The Issue Whether the North Fort Myers Homeowners Association, Inc.'s participation in the underlying proceeding entitles Florida Cities Water Company, Inc., to an award of attorney's fees and costs pursuant to Sections 120.57(1)(b)5 and 120.59(6), Florida Statutes.
Findings Of Fact By Consent Order 88-0384 between the Department of Environmental Regulation ("DER") and the Florida Cities Water Company, Inc., ("FCWC"), the FCWC agreed to complete certain modifications to its Waterway Estates wastewater treatment plant. The consent agreement established deadlines for said modifications. The FCWC was apparently unable to meet the deadlines for completion of modifications. By Consent Order 90-1747, executed in December, 1990, the DER extended the previously established deadlines and provided for issuance of a temporary operating permit by the DER to the FCWC. In December, 1990, the North Fort Myers Homeowners Association, Inc., ("Homeowners") filed a Petition for Administrative Hearing, challenging the consent agreement deadline extension and the provision related to issuance of a temporary operating permit by the DER to the FCWC. The case was referred to the Division of Administrative Hearings (DOAH Case No. 91-0235). In April, 1991, the DER and FCWC executed an Amended Consent Order #90- 1747, deleting the provisions related to issuance of a temporary operating permit. The DER thereafter moved to dismiss the Homeowners petition for hearing. In May, 1991, the Hearing Officer granted the motion to dismiss without prejudice and provided the Homeowners with an opportunity to file an amended petition. In June 1991, Homeowners filed an amended petition challenging the amended consent order. The DER and FCWC filed a joint motion to strike substantial portions of the amended petition. In July, 1991, the joint motion to strike was granted. In October, 1991, the DER filed a motion for summary recommended order of dismissal. On October 31, 1991, the Hearing Officer entered a Recommended Order of Dismissal. A Final Order was subsequently issued by the DER adopting the Recommended Order. During the pendency of DOAH Case No. 91-0235, Homeowners filed DOAH Case No. 91-6436, North Fort Myers Homeowners Association, Inc., v. State of Florida Department of Environmental Regulation, Florida Cities Water Company and Bradley Development Company. In this case, the Homeowners challenged the proposed award of a wastewater collection system permit to Bradley Development Company, the developer of the Barrett Park housing project. On October 1, 1991, FCWC moved to be dismissed as a party to Case No. 91-6436. The motion was granted on October 31, 1991. On December 12, 1991, based on Bradley Development Company's previously filed motion, the Hearing Officer entered a Recommended Order of Dismissal for failure to state a claim in Case No. 91-6436. A Final Order was issued by the DER adopting the Recommended Order and ordering the issuance of a collection system permit to Bradley. There is clear evidence that the Homeowners were opposed to the development of the Barrett Park housing project for a number of reasons, one of which was the fact that the project would tie into the apparently inadequate Waterway Estates wastewater treatment plant. The Homeowners desired to force the FCWC to complete the modifications required by relevant regulatory agencies prior to additional burdens being placed upon the treatment system. The evidence fails to establish that the participation of Homeowners in the foregoing proceedings was for an improper purpose.
Findings Of Fact The applicant, Tom Tona, owns the mortgage on the island consisting of Lots 1 and 2, Block 8, Elliots Point Subdivision, Fort Walton Beach, Florida. Mr. Tona has taken steps to perfect his ownership of the island and holds a property interest sufficient to afford him standing to apply for a permit. Elliots Point Subdivision is a residential subdivision development surrounding a lagoon which opens into Santa Rosa Sound in Fort Walton Beach, Florida. The island is located in the lagoon opening to Santa Rosa Sound. It has a large area of wetlands on the north shore. The wetlands function as a habitat for wildlife in the area. Water depths surrounding the island are shallow. The island currently acts as a barrier island for the property located on the shore of the lagoon. The barrier effect of the island helps to prevent the lagoon shore from erosion which would be caused by the wave action in the sound. However, the island, itself, is rapidly eroding due to the same wave action it protects the lagoon shore from. The evidence clearly demonstrated that unless this erosion is stopped the island will completely wash away along with the habitat, including wetlands, it now provides to wildlife and no longer protect the lagoon shore from the erosion it otherwise would experience without the presence of the island. The subdivision appears to be almost completely developed along the lagoon with single family dwellings. A canal consisting of two vertical seawalls runs in between the island and Elliots Point. The canal leads to a public boat ramp within the subdivision. The vertical sea wall of the canal along with the boats that pass through it is causing erosion to occur within the wetlands adjoining the seawall. It is this 55 foot area of the wetlands that Respondent proposes to construct part of the riprap revetment. Petitioner, Audrey Dickason, owns property on the far side of the lagoon from the island. Petitioner's property does not adjoin the island, but is close enough to the island to be within view of the island. On March 6, 1991, the applicant submitted an application to the Department of Environmental Regulation for a dredge and fill permit to construct a riprap revetment around the entire island. This was Mr. Tona's first application with the Department and at the time of filing Mr. Tona was very inexperienced in completing dredge and fill applications. The application was completed to the best of Mr. Tona's knowledge. Additionally, as happens with any form document, this application did not entirely fit the fact that this was an island project and the type of property interest Mr. Tona was asserting over the island. The application as originally filed did not list any adjacent property owners. Mr. Tona did not believe there were any adjacent property owners since an island was involved. Regardless of whether Mr. Tona should have listed any property owners of the subdivision, the failure to list any such property owners was not done to deceive or defraud the Department or the island's neighbors and in reality had no impact on the notification of parties who may have been interested in Mr. Tona's application. The owners of the property directly across from the island testified at the hearing and voiced their concerns to the Department during the processing of the application. Moreover, as indicated earlier, Petitioner's property does not adjoin the island. Since Petitioner's property does not adjoin the island, she was not entitled to be listed in Mr. Tona's application for the dredge and fill permit. The evidence simply did not establish that this debatable issue justifies the denial of Mr. Tona's application for a dredge and fill permit. The application filed by Mr. Tona also had the box indicating that he owned the property checked. The other box which could have been checked was that he would acquire an interest in the property. Neither box quite fit Mr. Tona's circumstances since he already had an interest in the property. The Department advised that it would be sufficient to check the ownership box and attach a copy of the mortgage assignment which gave Mr. Tona his interest. Mr. Tona followed the Department's advice. Again, the information as to ownership was not submitted to deceive or defraud the Department or the island's neighbors and in reality had no impact on the application process. In fact, the necessary information to determine Mr. Tona's interest was submitted to the Department. Again, there is nothing in the information submitted by Mr. Tona in the application which would justify denying that application as it has since been amended. As indicated above, after consulting with the Department, Mr. Tona amended his application so that the riprap revetment would only be constructed on a 55 foot strip along the northwest corner of the island immediately adjacent to the vertical seawall and on a 322 foot stretch of the island shore, beginning at the intersection of the vertical seawall and the southwest shore of the island and extending along the shore of the island to the edge of the wetland marsh on the north side of the island. The riprap would consist of clean limestone and would extend into state waters. The fill would not impede the flow of water or cause harmful erosion or shoaling. In fact, the purpose of the revetment is to stop the rapid erosion of the island which is currently taking place and preserve the wetland habitat which exists on the island. The evidence did not demonstrate that the type fill the applicant intends to use in the construction of the revetment would cause any significant pollution or water quality problems or adversely affect fish or wildlife. The evidence demonstrated that the placement of the fill would create more habitat for fish and wildlife. The revetment is intended to be a permanent structure. After evaluating the application for consistency with the relevant pollution control standards, the Department determined that the proposed revetment met departmental standards for water quality and the public interest and issued an Intent to Issue with a draft permit authorizing the construction of the riprap revetment described above subject to several standard permit conditions. The modifications of the application along with the permit conditions provide reasonable assurances that the project will not violate water quality standards as provided in Section 403.918, Florida Statutes. Additionally, the historical evidence the Department has gained through observing the impact of other riprap revetments in a similar environment on water quality provides strong support for the above conclusion and in itself is a reasonable assurance that water quality standards will not be adversely impacted by the construction of this riprap revetment. For similar reasons, the evidence demonstrated that the proposed revetment would not be contrary to the public interest. In essence, the evidence demonstrated that the revetment would not adversely impact the public health, safety, welfare or property of others, the current condition or relative value of the area surrounding the proposed project, the conservation of fish or wildlife and their habitats, or cause harmful erosion or shoaling, or involve historical or archaeological resources. In fact, the evidence demonstrated that the only effect on the environment the proposed revetment would cause would be a beneficial effect. Petitioner's fear that the grant of this permit will allow Mr. Tona to build a house on the island and thereby destroy her view is not the type of factor which may be considered in determining whether a dredge and fill permit should be granted or denied. See Miller v. Department of Environmental Regulation, 504 So.2d (Fla. 1st DCA 1988). Petitioner's concerns for the revetment's affect on the wildlife of the area were not established by any evidence. The evidence did demonstrate that Petitioner's concerns for the wildlife using the island were simply feinted by her and are belied by the fact that if the island is not preserved from erosion there will be no habitat for any wildlife to use once the island erodes away. Based on all the evidence, Mr. Tona's application for a dredge and fill permit to construct a riprap revetment should be granted.
Recommendation Based on the foregoing Findings of Fact and Conclusions of Law, it is RECOMMENDED that the Department of Environmental Regulation enter a Final Order issuing a dredge and fill permit to construct a riprap revetment as sought by Tom Tona in his permit application as amended and subject to the permit conditions contained in the Department's Intent to Issue. DONE and ENTERED this 23rd day of September, 1991, in Tallahassee, Florida. DIANE CLEAVINGER Hearing Officer Division of Administrative Hearings The DeSoto Building 1230 Apalachee Parkway Tallahassee, Florida 32399-1550 Filed with the Clerk of the Division of Administrative Hearings this 23rd day of September, 1991. APPENDIX TO RECOMMENDED ORDER CASE NO. 91-3872 The facts contained in paragraph 1 of Petitioner's Proposed Findings of Fact are adopted in substance, in so far as material. The facts contained in paragraphs 3 and 4 of Petitioner's Proposed Findings of Facts are subordinate. The facts contained in paragraphs 6, 7, 8 and 9 of Petitioner's Proposed Findings of Facts were not shown by the evidence. The facts contained in paragraph 5 of Petitioner's Proposed Findings of Fact are immaterial. The facts contained in paragraph 2 of Petitioner's Proposed Findings of Fact are adopted in substance, except for the finding relating to notice which was not shown by the evidence. The facts contained in paragraphs 1, 2, 3, 4, 5, 6, 7, 8, 9 and 10 of Respondent's Proposed Findings of Fact are adopted in substance, in so far as material. COPIES FURNISHED: Michael Mead P.O. Drawer 1329 Fort Walton Beach, Florida 32549 William Stone P.O. Drawer 2230 Fort Walton Beach, Florida 32549 Candi Culbreath Assistant General Counsel Department of Environmental Regulation 2600 Blairstone Road Tallahassee, Florida 32399-2400 Daniel H. Thompson General Counsel 2600 Blairstone Road Tallahassee, Florida 32399-2400 Carol Browner, Secretary Twin Towers Office Building 2600 Blairstone Road Tallahassee, Florida 32399-2400
The Issue Is the City of Mexico Beach (the City or Applicant) entitled to the issuance of a joint coastal permit and consent to use of sovereign submerged land for the Mexico Beach Canal (Main Canal) and a municipal flushing outlet adjacent to 8th Street (8th Street outlet)? Those permits would be issued by the Department of Environmental Protection (DEP) in response to DEP Application File No.: 0124938-001JC and DEP Application File No.: 0129039- 001JC, respectively.
Findings Of Fact Petitioners Edmond Blount, Sr.; Edmond Blount, Jr.; and Robert Davenport are residents of the City of Mexico Beach, Florida. As residents they have access to the Main Canal, the public beaches adjacent to the Main Canal, and beaches adjacent to the 8th Street outlet. Edmond Blount, Jr., and Robert Davenport oppose the issuance of any permits by DEP which would allow the City to conduct dredging and the placement of dredge materials associated with the Main Canal. Those Petitioners and Edmond Blount, Sr., oppose the grant of necessary permits by DEP upon the application by the City to conduct occasional maintenance excavation at the 8th Street outlet to alleviate potential damage through erosion to properties adjacent to the 8th Street outlet. The City of Mexico Beach is a municipality in Florida which serves as the local government for that community. The City owns the Main Canal and 8th Street outlet. DEP is an environmental regulator with authority to issue or deny joint coastal permits and to grant or deny consent to use sovereign submerged lands belonging to the State of Florida. The joint coastal permitting authority and right to grant consent to use is pursuant to Chapters 161, 253, and 373, Florida Statutes, and Chapters 18-21 and 62B-49, Florida Administrative Code. In particular, DEP has joint coastal permitting authority upon sovereignty lands in the State of Florida below the mean high waterline (MHWL) of any tidal water of the State. The reference to sovereign land is an association with lands below MHWL held in trust by the State of Florida. The term tidal waters refers to waters in which there is an astronomical effect on the elevation of that water. The Gulf of Mexico which fronts the City is a tidal water of the State of Florida. The MHWL is established along the coastal regions in Florida, to include the Gulf coast that fronts the City. The MHWL is set based upon charting information concerning the local mean high tide, the average height of the high waters, and where this average intersects the land. PERMIT APPLICATION FOR MAIN CANAL On June 30, 1997, the City applied to DEP for a ten-year permit/water quality certification and authorization to use sovereign submerged lands owned by the Board of Trustees of the Internal Improvement Trust Fund (the Trustees), which would allow the City to maintenance dredge the Main Canal entrance and place the dredge material on the beach east of the canal below the water's edge. This task would be accomplished by the use of hydraulic dredging device. In the course of these activities, approximately 660 cubic yards of material would be removed approximately four times a week. The application file number for the requested permit in the Main Canal project was: 0124938-001 JC. The City, through its application, provided a complete and appropriate application with adequate engineering data to support the proposed project. The Main Canal is located in the western part of the City and is partially located in sovereign submerged lands of the State of Florida where the canal intersects the Gulf of Mexico below the MHWL. On January 13, 1998, DEP gave notice of its intent to issue necessary permits for the activities to allow dredging and the placement of fill in association with the Main Canal. More specifically, the hydraulic dredge the City intends to use in the maintenance dredging of the Main Canal is a floating device which excavates the sand from the bottom of the entrance of the Main Canal and pipes the material onto the beach immediately east of the dredge site. The dredging activities may only be conducted in a manner designed to protect the beach-dune system, water quality and habitat for marine turtles. These restrictions in the conduct of the dredging are in accordance with the proposed joint coastal permit. The dredging activity is to remove and deposit clean beach sand that has been transported by coastal processes and deposited in the lee of the jetty within the Main Canal. There is no intent, nor permission under the proposed permit, that would allow disturbance of any sediments more landward of the extent of the canal. The dredging is necessitated because the entrance of the Main Canal slowly fills with sand being transported from west to east along the shoreline. The Main Canal is stabilized on both sides by jetties. The western-most jetty extends further out than the eastern-most jetty. The Main Canal has seawalls along its inside. A recreational area is located on the western side of the Main Canal. The Main Canal is highly utilized for purposes of commerce and recreation. The Main Canal constitutes an economic support for many residents of the City. The Main Canal in proximity to the Gulf and the Gulf itself are not considered outstanding Florida waters or aquatic preserves. The waters in the Main Canal and Gulf are Class III marine waters when considering the parameters for water quality under DEP statutes and rules. Competent evidence was presented concerning water quality sampling and results in the analysis of those samples for fecal coliform bacteria and total coliform bacteria in relation to the Main Canal at its entrance where dredging would take place under the terms of the permit. Some values for fecal coliform and total coliform exceeded the allowable limits for those parameters as envisioned by Section 62-302.530, Florida Administrative Code, as preexisting conditions. However, the dredge operations will not lead to further degradation of the existing Class III marine waters in the Main Canal and degradation of the Gulf. The relatively clean sand being excavated does not contain fines or organics, which, through the dredging and placement of the sand on the beach following the dredging, would contribute to degradation of water quality standards. The activity associated with the dredging and placement of those materials on the beach will not cause a significant adverse impact to the beach-dune system, nor will the transport of sand from west to east along the beach as it presently exists be interrupted by the dredging and placement of the sand. The dredged material is being placed immediately east of the dredge operation avoiding a disruption of the natural processes of transport. The proposed disposal area is located on the beach at least 100 feet east of the canal below the waters edge at approximately minus 0.5NGVD. Finally, the deposit of the sand on the beach contributes to beach stabilization as opposed to depriving the beach of sand. The proposed permit requires that the dredge pipeline be retracted upon a daily basis during marine turtle nesting season from May 1 until October 31 each year. By this limitation in the operation of the dredge pipeline, marine turtles are not hindered in their behavior nor is their habitat unduly disturbed. The placement of the dredged sand on the beach would not be in the dry upland where the turtles would typically nest. The DEP Bureau of Protected Species Management reviewed the permit application for any significant adverse impact on nesting sea turtles and recommends the approval subject to specific conditions such as have been described. The dredging of the sand from the Main Canal and placement of that material on the beach will not cause significant adverse impact to the property of others. The Main Canal project will not create any significant erosion or turbidity. Given the small volume and coarseness of the dredged sand, elevated turbidity levels are not expected. The dredging of material from the mouth of the Main Canal and placement on the adjacent beach does not block lateral access to the beach, because the hydraulic dredge pipeline is placed at the water's edge with a discharge of dredge material being made at the water's edge in the area of the intertidal zone where water comes up to the beach. The exact discharge point is seaward of the area described as the intertidal zone. Given that the project associated with the Main Canal is located in Class III marine waters, it must not be contrary to the public interest. The project is not contrary to the public interest. PERMIT APPLICATION FOR 8TH STREET OUTLET On June 13, 1997, the City applied to DEP for a ten- year permit/water quality certification and authorization to use sovereign submerged lands owned by the Board of Trustees. This would allow the City to conduct occasional excavation of the 8th Street municipal flushing outlet which connects to the Gulf, having in mind the alleviation of potential damage to adjacent beachfront properties. That potential damage would be expected to occur in the instance where there was an uncontrolled breach of the berm surrounding the 8th Street outlet due to high incidence of rainfall, thus eroding adjacent beachfront properties. With the advent of scheduled maintenance, excavation of the outlet that erosion is expected to be deterred. The application file number for the requested permit in the 8th Street outlet project was File No.: 0129039-001 JC. The City, in its application for necessary permits to conduct excavation at the 8th Street outlet, submitted a complete and appropriate application setting forth adequate engineering details. More specifically, the permit application contemplates the removal of approximately 20 to 40 yards of beach sand per excavation, with the material excavated being placed on the beach near the water's edge. The excavation would be approximately 4 to 5 feet wide, 50 feet long, and 2 to 3 feet deep. Ordinarily, the frequency of excavation would be one to two times per month. The excavation practices would be by the use of a backhoe other than in the sea turtle nesting season. While sea turtles are nesting, the plans contemplate excavation by hand by use of a shovel or similar tool. In addition, during the turtle nesting season the application contemplates that the excavation would be done during daylight hours, only twice a month, to reduce potential flooding of marine turtle nests due to a meandering outflow from the outlet. Other than in the marine turtle nesting season the excavation would be done on an "as needed" basis. On March 16, 1998, the DEP gave notice of its intent to issue a permit for the dredging at the 8th Street outlet. The conditions associated with the intended permit for dredging of the 8th Street outlet deter any significant adverse impacts to the beach-dune system. In the area of the 8th Street outlet, a large box culvert runs underneath U.S. 98, the main highway in the city. That highway runs parallel to the beach. Once the water flows through the culvert, it accumulates in the outlet south of the road. In the instance where rainfall is diminished, the flushing outlet does not flow to the Gulf and the beach berm, which accretes seaward of the outlet, traps the water that is being released via the culvert. By contrast, in instances where heavy rainfall occurs, the water in the outlet collects to a point that it begins to flow away from the culvert in the direction of the Gulf. If the beach berm has built up over time, the path of that flow in high incidence of rainfall can encroach on buildings that are adjacent to the culvert on the south side of U.S. 98. When the rainfall is sufficient, and the water begins to flow, it reaches a sufficient velocity to move sand as a bed load. Under those circumstances, when the water strikes a ridged object, like a house foundation, the local water velocity will act to carry away the sand more readily from that location where the house foundation is found, by scouring out the sand near the foundation, undermining the building and risking the collapse of the building onto the beach. In the course of this process the water breaches the beach berm and flows towards the Gulf. In the instance where the berm on the beach has been breached, the water that has been released begins to scour the beach and establish a pattern that can run down the beach roughly parallel to the Gulf for a distance before flowing into the Gulf. By contrast, the controlled release of water from the outlet would cause less of an impact, in that it would create an immediate access through the beach berm to the Gulf without creating the potential for harm to upland property or causing erosion or scouring of dunes and vegetation in beach areas, some of which might contain turtle nests. Unlike the circumstances with high incidence of rainfall where adjacent property is eroded and damaged, the use of controlled maintenance excavation to relieve the outlet would not cause significant and adverse impact to adjacent property owners. The controlled release of the water in the outlet, unlike the natural release of that water in high incidence of rainfall, is more in the interest of the public when considering adverse impacts to property. The introduction of the water in the outlet, and its constituents, onto the beach and its consequences, is no more a problem whether based upon the natural event of high incidence of rainfall or the routine release contemplated by the project. Therefore, the alternative method of releasing the water by use of scheduled excavation is not contrary to the public interest. If anything, the use of periodic excavation to relieve the outlet would limit the breadth of discharge and the amount of discharge. The 8th Street outlet and the Gulf area adjacent to that outlet are not within outstanding Florida waters or aquatic preserves. The project site for the 8th Street outlet and the Gulf are within Class III marine waters. The existing Class III marine water quality parameters for fecal coliform and total coliform when considered in accordance with Rule 62-302.530, Florida Administrative Code, have been exceeded in the 8th Street outlet. This is borne out by test results from samples gathered at the 8th Street outlet presented at hearing. However, as with the circumstance with the Main Canal, the effect of periodic excavation to relieve the outlet will not further degrade state waters found in the outlet. The results of water quality tests performed following sampling that relate to the amount of fecal coliform and total coliform in the Gulf that could be expected at the entrance of the Main Canal and as the discharge of water within the 8th Street outlet enters the Gulf show low values for those parameters. Therefore, it is not anticipated that the release of the water from the 8th Street outlet to the Gulf under controlled conditions contemplated by the permit application would cause a violation of the parameters for fecal coliform and total coliform in the Gulf, the receiving body of water, especially when compared to the existing release of water from the 8th Street outlet to the Gulf in high incidence of rainfall. This finding is also influenced by the fact that the most excessive values for total coliform and fecal coliform in the 8th Street outlet system were found 600 to 800 feet up the water course described as the 8th Street outlet. Similar to the Main Canal, the project contemplated at the 8th Street outlet would not require mitigation before being permitted by DEP. The 8th Street outlet project would not create significant adverse impacts on coastal sediment transport. The DEP Bureau of Protective Species Management reviewed the 8th Street outlet application and recommended approval with specific conditions. Those conditions offer adequate protection to marine turtles and their habitat. The conditions include project excavation that does not create parallel trenches in the sand that inhibit movement on the beach by sea turtles. The 8th Street outlet project will not create significant erosion concerns or turbidity concerns. The 8th Street outlet project does not block lateral beach access to the public, in that the excavation to relieve the outlet on a periodic basis is temporary, that is to say only in effect when the water is being released from the outlet to the Gulf. CONSENT TO USE SOVEREIGN SUBMERGED LANDS The 8th Street outlet project, as well as the Main Canal project, involves sovereignty submerged lands below the MHWL constituted of the beach and ocean bottom. The facts show that the City is entitled to consent of use to work on sovereign submerged lands in the Main Canal and 8th Street outlet projects.
Recommendation Based upon the facts found and the conclusions of law reached, it is RECOMMENDED: That DEP issue a final order granting the City the joint coastal permits and consent to use sovereign submerged lands in accordance with application File Nos.: 0124938-001JC and 0129039-001JC respectively, subject to specific conditions contained therein. DONE AND ENTERED this 10th day of November, 1998, in Tallahassee, Leon County, Florida. CHARLES C. ADAMS Administrative Law Judge Division of Administrative Hearings The DeSoto Building 1230 Apalachee Parkway Tallahassee, Florida 32399-3060 (850) 488-9675 SUNCOM 278-9675 Fax Filing (850) 921-6847 Filed with the Clerk of the Division of Administrative Hearings this 10th day of November, 1998. COPIES FURNISHED: Edmond Blount, Sr. Post Office Box 13855 Mexico Beach, Florida 32410 Edmond Blount, Jr. Post Office Box 13854 Mexico Beach, Florida 32410 Robert Davenport Post Office Box 13926 Mexico Beach, Florida 32410 Gerard Murnan Post Office Box 13378 Mexico Beach, Florida 32410 Paul G. Komarek, Esquire Daniel and Komarek, Chartered Post Office Box 2547 Panama City, Florida 32402 Ricardo Muratti, Esquire Department of Environmental Protection Mail Station 35 3900 Commonwealth Boulevard Tallahassee, Florida 32399-3000 John McInnis, City Manager City of Mexico Beach Post Office Box 13425 Mexico Beach, Florida 32410 Kathy Carter, Agency Clerk Department of Environmental Protection Mail Station 35 3900 Commonwealth Boulevard Tallahassee, Florida 32399-3000 F. Perry Odom, General Counsel Department of Environmental Protection Mail Station 35 3900 Commonwealth Boulevard Tallahassee, Florida 32399-3000
The Issue Whether Petitioner North Fort Myers Homeowners Association, Inc. (Homeowners) participated in DOAH Case No. 91-6436 for an improper purpose.
Findings Of Fact On September 11, 1991, Homeowners filed its Petition for Administrative Hearing and Request to Consolidate with Administrative Hearing set for November 7, 1991. The Petition alleged that Homeowners' interests would be adversely affected by Bradley's request for a permit for construction of a wastewater collection system that it planned to connect to Florida Cities Water Company's Sewage Treatment Plant. It was further alleged that Florida Cities current violations of federal water quality standards would increase as a result of such a connection. Bradley responded to the Petition by filing a Motion to Dismiss for failure to State a Claim/Or in the Alternative Motion for Summary Judgment. On October 31, 1991, Hearing Officer Quattlebaum granted Bradley's Motion to Dismiss for Failure to State a Claim. The Hearing Officer found that the Petition did not allege that the application for a wastewater collection system permit failed to comply with the agency's relevant rules and criteria. The Hearing Officer also ruled that the Petition did not identify when such criteria would be unmet by the project. Homeowners was given leave of ten days to file an Amended Petition. Homeowners timely filed its Amended Petition for Administrative Hearing on November 13, 1991. This Amended Petition continued to focus upon whether Bradley's wastewater collection system should connect to Florida Cities Water Company's Sewage Treatment Plant and the federal water quality issue as it relates to discharge after treatment. After Bradley filed its Motion to Dismiss the Amended Petition and Homeowners replied, Hearing Officer Quattlebaum entered a Recommended Order of Dismissal on December 12, 1991. The basis for the recommendation was that Homeowners had "failed to allege that the application for permit failed to comply with the relevant criteria as set forth in statute and rule which govern issuance of the permit." The Temporary Operating Permit under which Florida Cities was operating expressly allowed Bradley's wastewater collection system to connect to the sewage treatment plant upon satisfaction of the Department's permitting requirements for such a collection system. Homeowners lost its opportunity to address whether such a connection was proper when it failed to timely challenge this Temporary Operating Permit. The only agency action subject to challenge in this case was whether Bradley's application to construct the wastewater collection system complied with the Department's permitting requirements for the system. Florida Cities anticipated actions were irrelevant to this particular proceeding because final agency action had already been taken on the question of whether the connection could take place. Throughout this proceeding, Homeowners failed to comprehend that it had waived its opportunity to pursue a challenge to the connection of Bradley's wastewater collection system to the sewage treatment plant when it did not timely challenge Florida Cities' Temporary Operating Permit. The Order granting Bradley's Motion to Dismiss dated October 31, 1991, did not affirmatively set forth that the connection issue could not be pursued in DOAH Case No. 91-6436. Homeowners' lack of comprehension on this issue remains evident in the Amended Petition, the Motion for Reconsideration filed after the Recommended Order of Dismissal, the Response to the Motion for Attorney's Fees and the testimony presented at hearing. Lack of comprehension is a neutral condition which neither proves nor disproves that the Petition and Amended Petition were filed for improper purposes, as defined by Subsection 120.59(6)(e), Florida Statutes. No direct evidence of Homeowners' participation in the proceeding for an improper purpose was established at hearing. The attorney for Homeowners at the time the Petition and Amended Petition were filed denied that Homeowners was motivated by an improper purpose. It was seeking to protect water quality in its locale and to assure the local sewer treatment system is adequate. There was no evidence presented as to whether Homeowners has participated in other such proceedings involving Bradley and the same project for an improper purpose.
Recommendation Based upon the foregoing, it is recommended that the Department enter a Supplemental Final Order denying Bradley's request for attorney's fees and costs as Homeowners did not participate in this proceeding for an improper purpose as defined by Subsection 120.59(6)(e), Florida Statutes. RECOMMENDED this 26th day of June, 1992, in Tallahassee, Leon County, Florida. VERONICA E. DONNELLY Hearing Officer Division of Administrative Hearings The DeSoto Building 1230 Apalachee Parkway Tallahassee, Florida 32399-1550 (904)488-9675 Filed with the Clerk of the Division of Administrative Hearings this 26th day of June, 1992. APPENDIX TO RECOMMENDED ORDER, CASE NO. 91-6436 Homeowners' proposed findings of fact are addressed as follows: Accepted. See HO #1. Accepted. See HO #6. Accepted. Accepted. Accepted. See Preliminary Statement. Accepted. See Preliminary Statement. Accepted. Rejected. Contrary to fact. See separate order on that issue. Rejected. Pleading amended accordingly. Accepted. See HO #13. Rejected. Contrary to fact. See Preliminary Statement. The Department's proposed findings of fact are addressed as follows: Accepted. Accepted. See HO #1. 3. Accepted. See HO #2. 4. Accepted. See HO #3. 5. Accepted. 6. Accepted. 7. Accepted. See HO #4. 8. Accepted. See HO #4. 9. Accepted. See HO #5. 10. Accepted. See HO #6. 11. Accepted. 12. Accepted. See HO #6. Accepted. See Preliminary Statement. Accepted. See Preliminary Statement. Accepted. See Preliminary Statement. Accepted. See Preliminary Statement. Accepted. Rejected. Contrary to fact. See HO #7 - HO #13. Bradley's proposed findings of fact are addressed as follows: Accepted. See HO #1. Accepted. See HO #2. Accepted. See HO #3. Accepted. See HO #4. Accepted. See HO #5. Accepted. See HO #6. Accepted. See HO #6. Accepted. See Preliminary Statement. Accepted. See Preliminary Statement. Accepted. See HO #7 and HO #8. Accept that Homeowners failed to present any justifiable issue of law or fact that could be heard in relation to this permit. See HO #7 - HO #9. COPIES FURNISHED: HAROLD M STEVENS ESQ PO DRAWER 1440 FT MYERS FL 33902 FRANCINE FFOLKES ESQ ASST GENERAL COUNSEL DEPT OF ENVIRONMENTAL REGULATION 2600 BLAIRSTONE RD TALLAHASSEE FL 32399 2400 GERI L WAKSLER ESQ PEPER MARTIN JENSEN MAICHEL & HETLAGE 2000 MAIN ST - STE 600 FT MYERS FL 33901 DANIEL H THOMPSON ESQ GENERAL COUNSEL DEPT OF ENVIRONMENTAL REGULATION 2600 BLAIRSTONE RD TALLAHASSEE FL 32399 2400 CAROL BROWNER, SECRETARY DEPARTMENT OF ENVIRONMENTAL REGULATION 2600 BLAIRSTONE RD TALLAHASSEE FL 32399 2400
The Issue Whether or not Petitioner is entitled to a dredge and fill permit to construct a dock and seawall by provision of reasonable assurances that the project is in the public interest.
Findings Of Fact On May 8, 1989, the Petitioner, Kathryn Haughney, applied to DER for a permit to construct a dock and seawall on the shore of the Halifax River in Volusia County. The portion of the Haughney property where the dock and seawall would be constructed is separated from the Haughney home by John Anderson Drive, which parallels the river's edge and is separated from the river by a ribbon of undeveloped property at that location and to the south. A house is located at water's edge on the lot to the north of the proposed construction site. The Haughney home itself is set well back from John Anderson drive on the side of the street away from the river. The Halifax River is classified as a Class III water body under DER rules. The particular part of the Halifax River where the Haughney property is located and where the dock and seawall are proposed is also within the Tomoka Marsh Aquatic Preserve, which is an Outstanding Florida Water under DER rules. The dock as proposed by Petitioner will be 320 square feet. DER denied the permit application on July 19, 1990, but in so doing did not deny the application on the basis of the proposed dock, which, because of its dimensions, is exempt from DER permitting requirements. The seawall as proposed is to be 137 feet long. Petitioner applied to extend it 16 feet out into waters of the state at the northern end, gradually increasing to 34 feet into waters of the state at the south end. Additionally, 5 feet of riprap would also extend out into waters of the state along the seawall's entire length. The waters of the state that would be filled by the proposed seawall contain lush wetland vegetation that provides habitat for a number of macroinvertebrate species which are part of the food chain feeding fish and wading birds such as egrets and herons. Fiddler crabs and colonies of mussels have been observed on the site. The area to be filled provides a valuable habitat for fish and wildlife. There was no mitigation offered by Petitioner to make up for the loss of habitat to be occasioned by the proposed construction. Although Petitioner asserted DER had named no "endangered species" and that the Environmental Protection Administration had not designated this area as "endangered," those federal concerns were not at issue. If such federally designated species or location designation existed in the locale, it might militate against granting this application for permit, but in the negative, it is irrelevant. A vertical seawall exists immediately north of Petitioner's shoreline. The shoreline to the south remains undeveloped. (See Finding of Fact 2). Construction of seawalls, especially those that extend out from the existing shoreline, typically causes erosion on adjacent shorelines, and additional seawalls exaggerate wave energy and can have a cumulative erosive effect. The foregoing fact is found in reliance upon the testimony of Don Medellin, an Environmental Specialist II for DER, and Barbara Bess, an Environmental Manager for DER, both accepted as experts in environmental aspects of dredge and fill permits. The assertion that actual erosion on the property to the south has already occurred was contained in a letter from Petitioner's southern neighbor (DER Exhibit 6). Petitioner's representatives objected to consideration of this exhibit as "hearsay." They are correct and current erosion to the south is not found as a fact. Nonetheless, actual erosion in a pocket on the north end of Petitioner's shoreline has been shown by the direct testimony of Emmett and Martha Haughney, who assert that their property is eroding due to the existing seawall and that Petitioner wants a permit for a seawall to alleviate this erosion. Their evidence is confirmed by the personal observations and testimony of Mr. Medellin and Ms. Bess. Further, upon their testimony, it is accepted that this minimal pocket of erosion is most likely due to the existing seawall to the north and that if the Petitioner builds a seawall to the specifications now set out in the permit application, there is potential for similar and perhaps cumulative erosion to the shoreline to the south of Petitioner's lot. Neither the city nor county involved has land use restrictions which would prohibit Petitioner's proposed seawall except that Volusia County advocates riprap requirements if this permit application were granted. In its Notice of Permit Denial, DER advised Petitioner as follows: The Department has determined that the follow- ing changes to the project may make the project permittable: The vertical seawall should be eliminated and replaced with coquina rock riprap revet- ment. The riprap should be located further landward and conform to the slope of the existing embankment. Backfilling on the north property line is acceptable provided the fill area does not extend more than 10 feet westward in the most eroded area. Accordingly, the riprap could extend to the adjacent seawall and gradually extend in a more landward direc- tion to prevent excessive elimination of the littoral zone vegetation. Whatever alternative the applicant elects to choose, the removal or elimination of littoral zone vegetation must be offset in the form of mitigation if the impacts can not be reduced any further. Finally, the agent should eliminate the use of generic drawings which must be continually revised. All drawings should reflect the existing and proposed conditions and the impacts associated with the project. Petitioner's contractor, Andy Harris, testified to other alternatives that could be used by Petitioner in constructing her seawall, but the evidence of Mr. Medellin and Ms. Bess is persuasive that the alternative measures proposed by Mr. Harris would not provide the reasonable assurances the law requires DER to obtain from Petitioner.
Recommendation Upon the foregoing Findings of Fact and Conclusions of Law, it is RECOMMENDED that the Department of Environmental Regulation enter a Final Order affirming its July 19, 1990 Notice of Permit Denial. RECOMMENDED this 25th day of April, 1991, at Tallahassee, Florida. ELLA JANE P. DAVIS, Hearing Officer Division of Administrative Hearings The DeSoto Building 1230 Apalachee Parkway Tallahassee, Florida 32399-1550 (904) 488-9675 Filed with the Clerk of the Division of Administrative Hearings this 25th day of April, 1991. APPENDIX TO RECOMMENDED ORDER, CASE NO. 90-7215 The following constitute specific rulings pursuant to Section 120.59(2) F.S. upon the parties' respective proposed findings of fact (PFOF): Petitioner's letter to Hearing Officer (filed March 22, 1991) The first paragraph complains that a VCR was unavailable in the hearing room so that Petitioner's videotape could not be shown. Petitioner should have made arrangements for showing the tape and did not. Likewise, Petitioner never offered the tape in evidence (for viewing by the Hearing Officer afterwards in preparation of this Recommended Order). Therefore, it very properly was not considered. The next 3 paragraphs refer to the Casden letter (DER Exhibit 6), which is covered in FOF 8-9. The remaining paragraphs are rhetoric and legal argument upon which no ruling need to made under Section 120.59(2) F.S.; however, they are alluded to in the Conclusions of Law. Petitioner's letter to DER Counsel (filed March 25, 1991 by DER, suggesting it was Petitioner's proposed findings of fact) 1-3 For the reasons set out above, the Petitioner's videotape was not considered. The subject of erosion to the degree proved at the hearing is covered in the Recommended Order. 4-5, PS 1-3 Mere rhetoric and legal argument upon which no ruling need be made under Section 120.59(2) F.S.; covered in the Conclusions of Law to the degree appropriate. Respondent's PFOF: 1-11 Accepted as modified to reflect the greater weight of the credible and probative record evidence as a whole. That which is rejected is rejected as not proven or not persuasive. Unnecessary or irrelevant material has likewise been excluded. COPIES FURNISHED: Douglas MacLaughlin Assistant General Counsel Department of Environmental Regulation 2600 Blair Stone Road Tallahassee, Florida 32399-2400 Kathryn Haughney 2301 John Anderson Drive Ormond Beach, FL 32074 Emmett and Martha Haughney 2301 John Anderson Drive Ormond Beach, FL 32074 Carol Browner, Secretary Department of Environmental Regulation 2600 Blair Stone Road Tallahassee, FL 32399-2400 Daniel H. Thompson, General Counsel Department of Environmental Regulation 2600 Blair Stone Road Tallahassee, FL 32399-2400
Findings Of Fact The Proposed Permit This case involves a 65-acre site in north Lee County owned by the City of Ft. Myers. At all material times, the land has been zoned under industrial- equivalent designations. By leases that are not part of this record, Ft. Myers has leased 21.4 acres of the 65 acres to various governmental agencies, including Lee County, Lee County Sheriff's Office, and possibly the Florida Department of Juvenile Justice (formerly known as Department of Health and Rehabilitative Services). The following facilities are presently located on the 21.4 acres: Juvenile Detention Center, Lee County Stockade, Price Halfway House, Sheriff's Office Aviation Department, and Emergency Operations Center. By lease dated September 20, 1993, Ft. Myers leased the remaining 43.6 undeveloped acres to Lee County for a term of 50 years. This lease allows Lee County to use the 43.6 acres for $1 per year, but only for the operation of a Juvenile Justice Facility. Under Paragraph 20 of the lease, Ft. Myers may terminate the lease if Lee County ceases to operate the facility. Likewise, Lee County may terminate the lease if the Department of Juvenile Justice ceases to fund the County's operation of the facility. Under the lease, preference is given to juvenile residents of Ft. Myers. Paragraph 22 of the lease allocates liability to Lee County for claims or damages arising from released fuels, including from pipelines. The lease is not assignable without Ft. Myer's consent. By agreement dated December 17, 1993, Ft. Myers consented to the sublease of the entire 43.6- acre parcel to the Department of Juvenile Justice for the purpose of the construction of a juvenile residential commitment facility. Lee County receives no rent from the Department of Juvenile Justice. In Paragraph 10 of the agreement, the Department of Juvenile Justice agrees to maintain, at its expense, "all improvements of every kind . . .." Lee County must make any repairs to improvements if the Department of Juvenile Justice fails to do so. By subsequent agreement, Respondent Department of Management Services (DMS) became the agent for the Department of Juvenile Justice for the design, permitting, and construction of the juvenile justice facility. By Application for a surface water management permit executed June 16, 1994, DMS applied for a surface water management permit for the construction and operation of a 10.9- acre project known as the Lee County Juvenile Commitment Facility. This 10.9-acre project is part of the 43.6 acres leased to Lee County and subleased to the Department of Juvenile Justice. The application states that the existing 21.4 acres of developed sites, which are leased under separate agreements to different governmental entities, "will be permitted as is." The Staff Review Summary of Respondent South Florida Water Management District (SFWMD) describes the purpose of the application as follows: This application is a request for Authorization for Construction and Operation of a surface water management system to serve a 10.9 acre Institutional project discharging to Six Mile [Cypress] Slough via onsite wetlands and road- side swales. The application also requests Authorization for Operation of a surface water management system serving a 21.4 acre existing facility and 32.7 acres to remain unchanged for a total permitted area of 65.0 acres. Staff recommends approval of both authorizations with conditions. The Staff Review Summary accurately states that the owner of the land is Ft. Myers. Of questionable accuracy is the statement that Ft. Myers leases to Lee County the 21.4 acres devoted to the five existing facilities. Although Lee County probably is a lessee of some of these parcels, the Lee County Sheriff's Office is the lessee (or perhaps sublessee) of at least two parcels. One of the other parcels may involve a state agency, again under either a lease or a sublease. The Staff Review Summary inaccurately states that the project developer is Lee County. The project developer is DMS or its principal, the Department of Juvenile Justice. The Staff Review Summary reviews the existing development on the 21.4 acres. The improvements consist of the 4.8-acre Juvenile Detention Center, 2.9- acre Price Halfway House, 4.7-acre Lee County Stockade, 5.1-acre Sheriff's Office Aviation Department, and 3.9-acre Emergency Operations Center. The Staff Review Summary states that the footer of the Juvenile Detention Center was inspected in February 1980. The site drains into a 1.2- acre retention pond, which was a natural pond dug out to accept the drainage from the Juvenile Detention Center. A small amount of surface flow drains from the Juvenile Detention Center to a perimeter swale that drains west into a ditch running along Ortiz Avenue. The Staff Review Summary states that the building permit for the Price Halfway House was issued in October 1982. The site drains into the 1.2-acre retention pond, which was apparently enlarged a second time to accept the additional flow. A small amount of the flow from the Price Halfway House also drains to the perimeter swale and west into the Ortiz Avenue ditch. The Staff Review Summary states that the building permit for the Lee County Stockade was issued on May 25, 1976. SFWMD issued an exemption and a determination that no permit was required for two additions to the stockade in 1988 and 1989. For the additional impervious surface added by these additions, one inch of water quality treatment was provided. After the abandonment of a pumping system, drainage of the stockade site consists of water building up in existing onsite ditches and sheet flowing into the Ortiz Avenue ditch. The Staff Review Summary adds that a small retention area constructed at the southeast corner of the site treats stormwater from the stockade and the Sheriff's Office Aviation Department. The summary adds that a small amount of stormwater drains north into an exterior swale that drains into the Ortiz Avenue ditch. The Staff Review Summary states that a building permit was issued for the Sheriff's Office Aviation Department in August 1977. Stormwater from the site sheetflows to exterior swales north and south of the building. When the swales fill up, the water flows into the Ortiz Avenue ditch. The Staff Review Summary states that a building permit was issued for the Emergency Operations Center on October 11, 1977. Drainage from the center flows directly into the Ortiz Avenue ditch. Under "Water Quality," the Staff Review Summary reports that SFWMD "did not require compliance with discharge rate or criteria" based on Section 1.6, Basis of Review for Surface Water Management Permit Applications within the [SFWMD] March 1994 (Basis of Review), which contains guidelines issued by SFWMD for the construction and operation of surface water management systems. The summary adds that there have been no "water quality or quantity complaints associated with this site over the past 18 years since its initial construction." Noting that a surface water management permit is requested for the entire 65-acre parcel, the Staff Review Summary states that the above-described drainage systems for the five existing facilities are "operational and will remain as they now exist." Turning to the proposed development, the Staff Review Summary states that the remaining 43.6 undeveloped acres "will also be leased to Lee County by the City for the proposed commitment facilities." The facilities are accurately described as a 5.2-acre halfway house and a 5.7-acre bootcamp, both of which will be drained by internal drainage swales and culverts flowing into detention areas, which will discharge through a control structure into onsite wetlands leading to the Ortiz Avenue swale. Addressing designed discharge rates, the Staff Review Summary acknowledges that the bootcamp's discharge rate will exceed the allowable rate for a 25-year, three-day storm event. The allowable rate is .33 cfs, and the design rate is .37 cfs. The Staff Review Summary explains that this discrepancy results from the use of the minimum size orifice (three inches) in the control structure. Addressing water quality, the Staff Review Summary reports that commercially zoned sites are required to provide one-half inch dry pretreatment for water quality unless reasonable assurance can be provided that hazardous material will not enter the surface water management system. Determining that no hazardous material will be stored or generated on the site, SFWMD did not require the one-half inch dry pretreatment of runoff. Noting that no surface water management permits have ever been issued for any part of the 65-acre parcel, the Staff Review Summary recommends that, subject to the customary Limiting Conditions, SFWMD issue: Authorization for Construction and Operation of a 10.9 acre Institutional Project discharging to Six Mile Cypress Slough via onsite wetlands and roadside swales, Operation of a 21.4 acre existing facility and 32.7 acres to remain unchanged for a total permitted area of 65.0 acres. Limiting Condition 4 states that the permittee shall request transfer of the permit to the "responsible operational entity accepted by [SFWMD], if different from the permittee." Limiting Condition 8 adds: A permit transfer to the operation phase shall not occur until a responsible entity meeting the requirements in section 9.0, "Basis of Review . . .," has been established to operate and maintain the system. The entity must be provided with sufficient ownership or legal interest so that it has control over all water management facilities authorized herein. Special Condition 11 states: "Operation of the surface water management system shall be the responsibility of Lee County." The Permittee and the Entity Responsible for Maintenance The proposed permit consists of two authorizations. The first authorization is for the construction and operation of the surface water management system on the 10.9-acre parcel on which will be constructed the bootcamp and halfway house. The second authorization is for the operation of the existing surface water management system on the already-developed 21.4 acres and the unimproved surface water management system on the remaining 32.7 acres. There are two problems with the designation of Lee County as the entity responsible for maintaining the permitted surface water management systems. Basis of Review 9.1.B states: To satisfy [P]ermit [L]imiting [C]ondition [8], the Permittee must supply appropriate written proof, such as either by letter or resolution from the governmental entity that the governmental entity will accept the oper- ation and maintenance of all the surface water management system components . . .. The authorization for operation of the systems on the 21.4-acre and 32.7-acre parcels does not await any construction. Once the permit is issued, the authorization is effective. Therefore, all prerequisites to the designation must have been satisfied before the operation permit issues. For the 21.4-acre parcel, DMS has not provided reasonable assurance that Lee County is the lessee or sublessee of all of the parcels underlying the five existing facilities. In fact, it appears that Lee County is not the lessee or sublessee of all of these parcels. Even if Lee County were the lessee or sublessee of these five parcels, DMS has not provided reasonable assurance that Lee County has assumed responsibility for the maintenance of the surface water management system for the five parcels. Contrary to Basis of Review 9.1.B, there is no written agreement by Lee County to assume operational responsibility, nor is there even an actual agreement to this effect. SFWMD's rules sensibly require that written consent be obtained before the operation permit is issued. Likewise, DMS has failed to show that Lee County has agreed to assume responsibility for the operation and maintenance of the surface water management system for the 32.7-acre parcel. Again, SFWMD must obtain written consent before issuing the permit because no construction will precede operation for the surface water management system on this parcel. Unlike the situation as to the 21.4-acre parcel, the 32.7-acre parcel is leased to Lee County as part of the 43.6- acre parcel. But in the December 17, 1993, agreement, the Department of Juvenile Justice, not Lee County, assumes responsibility for maintaining all improvements, which arguably includes drainage improvements. As between Ft. Myers and Lee County, Lee County assumes secondary liability for the maintenance of all improvements. But the failure of the Department of Juvenile Justice to do so would likely represent a default under the agreement. In such a case, the lease and separate agreement probably would either be in litigation or Lee County would have terminated its obligations under the contracts. In either case, it is unlikely that Lee County would perform its secondary responsibility to maintain the drainage improvements, especially where it is receiving no rent from the Department of Juvenile Justice and priority is given to Ft. Myers juveniles in admission decisions. Construction will precede operation as to the 10.9- acre parcel so the parties have an opportunity, even after the construction and operation permit is issued, to secure the necessary written consent before the operation permit goes into effect. But similar deficiencies exist with respect to the 10.9- acre parcel because the same agreement imposes upon the Department of Juvenile Justice, not Lee County, the obligation to maintain improvements. An additional complication arises as to the 10.9-acre parcel. The Department of Juvenile Justice intends to contract with one or more private entities to operate the bootcamp and halfway house, so there is at least one more party that Lee County could claim was responsible for maintenance of the surface water management system. The question of who is responsible for maintaining the surface water management systems is important. Drainage quantities and directions can change if swales clog up with vegetation or other matter. In this case, one roadside swale in the area of the 21.4-acre parcel is blocked with vegetation. DMS and SFWMD have thus failed to provide reasonable assurance that the designated entity has assumed responsibility for the maintenance and operation of the existing systems or will assume responsibility for the maintenance and operation of the proposed system following its construction. Permit for Existing Development Section 1.6, Basis of Review, states: [SFWMD] issues construction and operation permits for proposed surface water management activities and operation permits for existing systems. The criteria herein are specifically designed to apply to proposed activities (construction and operation permits). Therefore, some of the criteria may not be applicable to the permitting of existing systems (operation permits). For example, in some cases, existing systems may not meet flood protection criteria. Criteria deviation for existing systems will be identified in staff reports. SFWMD has produced no evidence explicating the extent to which existing systems, such as the systems on the 21.4- and 32.7-acre parcels, are entitled to operating permits without meeting some of the criteria applicable to proposed systems, such as the system on the 10.9-acre parcel. There is nothing whatsoever in the record to explain why certain existing systems might not have to meet certain criteria, such as flood protection criteria. Except for the quantity deviation discussed below, there is nothing in the record disclosing the extent to which SFWMD has waived, or even considered the applicability of, certain or all criteria prior to the issuance of operation permits for the existing systems. In practice, SFWMD does not adhere even to the vague standards implied in 1.6. According to the SFWMD witness, the practice of SFWMD, as reflected in this case as to the systems on the 21.4- and 32.7-acre parcels, is to permit existing systems "as is, where is," as long as they have had no reported problems. There are numerous deficiencies in the "as is, where is" unwritten policy, apart from the obvious one that it conflicts with the assurance of 1.6 that only "some of the criteria may not be applicable" to existing systems. First, the record does not define what a "problem" is. Second, the record discloses no means by which reported problems are collected and later accessed, such as by a parcel index. The "as is, where is" policy is an abdication of the limited responsibilities that SFWMD imposes upon itself in 1.6, especially when applied to the present facts. The facts are straightforward. Neither Ft. Myers, Lee County, nor any other party has ever obtained a permit for any surface water management system, despite numerous improvements in the past 20 years requiring such permits, including the construction of a heliport, at which maintenance and refueling of helicopters takes place. In two relatively minor cases, discussed below, SFWMD erroneously determined that no permit was required. In one of those cases, the applicant, Lee County, candidly admitted the existence of a flooding problem. Based on the present record, neither DMS nor SFWMD has justified the issuance of an operation permit for the systems on the 21.4- and 32.7-acre parcels based either on Basis of Review 1.6 or on the "as is, where is" unwritten policy. Construction of the five improvements on the 21.4 acres began between 1975 and December 1977 with construction of a portion of the Lee County Stockade building and parking, Emergency Operations Center building and parking, and a now- removed barn for the Lee County Sheriff's Office. At the same time, a lake was dug, probably for fill purposes. By the end of 1977, about 2.39 acres of the 21.4 acres were converted to impervious surface. From 1978 to March 1980, another 0.96 acres of the 21.4 acres were converted to impervious surface by the construction of a perimeter dike and road. During this period, construction commenced on the Juvenile Detention Center, adding another 1.63 acres of impervious surface. Between March 1980 and December 1981, additions were made to the Lee County Stockade building and the lake for an additional 0.45 acres of impervious area. Between December 1981 and March 1984, the Price Halfway House building and parking were constructed, adding another 0.79 acres of impervious surface. Between March 1984 and February 1986, a heliport facility and landing area were constructed for the Lee County Sheriff's Office, adding another 1.01 acres of impervious surface. Between February 1986 and February 1990, an additional 2.31 acres of impervious surface were added through additions to the Lee County Stockade and parking area, juvenile detention center, and Emergency Operations Center parking area. Between February 1990 and April 1993, another addition to the Lee County Stockade added 0.62 acres of impervious surface. An additional 0.17 acres of lake was excavated. During this time, applicable rules and statutes required permits for the construction of "works" affecting surface water, including ditches, culverts, and other construction that connects to, or draws water from, drains water into, or is placed in or across the waters in the state. The buildings, parking, other impervious surfaces, ditches, swales, dikes, lake excavations, and, at one point, addition of a now- abandoned pump all constituted "works" for which surface water management permits were required. In 1988, Lee County or Ft. Myers applied for an exemption for an addition to the Lee County Stockade. The basis for the claim of exemption was that the parcel consisted of less than 10 acres and the total impervious surface did not exceed two acres. Although rules in effect at the time required consideration of the contiguous 65 acres under common ownership and the total impervious surface for the 9.7-acre "parcel" exceeded two acres, SFWMD erroneously issued an exemption letter. The second instance involving a claim of exemption took place in 1989 when Lee County submitted plans for another addition to the Lee County Stockade, adding 0.51 acres of impervious surface. The submittal acknowledged a "flooding" problem, but promised a master drainage plan for the "entire site." SFWMD determined that no permit would be required due to the promise of a master drainage plan. No master drainage plan was ever prepared. The flooding problem precluded issuance of the operation permit on an "as is, where is" basis for the already-developed 21.4-acre parcel, even assuming that SFWMD adequately justified the use of this unwritten permitting procedure. In fact, SFWMD has not explained adequately its "as is, where is" permitting procedure or even the undelineated permitting criteria referenced in 1.6, Basis of Review. The 65- acre parcel is a poor candidate for preferential permitting of existing systems. The owner and developer constructed the existing systems in near total disregard of the law. The two times that the owner and developer complied with the permitting process involved small additions for which exemptions should not have been granted. In one case, SFWMD exempted the proposed activity due to its error calculating minimum thresholds as to the areas of the parcel and the impervious surface. In the other case, SFWMD exempted the proposed activity partly in reliance on a promised master drainage plan that was not later prepared. To issue operation permits for the existing systems on the 21.4- and 32.7-acre parcels would reward the owner and developer of the 65-acre parcel for noncompliance with the law and provide an incentive for similarly situated landowners and developers likewise to ignore the law. Before issuing operation permits on systems that have received no comprehensive review and that have been added piecemeal over the years, SFWMD must evaluate the surface water systems on the entire 65-acre parcel to determine whether they meet all applicable criteria. The "as is, where is" unwritten policy has no applicability where there have been reports of flooding. If SFWMD chooses to dispense with criteria in reliance upon Basis of Review 1.6, it must be prepared to identify and explain which criteria are waived and why. Water Quality Basis of Review 5.2.2 provides that projects that are zoned commercial or industrial, such as the present one, must provide one-half inch of "dry" detention or retention pretreatment, unless reasonable assurances are provided "that hazardous materials will not enter the project's surface water management system." There is no existing or proposed dry detention on the 65 acres. The existing development includes the Sheriff's Office Aviation Department, which serves as a heliport. The fueling and maintenance of helicopters means that contaminants may enter the stormwater draining off the site. The functioning of the surface water system on this site is therefore of particular importance. There also may be more reason to question the functioning of the surface water system on this site. It is south of the Lee County Stockade, where flooding has been reported. The heliport site has also been the subject of more elaborate drainage improvements, such as the location of a small retention pond near the Stockade boundary and a pump, the latter of which has since been abandoned. The existing system on the 21.4-acre parcel, as well as the existing and proposed systems on the remainder of the 65 acres, require dry pretreatment for reasons apart from the presence of the heliport. The materials likely to be used with the existing and proposed developments are similar to those found on residential sites. SFWMD and DMS contend that there is therefore no need to require dry pretreatment as to these areas. However, the existing and intended institutional uses, such as jails and bootcamps, represent an intensity of use that exceeds the use typical in areas zoned residential. This increased intensity implies the presence of typical residential contaminants, such as petroleum-based products or cleaning solvents, but in greater volumes or concentrations, if not also, in the case of solvents, different compositions. The lease addresses potential liability for released petroleum. In the absence of a showing that such hazardous materials are prevented from entering the runoff, SFWMD must require dry pretreatment for the systems occupying the entire 65-acre parcel. DMS and SFWMD have thus failed to provide reasonable assurance that the existing systems satisfy applicable water quality criteria or that the proposed system will satisfy applicable water quality criteria. Water Quantity The 65-acre parcel adjoins Ortiz Avenue on the west and property owned by Petitioners on the east and south that is undeveloped except for a borrow pit some distance from the 65- acre parcel. The parcel is roughly 1000 feet east- west and 2700 feet north-south. The proposed halfway house is at the north end of the parcel. The halfway house is situated between a proposed detention pond on the west and a recreation field on the east. A paved road divides the halfway house from the rest of the 65- acre parcel. South of the road are the Lee County Stockade on the west, which abuts Ortiz Avenue, and the Juvenile Detention Center on the east. A berm separates these two sites. The berm runs from the road along the west shore of the twice- enlarged 1.2- acre retention pond and the west boundary of the Price Halfway House, which is south of the Juvenile Detention Center. To the west of the berm, south of the Lee County Stockade, is the Sheriff's Office Aviation Department or heliport facility, which abuts Ortiz Avenue. South of the Aviation Department is an outparcel used by the Florida Department of Corrections that also abuts Ortiz Avenue. East of the outparcel is the proposed halfway house with a proposed detention pond west of the halfway house and south of the outparcel. The Emergency Operations Center, which abuts Ortiz Avenue, is south of the detention pond and surrounded on three sides by the 32.7 acres to be left undisturbed at this time. There are perimeter berms around all of the parcels except for the Juvenile Detention Center and Price Halfway House, which are served by a single berm, and the Emergency Operations Center, which appears not to be bermed. The prevailing natural drainage is not pronounced either by direction or volume because the land is nearly level. The natural direction of drainage is to the south and west and remains so on Petitioners' land to the east and south and the undisturbed 32.7 acres to the south. The variety of drainage directions within the remainder of the 65- acre parcel reflects the extent to which berms, swales, ponds, pumps, roads, buildings, parking areas, and other works have been added to the northerly parcels. Runoff reaching the northern boundary of the 65 acres will be diverted due west around the proposed detention pond to the swale running along the east side of Ortiz Avenue. Runoff from the recreation field and halfway house building and parking area drain into the proposed detention pond, which releases water through a gravity control device to the Ortiz Avenue swale. There appears to be a connection routing some runoff from the south side of the recreation field to the Juvenile Detention Center, where it travels west in a roadside swale to the Ortiz Avenue swale. A little less than half of the area of the Juvenile Detention Center site drains into perimeter swales along the north and east borders and then to the west before emptying into the Ortiz Avenue swale. The remainder of the Juvenile Detention Center drains into the retention pond. The same is true of the Price Halfway House. The Lee County Stockade drains to each of its borders where the water then runs west along the north or south border to the Ortiz Avenue swale. The southern half of the Lee County Stockade site drains into the small retention pond at the northwest corner of the Sheriff's Office Aviation Department. Most of the runoff from the heliport facility runs to the southwest corner of the parcel, which is the location of the abandoned pump. From there, the runoff continues to the Ortiz Avenue swale. Very little if any of the runoff from the heliport enters the small retention pond on the northwest corner of the parcel. The bootcamp drains into the detention pond, which then releases water by a gravity control structure into a portion of the undisturbed 32.7-acres before entering the Ortiz Avenue swale. The Emergency Operations Center site drains in all directions away from the building and parking area, eventually draining into the Ortiz Avenue swale. Stormwater discharge rates from the proposed halfway house and bootcamp are 0.28 cfs and 0.37 cfs. Under SFWMD rules, the allowable maximums in the Six Mile Cypress drainage basin are 0.30 cfs and 0.33 cfs, respectively. SFWMD and DMS contend that the excessive discharge from the bootcamp is acceptable because the gravity control device for the proposed detention pond is of the smallest size allowable, given the indisputable need to avoid clogging and ensuing upstream flooding. Initially, SFWMD approved the discharge rates for the halfway house and bootcamp because, when combined, they did not exceed the total allowable value. However, this approach was invalid for two reasons. First, the two sites contain entirely independent drainage systems separated by several hundred feet. Second, after correcting an initial understatement for the value for the halfway house, the actual total exceeds the maximum allowable total. SFWMD contends that the slight excess is acceptable because of the inability to use a smaller orifice in the gravity control structure. However, the discharge quantity easily could have been reduced by design alternatives, such as enlarging the detention pond, which is mostly surrounded by land that is to be left undisturbed. The ease with which the minimum-orifice problem could have been avoided rebuts the presumption contained in Basis of Review 7.2.A that excessive discharge quantities are presumably acceptable if due to the inability to use a smaller orifice. Also, SFWMD and DMS have failed to show that the effect of the excessive discharge quantities is negligible, so the exception in the SFWMD manual for negligible impacts is unavailable. Neither SFWMD nor DMS provided any reasonable assurance as to the quantity of discharge from the 21.4 acres. Rough estimates suggest it is more likely that the quantity of discharge may greatly exceed the allowable maximum. SFWMD must evaluate the water-quantity issues before issuing operation permits for the systems on the 21.4- and 32.7- acre parcels and a construction and operation permit for the 10.9-acre parcel. Obviously, if SFWMD determines that all water quantity criteria are met as to the existing systems, it may issue operation permits for the systems on the 21.4- and 32.7- acre parcels. Otherwise, SFWMD must quantify the extent of the deviation and, if it seeks to waive compliance with any or all quantity standards in reliance on Basis of Review 1.6, evaluate the effect of the waiver and explain the basis for the waiver. DMS and SFWMD have thus failed to provide reasonable assurance that the existing systems satisfy applicable water quantity criteria or that the proposed system will satisfy applicable water quantity criteria. Impacts on Adjacent Lands Petitioners' property is impacted by the above- described drainage in two ways. First, Petitioners' property abutting the east side of Ortiz Avenue, south of the 65 acres, is especially vulnerable to flooding because the Ortiz Avenue swale is not a V-notch, but a half-V. The closed side of the swale prevents the water from running onto Ortiz Avenue. The open side of swale abuts Petitioners' property, so, if the swale's capacity is exceeded, stormwater will be released onto Petitioners' land. Second, perimeter berming along the east side of the 10.9- and 21.4- acre parcels will impede flow off the part of Petitioners' property located to the east of the 65 acres. A swale between the proposed halfway house and the Juvenile Detention Center will receive runoff from a small portion of Petitioners' property to the east and mostly north of the 65 acres. But there is no indication how much runoff from Petitioners' property can be so accommodated, how much runoff is impeded by the existing berm along the east side of the Juvenile Detention Center and Price Halfway House, and how much runoff will be impeded by the addition of new berms along the east side of the proposed halfway house and bootcamp. Basis of Review 6.8 requires that swales and dikes allow the passage of drainage from off-site areas to downstream areas. Rule 40E-4.301(1)(b), Florida Administrative Code, requires that an applicant provide reasonable assurances that a surface water management system will not cause adverse water quality or quantity impacts on adjacent lands. Neither SFWMD nor DMS obtained topographical information for Petitioners' property, as required by the Basis of Review. Rough estimates suggest that the proposed project may require Petitioners' property to retain considerably more stormwater from the design storm event of 25 years, three days. DMS and SFWMD have thus failed to provide reasonable assurance that the proposed system would not have an adverse impact on Petitioners' upstream and downstream land.
Recommendation It is hereby RECOMMENDED that the South Florida Water Management District enter a final order denying the application of the Department of Management Services for all permits for the operation and construction and operation of surface water management systems on the 65-acre parcel. ENTERED on June 19, 1995, in Tallahassee, Florida. ROBERT E. MEALE Hearing Officer Division of Administrative Hearings The DeSoto Building 1230 Apalachee Parkway Tallahassee, Florida 32399-1550 (904) 488-9675 Filed with the Clerk of the Division of Administrative Hearings on June 19, 1995. APPENDIX Rulings on Proposed Findings of Petitioners 1-18: adopted or adopted in substance. 19: rejected as subordinate. 20-21: adopted or adopted in substance. 22-24 (first sentence): rejected as irrelevant. 24 (remainder)-46: adopted or adopted in substance. 47-53: rejected as subordinate. 54-64 (first sentence): adopted or adopted in substance. 64 (second sentence)-66: rejected as subordinate. Rulings on Proposed Findings of Respondent SFWMD 1-10: adopted or adopted in substance. 11: rejected as unsupported by the appropriate weight of the evidence. 12: rejected as unnecessary. 13: adopted or adopted in substance. 14-15: rejected as subordinate. 16: rejected as unsupported by the appropriate weight of the evidence. 17 (except for last sentence): adopted or adopted in substance. 17 (last sentence): rejected as unsupported by the appropriate weight of the evidence. 18-32 (first sentence): rejected as unnecessary. 32 (remainder): rejected as unsupported by the appropriate weight of the evidence. 33: rejected as subordinate. 34: rejected as unsupported by the appropriate weight of the evidence, except that the proposed ponds are wet detention. 35 (first sentence): adopted or adopted in substance. 35 (remainder): rejected as unsupported by the appropriate weight of the evidence. 36-45: rejected as unnecessary. 46-47: rejected as unsupported by the appropriate weight of the evidence. 48-50 (second sentence): adopted or adopted in substance. 50 (remainder): rejected as unsupported by the appropriate weight of the evidence. 51-52, 55-57 (first sentence), and 58: adopted or adopted in substance, although insufficient water quality treatment. 53: adopted or adopted in substance. 54: rejected as unsupported by the appropriate weight of the evidence. 57 (second sentence): rejected as unsupported by the appropriate weight of the evidence. 59: rejected as unsupported by the appropriate weight of the evidence. 60: adopted or adopted in substance, except after "therefore." None of remainder logically follows from what is said in 1.6. 61: rejected as unsupported by the appropriate weight of the evidence. 62-64: rejected as subordinate, unsupported by the appropriate weight of the evidence, and irrelevant. 65: rejected as subordinate. 66: rejected as irrelevant. The burden is on the applicant and SFWMD, if it wishes to issue the permits, to provide reasonable assurances as to the adverse impact of the drainage systems. 67-68: rejected as subordinate. 69: rejected as unsupported by the appropriate weight of the evidence. 70: rejected as unsupported by the appropriate weight of the evidence. 71: rejected as repetitious. 72: rejected as irrelevant, except for past report of flooding, which is rejected as repetitious. 73: rejected as repetitious. 74: rejected as irrelevant and subordinate. 75 (first three sentences): adopted or adopted in substance. 75 (remainder): rejected as unsupported by the appropriate weight of the evidence. 1 and 2: rejected as irrelevant insofar as the same result is reached with or without the permit modifications. Rulings on Proposed Findings of Respondent DMS 1-4: adopted or adopted in substance. 5: rejected as subordinate. 6: rejected as unsupported by the appropriate weight of the evidence. 7: adopted or adopted in substance. 8: rejected as subordinate. 9: adopted or adopted in substance, except that the excessive discharge was not "caused" by the minimum-sized orifice, only defended on that basis. 10: adopted or adopted in substance. 11-12: rejected as subordinate. 13: rejected as irrelevant. 14: adopted or adopted in substance. 15: adopted or adopted in substance, except for implication that no flooding problems existed. 16: rejected as recitation of evidence. 17: rejected as subordinate. 18: rejected as irrelevant. 19: adopted or adopted in substance, to the extent that separateness of systems is relevant. 20: rejected as subordinate. 21: adopted or adopted in substance, except for last sentence, which is rejected as unsupported by the appropriate weight of the evidence. 22: rejected as subordinate. 23-30: rejected as unsupported by the appropriate weight of the evidence, recitation of evidence, and subordinate. 31: rejected as unsupported by the appropriate weight of the evidence. 32: rejected as unsupported by the appropriate weight of the evidence, based on the present record. 33: rejected as unsupported by the appropriate weight of the evidence and relevance. COPIES FURNISHED: Tilford C. Creel Executive Director South Florida Water Management District P. O. Box 24680 West Palm Beach, FL 33416 Russell P. Schropp Harold N. Hume, Jr. Henderson Franklin P.O. Box 280 Ft. Myers, Fl 33902 O. Earl Black, Jr. Stephen S. Mathues Department of Management Services 4050 Esplanade Way, Suite 260 Tallahassee, FL 32399-0950 Vincent J. Chen Toni M. Leidy South Florida Water Management District 3301 Gun Club Road West Palm Beach, FL 33401
The Issue The issue is whether Bayou Arbors, Inc. (Arbors), is entitled to a dredge and fill permit to construct docks in DeBary Bayou, Volusia County, Florida.
Findings Of Fact On January 8, 1986, DER received an application from Arboretum, a predecessor in interest of Arbors, to construct 12,758 square feet of docks in DeBary Bayou to provide ninety eight (98) boat slips, and to dredge 2,509 cubic yards of shoreline material from DeBary Bayou in areas within DER's jurisdiction under the proposed boat docks, and to place approximately 800 linear feet of concrete riprap along the shoreline after it was dredged. Following the initial application review process, which included on- site evaluations by several DER biologists, on April 14, 1986, DER prepared a Biological and Water Quality Assessment in which DER's staff recommended that the project be modified to delete the dredging, allowing the littoral zone to remain intact. On April 24, 1986, DER forwarded its Biological and Water Quality Assessment to Mr. Charles Gray, the property owner. In response to DER's recommendations, the Applicant submitted, and on April 30, 1986, DER received, a revised Application which deleted the originally-proposed shoreline dredging of 2,509 cubic yards of material as well as the placing of 800 linear feet of concrete riprap. This Application was submitted by Mr. Duy Dao, a Professional Engineer registered in the State of Florida. This Application proposed constructing approximately 17,000 square feet of docking facilities, providing ninety-eight boat slips, along approximately 2,580 linear feet of shoreline adjacent to twenty-four acres of uplands owned by the Applicant. The original and the revised drawings omitted a vertical scale from the cross-section drawings of the project. This omission gave the impression that the shoreline bank of DeBary Bayou was steeper than it actually is and that the water depths in DeBary Bayou adjacent to the north shoreline are deeper than they actually are. However, DER's biologists were on-site four times between February 25, 1986, and May 19, 1986. They observed the existing slope of the DeBary Bayou shoreline and the existing depths in DeBary Bayou, and the on-site observations negated the effect of the omission in the drawings. The omission in the drawings did not affect DER's evaluation of the project. On May 23, 1986, DER issued its Intent to Issue and Draft Permit No. 64-114399-4 to Arboretum. The Intent to Issue and the Draft Permit include the following Specific Conditions: Further construction on the Applicant's property along the DeBary Bayou shall be limited to uplands; Issuance of this permit does not infer the issuance of a permit for dredging in the Bayou at a future date, should an application for dredging be submitted; A deed restriction shall be placed on the condominium limiting boats moored at the facility to seventeen feet or less. A copy of the deed restriction shall be submitted to the Department within sixty days of issuance of this permit; There shall be no "wet" (on-board) repair of boats or motors at this facility; All boats moored at the dock shall be for the use of residents of the condominium only. Public use of the dock or rental or sale of mooring slips to non-residents of the condominium is prohibited; Manatee warning signs shall be placed at 100 foot intervals along the length of the dock(s); Turbidity shall be controlled during construction (by the use of siltation barriers) to prevent violations of Rule 17-3.061(2)(r), Florida Administrative Code. On June 29, 1987, Volusia County, DER and Arboretum entered into a "Joint Stipulation for Settlement" wherein Arboretum agreed not to construct more than twenty-six docks accommodating more than fifty-two boat slips along Arboretum's DeBary Bayou frontage of 2,580 feet. Furthermore, Arboretum agreed that it would modify the configuration and the design of the boat slips and the location of the boat docks; that it would post Slow Speed, No Wake zone signs and manatee education signs along DeBary Bayou from the 1-4 bridge west to a point 100 feet west of the western boundary of Arboretum's boat docks; and that as mitigation for the removal of vegetation from the littoral zone where the boat slips would be constructed, Arboretum would plant wetland hardwood trees. In addition to the Joint Stipulation for Settlement, on June 14, 1987, the property owners, Charles Gray and Sandra Gray, as part of their agreement with Volusia County, executed a "Declaration of Covenants, Conditions, and Restrictions" to which the Joint Stipulation for Settlement was attached as an exhibit. Said Declaration of Covenants, Conditions, and Restrictions, reiterated the Joint Stipulation's limitation of construction of boat docks in DeBary Bayou and further provided that said boat docks would not be constructed at the Arboretum project site in DeBary Bayou unless and until certain maintenance dredging set forth in Article II of the Declaration of Covenants, Conditions, and Restrictions occurred. Furthermore, Article III of said Declaration of Covenants, Conditions and Restrictions set forth certain prohibitions regarding constructing boat ramps on the Arboretum property and docking or storing boats along the DeBary Bayou shoreline except at the site of the proposed docks. In 1969, an artificial channel was excavated in DeBary Bayou adjacent to the north shoreline of DeBary Bayou by a dragline operating along the shoreline. At present, said channel has been partially filled by organic sediments originating in DeBary Bayou. There exists in Section 403.813(2)(f), Florida Statutes, an exemption from the DER's permitting requirements for the performance of maintenance dredging of existing man-made channels where the maintenance dredging complies with the statutory provisions and with the regulatory provisions found in Florida Administrative Code Rule 17-4.040(9)(d). The dragline excavation work performed in DeBary Bayou in 1969 created a structure which conforms to the definition of "channel" provided in Section 403.803(3), Florida Statutes. The maintenance dredging required by the Declaration of Covenants, Conditions, and Restrictions is to be performed by suction vacuuming of the silt sediment, from the 1969 channel and that dredged material is to be placed on Arbors' upland property at the project site. This maintenance dredging differs from the dredging originally proposed by the applicant in its application submitted in January 1986. The dredging originally proposed, which DER recommended against, was to be performed by back hoes and drag-lines which would have cut into the north shoreline of DeBary Bayou and would have affected the littoral zone along the project shoreline. The average water level in Lake Monroe and DeBary Bayou is approximately 1.8 feet above mean sea level. On April 18, 1987, transact studies in DeBary Bayou showed water levels at 3.2 feet above mean sea level and that water depths in DeBary Bayou to a hard sand/fragmented shell bottom ranged from approximately one foot along the south shoreline to approximately nine feet in deep areas in the former channel. The average depth of the channel is five feet below mean sea level. The water depth in DeBary Bayou ranges from approximately one to three feet. At times of average water levels, one to three feet of silt or unconsolidated sediment overburden covers the natural hard sand/shell bottom of DeBary Bayou. This silt and sediment overburden is composed of organic material and is easily disturbed. When it is disturbed, it raises levels of turbidity, although there was no evidence presented that the turbidity would violate state water quality standards. This silt and sediment overburden has been deposited at a faster rate than it would normally be deposited under natural conditions because of the Army Corps of Engineers' herbicidal spraying of floating plants in DeBary Bayou. As this silt and sediment overburden decomposes, it takes oxygen from the water. The presence of a strong odor of hydrogen sulfide indicates that the oxygen demand created by the sediment is greater than the available supply of oxygen at the sediment-water interface. This unconsolidated silt and sediment overburden does not appear to harbor either submerged vegetation or significant macroinvertebrate populations. The Shannon/Weaver diversity index of benthic macroinvertebrates at four locations in DeBary Bayou indicated lowest diversity at the project site and highest diversity at the 1-4 overpass, where a small patch of eel grass is growing. Removal of this silt and sediment overburden from the 1969 channel will enhance the system, enabling a hard bottom to be established, with a probability of subsequent establishment of a diversity of submerged macrophytes. Removal of the silt and sediment overburden from the 1969 channel will restore the natural hard sand/fragmented shell bottom in that area of DeBary Bayou. It is unlikely that boat traffic in the restored channel will cause turbidity which will violate state water quality standards. Removal of this silt and sediment overburden will improve water quality in DeBary Bayou by removing a source of oxygen demand. Removal of this silt and sediment overburden will create a better fish habitat by exposing some of the natural bottom of DeBary Bayou. Fish are unable to spawn in the unstable silt and sediment. Removal of this silt and sediment overburden will increase the depth of water in DeBary Bayou channel to between four to six feet. The maintenance dredging, required by the Declaration of Covenants, Conditions, and Restrictions, is limited by statute to the channel which was excavated in 1969. Therefore, a continuous channel will not be maintained from the project site eastward to Lake Monroe. At present, a sandbar exists at the confluence of DeBary Bayou and Lake Monroe. During low water, this sandbar restricts navigation into and out of DeBary Bayou to small craft. At present, boats can and do travel on DeBary Bayou for fishing and for other water-related recreational activities. However, due to water level fluctuations, boating on DeBary Bayou is easier during higher water periods. During lower water periods, navigation into and out of DeBary Bayou is still possible, but boaters must proceed using common sense and caution. The United States Fish and Wildlife Service (FWS) has no evidence that manatees presently use or have ever used DeBary Bayou. Adult manatees have an average girth of approximately three (3) feet. Without a continuous channel open to Lake Monroe, manatees are not likely to go up DeBary Bayou. Since the water at the sandbar at the mouth of DeBary Bayou at its confluence with Lake Monroe is generally less than three feet deep throughout the year, it is likely that these shallow waters will deter manatees from entering DeBary Bayou. DeBary Bayou is a spring-fed run from a spring a substantial distance upstream. The sheetflow of the spring water follows a circuitous route through marsh areas prior to reaching the area of this project. The proposed site is just west of the 1-4 overpass and Lake Monroe. The FWS's data show that the St. Johns River in Volusia County has an extremely low documented manatee mortality rate resulting from boat/barge collisions. Generally, boats greater than 23 feet long are more likely to kill manatees outright than smaller boats are. In marinas, manatees are very rarely killed by collisions with boats. Manatees and marinas are highly compatible. On August 1, 1986, the FWS issued a "no-jeopardy" opinion regarding Arbors' project. In this letter, the FWS stated that Arbors' project was not likely to jeopardize the continued existence of the manatee or to adversely modify the manatee's critical habitat. In the year since the FWS issued its no-jeopardy opinion, no manatee mortalities resulting from boat-barge collisions have been documented in the St. Johns River in Volusia County. The FWS recommended one boat slip per one hundred linear feet of waterfront, or twenty-six boat slips for the project. A single-family residence which would be entitled to one pier could berth an unlimited number of boats at that single pier. The FWS would have no control over the number of boats using that single pier. Arbors' project calls for twenty-six piers. The FWS's evaluation of Arbors' project is exactly the same as that agency's evaluation of any other marina project anywhere in areas designated as critical manatee habitat. All of the St. Johns River in Volusia County, Florida, is designated as critical manatee habitat. On July 16, 1986, after issuance of its Intent to Issue, DER received comments from the Florida Department of Natural Resources regarding Arbors' project and its potential impact on manatees. DER considered the possibility of boat/manatee collisions and had specifically considered this issue. DER did not agree with the broad and general concerns expressed by the Department of Natural Resources, and DER's rules have not adopted a specific requirement regarding a ratio between the length of a project's shoreline and the number of permittable boat slips. On July 16, 1986, the Department received a letter from the FWS concerning fisheries issues and navigation. This FWS letter was received after issuance of DER's Intent to Issue. Although DER considered these comments, DER disagreed with the FWS's recommendations regarding these issues. Water quality sampling and analysis showed that at present, there are no violations of DER's Class III water quality standard in DeBary Bayou, except for the dissolved oxygen criterion on some occasions during early-morning hours, and that result is to be expected. It is further not expected that there will be any water quality violations after the project is completed. If the work areas affected by driving piles to build floating docks and the work area around the maintenance dredging of the DeBary Bayou channel are contained within turbidity barriers, as required by general and specific conditions of the DER's proposed Draft Permit, it is anticipated that no violations of the Class III turbidity criterion will occur during construction of Arbors' project. By maintenance dredging the former DeBary Bayou channel, Arbors will remove the silt and sediment overburden from the channel and restore a deep (four to five feet below mean sea level) channel having a hard sand/fragmented shell bottom. Arbors' dock will be restricted to small boats whose operation in the deep channel will be unlikely to re-suspend silt and sediment and cause violations of the Class III turbidity criterion. Additionally, it is unlikely that any turbidity which is created by turbulence from boat propellers in a designated "No Wake, Slow Speed" zone will violate the Class III turbidity criterion. Although the entire project will be enhanced by the proposed maintenance dredging, such dredging is not a part of the permit application. From the evidence it appears that the project is permittable without the dredging. Although Arbors' project will result in the addition of some oils and greases associated with outboard motors to DeBary Bayou, the addition is not expected to result in violations of the Class III water quality standards. Additionally, release of heavy metals from anti-fouling paints should be minimal, and that release can be further controlled by specifically prohibiting over-water repair of boats and motors. Some addition of phosphorous to the waters of DeBary Bayou is anticipated due to use of phosphate-based detergents for washing boats. Additionally, minimal amounts of phosphorous may be added to DeBary Bayou from re-suspension of organic silts by turbulence from boat propellers. However, DER has no standards for phosphorous in fresh waters, and the minimal additional amounts of phosphorous expected from these sources are not anticipated to violate DER's general nutrient rule. Operation of boats at Arbors' proposed boat docks will cause no water quality problems which would not be caused by operation of boats at any other marina anywhere in Lake Monroe or anywhere else in the State of Florida. While WVC's expert, Robert Bullard, testified that Arbors' proposed boat docks could potentially cause violation of DER's Class III water quality criteria for turbidity, oils and greases, heavy metals and phosphorous, he was unable to testify that Arbors' project actually would cause such violation. His testimony in this regard was speculative and is not given great weight. No other WVC expert testified that Arbors' project was likely to cause violation of any criteria of DER's Class III water quality standards. It is anticipated that the shade cast by the boat docks will not have an adverse affect on water quality. Additionally, DeBary Bayou is a clear, spring-fed water body open to direct sunlight. The boat docks will cast shade which will enhance fish habitat. The proposed docks will not threaten any production of fish or invertebrate organisms. The mitigation plan proposed by the applicant and accepted by Volusia County and DER requires planting wetland hardwood tree species. These trees will certainly assist in stabilizing the bank of DeBary Bayou and minimizing erosion of the shoreline. Additionally, these trees will absorb nutrients from the water and will perpetuate the wooded wetland habitat along the DeBary Bayou shoreline. Arbors' own expert, Carla Palmer, also suggested the sprigging of eel grass in the dredged portion of DeBary Bayou. Such planting should be included as part of the mitigation plan. DER considered the cumulative impact of this docking facility. Four marinas are presently permitted on Lake Monroe and in the St. Johns River between Lake Monroe and Deland. DER considered these facilities' existence when it reviewed Arbors' application, and was satisfied that Arbors' boat dock facility would not have an adverse cumulative impact. There are no specific guidelines for a cumulative impact evaluation; accordingly, DER must apply its cumulative impact evaluation on a case-by-case basis. In the present case, there is no showing of adverse cumulative impacts from this project. Arbors' project will not adversely affect significant historical or archaeological resources recognized pursuant to applicable Florida or Federal Law. WVC was organized in March 1985, to oppose development in West Volusia County. WVC did not meet regularly and did not keep regular minutes of its meetings in the interim between organizing and filing the Petition in June 1986, for an administrative hearing on the Intent to Issue a permit for Arbors' project. When the Petition was filed, WVC did not have a membership roll, and was unsure how many members it had. Further, it is unclear as to how many members may have attended an "emergency" meeting to authorize filing said Petition. Approximately five months after said Petition was filed, WVC was incorporated and approximately nine months after the Petition was filed, WVC compiled a list of the people who were WVC members in June 1986. The emergency meeting WVC held in June 1986, to authorize filing said Petition was the first and the only such "emergency" meeting WVC ever held. The minutes of the emergency meeting have been lost. In June 1986, WVC may have had written rules authorizing emergency meetings and authorizing it to file suit, but its Chairman is unsure of this. Six of WVC's approximately 20 members may have lived within one mile of Arbors' project site in June 1986. Two of these members lived on waterfront property on Lake Monroe east of the 1-4 bridge. Some of these WVC members have never taken a boat west of 1-4 onto DeBary Bayou. WVC, as an organization, never sponsored outings or boat trips onto DeBary Bayou before filing the Petition. WVC's officers at the time of filing the Petition did not use DeBary Bayou for boating, fishing or swimming. No WVC members have ever seen manatees in DeBary Bayou. As with any other similar project on Lake Monroe, the boats which might be berthed at Arbors' project might add additional trash to the waters of Lake Monroe, might disturb the wildlife which WVC members might see on their property, and might cause wakes which might erode waterfront property. One of WVC's founders, who was an officer in June 1986, when WVC filed the Petition, stated that she would not be adversely affected in kind or degree any more than any other taxpayer in Florida. Friends timely intervened and its intervention was authorized by its membership at a regularly noticed meeting.
Recommendation Based upon the foregoing Findings of Fact and Conclusions of Law, it is RECOMMENDED that the Department of Environmental Regulation enter a Final Order granting Permit Number 64-114399-4, subject to those specific conditions set forth in paragraph 6 hereof and as modified by the stipulation entered into between Arboretum, Volusia County, and Department of Environmental Regulation, as more particularly described in paragraphs 7 and 8 hereof, and to include within the mitigation plan the sprigging of eel grass in areas of the dredged portion of DeBary Bayou. DONE AND ENTERED this 16th day of September 1987, in Tallahassee, Florida. DIANE K. KIESLING Hearing Officer Division of Administrative Hearings The Oakland Building 2009 Apalachee Parkway Tallahassee, Florida 32399-1550 (904) 488-9675 FILED with the Clerk of the Division of Administrative Hearings this 16th day of September 1987. APPENDIX TO RECOMMENDED ORDER IN CASE NO. 86-2463 The following constitutes my specific rulings pursuant to Section 120.59(2), Florida Statutes, on all of the proposed findings of fact submitted by the parties in this case. Specific Rulings on Proposed Findings of Fact Submitted by Petitioner and Intervenor, West Volusia Conservancy, Inc., and Friends of the St. Johns, Inc. 1. Each of the following proposed findings of fact are adopted in substance as modified in the Recommended Order. The number in parentheses is the Finding of Fact which so adopts the proposed finding of fact: 1(3); 2(5); 8(24); 13(8); 46(57); and 47(57). 2. Proposed findings of fact 3, 4, 7, 10, 11, 12, 28, 29, 32, 34, 35, 36, 40, 42, 43, 44, and 45 are rejected as being subordinate to the facts actually found in this Recommended Order. 3. Proposed findings of fact 5, 14, 15, 16, 17, 20, 23, 24, 25, 26, 27, 30, 31, 33, 39, and 41 are rejected as being unsupported by the competent, substantial evidence. 4. Proposed findings of fact 6, 9, 18, 19, 21, 22, 37, and 38 are rejected as irrelevant. Specific Rulings on Proposed Findings of Fact Submitted by Respondent, Bayou Arbors, Inc. 1. Each of proposed findings of fact 1-56 are adopted in substance as modified in the Recommended Order, in Findings of Fact 1-56. Specific Rulings on Proposed Findings of Fact Submitted by Respondent, Department of Environmental Regulation Each of the following proposed findings of fact are adopted in substance as modified in the Recommended Order. The number in parentheses is the Finding of Fact which so adopts the proposed finding of fact: 1-11(1-11); 13-28(12-27); 29-38(29-38); 39(38); and 40-48(39-47). Proposed finding of fact 12 is rejected as unnecessary. COPIES FURNISHED: Dale Twachtmann, Secretary Department of Environmental Regulation 2600 Blair Stone Road Tallahassee, Florida 32399-2400 Richard S. Jackson, Esquire 1145 West Rich Ave. Deland, Florida 32720 Dennis Bayer, Esquire P. O. Box 1505 Flagler Beach, Florida 32036 Philip H. Trees, Esquire P. O. Box 3068 Orlando, Florida 32802 Vivian F. Garfein, Esquire Department of Environmental Regulation 2600 Blair Stone Road Tallahassee, Florida 32301-8241
Findings Of Fact At all times pertinent to the issues herein, the Department was the state agency responsible for the regulation and issuance of dredge and fill permits for waters of the state. Hunt is a real property development company which owns the property in issue located contiguous to Sarasota Bay on the east and an artificial canal, dredged many years ago, located to the south. The property in issue includes submerged lands. Petitioners, Manasota and Manatee are environmental interest associations whose standing as parties hereto was stipulated to by Hunt and the Department. The Rosens are owners of a piece of land at the bayward end of the property located to the south of the artificial canal to the south of the property in issue. On September 2, 1988, Hunt applied to the Department for a dredge and fill permit to construct a dock system four feet wide and approximately one thousand feet in length along the northern edge of the artificial canal. Four access walkways would extend from the existing berm to the north out to the proposed dock. The request also sought permission to trim mangroves to facilitate construction of and provide access to the dock; to place 22 cubic yards of fill to stabilize an existing private road; and to relocate the existing access channel by dredging approximately 700 cubic yards of material. Petitioners do not object to the placement of the 22 cubic yards of fill. During the review process, the Department identified several deficiencies in the proposal which it required be modified before a permit could be issued. Hunt agreed to comply with all of the Department's modifying requirements. As a result, in its amended form the proposal calls for the dock to be reduced in size from 5,080 square feet to approximately 3,800 square feet; access points to be reduced from four to three; the installation of a flushing system consisting of a 30 inch culvert between the west end of the canal and the mangrove swamp to the north to enhance the water quality in the artificial canal; the submittal of historical information to demonstrate the existence of a historic canal which would support maintenance dredging; and the submittal of a mitigation proposal for the seagrasses which would be destroyed by the dredging of a new channel and for the mangroves to be trimmed to facilitate the dock construction. The revised application also sought permission to construct a previously approved (different permit) boardwalk, the mitigation for which has been completed and is apparently successful. This mitigation is located in the northern boundary of the Hunt property. The wetlands area adjacent to Hunt's north property line is a Class II, Outstanding Florida Water, (OFW). The property in issue is located contiguous to Sarasota Bay, a Class II water body designated as an OFW). This portion of the bay is not approved for shellfish harvesting. Sometime between 1951 and 1957, a channel was dredged from the Intracoastal Waterway running generally north and south in the bay, west across approximately 400 feet of bay bottom into what was then a mangrove forest on the east side of Longboat Key. The westernmost 1400 foot extension of that channel into the forest is the artificial canal in issue which receives untreated storm water runoff from Jungle Queen Way, the roadway to the south of the canal. The canal is a Class III water and is not an OFW. Approximately 1,225 feet of the southern shoreline of that canal is seawalled, with approximately 35% of the southern shoreline having mature mangrove trees along it. The entire northern shoreline is vegetated by mature mangrove trees. There is no seawall on the northern shore. The canal varies in depth from less than one foot at points to a maximum of 7 1/2 feet at other points. As a result of shoaling at the canal juncture with the bay, a sand spit has formed, and at low tide, water depth is minimal but allows the passage of shallow draft vessels if their motors are raised. The original channel has silted in to a great degree and has become vegetated by approximately 1,350 square feet of various shoal grasses. It is home to several species of water animal including crown conch, lightning whelk, venus sunray clams, jingle shell, banded tulip snail and common nassa snail as well as supporting a diverse and abundant group of bottom dwelling organisms. The grass beds are fish habitats as well as nursery and feeding grounds and fish species present include some important to commercial and sport fishing. Though the remains of the original channel are often indistinct and difficult to define, the Department, in its analysis of the application for permit, determined from a review of the documentary evidence presented , and it is also found here, that a historic channel exists as described, and is navigable at least fifty percent of the time. As such, the Department concluded that that channel qualified for the maintenance dredge exemption. The Department also concluded that a minimum amount of dredging would be required to clear the historic channel sufficiently to allow boats to utilize it during a full range of tidal conditions. The seagrass beds currently existing in the historic channel would be substantially damaged by a maintenance dredging in the area. Though the Department has no authority to require mitigation for this impact should Hunt exercised its right to maintenance dredge, as an alternative, Hunt proposed to dredge a hook shaped channel curving to the north around that portion of the historic channel which penetrates the grass beds. This alternative site is also located in Class II waters and an Outstanding Florida Water. Dredging at the alternative site would displace much the same amount of material, (approximately 700 cubic yards), and the resultant channel would be approximately the same length, width, and depth overall. The alternative site will cross an area which contains a shoal grass, Cuban Shoalweed, but utilization of this site will have a substantially lesser impact to the overall seagrass population than would dredging of the historic channel. If Hunt chooses to utilize the alternative route, it would have to comply with the Department's mitigation requirements which include transplanting the displaced grass from the alternative channel to another location. The conditions for the mitigation were developed by Department personnel in conjunction with the Department of Natural Resources whose personnel have agreed to participate in the transplantation. Hunt has agreed to undertake additional mitigation planting regardless of whether the transplant is successful. The Department has determined that Hunt's total mitigation program is sufficient to offset the adverse impacts of the proposed dredging. Any sea grasses in the area of the channel will be protected by the installation of signs indicating their location. Speed will be limited by the installation of "No Wake" zone signs, and, in addition, the natural dog-leg in the channel should minimize the impact to adjacent shorelines and reduce the potential for shoaling or erosion. The Department gathered water quality data for the area from 1988. This is consistent with the current statutory and rule criteria which permits the use of data existing in the year prior to application. To supplement this, however, the Department also required that Hunt submit water quality data for the actual project site as a part of the application process. From this input, existing ambient water quality standards were established. To insure that these existing ambient water quality standards within the OFW are maintained during construction, the Department has established a mixing zone and has indicated a requirement for the use of double turbidity curtains. Additional safeguards include limiting dredging to periods of low tide. The Department has concluded that these prosthetic activities will most likely result in maintenance of the water quality standards required for Class II and OFW. Any diminishment of those standards would be of limited duration. The Department was also satisfied that the project would not adversely impact in this area after construction was completed and the facility in operation. In support of this position, the Department relied on evidence tending to show that the design of a culvert proposed for incorporation into the project should significantly improve flushing of the water within the canal. Pollutant loading to the system should be reduced as a result of the biological filtration of the mangrove community which will absorb many of the excess nutrients currently in the canal water, and the removal of suspended solids. Expert evidence on the subject indicates that flushing time, currently estimated at 9 days, will be reduced to less than 4 days. Polluting activities, such as fueling facilities, live-aboards, and major repair and maintenance of boats in the canal will be prohibited. Any pollutants not removed by the natural filtration process described above will, therefore, remain in the canal water for less time than before. If vessels are docked in the canal, the minimal amount of resulting oil and grease pollution should not be sufficient to degrade water quality in either the canal or the bay to a point below acceptable established standards. In fact, such impact should be both non-detectable and non-measurable.. Hunt's plan calls for the removal of approximately 20 of the approximately 2,400 mangrove trees and the trimming of approximately 230 additional ones. Though this trimming, as a part of an exempt activity, is also exempt, and as a result, mitigation in not required, Hunt indicates its intention to plant 3 trees for every tree removed or trimmed, and this proposal, considered acceptable to the Department, has been incorporated as one of the permit conditions. The new mangrove area to be planted in mitigation should be fully established within 3 years of planting and will provide the same beneficial function as the replaced trees. Hunt's mitigation planting for the previously mentioned boardwalk project has been successful. To protect the manatee population as much as possible, the Department has also included conditions to the permit requiring the posting of manatee awareness signs along the canal and channel and the installation of a permanent informational display at the facility. These measures, though no guarantee of compliance by individual boaters, are currently the most effective safeguards short of prohibition of boat activity. The Department has concluded, and it is so found, that, considering the proposed project against the statutory criteria relating to dredge and fill permitting of this nature, the project, as conditioned, is in the public interest and would have no cumulative impact on the environment in the area. When the 36 special conditions attached to the permit by the Department are complied with, the effect on fish and wildlife resources in the area should be beneficial. As a result of the mitigation activities, both mangrove and seagrass populations should be increased and the shoreline enhanced. Water quality in the canal should be significantly improved above existing conditions, and the abandonment of the historic maintenance dredging operation, with its associated impacts, is clearly in the public interest. The incorporation of a permit condition precluding any subsequent maintenance dredging in the historic channel upon completion of the relocation is a safeguard clearly in the public interest. The evidence also indicates, supporting Departmental findings to that effect, that the project will not adversely affect the public health, safety, welfare or property of others; nor will it adversely affect the conservation of fish and wildlife, endangered, threatened or other. It will not adversely affect navigation or flow of water or cause harmful erosion or shoaling. It will not adversely affect fishing or recreational values or marine productivity in the area; nor will it endanger significant historical or archaeological resources which exist currently in the area.
Recommendation Based on the foregoing Findings of Fact and Conclusions of Law, it is, therefore: RECOMMENDED that a Final Order be entered in this case granting a Dredge and Fill permit to Hunt Building Corporation consistent with the terms and conditions outlined in the Department's Intent to Issue, dated March 29, 1990, under file NO. 41-1542543. RECOMMENDED this 3rd day of January, 1991, in Tallahassee, Florida. ARNOLD H. POLLOCK, Hearing Officer Division of Administrative Hearings The DeSoto Building 1230 Apalachee Parkway Tallahassee, Florida 32399-1550 (904) 488-9675 Filed with the Clerk of the Division of Administrative Hearings this 3rd day of January, 1991. APPENDIX TO RECOMMENDED ORDER IN CASES NO. 90-2350 & 90-2736 The following constitutes my specific rulings pursuant to S 120.59(2), Florida Statutes, on all of the Proposed Findings of Fact submitted by the parties to this case. FOR PETITIONERS, MANASOTA AND MANATEE: 1. Accepted. 2(a) - (e). Accepted and incorporated herein. Accepted and incorporated herein. Accepted. & 6. Accepted and incorporated herein. Accepted. - 12. Accepted and incorporated herein. Rejected as contrary to the evidence. Accepted. - 17. Accepted and incorporated herein. Accepted. - 22. Not appropriate Findings of Fact. Should be in Conclusions of Law. 23. - 26. Rejected. 27. - 30. Accepted and incorporated herein. 31. - 33. Accepted. Accepted except for last clause. Not a Finding of Fact but a comment on the state of the evidence. Rejected. Not proven. Not a proper Finding of Fact and not supported by authority. Accepted and incorporated herein except that the canal is a Class III water body. Accepted and incorporated herein. Not a Finding of Fact but a Conclusion of Law. Rejected. Accepted. Accepted but not determinative of any issue of fact or law. Ultimate Fact. Rejected. FOR RESPONDENT HUNT Accepted and incorporated herein. & 3. Accepted and incorporated herein. 4. & 5. Accepted and incorporated herein. 6. & 7. Accepted and incorporated herein. 8. - 10. Accepted and incorporated herein. 11. & 12. Accepted and incorporated herein. 13. Repetitive information. 14-1 & 2. Accepted and incorporated herein. Accepted. Accepted and incorporated herein. Accepted and incorporated herein. Accepted and incorporated herein. Accepted and incorporated herein. Accepted and incorporated herein. & 22. Accepted and incorporated herein. Accepted and incorporated herein. - 28. Accepted and incorporated herein. FOR RESPONDENT DEPARTMENT: 1. - 5. Accepted and incorporated herein. 6. - 8. Accepted and incorporated herein. Accepted. Accepted and incorporated herein. Accepted and incorporated herein. Accepted and incorporated herein. Accepted and incorporated herein. Accepted. - 18. Accepted and incorporated herein. Accepted and incorporated herein. Accepted and incorporated herein. & 22. Accepted and incorporated herein. 23. & 24. Accepted. Accepted and incorporated herein. - 31. Accepted and incorporated herein. 32. Accepted and incorporated herein. COPIES FURNISHED: Martin Rosen 672 Jungle Queen Way Longboat Key, Florida 34228 Thomas W. Reese, Esquire 123 Eighth Street North St. Petersburg, Florida 33701 Patricia Petruff, Esquire John V. Quinlan, Esquire Dye & Scott, P.A. P.O. Box 9480 Bradenton, Florida 33506 Cecile I. Ross, Esquire Department of Environmental Regulation Twin Towers Office Building 2600 Blair Stone Road Tallahassee, Florida 32399-2400 Dale H. Twachtmann Secretary Department of Environmental Regulation Twin Towers Office Building 2600 Blair Stone Road Tallahassee, Florida 32399-2400 Daniel H. Thompson General Counsel DER 2600 Blair Stone Road Tallahassee, Florida 32399-2400
