the groundwater flow model to determine the drawdown at the Stauffer site and through review of groundwater levels in the Floridan and the surficial aquifers. The United States Environmental Protection Agency (the "EPA") is in charge of managing the contamination at the Stauffer site. A remediation plan has been developed based, in part, on EPA records. The remediation plan includes the construction of a barrier wall in the subsurface around the contaminated area to prevent contaminated groundwater from migrating. The City's groundwater monitoring wells will detect movement of contaminants toward the well field. The monitoring of the wells and the mitigation plan will assist in preventing pollution of the aquifers. Condition (i) Condition (i) requires the City to demonstrate that the water use will not adversely affect offsite land uses existing at the time of the application. Primary existing land uses within the City's service area are residential, commercial, and light industrial. The proposed withdrawal will not adversely impact these land uses as shown in Figure 10 of the City Exhibit 1. Five sink holes are known to exist in the general area around the well field. The closest is approximately 1,000 feet from a proposed well location. Maximum drawdown at the distance is approximately 2 feet. This amount of drawdown does not significantly increase the potential for sinkhole activity. Condition (j) Condition (j) requires that the City demonstrate the water use will not adversely impact an existing legal withdrawal. The Pasco County Utilities' wells located to the north of the well field are listed on the WUP as plugged. Wells owned by Crest Ridge Utility Corp. are located within 0.5 to 0.8 miles of the well field. Drawdown at these wells, due to the average annual withdrawal, is approximately one foot, with an additional 0.4 feet during peak month withdrawal. This amount of drawdown will not create a water level impact at these wells. Maximum drawdown at domestic wells in the area due to the average annual withdrawal is approximately three feet, with an additional 1.5 feet during peak month withdrawal. This amount of drawdown is not likely to impact other wells in the area. The City's mitigation plan addresses any adverse impact that might occur from the City's withdrawal. Condition (k) Condition (k) requires the City to demonstrate that the water use will incorporate water conservation measures. The existing per capita use rate for the City's service area is 110 gpd. Its position well below the district goal of 150 gpd per person demonstrates that the City's water conservation measures are effective. The City uses an inclined block rate structure which encourages water conservation. It also encourages water conservation through a reclaimed water system that encourages conservation of public water supply. It currently uses a little over one million gallons per day of reclaimed water. The City also conserves water through a leak protection program, a water loss audit program, adherence to the District's watering restrictions and provision of a low-flow toilet rebate program through the County, a landscape code, and the provision of educational materials to users. Condition (l) Condition (l) requires the City to demonstrate that the water use will incorporate the use of alternative water supplies to the greatest extent possible. The City has an extensive reclaimed water program. It provides reclaimed water for its golf course, for residential irrigation, for public parks and recreation, and for public schools. The City expanded its reclaimed water storage system recently by doubling the amount of reclaimed water that it is able to store for redistribution. Condition (m) Condition (m) requires the City to demonstrate that the water use will not cause water to go to waste. The City performs an unaccounted-for water audit of its system as required by a special condition of its existing WUP. The unaccounted-for water use is approximately 4 percent, well below the District guidelines. Furthermore, the City's per capita use rate of 110 gpd is well within the District's goal of 150 gpd per person. The City also has an extensive reclaimed water system which offsets potable water supply and prohibits wasted drinking water as an irrigation source. Condition (n) Condition (n) requires that the City demonstrate that the water use will not otherwise be harmful to the water resources within the District. Facts found above support a conclusion that the City has provided reasonable assurances that it meets this condition. In addition, the water that is pumped locally by the City will offset the need for ground water that would have otherwise been obtained from elsewhere in the region. Notices The District published its Notice of Proposed Agency Action in the Tampa Tribune on October 22, 2010. The District published its Notice of Proposed Agency Action in the St. Petersburg Times on October 24, 2010.
Recommendation Based on the foregoing Findings of Fact and Conclusions of Law, it is recommended that the Southwest Florida Water Management District enter a Final Order determining that Petitioner Ross lacks standing and that his Petition, therefore, be dismissed. Should it be determined in a Final Order that Petitioner Ross has standing, it is recommended that the Southwest Florida Water Management District enter a Final Order that issues Water Use Permit No. 20000742.010 to the City of Tarpon Springs. DONE AND ENTERED this 14th day of April, 2011, in Tallahassee, Leon County, Florida. S DAVID M. MALONEY Administrative Law Judge Division of Administrative Hearings The DeSoto Building 1230 Apalachee Parkway Tallahassee, Florida 32399-3060 (850) 488-9675 Fax Filing (850) 921-6847 www.doah.state.fl.us Filed with the Clerk of the Division of Administrative Hearings this 14th day of April, 2011.
The Issue The issues are whether the proposed amendment to Rule 40E- 2.041(1), Florida Administrative Code, exceeds the agency's grant of rulemaking authority; enlarges, modifies, or contravenes the specific law implemented; or is vague, fails to establish adequate standards for agency discretion, and vests unbridled discretion in the agency.
Findings Of Fact Based upon all of the evidence, the following findings of fact are determined: Petitioner, Osceola Fish Farmers Association, Inc. (OFFA), is a non-profit corporation whose members consist of tropical fish farmers in Osceola County, Florida. The parties have stipulated that OFFA has standing to bring this action. Respondent, South Florida Water Management District (District or Respondent), is a public corporation operating pursuant to Chapter 373, Florida Statutes, with its principal office in West Palm Beach, Florida. Among other things, the District has the authority to regulate the uses of water within its geographic boundaries, including Osceola County. On an undisclosed date, the District began test drawdowns (a lowering of the elevation of the water through control structures) in the Alligator Chain of Lakes just east of St. Cloud in Osceola County, where OFFA's members are engaged in tropical fish farming. The drawdowns were undertaken for the purpose of allowing the Florida Fish and Wildlife Conservation Commission (FFWCC) to conduct demucking activities in the lakes to enhance aquatic habitat. Prior to beginning work, the FFWCC obtained an Environmental Resource Permit from the Department of Environmental Protection (DEP). However, the District did not require either itself or the FFWCC to obtain a consumptive use permit on the theory that a lake drawdown for demucking activities was not a consumptive use and therefore did not require a permit. In an effort to halt future scheduled drawdowns, OFFA participated in a United States Army Corps of Engineers proceeding which culminated in the preparation of an Economic Impact Statement for FFWCC's drawdowns; filed a complaint with DEP under Section 373.219(2), Florida Statutes, alleging that an unlawful consumptive use (without a permit) was taking place (which complaint was found to be insufficient); filed an action for injunctive relief in circuit court under Section 403.412, Florida Statutes (which was dismissed or dropped for undisclosed reasons); and finally initiated a proceeding against the District under Section 120.56(4), Florida Statutes, alleging that the District had adopted "an incipient non-rule policy of exempting lake 'drawdowns' from water use permitting requirements" (DOAH Case No. 00-3615RU). To avoid the consequences of an adverse ruling in the latter action, the District began rulemaking proceedings to adopt an amendment to Rule 40E-2.041(1), Florida Administrative Code, to codify its policy relative to lake drawdowns. As amended, the rule reads as follows: Unless expressly exempt by law or District rule, a water use permit must be obtained from the District prior to any use or withdrawal of water. The drawdown of lakes for environmental, recreational, or flood control purposes is not regulated by Chapter 40E-2 or 40E-20, F.A.C. (Underscored language represents amended language). Petitioner has challenged only the amendment, and not the existing rule. The effect of the rule is obvious - a lake drawdown for one of the three stated purposes in the rule will not require a permit, while all other lake drawdowns will. As specific authority for the proposed amendment, the District cites Sections 373.044 and 373.113, Florida Statutes. The former statute authorizes the District to "adopt rules pursuant to [Chapter 120] to implement the provisions of this chapter," while the latter statute authorizes it to "adopt rules pursuant to [Chapter 120] to implement the provisions of law conferring powers or duties upon it." The District has cited Sections 373.103(1), 373.219, and 373.244, Florida Statutes, as the specific laws being implemented. The first statute provides that if specifically authorized by DEP, the District has the authority to "administer and enforce all provisions of this chapter, including the permit systems established in parts II, III, and IV of [Chapter 373], consistent with the water implementation rule"; the second statute provides in relevant part that the District may "require such permits for consumptive use of water and may impose such reasonable conditions as are necessary to assure that such use is consistent with the overall objectives of the district or department and is not harmful to the water resources of the area"; and the third statute provides for the issuance of temporary permits while a permit application is pending. In regulating the uses of water within its boundaries, the District administers a comprehensive consumptive water use permit program under Part II, Chapter 373, Florida Statutes. Both parties agree that under Section 373.219(1), Florida Statutes (2000), all "consumptive uses" of water require a permit, except for the "domestic consumption of water by individual users," which use is specifically exempted by the same statute. The global requirement for permits is also found in Rule 40E-2.041 (the rule being amended), as well as Rule 40E- 1.602(1), which provides in relevant part that unless expressly exempted by statute or rule, "[a] water use individual or general permit pursuant to Chapters 40E-2 or 40E-20, F.A.C., must be obtained prior to use or withdrawal of water " The term "consumptive uses" is not defined by statute, but the District has promulgated a rule defining that term. By Rule 40E-2.091, Florida Administrative Code, the District has adopted by reference a document known as the "Basis for Review for Water Use Permit Applications with the South Florida Water Management District." Section 1.8 of that document contains definitions of various terms used in the permitting program, including "consumptive use," which is defined as "[a]ny use of water which reduces the supply from which it is withdrawn or diverted." The District's policy for lake drawdowns, as proposed in the rule amendment, is inconsistent with this definition. On this disputed issue, Petitioner's evidence is accepted as being the most persuasive, and it is found that a lake drawdown for any purpose is a consumptive use of water. Section 373.219(1), cited as a specific law being implemented, provides that the District "may require such permits for consumptive use of water and may impose such reasonable conditions as are necessary to assure such use is consistent with the overall objectives of the district and department and is not harmful to the water resources of the area." The District construes this language as authorizing it to decide which uses of water are a "consumptive use," and which are not, and to implement a rule which codifies those decisions relative to lake drawdowns. Not surprisingly, Petitioner views the statute in a different manner and argues that the statute simply allows the District to create a permit program that is consistent with Chapter 373; that under the law a permit is required for all consumptive uses, including lake drawdowns; and that the District has no authority to carve out an exception for a lake drawdown from the permitting process, no matter what the purpose. As noted above, the District has identified three instances (for environmental, recreational, and flood control purposes) when a lake drawdown does not require a consumptive use permit. These terms are not so vague that a person of common intelligence would have difficulty understanding them. However, the proposed rule contains no prescribed standards to guide the District in its administration of the rule.
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.
