The Issue The ultimate legal and factual issue in this matter is whether Engle Homes, Inc., and Lake Bernadette, Inc. (Permittees), have provided the Southwest Florida Water Management District (District) with reasonable assurances that the activities they propose to conduct pursuant to Management and Storage of Surface Water (MSSW) General Construction Permit No. 49005837.017 (the Permit) meet the conditions for issuance of permits established in Rules 40D-4.301, 40D-4.302, and 40D- 40.302, Florida Administrative Code. In particular, the issues of fact to be litigated are whether the Project will cause adverse water quality impacts to receiving waters and adjacent lands; whether the Project will cause adverse flooding of on-site or off-site property; whether the Project will cause impacts to existing surface water storage and conveyance capabilities; and whether the Project will adversely affect the property of others.
Findings Of Fact The Parties Engle Homes, Inc., and Lake Bernadette, Inc., are corporations licensed to operate in the State of Florida. The District is the administrative agency charged with the responsibility to conserve, protect, manage, and control water resources within its boundaries pursuant to Chapter 373, Florida Statutes, and the rules promulgated thereunder as Chapter 40D, Florida Administrative Code. Driscoll resides at 35716 Welby Court, Zephyrhills, Florida 33541, Lot 14, within the Timber Creek 2 Subdivision (Subdivision). Driscoll requested this hearing to show the District that there is a drainage problem on Lots 13 and 14, and the adjacent Geiger property to the south, which should be fixed at this time and as part of the Project. Driscoll wants "Engle Homes to propose a new solution to fix the entire Welby Court Geiger property problem," i.e., from Lots 4 through 14, and not a piecemeal solution as proposed in the Permit modification. The Subdivision Engle Homes, Inc., and Lake Bernadette, Inc., developed the Timber Creek 2 Subdivision. Lots 15 through 25 run east to west and are north of Welby Court. Lots 15 and 16 are located north of the cul-de-sac, on the eastern portion of Welby Court. Lots 3 through 14 run west to east, south of Welby Court. Lots 13 and 14 are south of the cul-de-sac on the eastern portion of Welby Court and are across the street and the cul-de-sac from Lots 16 and 15, respectively. Residences exist on Lots 5, and 7 through 14. Driscoll owns Lot 14, a corner lot, which is the southeastern most lot of the Subdivision. Don Geiger (Geiger) owns the land (approximately five acres) south of the property lines of Subdivision Lots 5 through Geiger's northern driveway, essentially a dirt road, runs parallel to Lots 5 through 14. Subsequent to the original construction activity involving the Subdivision, the developer realized that there was an "existing depression" (referenced on Engle Exhibit number 1), south of Lots 7 and 8, and on Geiger's property. Geiger complained to the District about standing water in this area. This depression area is approximately 90 feet long and 30 feet wide which needed to be "drained off" according to Geiger. The depressed area on Geiger's property was most likely caused when Lots 7 through 14 were graded and sodded, which raised the "lots up a few inches" above Geiger's driveway/property. Water is trapped during a storm event between the back yards and the depressed area. As a result, the southern end of the back yards, particularly Lots 7 and 8, and the driveway remain constantly wet. The Project On January 16, 2001, Engle Homes, Inc., and Lake Bernadette, Inc., filed MSSW Permit Application No. 49005837.017 with the District, to address the problems with the rear lot grading and the adjacent property. The actual Project area for the permit modification1 includes the southern portions of Lots 4 through 9 and south of the property lot line including Geiger's property. See Finding of Fact 5. The modified permit does not address the drainage area including the back yards of Lot 13 and Driscoll's Lot 14, and the other portion of Geiger's property/driveway to the south. On April 5, 2001, the District issued MSSW Permit No. 49005837.017 to Engle Homes, Inc., and Lake Bernadette, Inc., under the provisions of Chapter 373, Florida Statutes, and Chapter 40D-40, Florida Administrative Code, for the modification of a surface water management system to serve the Project area. The proposed Project will involve the construction of a concrete inlet box with a safety grate, storm sewers, and grass swales. Specifically, the project is intended to solve the drainage problems associated with the "existing depression" south of the boundary line for Lots 7 and 8 on Geiger's property (although Lots 4 through 9 ("area 1") are included within the Project area), and the back yards of Lots 7 and 8. A catch basin is proposed to be located south and on the lot line between Lots 8 and 9, which is expected to drain off the water in the depression area to the modified surface water management system. The inlet box will be placed in the corner between Lots 8 and 9. The collected water in the inlet box will be routed underground through a series of 18-inch storm sewer pipe straight north through a drainage easement between Lots 8 and 9 to Welby Court. The underground pipe ties into an existing pipe in front of Lot 9 on the street, then runs east along the Welby Court right-of-way and then north between Lots 19 and 20, and eventually north into a large permitted retention pond, located to the north of the Subdivision which will handle the stormwater. Driscoll's Alleged Drainage Problem There is another distinct drainage area, i.e., "area 2," which includes Geiger's property and the southern portions of Lots 13 and 14, where water drains from south to north into a roadside ditch to Geiger Cemetery Road ("area 3"), which runs south to north and east of Lots 14 and 15. During a September 2001 tropical storm, there was standing water on Geiger's driveway, directly south of Lots 13 and 14, which was present for more than 3 days. This was referred to by Mr. Barrett as a "small drainage problem that could easily be corrected." On the other hand, Geiger says that there is standing water on his driveway, south of Lots 13 and 14, "all the time." This caused Geiger to move his driveway "50 or 60 feet" south. According to Geiger, the berm, which runs across Lots 10 through 14, should be lowered and the backyards reconfigured. But this would be quite disturbing to the neighbors. Therefore, Geiger recommends the placement of drains south of Lots 13 and 14, which would direct the water out to the ditch at Geiger Cemetery Road and away from Driscoll's Lot 14. The modified Permit is not intended to solve this problem, although Driscoll wants this problem fixed. It is not necessary to resolve Driscoll's issue regarding whether there is a drainage problem in and around Driscoll's lot. The two drainage areas 1 and 2 discussed herein are not connected, although they are close in proximity. The solution to the first problem has no impact on the second, and there is no cited statutory or rule requirement that both issues must be addressed in this Permit application. This is Driscoll's quandary. Compliance with Rules 40D-4.301 and 40D-4.302, Florida Administrative Code The Project will not impact wetlands or surface waters. The Project will not adversely impact the value of functions provided to fish and wildlife, and listed species, including aquatic and wetland-dependent species, by wetlands or other surface waters and other water-related resources. The Project will not adversely impact the quality of receiving waters such that the water quality standards will be violated. The Project will not cause adverse secondary impacts to the water resources. The Project will not adversely impact the maintenance of surface or groundwater levels or surface water flows established pursuant to Section 373.042, Florida Statutes. The Project will not cause adverse impacts to a work of the District. The Project is capable, based on generally accepted engineering and scientific principles, of being effectively performed and of functioning as proposed. The Project will be conducted by an entity with financial, legal, and administrative capability of ensuring that the activity will be undertaken in accordance with the terms and conditions of the permit, if issued. The Project will comply with any applicable special basin or geographic area criteria established pursuant to Chapter 40D, Florida Administrative Code, by the District. The Project will not adversely affect the public health, safety, or welfare. The Project will not adversely impact the conservation of fish and wildlife, including endangered or threatened species, or their habitats. The Project will not adversely affect navigation. The Project will not cause harmful erosion or shoaling. The Project will not adversely affect fishing or recreational values or marine productivity in the vicinity of the Project. The Project will not adversely affect significant historical and archeological resources. The Project will not cause unacceptable cumulative impacts upon wetlands and other surface waters. The Project area is less than 100 acres. The Project does not require dredging or filling of wetlands, or construction of boat slips. The Project is not contrary to the public interest. The Project will not cause adverse water quantity impacts to receiving waters and adjacent lands, and will not adversely affect or impact the property of others, including Driscoll's property, Lot 14. "Area 1," between Lots 4 and 9, is a separate drainage area, and the water from this area does not drain to Lot 14. Driscoll's property is not within the Project area, and the Project was not intended to resolve his alleged drainage problem. The Project will not cause adverse flooding to on-site or off-site property. The Project will not cause adverse impacts to existing surface water storage and conveyance capabilities. Rather, the project is expected to improve the conveyance of water and drainage for "area 1" and the Project area.
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 issuing Management and Storage of Surface Water General Construction Permit No. 49005837.017. DONE AND ENTERED this 24th day of October, 2001, in Tallahassee, Leon County, Florida. CHARLES A. STAMPELOS 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 October, 2001.
Findings Of Fact On November 1, 1982, Respondent Janson filed a Joint Application for a dredge and fill permit from Respondent, Department of Environmental Regulation, and from the Department of the Army Corps of Engineers. The project described in that application involved the construction of an approximately 1,000-square- foot, pile-supported residence, landward of the mean high water line but within the landward extent of Robinson Creek in St. Johns County, Florida. The proposed project also involved the placement of approximately 35 cubic yards of fill and a 30-foot culvert within a small (approximately 4-foot), tidally- influenced roadside ditch for driveway access and parking. The original application sought permission to place part of a concrete driveway and tool shed within the landward extent of Robinson Creek. The project is to be constructed on Lot 47, J.A. Lew Subdivision. Respondent Janson owns Lot 47, as well as Lots 45 and 46, which lots are north of and adjoining Lot 47 and also adjoining Robinson Creek. The next adjoining property owner to the north is the City of St. Augustine, Florida, which presumably owns the street. The adjoining property owner to the south of Lot 47 is Virginia P. Melichar. Neither Melichar nor the City objected to the Department's approval of the dredge and fill permit application. In support of his application, Janson retained the services of a registered surveyor and civil engineer, who performed a survey on Lot 47 to determine the location of the mean high water line with reference to the proposed project. That expert determined the location of the mean high water line to be at elevation 2.4 feet. Accordingly, all work contemplated by the dredge and fill permit is upland from the mean high water line. T.J. Deuerling, an environmental specialist for Respondent, Department of Environmental Regulation, visited the project site on December 13, 1982 and on December 30, 1982 in order to prepare the Department's Biological and Water Quality Assessment. As a result of those site visits, Deuerling recommended to Respondent Janson that he modify his permit application by moving the concrete slab and tool shed from the marsh area onto the uplands. Janson did so revise his application. In spite of the name of the permit being sought by Respondent Janson, the project involves no dredging. However, the culvert and its attendant fill would be placed in the man-made roadside ditch. That ditch constitutes a very weak transitional marsh. Although the culvert will eliminate some vegetation within that ditch, the effect of the elimination will be insignificant on water quality. The pilings for the pile-supported residence will also eliminate a small area of marsh. The anticipated shading caused by the pile-supported residence may impact somewhat on the vegetation in a small area below the residence; however, due to the fact that the floor of the house will be eight feet above the ground, light will still be able to penetrate. Therefore, the vegetation below the pile-supported residence will continue to act as a filter for pollutants. Janson has mitigated the small loss in wetlands by modifying his project so as to remove the concrete slab and tool shed from the marsh area to the uplands. Due to the project's small size, no storm water impact can be expected. Additionally, no evidence was introduced to show a violation of any water quality standard as a result of the proposed project. On March 16, 1983, Respondent, Department of Environmental Regulation, executed its Intent to Issue the dredge and fill permit in accordance with the revised application and subject to the conditions that: (1) turbidity curtains be employed in the ditch during the placement of fill over the culvert to contain any turbidity generated, and (2) construction on the uplands be confined to periods of normal water level conditions. On July 5, 1983, the Department of the Army Corps of Engineers issued its Permit and Notice of Authorization. The essence of the testimony presented by the Petitioners, including that of the employees of the St. Johns River Water Management District, who testified in opposition to the proposed project, is that even though Janson's proposed project would not impact water quality in a way that was either significant or measurable (although no one even suggested any specific water quality standard that might be violated), approval of Janson's permit might set a precedent for other projects which might then have a cumulative impact in some unspecified way at some unspecified location. No evidence was offered to show that Respondent, Department of Environmental Regulation's review of permit applications is other than site specific. Further, no evidence was introduced to show any proposed project anywhere having any impact with which Janson's project could be cumulative. Petitioners Sandquist and Shuler live in the neighborhood of the proposed project, perhaps as close as two blocks away.
Recommendation Based on the foregoing Findings of Fact and Conclusions of Law, it is RECOMMENDED that a Final Order be entered dismissing with prejudice the petition filed herein as to each individual Petitioner and issuing a dredge and fill permit to Respondent Janson in accordance with his revised application. DONE and RECOMMENDED this 13th day of January, 1984, in Tallahassee, Leon County, Florida. LINDA M. RIGOT, 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 13th day of January, 1984. COPIES FURNISHED: Stormy Sandquist 3 Aviles Street St. Augustine, FL 32084 Marion C. Snider Volla F. Snider 79 Fullerwood Drive St. Augustine, FL 32084 Carmen Ashton 51 East Park Avenue St. Augustine, FL 32084 Reuben D. Sitton Gail P.Sitton 35 Seminole Drive St. Augustine, FL 32084 Sandra N. Shuler 22 East Park Avenue St. Augustine, FL 32084 Patty Severt Greg Severt 1 Fern Street St. Augustine, FL 32084 Nancy Moore Paul Moore, Jr. 6 Fern Street St. Augustine, FL 32084 John D. Bailey, Jr., Esq. P.O. Box 170 St. Augustine, FL 32085-0170 Charles G. Stephens, Esq. Department of Environmental Regulation 2600 Blair Stone Road Tallahassee, FL 32301 Victoria Tschinkel, Secretary Department of Environmental Regulation 2600 Blair Stone Road Tallahassee, FL 32301
The Issue The issue is whether Vista of Fort Walton Beach, LLC (Vista), should be issued Surface Water Management Permit No. 04-2012-0013G authorizing the construction of an earthen embankment dam and impoundment to impound stormwater runoff from a proposed commercial development in the City of DeFuniak Springs (City), Walton County, Florida.
Findings Of Fact The District has regulatory jurisdiction over the construction of certain types of impoundments within its boundaries. If an impoundment is at least ten feet high but less than 25 feet in height and has an impounding capacity of at least 50 acre-feet, a general permit is required. See Fla. Admin. Code R. 40A-4.041(1). Vista, a limited liability corporation, owns an odd- shaped parcel in the City on which it intends to build a small commercial development consisting of a 17,000-square foot building, a parking lot, and related amenities. The vacant parcel abuts the north side of U.S. Highway 90 just east of 18th Street and is approximately 1.66 acres in size. The property is partially wooded and has a small wetland area on its northeastern corner. In conjunction with the proposed commercial development, Vista intends to construct an impoundment to control stormwater runoff from the project. Because the impoundment will be ten feet high and have an impounding capacity of at least 50 acre-feet, Vista is required to obtain a general permit. See Fla. Admin. Code R. 40A-4.041(1). Vista filed a permit application with the District on June 8, 2012. On August 8, 2012, the District gave notice that it intended to issue a surface water management permit to Vista. The permit allows the construction of a stormwater retention basin. A mitigation plan for impacts to 0.23 acres of wetlands was also approved but is not at issue in this proceeding. As described in the District staff report, the project will encompass one earthen embankment dam and impoundment to impound the storm runoff. It will operate as a dry stormwater retention basin designed to impound water only during rainfall events. The facility will utilize a pipe and riser spillway system, and the basin outfall will be protected by a rip-rap lined plunge pool. Due to space restrictions, an engineered retaining wall will be incorporated into the embankment's north side slope. The stormwater will discharge through controlled overflow structures into a nearby wetland area that lies northeast of Vista's property and will then be integrated into an existing channel that eventually forms the headwaters of Sandy Creek to the north. Petitioner has resided on her property since around 1932. Her odd-shaped parcel, described as being between five and seven acres in size, lies immediately to the north of Vista's property. A small wetland is located on the southeastern corner of her property. The two parcels share a common boundary line, appearing to be no more than a hundred feet or so. Because the boundary line is lower than the highest part of each owner's property, a "trench" has formed along the line. Wabash Avenue, a platted but un-built roadway that begins on U.S. Highway 90, runs to the northwest through the wetland area and along the eastern boundaries of both properties. As alleged in the Second Amended Petition, Petitioner is concerned that the project will cause flooding on her property. In a broader sense, she appears to be opposed to any commercial development on Vista's property. The back side of the Vista parcel slopes downhill to a recessed area that is adjacent to both properties. Although some fill has already been placed on the property in preparation for the development, the applicant intends to add "a lot" more fill to the entire parcel to create a gradual slope down to the edge of Wabash Avenue. A basin or pond around 0.20 acres in size will be formed within the fill area and a retaining wall consisting of multiple segments will be constructed around the basin. The wall will be separated from Petitioner's property by a 20-foot buffer, while at its closest point the basin will be "35 feet or so" from her property line. The plans submitted by the applicant demonstrate that the system will be built in accordance with all District standards and should operate in a safe manner. Before construction can begin, the District must approve the retaining wall design specifications. During rain events, the first inch of water will be retained on site for treatment. Additional water will be stored in the basin and then slowly allowed to discharge from the basin into the wetlands. The point of discharge from the basin is at a location a minimum of 20 feet south and east of Petitioner's property line. To ensure that the retention system will not discharge runoff at a higher rate than was discharged before development, Vista performed hydrologic calculations demonstrating pre- and post-development runoff. According to accepted models developed by the United States Department of Agriculture and its predecessor, the Soil Conservation Service, the current peak runoff from the Vista property is 2.46 cubic feet per second (CFS) during a two-year, 24-hour storm event. After development, the volume of water will be reduced to 0.74 CFS. During a 25-year, 24-hour storm event, the volume of runoff post-development is anticipated to drop from 12.59 CFS to 6.51 CFS. Finally, during a 100-year, 24-hour storm event, post- development runoff will be slightly reduced from 19.64 CFS to 18.99 CFS. Therefore, as sited, sized, and designed, the project will reduce runoff during all anticipated storm events. The foregoing calculations were not credibly contradicted and satisfy the requirement that an applicant give reasonable assurance that the project will not cause an increased flow such that it will endanger downstream property in times of flood with respect to state or frequency. See Fla. Admin. Code R. 40A-4.301(2)(f). They also confirm that water in the impoundment will not be raised to a level that could be harmful to the property of others. See Fla. Admin. Code R. 40A- 4.301(2)(c). Thus, the potential for flooding on Petitioner's property will be reduced if the project is constructed as permitted. The Department of Transportation (DOT) is currently repairing the drainage system on U.S. Highway 90 in front of the Vista property. Stormwater from that project drains into the wetlands through an easement deeded to the City at the rear of the Vista property. Petitioner pointed out that after the DOT project began, and fill was added to the Vista property, she has experienced an increase in water on her property. Whether the DOT project is responsible in any way for this hydrologic change is not known. However, accepted testimony by two professional engineers supports a finding that Vista is not responsible for any hydrologic changes on Petitioner's property. Vista was not required to take into account any runoff from the DOT project in making its hydrologic calculations because the amount of runoff from its own property will actually be reduced by the retention system. At hearing, Petitioner contended that a fence she built on the common boundary line with Vista sometime after 1990 was illegally removed by Vista in order to construct the basin. According to Mr. George, who first surveyed the property line in 1990 and then surveyed it a second time a few years ago, the fence was built a few feet beyond Petitioner's property line and lies within the buffer zone between the basin and her property. Petitioner argues that even if this is true, the doctrine of adverse possession applies and she is now the owner of the property on which the fence was built. This type of dispute, however, can only be resolved in circuit court, and not in an administrative forum. See § 26.012(2)(g), Fla. Stat. The District has examined the property records and is satisfied that Vista has ownership of the property on which the impoundment will be built. Notably, the basin will not be located within the 20-foot buffer where the fence once stood and which is dedicated to the City as an easement. Finally, through cross-examination at hearing, Petitioner suggested that any project designed by humans carries with it the remote possibility that it will fail and create a catastrophic situation on her property. In the unlikely event that the design and operation of the retention basin threaten the safety of adjoining property owners, section 373.429 and rule 40A-1.205 enable the District to revoke, suspend, or modify a permit to protect the safety of others.
Recommendation Based on the foregoing Findings of Fact and Conclusions of Law, it is RECOMMENDED that the Northwest Florida Water Management District enter a final order approving the issuance of Surface Water Management System Permit No. 04-2012-0013G to Vista. DONE AND ENTERED this 11th day of March, 2013, 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 11th day of March, 2013. COPIES FURNISHED: Jonathon Steverson, Executive Director Northwest Florida Water Management District 152 Water Management Drive Havana, Florida 32333-4712 Helen J. Crenshaw 61 North 18th Street DeFuniak Springs, Florida 32433-9547 Kevin X. Crowley, Esquire Pennington, Moore, Wilkinson, Bell & Dunbar, P.A. Post Office Box 10095 Tallahassee, Florida 32302-2095 James Busby Vista of Fort Walton Beach, LLC Post Office Box 760 Fort Walton Beach, Florida 32549-0760
Findings Of Fact Respondent TCI has more than 70 homes completed or under construction in furtherance of plans to build 141 single family residences as part of Tymber Creek Phase I, a development in Volusia County. The development site is partially bounded by the Little Tomoka River, a natural body of water which is navigable in fact. The site of the construction respondent DER proposes to permit is home to wildlife of various kinds, including woodpeckers, great horned owls, herons, mussels, manatees, snakes, turtles and alligators. At the present time, boat traffic on the Little Tomoka River is negligible. The dock TCI proposes to build would have a total area of 120 square feet and would not impede the flow of the river. It would protrude over the water no more than five feet along the bank of the river at a point where the river widens, described by some of the witnesses as a lagoon, and would not constitute a hazard to navigation. With respect to the dock, the foot bridges, the boat ramp and the removal of the agreed upon portion of unauthorized fill, the permit DER proposes to issue would be before the fact. According to DER's appraisal of TCI's original, revised permit application, which was received in evidence as DER's exhibit No. 5, TCI made revised application, on November 29, 1977, for "after-the-fact approval for the placement of approximately 3500 cubic yards of fill After TCI had filled, it constructed parking and recreational facilities. In evaluating TCI's application, Steve Beeman, a DER employee, described the site in January of 1978: Approximately 1.6 acres of filled flood plain is presently covered by a sports complex including tennis courts, swimming pool and recreation building and an asphalt parking lot. An additional 3000 square feet has been filled and paved (asphalt was applied after receipt of DER cease and desist notice) for [access to] a [proposed] boatramp and parking area, and approximately 14,000 square feet of swamps have been filled in the construction of a 1800+ feet "natural trial". DER's exhibit No. 5. By letter dated February 22, 1978, respondent DER notified respondent TCI of its intent to deny TCI's initial application, as revised. Among the reasons DER gave for its intended denial were expected violations of various water quality standards, including a prohibition against oils and greases in concentrations greater than 15 mg. per liter ("or that no visible oil, defined as iridescence, be present to cause taste or odors, or interfere with other beneficial uses.") DER's exhibit No. 4. Rule 17-3.05(2)(r) , Florida Administrative Code. This water quality standard violation was anticipated because of "the [projected] focussing of stormwater runoff into the Little Tomoka River, across paved surfaces, which are high in petroleum based pollutants." DER's exhibit No. 5. In its notice of intent to issue a permit, DER proposes to authorize TCI "to realign (straighten) existing boatramp access road." DER's exhibit No. Mr. Wheeler's letter to Mr. Shirah of April 6, 1978, DER's exhibit No. 2, describes the proposed access road change as part of "discussions and agreements concerning resolution of the initial unauthorized fill and subsequent after-the- fact application." A drawing attached to this letter indicates that the contemplated alteration of the roadway would decrease the amount of paved surface to some unspecified extent. Another part of these "discussions and agreements concerned removal of some 1900 cubic yards of fill. Most of the fill designated for removal had been placed with the idea of creating a dry pathway through the marshy area separating the Little Tomoka River from an asphalt parking area. So placed, the fill dirt acts as a dike, preventing the preexisting communication between the waters of the Little Tomoka River and the waters of the adjacent marsh. At the hearing, Mr. Wheeler testified that, if revised in accordance with DER's exhibit No. 2, TCI's project would pose no threat to water quality, but he conceded that the effects of gasoline boat motors were not considered. An increase in beat traffic would likely result in an increase in oils and greases in the waters of the Little Tomoka River.
Recommendation Upon consideration of the foregoing, it is RECOMMENDED: That respondent DER, deny the permit is proposed to issue to respondent TCI in letters to petitioners dated April 7, 1978. DONE and ENTERED this 23rd day of August, 1978, in Tallahassee, Florida. ROBERT T. BENTON, II Hearing Officer Division of Administrative Hearings Room 530, Carlton Building Tallahassee, Florida 32304 (904) 488-9675 COPIES FURNISHED: Segundo J. Fernandez, Esquire Assistant General Counsel Twin Towers Office Building 2600 Blair Stone Road Tallahassee, Florida Judson I. Woods, Jr., 32301 Esquire Post Office Box 1916 Ormond Beach, Florida 32074 Tymber Creek, Inc. c/o Stan Shirah Route 40 Twin River Drive Ormond Beach, Florida 32074
The Issue The issue in this case is whether the Southwest Florida Water Management District (District) should issue to Century Realty Funds, Inc. (Century) Environmental Resource Permit (ERP) No. 44000227.002 (the ERP), which would modify Management and Storage of Surface Waters (MSSW) Permit No. 400227.000 (the Permit) and Stormwater Exemption No. EO1481, issued by the District to Century in July 1985 for construction of a surface water management system for Angler's Green Mobile Home Park located in Mulberry, Polk County, Florida.
Findings Of Fact The District issued Management and Storage of Surface Waters (MSSW) Permit No. 400227.000 and Stormwater Exemption No. EO1481 to Century in July 1985 for construction of a surface water management system for Angler's Green Mobile Home Park (MHP) located in Mulberry, Polk County, Florida. Angler’s Green MHP Angler’s Green MHP is an 83-acre residential golf course development of approximately 385 homes located off of State Road 37 near Mulberry. Residents at Angler’s Green own their own mobile homes and lease the residential lots pursuant to annual leases expiring December 31 of each year, with guaranteed renewal conditioned upon owner compliance with the terms and conditions of the lease. Prior to being developed as a mobile home park, the property which is now Angler’s Green MHP was part of a phosphate mining operation and was reclaimed under a phosphate mining land reclamation plan approved by the Florida Department of Natural Resources and a reclamation contract dated September 4, 1984. Final contours of the Angler’s Green site were made in accordance with the approved reclamation plan. After reclamation contouring, a 23-acre manmade (former phosphate mine pit) lake remained in the northeast quadrant of the Angler's Green site. The resulting lake had a finger arm (bay or cove) extending from the southwest corner of the main body of the lake, oriented in a north-to-south direction and located west of a peninsula of land extending into the northwest part of the lake from the north. The lake also had a short, narrow canal leading into the main body of the lake from the south; the canal connected at a right angle to longer narrow waterway to the south of and extending parallel to the main body of the lake in an east-to-west orientation. There also were two smaller ponds on the property after reclamation contouring. After reclamation, surface water onsite generally flowed westerly and discharged from the property to a railroad ditch along the western boundary of the property. The recorded post-reclamation, pre-development water level for the 23-acre lake, as indicated on the site grading plans, was around 127.1 to 127.8 feet above Mean Sea Level (M.S.L.). The 1985 Permits On July 10, 1985, the District issued MSSW Permit No. 400227.000 and Stormwater Exemption No. EO1481 to Century to authorize the construction of a surface water management system for Angler’s Green. The MSSW Permit had an expiration date of July 10, 1988. As designed, the permitted Angler’s Green surface water management system was to route internal stormwater runoff to swales, detention ponds, and catchment areas before discharging through a sidebank sand filtration system (a berm approximately 300 feet long containing an 8” perforated drain pipe covered by a filter fabric and sand filter material) to receiving waters at the northwest corner of the property. The permitted system was designed with five drainage areas known as Basins A through E. Basin A was in the southeast quadrant of the site; Basin B was to its east in the southeast quadrant of the site; Basin E was to the north of Basin A and included the 23-acre former phosphate mining pit reclaimed as an artificial lake, which was referred to as “Lake E” or sometimes “Pond E"; Basin C was to the west of Basin E; and Basin D was to the west of Basin C and to the north of Basin B. The two smaller ponds on the property were designated Pond C-1 and Pond B-1 and were located in Basin C and Basin B, respectively. Basin D was in the northwest corner of the site; the discharge structure was in the northwest corner of Basin D. As the system was designed, stormwater from Basin E would appear to sheet flow naturally into Lake E; stormwater from Basin A would appear to flow naturally to the southwest, away from Lake E, but the system routed the water from the southwest corner of Basin A to the western end of the waterway on Lake E through an underground pipe. Stormwater from Basin B was to flow to and be retained in Pond B-1; as the system was designed, surface water was not designed to discharge offsite from Basin B. As designed, Lake E served as a detention pond for water from Basin E and Basin A. It was to have a control structure (CS-1) in the arm of Lake E that would produce a seasonal fluctuation range of two feet, from 127.5’ above M.S.L. to 129.5’ above M.S.L. Stormwater discharging from CS- 1 was to be conveyed by pipe to Pond C-1, where it was to mingle with surface water draining from Basin C. When full, Pond C-1 would cascade into the golf course area in Basin D and, as necessary, in a portion of Basin B. After catchment and detention in the golf course area, overflow was eventually and ultimately to discharge offsite through the side-bank sand filtration system in the northwest corner of Basin D. In this manner, the Angler’s Green surface water management system was designed to accommodate the 24-hour, 25- year storm event, which was estimated to produce approximately 8 inches of water in a 24-hour period. It also was designed to comply with the water quality requirements as specified in Florida Administrative Code Chapter 17-25 (1985 Ann. Supp.) by detaining the first half-inch of runoff before discharging it offsite through the sidebank sand filtration system in the northwest corner of Basin D. (All rule citations are to the Florida Administrative Code.) Omission of the Stangls During the review process, the District noted from drawings submitted as part of Century's MSSW Permit application that the project area did not include approximately the eastern third of the main body of Lake E. District staff brought this to Century's attention in a request for additional information (RAI) and stated: "If possible, you should obtain a perpetual right to operate and maintain the lake from other owners." In response, Century falsely represented to the District that L. Kirk McKay, a joint venture partner of Century, was the only riparian owner on Lake E and that Century had obtained from him a perpetual right to operate and maintain Lake E as part of the MSSW Permit. In fact, the Stangls owned property on the east side of the lake, including approximately 500 feet of lakefront and contiguous lake bottom. The Stangls and two partners purchased the property from McKay himself in 1979. The Stangls bought out their partners in 1984. The District relied on Century's misrepresentation. The District would not have issued the MSSW Permit to Century if the District had known that Century did not own or control all the land being used for the Permit--specifically, including all of Lake E. See Rule 40D-4.101(1)(d) and (2)(d)6. (1985) (application must include "evidence of ownership or control"). In addition, because the District was unaware of the Stangls' ownership of a portion of Lake E, the District did not require Century to give the Stangls direct, actual notice of the Century's permit application. Instead, the District only required that Century publish notice of the District’s receipt of the permit application. Notice was published on April 3, 1985, in the Lakeland Ledger, a newspaper of general circulation qualified under the terms of Section 50.011, Florida Statutes. But the Stangls did not see the published notice, were unaware of the permit application, and did not ask to participate in the permitting process. The Stangl property adjacent to Angler’s Green remained undeveloped and unoccupied until 1999, when the Stangls' son, John, established a business on the site. Prior to 1999, the Stangls visited the property a couple times a year. They were fully aware of the construction and operation of Anglers Green as a mobile home park across Lake E. During this time, Century leased 385 lots with guaranteed annual renewal conditioned only upon compliance with lease terms and conditions. Amenities under the leases included clubhouse and golf course privileges. At no time before 2000 did the Stangls take any action to challenge the validity of Century's 1985 MSSW Permit. 1985 Surface Water Management Permitting Requirements In 1985, permitting requirements for surface water management systems were divided between two regulatory schemes. Surface water management permits in Polk County were issued by the District under Chapter 373, Florida Statutes, and Rule Chapters 40D-4 and 40D-40, which addressed water quantity and flooding issues for projects greater than and less than 40 acres, respectively. Water quality permits or exemptions from water quality permitting requirements were issued by the Department of Environmental Regulation under Chapter 403, Florida Statutes, and Rule Chapter 17-25 to address water quality concerns. It was not until 1988 that permitting requirements were consolidated into the MSSW regulatory program administered by the District under Rule Chapters 40D-4 and 40D-40. In 1985, the District did not have a Basis of Review (BOR) to specify system design requirements for applicants to provide reasonable assurances that the conditions for issuance of surface water permits were satisfied. Standards and criteria for the design and performance of surface water management systems were contained in Rule 40D-4.301(2) (1985) Under subsection (2)(i) of that rule, projects designed to meet the requirements of Chapter 17-25 [Regulation of Stormwater Discharge] were presumed to meet applicable State water quality requirements. There were no requirements for wet detention pond littoral zones. 20. Under Rule 17-25.03(2)(b) (1985 Ann. Supp.), stormwater management systems for projects with drainage areas less than 100 acres that provided retention or detention with filtration of the first half-inch of runoff were exempt from the permitting requirements of Rule Chapter 17-25. 21. In 1985, District Rule 40D-4.301(2)(j) (1985) allowed for natural areas and existing water bodies to be used for stormwater retention or detention purposes when not in conflict with environmental or public use considerations. Areas that could be considered for this purpose included previously-degraded areas or man-made areas (such as borrow pits). Apparently, the District allowed Century to use Lake E as a detention pond under this provision. Deviations from MSSW Permit Angler’s Green MHP was constructed in two phases, with the first phase completed in 1985, and the second phase completed in 1987. Construction of at least the part of the surface water management system to serve the first phase took place prior to 1985; it was not clear from the evidence whether construction of the part of the surface water management system to serve the second phase also took place prior to 1985, but it clearly took place prior to construction of the second phase in 1987. Condition No. 4 of Century's MSSW Permit required the submittal of a certification that the system was constructed in accordance with the approved and permitted design. But Century did not provide any such certification. Century also never certified to the District that its new stormwater discharge facility, as constructed, continued to qualify for exemption from State water quality requirements. Although the surface water management system was constructed and operating, the District never transferred the 1985 Permit to the operation phase. In several respects, the Angler’s Green surface water management system was not constructed as designed, approved, and permitted in 1985. The pipe to convey stormwater from the southwest corner of Basin A back to the Lake E waterway apparently never was constructed; instead, stormwater from Basin A was routed to Pond B-1. (There also was a berm constructed in Basin A near the southern boundary of the site; but that berm apparently was a visual berm, and there was no evidence that it affected performance of the surface water management system.) Control structure CS-1 (which was supposed to be located in the arm or bay of Lake E) and the pipe to convey overflow from there into Pond C-1 also never were constructed. By the early 1990's, Angler's Green was experiencing flooding in the golf course area in Basin D and B for extended periods of time. In November 1993, the District responded to a complaint of flooding in that vicinity. Upon investigation, the District determined that malfunction of the surface water management system serving Reservation Lakes (now known as Paradise Lakes), a development to the north and downstream of the Angler's Green system, was causing water to back up through the wetlands and the sand filtration system in the northwest corner of the Angler’s Green project. As a result, water overtopped the discharge structure, equalized at levels above the top of the discharge structure's berm, and flooded the golf course for extended periods of time. At some undetermined point in time, an unpermitted pond was dug in Basin D, apparently in an attempt to alleviate flooding of the golf course. In addition, possibly for the same purpose, a pump was installed in Basin D near Pond C-1, and a pipe was installed to convey stormwater from there into Lake E. The sidebank sand filtration system designed to provide filtration of stormwater prior to discharge from the northwest corner of the site does not appear to exist today. It may be present but difficult to see after 15 years of plant growth; or it may have been removed or disturbed as a result of re-grading in the area. However, the evidence proved that the discharge structure was present in 1993, and there is no reason to believe that it was not installed during construction of the surface water management system--i.e., by 1987 at the latest. In addition, at some undetermined point in time, a pipe was installed at the northeast corner of Lake E to convey overflow from Lake E eastward to a drainage ditch located alongside SR 37 to the north of the Stangls' property. No witnesses could testify as to when the pipe to the SR 37 ditch was installed or its elevation. (The District and Century state in their PRO that Map No. 2 in P/I Exhibit 14--an aerial map/survey submitted to the District by Century on August 13, 1990, as part of Century's 1990 Water Use Permit No. 209993.000 application--notes the pipe's elevation as 127.95 feet above M.S.L.; but no such finding could be made from review of the exhibit.) Roads in Angler's Green have inverted crowns to convey runoff from roads, driveways, and roofs away from mobile home lots. Some runoff from these impervious surfaces appears to be directed into a swale on the east side of the site; this swale leads to Lake E. In addition, approximately 12 drains have been installed in or near roads in Angler's Green that convey water through pipes directly into Lake E or Pond C-1. Under current Rule Chapters 40D-4 and 40D-40, road drains connecting impervious surfaces to Lake E would have to be shown on application construction drawings, and separate stormwater calculations would have to be provided in an application. But in 1985 this was not required. Century's calculations, together with flow arrows on drawings showing the direction of stormwater flow towards the detention ponds, were considered sufficient--especially since Century's calculations used a relatively high runoff co-efficient. As a result, the existence of these drains and pipes are not considered to be substantial deviations from the original, approved design. Similarly, approximately 64 roof drains and pipes conveying water from roofs directly into Lake E and Pond C-1 would not be considered substantial deviations from the original, approved design. In addition, these apparently were installed by mobile homeowners over the years, not by Century. From 1985 to 2000, the District did not have occasion to address regulatory concerns at Angler’s Green, except for the complaint of flooding in the golf course area that occurred in November 1993 and a more recent complaint about an area of the golf course that was designed to flood under certain conditions. Otto Stangl’s Complaint and the District’s Response Around November 1999, John Stangl noticed a fish kill in the ditch along SR 37 near the Stangl property. He also was contacted by a governmental compliance officer concerning the fish kill. Upon investigating, John Stangl saw the unpermitted pipe leading from Lake E that was discharging into the SR 37 ditch where the fish kill was observed, as well as the unpermitted pump that was pumping water from the Angler’s Green golf course area through a pipe that discharged into Lake E. In February 2000, Otto Stangl complained to the District about the fish kill and the existence of the unpermitted structures associated with Lake E. Upon receiving Otto Stangl’s complaint, District staff conducted site visits of the Angler’s Green project. Staff observed the unauthorized pump and pipe conveying water from Pond C-1 to Lake E and the unauthorized pipe conveying water from Lake E to the SR 37 ditch. Staff also observed that the Lake E control structure was missing, the pipe to convey stormwater from Basin A to Lake E was missing, and Basin D had been re-graded. In February 2000, the District also became aware of the fact that Century did not have full ownership or control of Lake E. On March 15, 2000, the District issued Century Notice of Non-Compliance and directed Century to either construct the system as designed and permitted or to seek a permit modification. On May 8, 2000, Century submitted a letter application to modify the original MSSW Permit No. 400227.000 by constructing the originally permitted Lake E control structure and pipe conveying water from Lake E to Pond C-1, but in a different location in Lake E than originally permitted due to the existence of homes at the location where these structures were originally planned. The application was subsequently amended to be a formal modification upon Century’s request for further modification to allow Basin A stormwater to flow to Pond B-1 and to expand Pond B-1 and add a control structure and an effluent filtration system. Despite having actual knowledge since at least February 2000 that the Angler's Green surface water management system was built partially on their property, the Stangls did not ask for a hearing on the 1985 Permit. Instead, they awaited the District's consideration of Century's modification application and sought to challenge the District's notice of intent to grant the modification permit issued on October 29, 2001. The District’s Regulatory Compliance Practices In the 1980's, the District appeared to pay little or no attention to construction of permitted projects or submission of required post-construction certifications. Many projects permitted by the District in the 1980’s, such as Angler’s Green, were built and operating although no certifications had been submitted; as a result, the permits issued for these projects never were transferred to the operation phase. Eventually, some projects not built in compliance with issued permits came to the attention of the District, typically through third-party complaints about drainage problems and flooding. By this time, there was a large backlog of issued construction permits for which no required post-construction certifications had been submitted. The backlog of these older projects was so large that the District decided not to initiate an aggressive, systematic, and comprehensive review of all permits for which no required certifications had been submitted. Instead, projects were checked on an ad hoc basis as complaints regarding the functioning of their surface water management systems were registered. When it came to the attention of the District in this manner that a project had been built under an MSSW permit but that no required certifications had been submitted, the District first attempted to secure the required certifications in the form of certified as-built construction drawings and a Statement of Completion, as required by BOR 2.7. In so doing, it was common practice for the District to accept certifications beyond the expiration date on a permit. If projects were substantially completed, the District would not deem the permit as expired simply because the required certifications had not been submitted before the expiration date; and such projects did not lose their status as being permitted. It should be noted that, according to the testimony of the District's expert, William Hartmann, this agency practice was not based on an interpretation of Rule 40D- 4.321(1)(b) (1985) (on duration of construction permits). Rather, the agency practice was to ignore the expiration of the construction permit under those circumstances. In addition, it does not appear from the evidence that the District ever before has faced the situation presented in this case--where a person on whose property part of a surface water management system was built without the person's consent opposes modification and asserts the construction permit has expired. In cases where the agency's practice was applied, if the required certified as-built construction drawings and Statement of Completion could not be provided because the project was not built in accordance with the MSSW permit, the District would require the permittee to either bring the system into compliance with the approved permit designs or obtain a modification of the construction permit. Letter modifications would be accepted when the requested modification would not substantially alter the permit authorization, increase the authorized offsite discharge, impact the environmental features of the project, decrease the required retention/detention, decrease the required flood control elevations for roads or buildings, or decrease pollution removal efficiency. See Rule 40D-4.331(2)(b) (1985). (The current version of the rule adds renewal or extension of the existing permit duration.) Alterations meeting the threshold requirements for a letter modification would be presumed to meet the conditions for issuance for a permit. Otherwise, formal permit modifications would be required. When application is made for a permit modification, the District’s practice is to evaluate those aspects of the surface water management system being modified. Review generally would not extend to the entire system. Permittees seeking to modify their surface water management systems generally are not required by the District to bring the unmodified portions of the system into compliance with current design criteria. Proposed ERP Permit Modification ERP Application No. 44000227.002 seeks authorization to modify portions of the Angler’s Green surface water management system. The specific alterations for which approval is sought are: permanent removal of the existing, unpermitted 18-inch pipe between Lake E and SR 37 roadside ditch; permanent removal of the pump and associated piping conveying water from Pond C-1 to Lake E; installation of the control structure (CS-1), together with installation of pipe to convey water from the control structure to Pond C-1, as designed and approved in the 1985 Permit but different location in the northwest corner of the main body of Lake E; re-grading of the northwesterly portion of the golf course to more closely conform to the original permitted plan and help keep Basin B separate from Basin D; reconstruction of the side-bank sand filter system in the northwest corner of the property, as designed and approved in the 1985 Permit but with a slightly higher invert elevation (122.04 feet above M.S.L.) to prevent water from backing up into Angler's Green from Paradise Lakes again, and with a concrete flume and spreader swale between Pond C-1 and the berm of the side-bank sand filter system; enlargement of Pond B-1; installation of a control structure on Pond B-1; and installation of 100 feet of 6-inch side-bank sand filter discharging to the southwest corner of the property from Pond B-1. By removing the unpermitted pipe to the roadside ditch along SR 37 and by constructing control structure CS-1, with the same control elevations as in the 1985 Permit (albeit at a different location in Lake E), and connecting CS-1 by pipe to Pond C-1 as envisioned in the 1985 Permit, the function of Lake E should approximate its function under the design approved in 1985. Modifying the permitted design to authorize Basin A to flow to Pond B-1 instead of Lake E results in less water flowing to Lake E; these changes will not increase water quantity or quality impacts to Lake E, as compared to the 1985 Permit. As compared to reclamation conditions prior to implementation of the 1985 Permit, water quantity and quality impacts to Lake E would be expected both under the system as designed and permitted in 1985 and as proposed to be modified, by virtue of the similar use of Lake E as a detention pond under either system. Pond B-1 is being enlarged to better accommodate the flow from Basin A. The control structure being added at Pond B-1 will control flow into the swale to the west so as to address water quantity impacts in that area. Stormwater calculations for the revised Pond B-1 demonstrated that the post-development discharge rate will not exceed the pre- development discharge rate, so that there are no concerns for adverse water quantity impacts to receiving waters or adjacent lands or flooding impacts to on-site or off-site property. The historical flows to the west are still maintained. The discharge structure being added at Pond B-1 will account for treatment of the Basin A flow. Based on calculations for revised Pond B-1, the enlarged pond will retain and percolate half an inch of stormwater runoff from the contributing area in 36 hours (which is consistent with current BOR design requirements). The proposed Pond B-1/Basin B modifications, including the routing of Basin A stormwater to Pond B-1, will not adversely affect the quality of receiving waters in that vicinity such that state water quality standards would be violated. Angler's Green is located in the Southern Water Use Caution Area of Polk County. No surface or groundwater levels or surface water flows have been established for this area under Section 373.042, Florida Statutes. The proposed modifications do not involve any works of the District. The proposed modifications are based on generally accepted engineering and scientific principles and employ treatment methods of effluent filtration which involve commonly accepted designs that can be effectively performed and function as proposed. There are no concerns about Century’s financial, legal, or administrative capability to undertake the proposed modifications as specified in the permit, if issued. There are no applicable special basin or geographic area criteria established for this area. Environmental Concerns As with its review of the proposed permit modification for water quantity impacts, the District's review of environmental concerns was limited to review of impacts from the proposed modifications to the original permitted design; unmodified portions of the original permit were not reviewed for compliance with current requirements. An approximately 20 square-foot permanent impact is proposed to Lake E due to the placement of the control structure (SW-1) in the water. A 379 square-foot temporary impact is proposed to Lake E due to the placement of a cofferdam to facilitate construction of the control structure. Temporary impacts to Lake E resulting from the construction of the control structure would be addressed through the use of sediment and erosion controls to prevent possible sedimentation and turbidity that may arise during the construction activity. The placement of a control structure in Lake E would create very minor permanent impacts resulting from the loss of the footprint of the control structure. These impacts would be insignificant. Due to the very minor nature of these proposed impacts, no mitigation would be required, and no loss of wetlands would be required to be recorded on the Wetlands/Surface Water Table. Construction of SW-1 would not adversely impact the value of functions provided to fish and wildlife, and listed species including aquatic and wetland dependent species, by wetlands, other surface waters and other water related resources of the District. No secondary impacts would be expected from construction of SW-1. No unacceptable cumulative impacts upon wetlands and other surface waters would be expected to occur as a result of construction of SW-1. The project area includes .71 acre of herbaceous/forested wetlands (WL-1) in the northwest corner. The potential for secondary impacts is addressed by an existing fence surrounding WL-1, which eliminates concerns for secondary impacts to this wetland area. No adverse impacts would be anticipated to occur to these wetlands, and no adverse secondary impacts to the water resources would be expected to occur as a result of the proposed modifications themselves. The proposed modifications would not cause unacceptable cumulative impacts to wetlands and other surface waters. Class II or Class III waters would not be affected by the proposed modification project. Therefore, Rule 40D- 4.302(1)(c) is not applicable. No seawalls, lagoons or estuaries are involved in this project. Therefore, Rule 40D-4.302(d) is not applicable. The proposed modifications would not be contrary to the public interest. Relocation of a control structure and enhancement of the Basin B portion of the system would create no significant change in impacts. The proposed modifications constitute a slight improvement over water quality from the original permitted design. No threatened or endangered species were identified for Angler’s Green. The proposed relocation and construction of the Lake E control structure, preservation of onsite wetlands in the northwest corner, and re-design of Pond B-1 present no environmental concerns. Consequently, the proposed modifications do not create any potential for adverse effects regarding the conservation of fish and wildlife, including endangered or threatened species or their habitats. The proposed modifications do not adversely affect the fishing or recreational values or marine productivity in the vicinity of the activity. The project area does not involve navigable waters and does not affect the flow of water or cause harmful erosion or shoaling. Hence, Rule 40D-4.302(1)(a)(3) does not apply to this permit modification application. There are no significant historical and archaeological resources involved in this Project. Therefore, Rule 40D-4.302(1)(a)(6) is not applicable to this permit modification application. The proposed modifications would not be contrary to the public interest; they would not adversely affect the public health, safety or welfare or the property of others. No adverse impacts are anticipated to occur as a result of the proposed modifications. The proposed modifications maintain the historic water elevation for Lake E and maintain historic flows for the project area. The modified system should also provide some improvement in water quality.
Recommendation Based upon the foregoing Findings of Fact and Conclusions of Law, it is RECOMMENDED that the Southwest Florida Water Management District enter a final order denying Century's permit modification application designated ERP No. 44000227.002. DONE AND ENTERED this 8th day of July, 2002, in Tallahassee, Leon County, Florida. ________________________________ J. LAWRENCE JOHNSTON Administrative Law Judge Division of Administrative Hearings The DeSoto Building 1230 Apalachee Parkway Tallahassee, Florida 32399-3060 (850) 488-9675 SUNCOM 278-9675 Fax Filing (850) 921-6847 www.doah.state.fl.us Filed with the Clerk of the Division of Administrative Hearings this 8th day of July, 2002. COPIES FURNISHED: Joseph D. Magri, Esquire Merkle & Magri, P.A. 5510 West LaSalle Street Tampa, Florida 33607-1713 Joseph P. Mawhinney, Esquire Clark, Campbell & Mawhinney, P.A. Post Office Box 6559 Lakeland, Florida 33802 Martha A. Moore, Esquire Southwest Florida Water Management District 2379 Broad Street Brooksville, Florida 34604-6899 E. D. Sonny Vergara, Executive Director Southwest Florida Water Management District 2379 Broad Street Brooksville, Florida 34604-6899
The Issue The issue in this case is whether the Department of Environmental Protection (DEP or Department) should exempt Petitioner's alleged maintenance-dredging from wetland resource permitting under Florida Administrative Code Rule 62- 312.050(1)(e).1
Findings Of Fact Petitioner has applied for a maintenance-dredging exemption from wetland resource permitting for two channels in Goose Bayou on the two ends of a U-shaped upland cut canal adjacent to Goose Bayou. Rule 62-312 provides in pertinent part: No permit shall be required under this chapter for dredging or filling . . . for the projects listed below. * * * (e) The performance of maintenance dredging of existing manmade canals, channels, and intake and discharge structures, where the spoil material is to be removed and deposited on a self-contained, upland spoil site which will prevent the escape of the spoil material and return water from the spoil site into surface waters of the state, provided no more dredging is performed than is necessary to restore the canal, channels, and intake and discharge structures to original design specifications, and provided that control devices are used at the dredge site to prevent turbidity and toxic or deleterious substances from discharging into adjacent waters during maintenance dredging. This exemption shall apply to all canals constructed before April 3, 1970, and to those canals constructed on or after April 3, 1970, pursuant to all necessary state permits. This exemption shall not apply to the removal of a natural or manmade barrier separating a canal or canal system from adjacent waters of the state. Where no previous permit has been issued by the Board of Trustees of the Internal Improvement Trust Fund or the United States Army Corps of Engineers for construction or maintenance dredging of the existing manmade canal or intake or discharge structure, such maintenance dredging shall be limited to a depth of no more than 5 feet below mean low water. There was no evidence of any dredging or application for dredging in the vicinity of the proposed alleged "maintenance- dredging" prior to 1971. There was evidence and a stipulation that Heritage Homes of Fort Walton, Inc. (Heritage Homes), applied to the State of Florida in or around 1971 to dredge two navigation channels in Goose Bayou for a project known as Venetian Villas and to remove two plugs separating a land-locked U-shaped canal from Goose Bayou. The navigation channels were to be 50 feet wide by five feet deep. The southern channel was to be 640 feet long, while the northern channel was to be 450 feet long. This proposal did not receive any governmental authorization. There was evidence and the parties stipulated that in 1973, based on the proposed project modifications, the State of Florida Department of Pollution Control (DPC), a predecessor of DEP, issued water quality certification, and the State of Florida Board of Trustees of the Internal Improvement Trust Fund (BOT) issued a permit for the project, as modified. It appears that the issuance of the water qualify certification and BOT permit was part of some kind of settlement reached between Heritage Homes and the State of Florida for dredge-and-fill violations. It appears that the settlement also involved the conveyance of ten acres of land to the State of Florida in lieu of payment for the spoil used in filling the marsh lands between Goose Bayou and the U-shaped canal. There was evidence and the parties stipulated that, at some point in time, the DPC certification and a BOT permit were transferred from Heritage Homes to West Florida Construction Company (West Florida). There was evidence and the parties stipulated that, as of July 13, 1973, neither Heritage Homes nor West Florida had applied to the United States Army Corps of Engineers (Corps) for a permit. There was evidence and the parties stipulated that, over time and after receiving comments from various governmental agencies, West Florida's proposed project changed to involve a yacht basin/marina, a proposed southern channel, elimination of the proposal for a northern channel, and plugging the U-shaped canal to keep it separate from Goose Bayou. The location of the single, southern channel under this proposal was different from the proposed location of the southern channel under the Heritage Homes proposal, which was to start at the southernmost arm of the U-shaped canal. Instead, under West Florida's proposal, the single, southern channel was to be located directly north of the southernmost arm of the U-shaped canal. There was evidence and the parties stipulated that, by August 21, 1974, West Florida applied to the Corps for a permit to dredge the single, southern channel (50 feet wide, 565 feet long, and four feet deep), to keep the northern canal plugged, and to construct a yacht basin/marina. There was evidence and the parties stipulated that, the United States Department of the Interior Fish and Wildlife Service (FWS) and the United States Environmental Protection Agency (EPA) recommended several changes to the project before they could recommend that the Corps issue a permit for the 1974 application; however, it does not appear that the recommended changes were ever made or that the Corps ever took any action on the 1974 application or issued any permit for the proposed project. At some point in time after 1974, the two plugs were removed, which connected the U-shaped canal to Goose Bayou. There is now a wide, shallow channel from the waterward ends of the U-shaped canal into Goose Bayou. The evidence did not prove that these channels, which Petitioner now seeks to maintenance- dredge, were ever dredged by man. Their width and shallow depth are more consistent with natural scouring from surface water runoff leaving the canal system at low and extreme low tides than with dredging. There was no evidence of soil borings, which could have verified whether the channels had been dredged by man. Even if originally dredged, there was no evidence that a dredged channel had been maintained over the years. Mr. Stoutamire testified that DEP does not consider maintenance- dredging to include the restoration or rebuilding of a channel that has not been maintained and no longer exists. This interpretation of the maintenance-dredging exemption is reasonable. Mr. Stoutamire also testified that DEP interprets the last sentence of Rule 62-312.050(1)(e), limiting maintenance- dredging to no more than five feet below mean low water where no previous permit has been issued, to refer to canals constructed before April 3, 1970, since maintenance-dredging of canals constructed after that date would not be exempt if not previously permitted. This interpretation is reasonable.2 Petitioner's application did not state that control devices would be used to prevent turbidity and toxic or deleterious substances from discharging into adjacent waters during dredging.
Recommendation Based upon the foregoing Findings of Fact and Conclusions of Law, it is RECOMMENDED that the Department enter a final order denying Petitioner a maintenance-dredging exemption under Rule 62- 312.050(1)(e). DONE AND ENTERED this 16th day of September, 2009, in Tallahassee, Leon County, Florida. S J. LAWRENCE JOHNSTON Administrative Law Judge Division of Administrative Hearings The DeSoto Building 1230 Apalachee Parkway Tallahassee, Florida 32399-3060 (850) 488-9675 Fax Filing (850) 921-6847 www.doah.state.fl.us Filed with the Clerk of the Division of Administrative Hearings this 16th day of September, 2009.
The Issue Whether the application of Telegraph Cypress Water Management District to modify an existing surface water management system permit should be granted.
Findings Of Fact The South Florida Water Management District (District) is a public corporation in the State of Florida existing pursuant to Chapter 25270, Laws of Florida, 1949, and operating pursuant to Chapter 373, Florida Statutes, and Chapter 40E, Florida Administrative Code. The District is a multipurpose water management agency with principal offices in West Palm Beach, Florida. Telegraph Cypress Water Management District (TCWMD) is a water control district organized pursuant to Chapter 298, Florida Statutes. Agricultural operations have been conducted within the TCWMD for more than 30 years by the landowner, Babcock Florida Company. The TCWMD is the permittee of record. James D. English, Jr., owns, along with other members of his family, an orange grove and pasture in Lee County, Florida. The English family has owned the property for approximately 120 years. On November 10, 1992, James D. English, Jr., and the Panacea Timber Company filed a petition for formal administrative hearing challenging the District's intent to issue SWM Permit Modification No. 08-00004-S. Cypress Creek Partnership is a Florida General Partnership of which James D. English, Jr., is a principal. The partnership engages in agricultural activities in Lee County, Florida. The Alva Cemetery, Inc., is a Florida not-for-profit corporation which owns and manages a cemetery facility in Lee County Florida. The cemetery has been in active use for approximately 120 years. In recent years, Alva Cemetery has experienced occasions of excess water encroaching onto the cemetery property. On November 12, 1992, Alva Cemetery, Inc., filed a petition for administrative hearing challenging the District's intent to issue SWM Permit Modification No. 08-00004-S. James D. English, Jr., Cypress Creek Partnership and Alva Cemetery, Inc., are herein referred to as Petitioners. The TCWMD and the Petitioner English share a common property boundary. The Alva Cemetery is surrounded by the English property. All lands involved in this matter historically drain towards the Caloosahatchee River. The TCWMD includes approximately 89,120 acres of land located in Charlotte and Lee Counties, Florida. The land uses within the TCWMD include agricultural, cattle, and timber operations. Generally, the fields have been leased to third party farmers who use the field for several years. When the fields are not actively farmed, they are returned to a fallow state and used as pasture land until fertility is restored at which time they are reactivated for farming. Active farms fields are generally surrounded by a perimeter ditch and dike system. Pumps may be used to water and de-water the fields. When the field is returned to a fallow state, the ditch and dike system are not maintained and become less prominent either by action of weather or by intent. Pumps are not present. All of the TCWMD lies generally north to northwest of the property owned by the Petitioners. Surface waters flow onto the Petitioners' lands from the north. The Telegraph-Cypress system is unique and is the largest of its kind in South Florida Water Management District jurisdiction. The TCWMD system includes storage/detention facilities, control structures, pumping stations and an extensive network of internal canals. There are nine separate water management basins within the TCWMD. The Petitioners asserted that the water management basins identified by the District and the TCWMD are incorrect. The greater weight of the evidence establishes that the District's identification and delineation of the nine basins is based on historical hydrologic characteristics of the TCWMD and is a reasonable determination of basin boundaries. The land encompassed by the instant application for permit modification includes three of the nine basins and encompasses approximately 51,400 acres of the TCWMD. Surface water discharge from the relevant farm fields flows via the internal canal network and sheet flow to the three common detention basins: Telegraph Swamp, North Telegraph Swamp ("Telegraph North") and Curry Lake. The Telegraph North basin lies to the north of and discharges into the Telegraph Swamp basin and includes 13,799 acres of which 4,094 acres are farm fields. The drainage into the Curry Lake basin does not impact either the Telegraph North or Telegraph Swamp basins or the Petitioners' properties. The evidence establishes that as to the Telegraph North and Curry Lake drainage basins, the permit modification meets applicable permitting criteria. There is no credible evidence to the contrary. Telegraph Swamp is the largest of the three relevant detention systems. The Telegraph Swamp basin includes a total of 32,707 acres of which 4,381 acres are farm fields. Telegraph Swamp is a 4,390-acre wetland vegetated by cypress trees and sawgrass, with a base of muck soils, humus, topsoil, leaf litter and other organic material. Located at the south end of Telegraph Swamp are surface water management control structures (the Big Island Dike) built in 1975 and permitted in the original 1980 permit. The structures include three broad-crested weirs and one flash-board weir. Telegraph Swamp has been compared to a "sponge" capable of absorbing vast quantities of surface water discharges within the TCWMD before the control structures at the south end of the swamp are over-topped. Water discharged from the control structures flows through canals and creeks to the Caloosahatchee River. During storm events water is discharged over the control structures and into a swamp area south of Big Island Dike. From there, the water flows southerly, into Telegraph Creek, Big Island Canal and Cypress Creek and then into the Caloosahatchee. The Petitioners expressed concern that TCWMD could inappropriately discharge water from the control gates in the Telegraph Swamp weir. Based on evidence admitted at the hearing, the permit modification should include the following special condition: Discharge structures in the Telegraph Swamp basin shall remain fixed so that discharge cannot be made below the control elevations, except that structure gates and weirs may only be removed during emergency conditions upon notification to and consent by the District's Fort Myers Service Center regulatory area manager or designee. The Basis of Review for Surface Water Management Permit Applications within the South Florida Water Management District--September 1989, incorporated into Chapter 40E, Florida Administrative Code, provides the applicable water quantity permitting criteria relevant to this proceeding. The Petitioners assert that the control gates are required to be locked in accordance with Basis of Review section 3.2.4.1.b, which states: Discharge structures shall be fixed so that discharge cannot be made below the control elevation, except that emergency devices may be installed with secure locking devices. Either the District or an acceptable govern- mental agency will keep the keys for any such devices. The Petitioners are correct. The rule requires secure locking devices. Such condition should be added to the permit The keys may remain with the TCWMD as "an acceptable governmental agency." In 1980, the District issued Surface Water Management Permit No. 08- 00004-S for the TCWMD to operate an existing surface water management system for an existing agricultural operation. The 1980 permit specifically authorizes "[o]peration of a water management system serving 89,120 acres of agricultural lands by a vast network of internal drainage and irrigation canals, a major dike, a major canal and 4 water control structures discharging via small tributary creeks and sloughs into the Caloosahatchee River." Although the permit has been subsequently modified, the authorization to operate the system has not been amended. While District enforcement staff have occasionally noted "performance deficiencies" on the TCWMD property, there have been no permit violations by the permittee. Deficiencies which have been called to the TCWMD's attention have been resolved. Special condition number five to the 1980 permit provides that "[d]ischarges of water onto adjacent lands may be continued to the extent that increased problems are not caused by such discharges." The Petitioners assert that the District has failed to acknowledge that water discharged from the Telegraph Cypress system flows into the Cypress Creek canal and has failed to consider the impact on the Cypress Creek receiving body. However in the staff report to the 1980 permit states as follows: The Telegraph Cypress basin has three major drainage outlets. These are Trout Creek on the west, Telegraph Creek in the center and Cypress Creek to the east. There is a fourth outlet in the northeastern corner of the property known as Jack's Branch, however, this outlet is small compared to the three major ones. Much of Telegraph's southeastern area was previously drained by Spanish Creek and County Line Canal. This historical drainage pattern was blocked when a company which is presently known as Golden Grove constructed a dike across their northern boundary. This dike causes increased flow in a westerly direction around the west end of the dike, thence southerly towards Cypress Creek. This increased flow has caused excess water problems to property owners downstream. In addition, the dike has blocked virtually all flow to Spanish Creek. The evidence fails to establish that, as asserted by the Petitioners, the District has failed to acknowledge the discharge of water to Cypress Creek or to consider the condition of the Cypress Creek receiving body. In the instant case, the condition of the Cypress Creek receiving body was not re- addressed because the permit modification being sought will cause no additional adverse impacts on existing conditions. Although not individually numbered and identified in the original 1980 permit, the evidence establishes that in 1980, all of the farm fields which are subject to this permit modification application were in existence. The applicant seeks no new water control structures. Other than that required to reactivate fallow farm fields, there is no new construction proposed in the instant application. The Petitioners assert that the instant permit modification application will result in construction of new farm fields. The evidence is contrary to the assertion. Proposed permit special condition No. 10 states that the permit does not include the construction of any new farm fields. The farm fields covered in the staff report would be permitted for reactivation from a fallow state without further permitting activity in the future, and without individual retention for each farm field. The modifications to the original 1980 permit have increased the total farm land area. There is no evidence that, except as specifically permitted and approved by the District, there has been alteration of historical discharge rates or routes. There has been considerable confusion regarding the permitting status of the operations as farm fields have been reactivated. Such reactivation entails grading and leveling fields, reconstruction of ditches and dikes and installation of pumping equipment. In order to provide for standardization in farm field reactivation, and to better monitor such activities, the District requested that the TCWMD seek to modify the existing permit. On February 8, 1991, the TCWMD submitted an application to modify the existing permit for the purpose of reactivating the existing farm fields located within the Telegraph North, Telegraph Swamp, and Curry Lake drainage basins. The proposed SWM permit modification authorizes the continued use of the previously permitted surface water management system for existing active and fallow farm fields and allows the reactivation of currently fallow farm fields without further permit modification by the District. Proposed SWM permit special condition No. 16 states that the District requires notification in letter form 30 days prior to all farm field reactivation activities. The proposed modification of the permit will provide the District with an enhanced ability to inspect the reactivated farm fields. Inherent in such reactivation is ditching and diking of the fields. Such operations have been authorized since the 1980 permit was issued. The work associated with field reactivation will be conducted in accordance with existing design criteria as set forth in the application. Based on evidence admitted at the hearing, the permit modification should include the following special condition: Ditches and dikes associated with the farm fields encompassed by this authorization shall be constructed/maintained in conformance with the "Typical Field Layout And Detail Sheet," revised 10/12/93. The evidence establishes that the operations of the TCWMD as proposed by the permit modification application are within the authorization of the existing permit as previously modified. Otherwise stated, the award of this modification will have no substantial impact on the operation of the permitted surface water management system. The modification will result in no additional discharge of surface water from the control structures. The District has established water quantity criteria intended to insure that adverse impacts do not occur due to excess discharge. (Based upon the Hearing Officer's ruling on a District's Motion in Limine, water quality issues were not addressed at hearing.) The criteria are set forth at Chapter 40E-4.301, Florida Administrative Code, and in the Basis of Review. In relevant part, the District criteria require an applicant to provide reasonable assurances that the surface water management system provides adequate flood drainage and protection, that the system will not cause adverse water quantity impacts on receiving waters and adjacent lands, and that the system will not cause adverse impacts on surface and groundwater levels and flows. Modification of a permit must not result in additional adverse off-site impacts. In this case, reasonable assurances have been provided that the proposed modification will not exacerbate the historical and current drainage conditions. The permit modification application at issue does not propose to alter the rates or routes of water currently authorized for discharge from Telegraph Swamp. Reactivation of the farm fields will not impact receiving bodies in any manner different from that which presently exists under previous permits. In providing reasonable assurances, the TCWMD analyzed the water storage capacity available in the detention basins, performed flood routing projections and calculated peak discharge rates for the permit area. As required by the district, the TCWMD utilized a standard hypothetical 25-year/3- day storm event in order to determine whether sufficient capacity was available to handle the resulting stormwater. The projections provide reasonable assurances that the common detention areas have the capacity to provide adequate flood drainage and protection and are accepted. Rule 40E-4.091(1)(a), Florida Administrative Code, incorporates by reference a document identified as the "Basis of Review for Surface Water Management Permit Applications within the South Florida Water Management District--September 1989" Section 3.2.1.2.b requires that: the proposed project modification must meet the allowable discharge rate; and the allowable discharge rate for a previously permitted project is that which was set in the previous permit. The TCWMD prepared and submitted discharge calculations establishing that the post-development discharges will not exceed the discharge rate previously accepted by the District. Since 1984, the District has previously accepted a peak allowable discharge rate of 39 cubic feet per second per square mile (csm). The csm figure is based upon the historical TCWMD discharge rate within the Caloosahatchee River basin. As previously stated, reactivation of the farm fields will not impact the receiving bodies in any manner different from that which presently exists under previous permits. The District asserts that the 39csm discharge rate has been "permitted" since the 1984 modification was approved. The Petitioner asserts that the 39csm discharge rate has never been "permitted" by the District. The evidence establishes that since the 1984 application for permit modification, the discharge rate of 39csm has been utilized by TCWMD and has been accepted by the District, but that the actual permits do not specifically identify the discharge rate as 39csm. In projecting discharge rates, the TCWMD used a time of concentration of one hour. The time of concentration (T.O.C.) is the time in which water would move from the farm fields to the control structure in each sub-watershed. Otherwise stated, a projected T.O.C. of one hour means that the storm water would move from the field to the control structure in one hour. The T.O.C. of one hour is a conservative estimate and likely substantially overestimates the speed at which the water will move. The three basin areas contain a total of more than 80 square miles. Water will travel an average distance of two miles from field to detention basin through ditches, swales and existing low areas. Again conservatively, the TCWMD did not include projected travel time through such conveyances, resulting in a longer T.O.C. and resulting in a higher peak discharge rate than is probable. Although there appeared to be some confusion on the part of the District staff as to the application of the T.O.C. by the TCWMD, the TCWMD engineer who performed the calculation testified at hearing and was qualified as an expert witness in civil engineering, hydrology and surface water management. His testimony and projections are reasonable and are credited. Proposed SWM permit modification special condition No. 11 states that farm field discharge shall be directed to and conveyed via existing ditches, wetlands and/or sheetflow areas per existing site conditions. No new outfall ditches are permitted under this modification. Flood routings were calculated assuming all farm fields would be activated simultaneously and pumping the maximum capacity of 390 gallons per minute per acre (the equivalent of 20-21 inches of surface water pumped from each field daily). It is highly unlikely that all farm fields would be active simultaneously or that stormwater would continue to fall with such velocity to permit continued pumping at maximum capacity for an extended period. Even based on the conservative assumptions utilized by the TCWMD engineers, the projected peak discharge rate at the Telegraph Swamp control structure is 37csm to 38.5csm, within the maximum of 39csm previously accepted by the District. The computer modeling performed by the TCWMD engineer in calculating the peak discharge rate is accepted as reasonable. The TCWMD did not include offsite inflow in its analysis of projected capacity or discharge rates. There is anecdotal evidence that on occasion, water may flow into TCWMD from Jack's Branch or from across roadways to the north and west of the TCWMD; however, given the vast storage capacity of the TCWMD detention areas, there is no evidence that the quantity of offsite inflows is of such significance as to render the TCWMD projections unreasonable. As previously stated, the TCWMD calculations are reasonable and are accepted. The evidence establishes that the peak discharge rate resulting from approval of the instant permit modification will not exceed 39csm. The Petitioners offered their own peak discharge rate calculations, based on a "worst possible case scenario." The assumptions on which the Petitioners' projections are based are unreasonable and are rejected. Based on recommendations received at the hearing, the permit modification should include the following special condition: Pumped discharge from farm fields for which pumps are not currently installed shall be limited to 75 gallons per minute per acre of farmed area. Pumps are currently installed in fields number 7, 8, 9, 10, 12, 14, 15, 24 north and south, 28, east half of 34, 64, 67, 68, 69 and 80. The Petitioners assert that the system is currently causing adverse impacts to their properties in the form of flooding. The greater weight of the evidence establishes that the system presently does not cause adverse water quantity impacts on receiving waters and adjacent lands, and does not cause adverse impacts on surface and groundwater levels and flows. The evidence establishes that award of the application for permit modification will not adversely alter the current operations. It is clear that the Petitioners have been impacted by changes in the historical drainage patterns in the area; however, such changes had substantially occurred by 1980 when the original permit was issued. The greater weight of the credited evidence establishes that such impacts are not the result of the activities authorized in the original 1980 permit and in subsequent modifications, but instead are the result of unrelated actions by third parties not involved in this administrative proceeding. There is no credible evidence that the permit modification sought in the instant proceeding will adversely affect the Petitioners. The 1980 permit addresses existing water quantity problems in the area of the TCWMD project. For example, the construction of the Golden Grove Dike resulted in blockage of historical drainage towards Spanish Creek and the diversion of excess waters into Cypress Creek. During the 1980's the District required that culverts be installed in the Golden Grove Dike which eventually restored some surface water flow through the dike construction and on towards the south, although during some storm events water flow continues around the dike and into Cypress Creek. The Petitioners offered anecdotal evidence as to reduced water flows in some local creeks and increased flows thorough Cypress Creek. The Respondent offered evidence indicating that water flow through Cypress Creek may be less than 30 years ago, due to the digging of a canal between Spanish Creek and Cow Slough and the extension of the Clay Gully Canal's diversion of water into Telegraph Swamp. None of the evidence on this point was persuasive, however it is not relevant. Clearly, the instant permit modification application will not adversely affect the existing situation in the receiving bodies. The Petitioners assert that other receiving waterways have become clogged with vegetation, debris or soil, have accordingly reduced capacities, and are unable to accommodate historical discharge levels. Based on the lack of capacity, the Petitioners suggest that waters move towards the eastern portion of Telegraph Swamp and are discharged, flow towards, into and over the banks of Cypress Creek, and flood their properties. The TCWMD conducted a study of backwater profiles based upon credited field data. The study is found to be reasonable and is credited. Based upon the study, approximately 90 per cent of the water discharged from Telegraph Swamp is conveyed to the Caloosahatchee via Big Island Canal, Telegraph Creek and the swamp area south of the control structure. The remaining 10 per cent of the water enters the Bullhead Strand-Lightered Canal-Cypress Creek watercourse. Water flows from Telegraph Swamp into Cypress Creek via Bullhead Strand and the South Lightered Canal, however, the canal has become so restricted by vegetation that it provides little direct water flow between the strand and the creek and is more properly regarded as an area of enhanced sheet flow. The evidence does not establish that the surface water traveling from Bullhead Strand to Cypress Creek is of significance. Coupled with the existence of the Big Island Canal (which connects Telegraph Swamp to Telegraph Creek) it is unlikely that post-development surface water discharged from the Telegraph Swamp into Cypress Creek exceeds pre-development discharges. The Petitioners claim that two culverts in the Big Island canal restrict the flow of water through the canal and result in increased discharge to the east and to Cypress Creek. The greater weight of the evidence establishes that during period of time when the culverts are unable to accommodate water flow, the water travels into a broad flood plain, around the culverts and returns to the Big Island Canal. The evidence establishes that the proposed modification will not result in additional adverse off-site impacts. The adverse conditions affecting Cypress Creek existed at the time of the 1980 permit and are addressed in the staff report to that permit and to subsequent permit modifications. There is no credible evidence that modification of the permit as sought in this case will result in adverse impacts beyond those which have existed at the time of the award of the original permit. The Petitioners assert that the fields included within the permit modification application lack individual retention areas. The lack of individual detention areas is immaterial in this case where sufficient downstream detention capacity is available through the common detention areas. The Petitioners asserts that the Telegraph Swamp is an "above-ground impoundment" and that as such is fails to comply with requirements related to such water storage systems. The Telegraph Swamp is not a typical "above-ground impoundment" as that term is routinely applied by the District. The regulations addressed by the Petitioners clearly state that they are not intended to be inclusive and are intended to provide guidelines and basic performance criteria for commonly encountered south Florida situations. Telegraph Swamp is not a commonly encountered south Florida situation. There is no evidence that the decision not to apply the "above-ground impoundment" regulations to the Telegraph Swamp is unreasonable. The Petitioner suggest that the TCWMD application for permit modification is deficient and fails to provide information in compliance with the Basis of Review. The Basis of Review is directed towards applications for new construction. The District reasonably does not interpret the all elements of the Basis of Review to apply to existing operations. The original staff report for this permit modification application fails to acknowledge that Cypress Creek is a receiving body. However, as stated previously, the 1980 application and subsequent modifications have clearly addressed the fact that Telegraph Swamp waters discharge to Cypress Creek via intervening waterways. The failure to include the reference in the staff report to this application for modification is irrelevant.
Recommendation Based on the foregoing, it is hereby RECOMMENDED that the South Florida Water Management District enter a Final Order issuing Surface Water Management Permit Modification No. 08-00004-S including the additional permit conditions set forth herein, to the Telegraph Cypress Water Management District. DONE and RECOMMENDED this 1st day of April, 1994 in Tallahassee, Florida. WILLIAM F. QUATTLEBAUM Hearing Officer Division of Administrative Hearings The DeSoto Building 1230 Apalachee Parkway Tallahassee, FL 32399-1550 (904) 488-9675 Filed with the Clerk of the Division of Administrative Hearings this 1st day of April, 1994. APPENDIX TO RECOMMENDED ORDER, CASES NO. 92-6900 and 92-6901 To comply with the requirements of Section 120.59(2), Florida Statutes, the following constitute rulings on proposed findings of facts submitted by the parties. Petitioners James D. English and Cypress Creek Partnership The proposed findings of fact submitted by Petitioners James D. English and Cypress Creek Partnership consist of unnumbered paragraphs. Pages forty-five through fifty-nine of the proposed findings of fact submitted by Petitioners James D. English and Cypress Creek Partnership were stricken as set forth in the Order On Motion To Strike issued March 29, 1994. The paragraphs of pages five through forty-four of the proposed findings of fact submitted by Petitioners James D. English and Cypress Creek Partnership have been consecutively numbered and are accepted as modified and incorporated in the Recommended Order except as follows: 1-2. Rejected, argument, not findings of fact. 7-9. Rejected, argument, not findings of fact. The staff report is not dispositive. 10-12. Rejected. The greater weight of the evidence establishes that, although the 39csm figure is not set forth in the permit, as of the 1984 modification, the TCWMD calculations have been based on a peak discharge rate of 39csm and that the District has accepted the calculations previously. The applicable criteria in the instant case require that the allowable discharge rate for a previously permitted project is that which was set in the previous permit. 13. Rejected, recitation of testimony is not finding of fact. 15-16. Rejected, argument, not finding of fact, irrelevant, cumulative. 17-18. Rejected, recitation of testimony is not finding of fact. 19. Rejected, contrary to the greater weight of credible and persuasive evidence which establishes that 39csm has been the peak discharge rate accepted by the District since 1984. The flow rate projected by the TCWMD does not exceed the accepted peak discharge rate. 24. Rejected, recitation of testimony is not finding of fact. 26-28. Rejected, recitation of testimony is not finding of fact. 29-30. Rejected, argument, not finding of fact. Rejected, irrelevant. Rejected, argument, not finding of fact. Rejected, irrelevant. The greater weight of the credible and persuasive evidence establishes that 39csm has been the District's accepted peak discharge rate and that this modification will not result in peak discharge rates in excess of that which has been previously accepted. Rejected, not supported by the greater weight of credible and persuasive evidence. The assumptions underlying the Petitioners' calculation of theoretical maximum discharge are rejected as unreasonable. Rejected, unnecessary. 36-45. Rejected, irrelevant. The anecdotal evidence fails to establish that offsite inflows are of such quantity as to render the TCWMD projections unreasonable. The proposed findings also consist of recitation of testimony or argument and are not findings of fact. 46-52. Rejected, contrary to the greater weight of credible and persuasive evidence. The evidence fails to establishes that the swamp is an "above-ground impoundment" as that term is routinely applied by the District. The proposed findings also consist of recitation of testimony or argument and are not findings of fact. 53-67. Rejected, irrelevant. An applicant for a permit modification is not required to supply every item on the checklist. An application for a modification to an existing permit often need not contain all the items described. 69. Rejected, cumulative. 70-71. Rejected, argument, not finding of fact. 72-81. Rejected, not supported by the greater weight of credible and persuasive evidence which establishes that the identification and delineation of the nine basins is based on historical hydrologic characteristics of the TCWMD and is a reasonable determination of basin boundaries. The proposed findings also consist of recitation of testimony or argument and are not findings of fact. 82. Rejected, subordinate. 83-85. Rejected, irrelevant. The confusion on the part of District staff as to what T.O.C. was utilized by the TCWMD engineer is irrelevant. This proceeding is not a review of preliminary staff activity. The applicant must establish entitlement to the permit at the hearing. 86-87. Rejected, recitation of testimony is not finding of fact. Rejected. The confusion on the part of District staff as to what T.O.C. was utilized by the TCWMD engineer is irrelevant. Rejected, unnecessary. Rejected, recitation of testimony is not finding of fact. 91-94. Rejected, irrelevant, the discharge projections calculated by the TCWMD as explicated at the hearing are credited. In any event, the evidence establishes that this modification will result in no additional discharge of surface water from the control structures. 95-97. Rejected, irrelevant. The evidence establishes that this modification will result in no additional discharge of surface water from the control structures. Petitioner Alva Cemetery Petitioner Alva Cemetery's proposed findings of fact are accepted as modified and incorporated in the Recommended Order except as follows: 2. Rejected, not supported by the greater weight of credible and persuasive evidence. 4-5. Rejected, irrelevant. Rejected, irrelevant. This is a de novo hearing, not a review of preliminary staff work. The evidence at hearing establishes that the permit modification will not cause additional adverse affect on existing receiving bodies. Rejected, irrelevant. The evidence fails to establish that Hall Creek and Fichter Creek are receiving bodies of such capacity that their omission from staff report is material. Rejected, irrelevant. Rejected, irrelevant. The evidence fails to establish that offsite inflows are of such quantity as to be relevant. 11. Rejected, not supported by the greater weight of credible and persuasive evidence. The Applicant's analysis is credited. As to T.O.C., even the less conservative T.O.C. projections indicate a peak discharge rate within that previously accepted by the District. 12-13. Rejected, irrelevant. Rejected, irrelevant. Such return overflows are unnecessary in this situation where the detention areas have the capacity to provide adequate flood drainage and protection. Rejected, not supported by the greater weight of credible and persuasive evidence. Rejected, not supported by the greater weight of credible and persuasive evidence. 18-20. Rejected, cumulative. 21. Rejected, immaterial. There is no evidence that this permit modification application will cause additional adverse impact on receiving bodies. The failure to address nonexistent impacts is immaterial. Rejected, errors in staff report are irrelevant. The evidence admitted at hearing is accepted as correct. First paragraph is rejected, cumulative. Second paragraph is rejected, not supported by the greater weight of credible and persuasive evidence. Rejected, anecdotal testimony is not supported by the greater weight of credible and persuasive evidence. Rejected. The greater weight of credible and persuasive evidence establishes that all farm fields affected by this permit modification application were in existence by the 1980 permit. Rejected, not supported by the greater weight of credible and persuasive evidence. The assumptions underlying the Petitioners' calculation of theoretical maximum discharge are rejected as unreasonable. Rejected, irrelevant. The greater weight of credible and persuasive evidence fails to establish that the cemetery flooding is related to actions by the TCWMD. Further, the evidence fails to establish that, even if the flooding was related to the TCWMD, the instant permit modification application will cause additional adverse impacts. Respondent Telegraph Cypress Water Management District Respondent Telegraph Cypress Water Management District's proposed findings of fact are accepted as modified and incorporated in the Recommended Order except as follows: 18. Rejected, subordinate. 19-20. Rejected, not credited and unnecessary. Rejected as to assertion that the 39csm discharge rate was set in the 1984 permit modification, not supported by the evidence. Review of the document admitted into evidence as the 1984 modification fails to reveal that the figure of 39csm is set forth therein. Rejected, cumulative. Rejected, unnecessary. Respondent South Florida Water Management District Respondent South Florida Water Management District's proposed findings of fact are accepted as modified and incorporated in the Recommended Order except as follows: 30. Rejected as to assertion that the 39csm discharge rate was set in the 1984 permit modification, not supported by the evidence. Review of the document admitted into evidence as the 1984 modification fails to reveal that the figure of 39csm is set forth therein. Pages 17-19 of the Proposed Recommended Order set forth revisions to the staff report which originally form the basis for the preliminary agency action in this matter. As the hearing is a de novo review of this matter, it is unnecessary for this Recommended Order to address the revision of the staff report, which has limited probative value. COPIES FURNISHED: Tilford C. Creel Executive Director South Florida Water Management District Post Office Box 24680 West Palm Beach, Florida 33416 Melville G. Brinson, Esquire 1415 Hendry Street Fort Myers, Florida 33902 Frank A. Pavese, Sr. Esquire 1833 Hendry Street Fort Myers, Florida 33902 Scott Barker, Esquire Post Office Box 159 Fort Myers, Florida 33902 John J. Fumero, Esquire Toni M. Leidy, Esquire South Florida Water Management District 3301 Gun Club Road West Palm Beach, Florida 33416
Findings Of Fact Description of Proposed Fill Project DER proposes to deny three alternative proposals to fill all or part of Petitioners' real property located in Key West, Florida. The property is rectangular, approximately three acres in size, with 300 feet bordering Roosevelt Boulevard (High-Way A1A) to the south and approximately 300 feet bordering Key West International Airport to the north. The easterly property line is 489.4 feet and the westerly line is 434.63 feet. The Straits of Florida (Atlantic Ocean) are immediately on the other side of Roosevelt Boulevard to the south. The property has a strip of approximately 90 feet of upland and transitional wetland adjacent to Roosevelt Boulevard, with the rest of the property being covered by a salt pond of approximately 40 acres in size (Jnt. Ex. 1). Petitioners initially submitted a permit application in July, 1983, to fill the entire property for construction of multifamily housing units. On May 4, 1984, after discussion with a DER permitting official, Petitioners submitted a second application containing two alternative, less extensive development proposals. The first alternative involves the placement of fill over a 300' x 230' area (approximately 9722 cubic yards) extending 230 feet from the property along Roosevelt Boulevard out into the water. This alternative would entail construction of 24 family housing units, consisting of six basic structures, each four-stories high. The second alternative involves subdividing the property into six separate lots connected by a central fill road with cul-de- sac. Each lot, approximately .4 acres in size, would contain a single family house on pilings and an associated fill pad for parking. The fill pads would be connected to a approximately 300' x 30' entrance road constructed on fill material. Presumably, this second alternative would contain the same amount of total fill as required in the first. As it presently exists, the salt pond (a part of which applicant would fill) serves several significant and beneficial environmental functions. In regard to water quality, the pond stores, filters, and purifies large quantities of storm water which drain from the airport and South Roosevelt Boulevard. The filling of any portion of this pond would diminish this capacity. (Jnt. Ex. 1) Because of their relatively isolated nature, the organic detrital material that is produced from the leaf litter of fringing mangroves is broken down into a very fine and readily usable form by bacteria. As a result, when there is an occasional exchange between the salt pond and tidal waters, the exported organics are in a very desirable form for higher trophic levels in the food web such as small fish, crustaceans, filter feeders, and various larval forms of marine life. (Jnt. Ex. 1) The salt pond proper provides valuable habitat for fish and wildlife, most notable of which are avifauna. The pond has apparently become established as a healthy, self-sustaining ecosystem providing permanent and temporary food, shelter and refuge for many faunal species which play significant and necessary ecological roles both in the salt ponds and other tidal and brackish water systems. (Jnt. Ex. 1) Through the placement of fill and the displacement of present salt pond habitat, water quality and the biological resources in the immediate and surrounding areas would be expected to undergo degradation. (Jnt. Ex. 1) Through the encroachment of development in this area, which presently lacks residential development, biological integrity standards would be expected to fall below acceptable levels. The proposed fill areas would reduce wind- driven circulation in the pond so as to stress levels of oxygen, salinity, temperature and turbidity. Runoff from the proposed fill would introduce nutrients and elevate turbidity during storm events. Finally, elevated turbidity levels could be expected during the actual filling process and the various species of fish and wildlife now located over the project site would be temporarily disturbed by construction activities and permanently displaced in the long term through the loss of habitat. (Jnt. Ex. 1) There is a 40' zoning setback and another 50' easement owned by the City of Key West, which together form a 90' strip on the property adjacent to Roosevelt Boulevard. This 90-foot strip is largely upland and some transitional wetland. There is no zoning impediment to any of the development alternatives proposed by Petitioners. The property is currently zoned R2H (multifamily residential) by the City of Key West. II. DER's Action on the Application After DER received and reviewed Petitioners initial application on July 22, 1983, a completeness summary was sent on August 17, 1983, requesting additional information. DER received the additional information on March 23, 1984, after which it notified Petitioners that additional information was needed. Petitioners met with DER officials on April 20, 1984, and submitted additional information on May 4, 1984, including the two alternative proposals. DER issued the "Intent to Deny" all three of the proposed projects on July 19, 1984 (Jnt. Ex. 1). On May 16, 1984, a DER Environmental Specialist visited the site of the proposed projects and conducted a biological and water quality assessment. This assessment was later submitted, in report form, as the Permit Application Appraisal, dated June 7, 1984. This appraisal, uncontested by Petitioners, indicates that each of the three fill proposals would take place in waters of the state and result in water quality violations under Rules 17-3.051(1), 17- 3.061(2)(c), (j) and (r); 17-3.121(7), (13) and (28); Chapter 17-4, Florida Administrative Code; and Chapter 403, Florida Statutes. Water quality problems associated with the project were identified as diminished storm water treatment, reduced beneficial deterital material, stress on oxygen levels, salinity, temperature, and turbidity, and an introduction of nutrients. (Jnt. Ex. 1) Although a DER dredge and fill permitting official testified that any filling of the salt pond would be detrimental to the birds and animals which feed there on a daily basis, and that, in his view, a "substantial amount" of filling would not be allowed by DER, there are development projects (other than the three presented by Petitioners) which, in his view, may qualify for a permit under DER rules. DER has, in the past, issued permits authorizing the construction of above-ground residences over wetland properties. Under DER's permitting standards, one or more single-family residences could be built on the property if the structures were built on stilts, did not violate water quality standards, had acceptable drainage, and did not result in adverse storm water discharges. In evaluating such an application, any mitigation an applicant could provide, such as enhancing flushing in the salt ponds by the installation of a culvert to open water, would be balanced against any adverse impacts expected from the filling activity. The three alternative filling proposals submitted by Petitioners (including drawings and designs) do not, however as yet, fall within or satisfy these general perimeters of permitting acceptability.
Recommendation Based on the foregoing, it is RECOMMENDED: That Petitioners' application to fill (containing three alternative proposals) be denied for failure to prove compliance with applicable permitting standards contained in Chapter 403, Florida Statutes, and Chapters 17-3 and 17- 4, Florida Administrative Code. DONE and ORDERED this 26th day of July, 1985, in Tallahassee, Florida. R. L. CALEEN, JR. 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 26th day of July, 1985.
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 The issue is whether the City's applications for an individual stormwater permit and a noticed general environmental resource permit for Phase 1A of the proposed Hogtown Creek Greenway should be approved.
Findings Of Fact Based upon all of the evidence, the following findings of fact are determined: Background In these two cases, Respondent, City of Gainesville (City), seeks the issuance of a stormwater system management permit (stormwater permit) to construct a 2,000-foot long asphaltic trail/boardwalk, a parking facility and associated improvements for Phase 1A of the Hogtown Creek Greenway project in the north central portion of the City. That matter is docketed as Case No. 97-2845. The City also seeks the issuance of a noticed general environmental resource permit (NGP) to construct 481 square feet of piling supported structures over wetlands or surface waters for the same project. That matter has been assigned Case No. 97-2846. Respondent, St. Johns River Water Management District (District), is the regulatory agency charged with the responsibility of reviewing and approving the requested permits. Petitioner, Greenspace Preservation Association, Inc., is a not-for-profit Florida corporation primarily composed of persons who own real property adjacent to the route proposed by the City, as well as local environmental interests. Petitioners, Frank Ward, Sal Locascio, Frederick P. Peterkin, and Harold M. Stahmer, are individuals who own real property adjacent to the route proposed by the City for the Greenway. The parties have stipulated that Petitioners are substantially affected by the District's proposed action and thus have standing to initiate these cases. On March 28, 1997, the City filed applications for a stormwater permit and a NPG for Phase IA of the Hogtown Creek Greenway project. After conducting a review of the applications, including an on-site visit to the area, in May 1997, the District proposed to issue the requested permits. On June 9, 1997, Petitioners timely filed a Petition for Initiation of Formal Proceedings as to both intended actions. As amended and then refined by stipulation, Petitioners generally allege that, as to the stormwater permit, the City has failed to provide reasonable assurance that the project meets the permitting requirements of the District; the City has failed to provide reasonable assurance that the stormwater system will not cause violations of state water quality standards; the City has failed to provide reasonable asurance that the project satisfies the District's minimum required design features; and the City has failed to provide reasonable assurance that the stormwater system is capable of being effectively operated and maintained by the City. As to the NPG, Petitioners generally allege that the piling supported structure is not less than 1,000 square feet; the jurisdictional wetlands are greater than the area shown on the plans submitted by the City; the City has failed to provide reasonable assurance that the system will not significantly impede navigation; the City has failed to provide reasonable assurance that the system does not violate state water quality standards; the City has failed to provide reasonable assurance that the system does not impede the conveyance of a watercourse in a manner that would affect off-site flooding; the City has failed to provide reasonable assurance that the system will not cause drainage of wetlands; and the City failed to provide reasonable assurance that the system does not adversely impact aquatic or wetland dependent listed species. Respondents deny each of the allegations and aver that all requirements for issuance of the permits have been met. In addition, the City has requested attorney's fees and costs under Section 120.595(1)(b), Florida Statutes (Supp. 1996), on the theory that these actions were filed for an improper purpose. A General Description of the Project The Hogtown Creek Greenway is a long-term project that will eventually run from Northwest 39th Street southward some seven miles to the Kanapaha Lake/Haile Sink in southwest Gainesville. These cases involve only Phase 1A of that project, which extends approximately one-half mile. This phase consists of the construction of a 2,000-foot long asphaltic concrete trail/boardwalk, a timber bridge and boardwalk, a parking facility, and associated improvements. The trail will extend from the Loblolly Environmental Facility located at Northwest 34th Street and Northwest 5th Avenue, to the intersection of Northwest 8th Avenue and Northwest 31st Drive. The trail will have a typical width of ten feet. For the majority of its length, the trail will be constructed of asphaltic concrete overlying a limerock base, and it will generally lie at the existing grade and slope away from the creek. Besides the trail, additional work involves the repaving of Northwest 5th Avenue with the addition of a curb and gutter, the construction of an entrance driveway, paved and grassed parking areas, and sidewalks at the Loblolly Environmental Facility, and the widening and addition of a new turn lane and pedestrian crosswalk at the intersection of Northwest 8th Avenue and Northwest 31st Drive. The Stormwater Permit Generally The entire Phase IA project area lies within the Hogtown Creek 10-year floodplain. It also lies within the Hogtown Creek Hydrologic Basin, which basin includes approximately 21 square miles. The project area for the proposed stormwater permit is 4.42 acres. Water quality criteria Phase IA of the Greenway will not result in discharges into surface groundwater that cause or contribute to violations of state water quality standards. When a project meets the applicable design criteria under the District's stormwater rule, there is a presumption that the project will not cause a violation of state water quality standards. There are two dry retention basins associated with the project. Basin 1 is located at the cul-de-sac of Northwest 5th Avenue and will capture and retain the stormwater runoff from the new and reconstructed impervious areas at the Loblolly Facility. Basin 2 is located at the parking area and will capture and retain stormwater runoff at the existing building and proposed grass parking area. Under the stormwater rule, the presumptive criteria for retention basins require that the run-off percolate out of the basin bottom within 72 hours. The calculations performed by the City's engineer show that the two retention basins will recover within that timeframe. In making these calculations, the engineer used the appropriate percolation rate of ten inches per hour. Even using the worst case scenario with a safety factor of twenty and a percolation rate of one-half inch per hour, the two retention basins will still recover within 72 hours. The presumptive criteria for retention basins require that the basin store a volume equal to one inch of run-off over the drainage area or 1.25 inches of run-off over the impervious area plus one-half inch of run-off over the drainage area. The calculations performed by the City's engineer show that the two retention basins meet the District's volume requirements for retention systems. An applicant is not required to utilize the presumptive design criteria, but instead may use an alternative design if the applicant can show, based on calculations, tests, or other information, that the alternative design will not cause a violation of state water quality standards. As a general rule, the District applies its stormwater rule so that water quality treatment is not required for projects or portions of projects that do not increase pollutant loadings. This includes linear bicycle/pedestrian trails. The City's proposed trail will not be a source of pollutants. The City will install signs at both entrances to the trail to keep out motorized vehicles. Except for emergency and maintenance vehicles, motorized vehicles will not be permitted on the trail. The infrequent use by emergency or maintenance vehicles will not be sufficient to create water quality concerns. The construction of a treatment system to treat the stormwater from the trail would provide little benefit and would only serve to unnecessarily impact natural areas. Although treatment of the stormwater run-off from the trail portion of the project is not required under District rules, the run-off will receive treatment in the vegetated upland buffer adjacent to the trail. The District's proposed other condition number 3 will require the City to plant vegetation in unvegetated and disturbed areas in the buffer. This will reduce the likelihood of erosion or sedimentation problems in the area of the trail. Although disputed at hearing, it is found that the City's engineer used the appropriate Manning coefficient in the calculations regarding the buffer. Even without a vegetated buffer, run-off coming from the bicycle trail will not violate state water quality standards. The City will install appropriate erosion and sediment controls. These include siltation barriers along the entire length of both sides of the proposed trail prior to commencing construction. Such barriers will not allow silt or other material to flow through, over, or under them. The City will also place hay bales and any other silt fencing necessary to solve any erosion problem that may occur during construction. In addition, the permit will require an inspection and any necessary repairs to the siltation barriers at the end of each day of construction. Saturation of the limerock bed under the paved portion of the trail is not expected to cause a problem because heavy vehicles will not regularly use the trail. The trail portion of the project can be adequately maintained to avoid deterioration. Sensitive Karst Areas Basin criteria The two proposed dry retention basins for Phase 1A are located within the District's Sensitive Karst Areas Basin. They include all of the minimum design features required by the District to assure adequate treatment of the stormwater before it enters the Floridan aquifer and to preclude the formation of solution pipe sinkholes in the stormwater system. There will be a minimum of three feet of unconsolidated soil material between the surface of the limestone bedrock and the bottom and sides of the two retention basins. The appropriate mechanism for determining the depth of limestone is to do soil borings. The soil borings performed by the City show that there is at least three feet of unconsolidated material between the bottom of the basins and any limerock where the borings were taken. In other words, limestone would not be expected to be within three feet of the bottom of either basin. Based on the soil boring results, the seasonal high water table is at least six feet below ground level. The depth of the two retention basins will be less than ten feet. Indeed, the depth of the basins will be as shallow as possible and will have a horizontal bottom with no deep spots. To make the retention basins any larger would require clearing more land. A large shallow basin with a horizontal bottom results in a lower hydraulic head and therefore is less potential for a sinkhole to form. Before entering the basins, stormwater will sheet flow across pavement and into a grass swale, thereby providing some dispersion of the volume. Finally, the two retention basin side slopes will be vegetated. Special condition number 7 provides that if limestone is encountered during excavation of a basin, the City must over- excavate the basin and backfill with three feet of unconsolidated material below the bottom of the basin. Drainage and flood protection Contrary to Petitioners' assertions, the project will not adversely affect drainage or flood protection on surrounding properties. The trail will be constructed generally at existing grade. Because the trail will be constructed at existing grade, the net volume of fill necessary for Phase 1A is approximately zero. Therefore, there will not be a measurable increase in the amount of runoff leaving the site after construction, and the trail will not result in an increase in off-site discharges. District rules require that the proposed post- development peak rate of discharge from a site not exceed the pre-development peak rate of discharge for the mean annual storm only for projects that exceed fifty percent impervious surface. The proposed project has less than fifty percent impervious surface. Even though it is not required, the City has demonstrated that the post-development rate of discharge will not exceed the pre-development peak rate of discharge. Both basins will retain the entire mean annual storm so that the post-development rate of discharge is zero. Even during a 100-year storm event, the retention basins willl not discharge. Therefore, there will not be any increase in floodplain elevations during the 10, 25, or 100-year storm events from the proposed project. Operation and maintenance entity requirements The applicable requirements of Chapter 40C-42, Florida Administrative Code, regarding operation and maintenance, have been met by the applicant. The City proposes itself as the permanent operation and maintenance entity for the project. This is permissible under District regulations. The duration for the operation and maintenance phase of the permit is perpetual. The City has adequate resources and staff to maintain the phase 1A portion of the project. The public works department will maintain the stormwater management system out of the City's utility fund. The City provides periodic inspections of all of its stormwater systems. These inspections are paid for out of the collected stormwater fees. The City will also conduct periodic inspections of the project area, and the two retention basins will be easily accessed by maintenance vehicles. The City will be required to submit an as-built certification, signed and sealed by a professional engineer, once the project is constructed. Monthly inspections of the system must be conducted looking for any sinkholes or solution cavities that may be forming in the basins. If any are observed, the City is required to notify the District and repair the cavity or sinkhole. Once the system is constructed, the City will be required to submit an inspection report biannually notifying the District that the system is operating and functioning in accordance with the permitted design. If the system is not functioning properly, the applicant must remediate the system. The City will be required to maintain the two retention basins by mowing the side slopes, repairing any erosion on the side slopes, and removing sediment that accumulates in the basins. Mowing will be done at least six times per year. The City will stabilize the slopes and bottom areas of the basins to prevent erosion. The City has a regular maintenance schedule for stormwater facilities. The project will be included within the City's regular maintenance program. The City has budgeted approximately $80,000.00 for maintenance of the trail and vegetated buffer. Also, it has added new positions in its budget that will be used to maintain and manage the Greenway system. Finally, City staff will conduct daily inspections of the Phase 1A trail looking for problems with the vegetated buffer, erosion problems along the trail, and sediment and debris in the retention basin. If the inspections reveal any problems, the staff will take immediate action to correct them. The Noticed General Environmental Resource Permit Generally By this application, the City seeks to construct 481 square feet of piling supported structures over wetlands or surface waters. The proposed structures include a 265 square foot timber bridge over an un-vegetated flow channel, which connects a borrow area to Possum Creek, and a 216 square foot boardwalk over two small wetland areas located south of the flow channel. None of the pilings for the bridge or boardwalk will be in wetlands, and no construction will take place in Hogtown or Possum Creeks. The paved portion of the trail will not go through wetlands, and there will be no dredging or filling in wetlands. The receiving waters for the project are Hogtown and Possum Creeks. Both are Class III waters. Hogtown Creek originates in north central Gainesville and flows southwest to Kanapaha Lake/Haile Sink in southwest Gainesville. Possum Creek originates in northwest Gainesville and flows southeast to its confluence with Hogtown Creek south of the proposed bridge structure. Wetlands The total area of the proposed bridge and boardwalk over surface water or wetlands is approximately 481 square feet. The wetland delineation shown on the City's Exhibit 5A includes all of the areas in the project area considered to be wetlands under the state wetland delineation methodology. The United State Army Corps of Engineers' wetland line includes more wetlands than the District wetland line. The former wetland line was used to determine the area of boardwalk and bridge over wetlands. Even using this line, however, the total area of boardwalk over surface waters or wetlands is approximately 481 square feet and is therefore less than 1,000 square feet. Navigation The proposed system does not significantly impede navigation. Further, the structures will span a wetland area and an un-vegetated flow channel, both of which are non-navigable. In fact, the flow channel generally exhibits little or no flow except after periods of rainfall. Water quality The construction material that will be used for the bridge and boardwalk will not generate any pollutants. Morever, chemical cleaners will not be used on those structures. Silt fences will be used and vegetation will be planted in the vicinity of the bridge and boardwalk to prevent erosion and sedimentation problems. The amount of erosion from drip that comes off the boardwalk will be minimal. Therefore, the bridge and boardwalk will not cause a violation of state water quality standards. Off-site flooding The project will not impede conveyance of any stream, river, or other water course which would increase off-site flooding. The structures will completely span the wetland areas and flow channel, and no part of the structures, including the pilings, will lie within any water or wetland areas including the flow channel. There will be a span of 2.5 to 3 feet from the horizontal members of the bridge and boardwalk down to the ground surface which will allow water to pass through unobstructed. Further, there will not be any cross ties or horizontal obstructions on the lower portions of the boardwalk or bridge pilings. Further, due to the spacing of the pilings, the boardwalk and bridge will not trap sufficient sediment such as leaves to impede the conveyance of the flow channel. Therefore, conveyance through the flow channel will not be affected by the structures. Because the boardwalk and bridge are not over Hogtown or Possum Creeks, they will not cause any obstruction to the conveyance of the creeks. Aquatic and wetland dependent listed species The project will not adversely affect any aquatic or wetland dependent listed species. These species are defined by District rule as aquatic or wetland dependent species listed in Chapter 39-27, Florida Administrative Code, or 50 Code of Federal Regulations, Part 17. No such species are known to exist in the project area, and none are expected to exist in the location and habitat type of the project area. Therefore, contrary to Petitioners' assertions, there are no listed salamander, frog, turtle, or lizard species known to occur within the Hogtown Creek basin. Although it is possible that the box turtle may be found in the project area, it is not an aquatic or wetland dependent listed species. One baby American alligator (between two and three feet in length) was observed in the borrow pit area of the project on September 11, 1997. Except for this sighting, no other listed animal species have been observed in the project area. As to the alligator, the only area in which it could nest would be in the existing excavated borrow pit, and none of the proposed construction will take place in that area. More than likely, the alligator had walked into the area from Clear Lake, Kanapaha Prairie, or Lake Alice. The proposed structures will not affect the movement of the alligator nor its feeding habits. Drainage of wetlands Because the boardwalk and bridge are elevated structures over waters and wetlands, and the City has not proposed to construct ditches or other drainage systems, the proposed system will not cause drainage of the wetlands. Coral/macro-marine algae/grassbeds The proposed system is not located in, on, or over coral communities, macro/marine algae, or a submerged grassbed community. D. Were the Petitions Filed for an Improper Purpose? Prior to the filing of their petitions, Petitioners did not consult with experts, and they prepared no scientific investigations. Their experts were not retained until just prior to hearing. Petitioners are citizens who have genuine concerns with the project. They are mainly longtime residents of the area who fear that the Greenway will not be properly maintained by the City; it will increase flooding in the area; it will cause water quality violations; and it will attract thousands of persons who will have unimpeded access to the back yards of nearby residents. Although these concerns were either not substantiated at hearing or are irrelevant to District permitting criteria, they were nonetheless filed in good faith and not for an improper purpose.
Recommendation Based on the foregoing Findings of Fact and Conclusions of Law, it is RECOMMENDED that the St. Johns River Water Management District enter a final order approving the applications of the City of Gainesville and issuing the requested permits. DONE AND ENTERED this 19th day of December, 1997, in Tallahassee, Leon County, Florida. DONALD R. ALEXANDER Administrative Law Judge Division of Administrative Hearings The DeSoto Building 1230 Apalachee Parkway Tallahassee, Florida 32399-1550 (904) 488-9675 SUNCOM 278-9675 Fax Filing (904) 921-6847 Filed with the Clerk of the Division of Administrative Hearings this 19th day of December, 1997. COPIES FURNISHED: Henry Dean, Executive Director St. Johns River Water Management District Post Office Box 1429 Palatka, Florida 32178-1429 Samuel A. Mutch, Esquire 2790 Northwest 43rd Street Suite 100, Meridien Centre Gainesville, Florida 32606 Jennifer B. Springfield, Esquire Mary Jane Angelo, Esquire Post Office Box 1429 Palatka, Florida 32178-1429 Richard R. Whiddon, Jr., Esquire Post Office Box 1110 Gainesville, Florida 32602-1110
