The Issue The issue for determination is whether Jupiter Hills Lighthouse Marina is entitled to be issued a permit by the Department of Environmental Protection for its project application submitted July 29, 1992, and revised November 15, 1993, to enlarge an existing marina and add new slips.
Findings Of Fact On July 29, 1992, Jupiter Hills Lighthouse Marina (Respondent Jupiter Hills) submitted an application to the Department of Environmental Protection (Respondent DEP) for a permit to enlarge an existing dock facility to 488 feet and to increase the existing 6 slips to 48 new slips. Respondent Jupiter Hills is located 0.7 miles north of Martin County Line Road, on U. S. Highway One, Indian River Lagoon, Jensen Beach to Jupiter Inlet Aquatic Preserve, more particularly described as Martin County, Section 19, Township 40 South, Range 43 East, Indian River Lagoon Class III Waters. On November 15, 1993, Respondent Jupiter Hills amended its application at the request of Respondent DEP. The revised proposed project increases the dock facility from 6 slips to 18 slips, restricting 12 of the 18 slips for sailboat use; and proposes a new 149 foot long T-shaped pier from the existing pier, creating a total dimension of 180 feet by 60 feet. Further, Respondent Jupiter Hills proposes to remove four existing finger piers and 10 existing mooring pilings, to add eight finger piers and 34 new mooring pilings, and to place riprap along the existing seawall and new pier. The proposed project is located in an Outstanding Florida Water (a designated aquatic preserve), the Jensen Beach to Jupiter Inlet Aquatic Preserve, which is a part of the Indian River Preserve. Significant water quality parameters for this proposed project include coliform bacteria, heavy metals, and oil and grease. Water quality standards for oil and grease are not being currently met. However, to address this noncompliance, Respondent Jupiter Hills has agreed to include, as part of this project, the installation of an exfiltration trench to trap grease coming from the uplands. This trench will improve water quality, causing a net improvement of water quality in the proposed project area. Stormwater from the area, including a portion of U. S. Highway One and parking areas within U. S. Highway One right-of-way, discharge directly into Respondent Jupiter Hills. This stormwater then drains directly into tidal waters. The exfiltration trench is designed to intercept up to three-fourths of an inch of the stormwater flow currently draining into the basin. The owners of Respondent Jupiter Hills will maintain the exfiltration trench. They have signed a long-term agreement with Respondent DEP for the maintenance of the trench, and the agreement is included in Respondent DEP's Intent to Issue. Water quality standards for fecal coliform are currently being met. The construction of the proposed project will not preclude or prevent continuing compliance with these standards. Respondent Jupiter Hills has proposed a sewage pump-out station which is not currently in the area and which will encourage boaters to pump boat sewage into the city treatment area instead of dumping the sewage into the water. The pump-out station will be connected to the central sewage system, but boaters will not be required to use the sewage pump-out station. However, since liveaboards are more likely to cause fecal coliform violations, Respondent Jupiter Hills has agreed that no liveaboards will be permitted in the proposed project. Water quality standards for heavy metals are currently being met. The construction of the proposed project will not preclude or prevent continuing compliance with these standards. Respondent Jupiter Hills proposes to use construction materials which have not been treated by heavy metals. Also, because the proposed project area flushes in one tidal cycle, any additional metals from the boats themselves would be swept away quickly. The proposed project will not adversely impact or affect the public health, safety or welfare or the property of others. Respondent Jupiter Hills has provided reasonable assurance that water quality standards will be met, continue to be met, and not violated. As a result, the public health and safety are protected. The proposed pump-out facility will reduce the incidences of illegal head discharges into the Jupiter Sound. Thus, this facility will benefit the health and safety of swimmers or others participating in water-related activities in the Jupiter Sound. The proposed project will not adversely affect the conservation of fish and wildlife, including endangered or threatened species, or their habitats. Respondent Jupiter Hills has agreed to several measures designed to reduce any adverse impacts to fish and wildlife and the measures have been incorporated into the Intent to Issue. Respondent Jupiter Hills has agreed to not allow new power boats to dock at the proposed facility, which will prevent adverse affects on the manatee population in the area. Additionally, the proposed pump-out facility will improve the water quality, resulting in a benefit to fish and wildlife, including the Benthic habitat and seagrasses. Respondent Jupiter Hills has further agreed to install navigational signs, directing boaters away from manatees, and no wake signs, indicating the presence of manatees; these signs do not presently exist. Furthermore, Respondent Jupiter Hills has agreed to post signs directing boaters away from any seagrasses located in the proposed project area. Whether seagrasses in the proposed project area will be adversely affected is also a factor to be considered. Inspections and surveys of the proposed project area in December 1992 and mid-March 1993 revealed one patch of Halophila decipiens and Halophila johnsonii at the 100 foot contour but no seagrasses within the footprint of the proposed project. A survey of the area in late April 1994 revealed some seagrasses in the proposed project area but no seagrasses within the footprint of the proposed project. In September 1995, an examination of the area revealed Halophila decipiens just waterward of the existing slips down to the southern property boundaries 20 to 30 feet wide and revealed sparse seagrasses approximately 300 to 500 feet from the shoreline. Halophila decipiens is more abundant and thick in the summer and tends to die off and at its thinnest in the winter. Neither Halophila decipiens nor Halophila johnsonii are threatened or endangered species of seagrasses. The seagrasses provide a significant environmental benefit. The benefits include nutrient recycling in the area and providing habitat for Benthic invertebrates, such as crabs, which are at the bottom of the food chain. Also, other plants grow on the seagrasses, such as algae, and the other plants provide food for other organisms. Manatees eat several seagrasses, including Halophia decipiens but it is not one of the manatees preferred seagrasses. Seagrasses can be adversely affected in two ways. One way is that prop dredging could scar the seagrasses. However, as to the proposed project, the depth of the water in the area of the seagrasses will prevent any adverse affects from prop dredging. The second way that seagrasses can, and will, be adversely affected is being shaded by the proposed dock or by boats tied-up to the dock. The density of the seagrass, pertaining to this proposed project, is thin and low and approximately one percent of actual coverage. In determining whether the proposed project is clearly in the public interest, Respondent DEP uses a balancing test which consists of taking the public interest criteria and weighing the pros and cons of the proposed project. Balancing the adverse impacts on the seagrasses and the positive effects of the public interest criteria, the proposed project is clearly in the public interest. The slips in the proposed project will increase by 12; however, the slips can only be used by sailboats. Since sailboats move slowly, the manatees in the area will not be adversely affected by the proposed project. Neither navigation nor the flow of water will be adversely affected by the proposed project. Further, no harmful erosion or shoaling will be caused by the proposed project. Adequate depths are off of the end of the dock for boats to safely navigate. Shoaling is not a potential problem, and therefore, any potential shoaling which may develop will not adversely affect navigation. The proposed dock will not impact navigation into the Intracoastal Waterway (ICW) because the dock will not extend into the ICW and because Respondent Jupiter Hills will provide navigational aids to guide boaters to access the Atlantic ICW. Furthermore, there is sufficient depth for navigation between the end of the proposed dock and the sandbar where the seagrasses are located. Boat traffic coming from the south will primarily originate from the residences to the south. The proposed dock will force these boaters 200 feet offshore where the natural channel is located. Additionally, the dock will keep boaters further offshore from the riparian land owners to the north, including the Petitioners. To improve the public interest aspects of the project, Respondent DEP proposed that Respondent Jupiter Hills install riprap, which Respondent Jupiter Hills agreed to do. Installation of the riprap will be 367 feet along the perimeter of the proposed dock and in a 10 by 50 foot area along the bulkhead north of the dock. Some shoaling will result but will not affect navigation. The riprap will provide substrate and shelter for marine life. The fishing or recreational values or marine productivity will not be adversely affected by the proposed project. Marine productivity will increase because the sewage pump-out station will improve the water quality which will benefit the Benthic community. The proposed project will be of a permanent nature. Significant historical and archaeological resources will not be adversely affected by the proposed project. The Department of State, which is responsible for historical and archaeological resources, reviewed the Notice of Intent and has no objection to the proposed project. The current condition and relative value of functions being performed by areas affected by the proposed project will be increased and, therefore, benefited. No cumulative impacts are associated with the proposed project. The proposed project is not in an area of pristine shoreline; the area is highly developed. Approximately 1,200 feet to the south of the proposed project is a 270 foot dock with about 50 slips. When considered with the other docks in the area, the extension of the dock in the proposed project will not significantly or measurably further violate the water quality. Respondent Jupiter Hills has provided reasonable assurance that the proposed project is clearly in the public interest.
Recommendation Based on the foregoing Findings of Fact and Conclusions of Law, it is RECOMMENDED that the Department of Environmental Protection issue a final order issuing Permit No. 432170499 to Jupiter Hills Lighthouse Marina. DONE AND ENTERED this 8th day of April, 1996, in Tallahassee, Leon County, Florida. ERROL H. POWELL, 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 8th day of April, 1996. APPENDIX The following rulings are made on the parties' proposed findings of fact: Petitioners Proposed Findings of Fact Partially accepted in finding of fact 1. Partially accepted in finding of fact 3. Partially accepted in findings of fact 1 and 2. Partially accepted in finding of fact 2. Partially accepted in finding of fact 10. Rejected as being irrelevant, or unnecessary. See, conclusion of law 43. Also, partially accepted in findings of fact 19-27, 34-35. Partially accepted in finding of fact 4. Partially accepted in finding of fact 5. Partially accepted in findings of fact 5 and 6. Partially accepted in finding of fact 7. Partially accepted in finding of fact 9. Rejected as being unnecessary. Also, see finding of fact 18. Partially accepted in finding of fact 10. Partially accepted in findings of fact 8, 9, and 10. Partially accepted in finding of fact 9. Partially accepted in findings of fact 12 and 13. Partially accepted in finding of fact 11. See, conclusion of law 46. Partially accepted in findings of fact 9 and 16. Partially accepted in finding of fact 18. Partially accepted in finding of fact 18. Partially accepted in finding of fact 31. Partially accepted in findings of fact 18 and 28. Partially accepted in findings of fact 29 and 30. Partially accepted in finding of fact 31. Partially accepted in finding of fact 33. Partially accepted in finding of fact 9. Partially accepted in finding of fact 37. Partially accepted in finding of fact 36. Rejected as being argument, or a conclusion of law. Rejected as being argument, or a conclusion of law. Partially accepted in finding of fact 23. Partially accepted in finding of fact 23. Partially accepted in finding of fact 24. Rejected as being irrelevant, or unnecessary. Partially accepted in finding of fact 20. Partially accepted in finding of fact 20. Partially accepted in finding of fact 20. Rejected as being irrelevant, unnecessary, argument, or a conclusion of law. Rejected as being irrelevant, unnecessary, argument, or a conclusion of law. Partially accepted in finding of fact 20. Rejected as being irrelevant, unnecessary, argument, or a conclusion of law. Partially accepted in findings of fact 20 and 21. Partially accepted in finding of fact 26. Partially accepted in findings of fact 3 and 20. Partially accepted in finding of fact 20. Rejected as being not supported by the greater weight of the evidence, argument, or a conclusion of law. Rejected as being irrelevant, unnecessary, argument, or a conclusion of law. Rejected as being irrelevant, unnecessary, argument, or a conclusion of law. Rejected as being irrelevant, unnecessary, argument, or a conclusion of law. Rejected as being not supported by the greater weight of the evidence, argument, or a conclusion of law. Rejected as being irrelevant, unnecessary, argument, or a conclusion of law. Partially accepted in findings of fact 19-27. Rejected as being irrelevant, unnecessary, argument, or a conclusion of law. Rejectd as being irrelevant, unnecessary, argument, or a conclusion of law. Rejected as being irrelevant, unnecessary, argument, or a conclusion of law. Rejected as being irrelevant, unnecessary, argument, or a conclusion of law. Rejected as being irrelevant, unnecessary, argument, or a conclusion of law. Respondent Jupiter Hills' Proposed Findings of Fact Partially accepted in finding of fact 1. Partially accepted in finding of fact 1. Partially accepted in finding of fact 2. Partially accepted in findings of fact 1 and 2. Partially accepted in finding of fact 13. Partially accepted in finding of fact 13. Partially accepted in findings of fact 30 and 31. Partially accepted in finding of fact 14. Partially accepted in finding of fact 17. Partially accepted in finding of fact 29. Partially accepted in finding of fact 34. Partially accepted in finding of fact 36. Partially accepted in finding of fact 13. Partially accepted in finding of fact 38. Partially accepted in finding of fact 39. Partially accepted in findings of fact 29, 30 and 33. Partially accepted in finding of fact 31. Partially accepted in finding of fact 15. Partially accepted in findings of fact 4, 5, 8, and 11. Partially accepted in findings of fact 5 and 6. Partially accepted in finding of fact 9. Partially accepted in findings of fact 5, 8, and 9. Partially accepted in finding of fact 9. Partially accepted in finding of fact 9. Partially accepted in finding of fact 9. Partially accepted in finding of fact 16. Partially accepted in findings of fact 9, 14, 15, and 16. Partially accepted in findings of fact 18, 24, and 27. Partially accepted in findings of fact 18 and 28. Partially accepted in finding of fact 28. Partially accepted in finding of fact 18. Partially accepted in finding of fact 22. Partially accepted in finding of fact 21. Partially accepted in findings of fact 20 and 26. Partially accepted in finding of fact 26. Partially accepted in findings of fact 20 and 26. Rejected as being irrelevant, or unnecessary. Rejected as being unnecessary, argument, or a conclusion of law. Partially accepted in finding of fact 27. Partially accepted in finding of fact 27. Rejected as being argument, or a conclusion of law. Rejected as being unnecessary, argument, or a conclusion of law. Rejected as being irrelevant, unnecessary, argument, or a conclusion of law. Partially accepted in finding of fact 25. Partially accepted in finding of fact 33 Partially accepted in finding of fact 33. Partially accepted in finding of fact 40. Rejected as being irrelevant, or unnecessary. Rejected as being irrelevant, or unnecessary. Rejected as being irrelevant, or unnecessary. Partially accepted in finding of fact 10. Rejected as being unnecessary, or a conclusion of law. Partially accepted in findings of fact 27 and 41. Respondent DEP's Proposed Findings of Fact Partially accepted in finding of fact 1. Partially accepted in finding of fact 2. Partially accepted in finding of fact 3. Partially accepted in finding of fact 4. Partially accepted in finding of fact 5. Partially accepted in finding of fact 6. Partially accepted in finding of fact 7. Partially accepted in finding of fact 8. Partially accepted in findings of fact 9 and 10. Partially accepted in finding of fact 11. Partially accepted in findings of fact 12 and 13. Partially accepted in finding of fact 15. Partially accepted in finding of fact 14. Partially accepted in finding of fact 15. Partially accepted in finding of fact 16. Partially accepted in finding of fact 17. Partially accepted in finding of fact 18. Partially accepted in findings of fact 19 and 20. Partially accepted in finding of fact 20. Partially accepted in finding of fact 20. Partially accepted in finding of fact 20. Partially accepted in finding of fact 21. Partially accepted in finding of fact 22. Partially accepted in findings of fact 25 and 26. Partially accepted in finding of fact 26. Partially accepted in finding of fact 26. Partially accepted in finding of fact 27. Partially accepted in finding of fact 27. Partially accepted in finding of fact 28. Partially accepted in finding of fact 29. Partially accepted in finding of fact 30. Partially accepted in finding of fact 31. Partially accepted in finding of fact 32. Partially accepted in finding of fact 33. Partially accepted in finding of fact 33. Partially accepted in finding of fact 34. Partially accepted in finding of fact 35 Partially accepted in finding of fact 36. Partially accepted in finding of fact 37. Partially accepted in finding of fact 37. Partially accepted in finding of fact 38. Partially accepted in finding of fact 39. Partially accepted in finding of fact 40. Partially accepted in finding of fact 41. NOTE: Where a proposed finding of fact has been partially accepted, the remainer has been rejected as being irrelevant, unnecessary, cumulative, not supported by the evidence presented, not supported by the greater weight of the evidence, argument, or a conclusion of law. COPIES FURNISHED: J. A. Jurgens, Esquire Post Office Box 1178 Winter Park, Florida 32790-1178 Timothy C. Laubach, Esquire Sears and Manuel, P.A. 1218 Mount Vernon Street Orlando, Florida 32803 M.Tracy Biagiotti, Esquire Scott Hawkins, Esquire Jones, Foster, Johnston & Stubbs, P.A. Post Office Box 3475 West Palm Beach, Florida 33402 (Attorney for Jupiter Hills Lighthouse Marina) Lynette L. Ciardulli Assistant General Counsel Department of Environmental Protection 2600 Blair Stone Road Tallahassee, Florida 32399-2400 Douglas MacLaughlin Assistant General Counsel Department of Environmental Protection 2600 Blair Stone Road Tallahassee, Florida 32399-2400 Kenneth Plante General Counsel Department of Environmental Protection Douglas Building 3900 Commonwealth Boulevard Tallahassee, Florida 32399-3000 Virginia B. Wetherell, Secretary Department of Environmental Protection Douglas Building 3900 Commonwealth Boulevard Tallahassee, Florida 32399-3000
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
Findings Of Fact The Guana River Marsh Aquatic Preserve (the Preserve) is state-owned property. Title is held by the Board of Trustees of the Internal Improvement Trust Fund. It includes some 13 miles of Atlantic Ocean beach within St. Johns County. Within the boundaries of the Preserve is included the Guana River State Park (the Park). It, too, is state-owned. It is managed and operated by the Division of Recreation and Parks (the DRP) of the Department of Environmental Protection (the DEP). Some of the Preserve's Atlantic Ocean beaches are included within the boundaries of the Park. The "wet sand," or "hard sand," area of the Atlantic Ocean beaches in the Preserve is the area of the beach between mean high water and mean low water. The mean high water line is essentially the landward extent of the ocean at mean high tide; the mean low water line is essentially the landward extent of the ocean at mean low tide. When the tide is low, this entire area of the beach is exposed. It remains wet and, generally, relatively hard-packed during the time it is exposed. However, there are beds of "red shell" in this part of the beach that are softer. In the summer, this part of the beach averages approximately 50 feet in width. In the winter, when the waves and tides generally are higher, it is narrower. In the Preserve, the mean high water line usually is indicated both by debris washed up during the highest tides and left on the beach and by a "shelf." This "shelf," made by the erosive action of the ocean waves during the highest tides and during storms, rises at an angle of approximately 45 degrees and can be from one to four or five feet high. Landward of this shelf is the "dry sand" or "soft sand" beach, also sometimes referred to as the "upper beach." It extends landward from the mean high water line to the vegetation line, where the dunes start. Usually, some pioneer vegetation is found in the uppermost reaches of this part of the beach, forming what is called the "foredune" area of the beach. The tides along the Atlantic Ocean beaches in the Preserve are semi- diurnal, i.e., there usually are two high tides and two low tides a day. These high and low tides last approximately one hour, and each day they occur approximately an hour later than they did the day before. There are five beach access points with motor vehicle parking areas located along U.S. Highway A1A within the Preserve. Three are within the Park. There is parking for approximately 120, 68, 79, 42 and 25 vehicles in these five parking areas. There also is a current proposal for the addition of three more access points in the Park, with parking for a total of 340 vehicles, five beach bathhouses, and five pedestrian overpasses. There are many other places where pedestrians can walk from A1A to the beaches, including 30 County-controlled access points. But there are no lawful parking areas adjacent to any of these other access points at this time, and parking on the right-of-way of A1A is prohibited. Currently, the only lawful motor vehicle access to the Atlantic Ocean beaches in the Preserve is to the south of the Preserve. Prior to the agency action challenged in these proceedings, motor vehicles lawfully could be driven onto the beach at this access point and be driven north into the Preserve, so long as they remained below the mean high water line. A former access near the north end of the Preserve has been cordoned off. To leave the Preserve, motor vehicles would have to be turned around and driven back south to the same motor vehicle access point. Due to the restricted access to the Atlantic Ocean beaches in the Preserve, not much use is made of those beaches. In comparison, beaches to the south are used much more heavily. Of the relatively few who use the motor vehicle access to the south and drive on the beach north through the Preserve, some ultimately use the beaches to picnic, swim, surf, beach-comb and similar activities; some probably just drive on the beach. There was no evidence quantifying the uses currently being made of the beaches in the Preserve. In the past, homemade motor vehicles called "skeeters" were built with a light-weight chassis and over-sized wheels. They were used for driving on both the hard and soft areas of the beaches, as well as illegally in the dunes. This practice has been curtailed due to better enforcement of the prohibitions against driving in the dunes, a generally heightened environmental consciousness among the public, and prohibitions against driving the "skeeters" on public highways. Generally, there has been less driving on the beaches of the Preserve in recent years, although the practice persists at a reduced level. At all times of the year, it sometimes is impossible to drive along the entire length of the beaches in the Preserve without driving on the soft sand area. This is especially true during the winter months when the waves and tides are higher and storms are more frequent. But even in the summer months, there are times when "red shell beds" in the "wet sand" part of the beach must be circumvented to avoid getting stuck. Especially when the tide is not at its lowest, the only way to avoid some of these "red shell" beds is to drive over the "shelf" and onto the "soft sand." Depending on the tides, this may also be necessary in order to turn a vehicle around on the beach. In many places, the "soft sand" area is not very wide, and it would be necessary under those circumstances to drive in the "foredune" area. The times of the daily high and low tides can be obtained relatively easily by members of the public. But there is no assurance that all persons who would drive on the beaches would know the times of the tides. Nor is there any assurance that persons who drive the "wet sand" or "hard sand" part of the beaches at low tide also would plan to both start their beach drive and their return trip during low enough tides to be able to avoid driving on the "soft sand" part of the beach. For these and other reasons, it would be difficult, if not practically impossible, to effectively monitor beach driving throughout the Preserve and consistently enforce a restriction to driving only on the "wet sand" or "hard sand" areas of the beach. In the summer months, sea turtles lay eggs in nests dug in the sand of the foredune and dune areas of the Atlantic Ocean beaches in the Preserve. After a period of incubation in the nests, the turtle hatchlings dig themselves out of the nests and crawl to the ocean to begin their lives in the sea. Driving motor vehicles over nests on those parts of the beaches in the summer months could crush eggs in their nests or pack the sand hard enough to reduce the number of hatchlings that emerge from the nest alive. In addition, driving motor vehicles in these area, even in other parts of the year, can leave ruts in the beach that disorient hatchlings that leave the nests in summer so that fewer reach the ocean alive. Sea turtles crawl out of the ocean to their nest sites at night. Artificial lighting can disturb their nesting and egg-laying activities. However, it seems that moving lights, or lights that turn on and off (in the manner of car lights), create more of a disturbance than stationary lights, such as those more often found at residences along the beaches in the Preserve. The Management Plan does not prohibit artificial lighting along the beaches in the Preserve, but it recommends that further attention be given to this problem and that ways to address the problem be explored and pursued in cooperation with the County. Various shore birds, including the threatened least tern, make their nests in the foredune area of the beaches in the Preserve. Driving on the foredunes destroys and disturbs nesting habitat and disturbs the nesting activities of these birds. In addition, both these ground nesting shore birds and a variety of migratory birds make use of different areas of the beaches to rest and feed. Driving on the beaches disturbs these activities, as well. The only known nesting colony of least terns in St. Johns County is located in the Park, where beach driving is prohibited. The Division of Parks and Recreation (DPR) of the Department of Environmental Protection (DEP) has utilized F.A.C. Rule 16D-2.002(4)-(5) to prohibit driving or parking motor vehicles on the beaches of the Park by not designating the beaches as driving or parking areas within the Park. At least parts of the beaches in the Park have been posted as areas where driving motor vehicles is prohibited. In order to develop a management plan for the Preserve, the manager of the Preserve personally researched the geology, climate and natural resources of the Preserve, as well as the records of the County, and also collected data pertaining to the Preserve from several state agencies. Over the course of a year, the manager's input was taken into consideration, and a management plan, called the Guana River Marsh Aquatic Preserve Management Plan (the Management Plan), was developed for the Preserve. It was adopted by the Board of Trustees of the Internal Improvement Trust Fund on December 17, 1991. The Management Plan recites in pertinent part: At the present time, motorized vehicular traffic is permitted, by county ordinance, below the natural vegetation line on the beaches adjacent to the Atlantic Ocean in St. Johns County. Vehicles are not allowed on the 4.2 miles of beach within Guana River State Park. The coarse coquina sand and steep profiles of the beaches in the preserve make driving on the wet sand area difficult. Drivers are forced to cross the dry sand area, damaging the foredunes, pioneer dune vegetation and sea turtle nesting habitat. Due to the negative environmental impacts resulting from this activity, motorized vehicular traffic shall not be considered an authorized activity on sovereign submerged lands within [Prime Resource Protection Area] PRPA beach management areas of the preserve, and therefore will be prohibited. Under the Management Plan, all of the Atlantic Ocean beaches in the Preserve are Prime Resource Protection Area, and the driving of motorized vehicles on them is prohibited. On June 11, 1993, the DEP's DRP sent St. Johns County a letter advising that, based on the Management Plan, DEP no longer would permit the driving of motor vehicles on the Atlantic Ocean beaches in the Preserve. The proposed amendment to F.A.C. Rule 18-20.004(7), incorporating the Management Plan, was noticed in the Florida Administrative Weekly on August 6, 1993. On or about August 18, 1993, the DEP agreed not to enforce the beach driving prohibition in the Preserve until these cases are resolved.
The Issue The issue to be determined in this case is whether proposed Florida Administrative Code Rule 40E-10.041(3)(d) of the South Florida Water Management District (“the District”) is an invalid exercise of delegated legislative authority.
Findings Of Fact The Conservancy is a non-profit Florida corporation with its offices in Naples, Florida. It has 6,200 members residing in Southwest Florida. The mission of the Conservancy is to protect the environment and natural resources of Southwest Florida. The Caloosahatchee River is an important focus of the Conservancy’s organizational activities and objectives. A substantial number of the members of the Conservancy use the Caloosahatchee River for drinking water, boating, fishing, wildlife observation, and scientific research. The proposed rules create a prospective reservation of water in the not-yet-operational Caloosahatchee River (C-43) West Basin Reservoir “for fish and wildlife.” The Conservancy’s interests would be substantially affected by the proposed reservation. The District is a regional water management agency created, granted powers, and assigned duties under chapter 373, Florida Statutes (2013). It is headquartered in West Palm Beach, Florida. Proposed rule 40E-10.041(3) states: (3) Caloosahatchee River (C-43) West Basin Storage Reservoir: All surface water contained within and released, via operation, from the Caloosahatchee River (C-43) West Basin Storage Reservoir is reserved from allocation. The water reserved under this paragraph will be available for fish and wildlife upon a formal determination of the Governing Board, pursuant to state and federal law, that the Caloosahatchee River (C-43) West Basin Storage Reservoir is operational. The reservation contained within this subsection and the criteria contained in section 3.11.4 of the Applicant’s Handbook for Water Use Permit Applications within the South Florida Water Management District, incorporated by reference in Rule 40E-2.091, F.A.C., shall be revised in light of changed conditions or new information prior to the approval described in paragraph (3)(b) above. Pursuant to subsection 373.223(4), F.S., presently existing legal uses for the duration of a permit existing on [RULE ADOPTION DATE] are not contrary to the public interest. The Conservancy challenges only paragraph (3)(d), contending that it modifies or contravenes the implementing statute, section 373.223(4).
Findings Of Fact Petitioner, JOHN C. GROSS, a citizen and resident of Edgewater, Florida, owns approximately 114 acres of submerged and semisubmerged land, which at times extends from 3 to 9 feet above the water and which lies in the near vicinity of Ponce de Leon Inlet, New Smyrna Beach. His property is located due southwest of the inlet and west of the Intracoastal Waterway. The Intervenor, FRANCES TURNER PRICE, is the owner of an oceanfront house and lot located at 2113 Ocean Drive, New Smyrna Beach, Florida, which is directly adjacent to and west of a portion of the proposed spoil disposal area referenced herein. The Ponce de Leon Inlet was first dredged by the COE in 1968, pursuant to a 1965 Act of Congress, and has been dredged periodically since that time. No dredging has taken place there since March, 1978. During the past several years, numerous complaints have been received by the COE from users of the waterway concerning the increased clogging of the inlet channel. These users include operators of relatively large boats, such as commercial fishermen and shrimpers, large yacht owners, and the United States Coast Guard, which maintains and operates a station in the area. Based on these complaints, Mr. Aston, COE Navigation Branch, caused an investigation to be made which revealed an extensive and worsening shoaling which, if not corrected, would further reduce the channel opening. This investigation included several hydrographic surveys using Fathometers (accomplished in November, 1952, and subsequently thereto). The channel, which runs basically east and west from the Intracoastal Waterway to the Atlantic Ocean, is currently navigable (but not safely) by larger draft vessels such as are described above. Because of the prevailing winds from the northeast, larger vessels come in from the northeast; have to come around the jetty, which juts into the ocean north of the channel; and then have to stay close to the jetty to avoid the heavy shoaling in the dredged channel originally in the center of the inlet. 1/ This is dangerous because sport fishermen are frequently anchored in the water just south of the jetty, in the way of the boats going in and out. This danger is compounded by the fact that boats going in and out cannot see each other, because of the jetty to the north and the land to the south, until they both are committed to the channel. Therefore, once in and committed, they are in danger of collision because of the narrowness of the passage and the need to avoid the small fishing boats anchored therein. As a result, the original channel, which provides safer passage, needs to be dredged again immediately to prevent more groundings and collisions with resultant loss of life and property damage such as the 50 which have already occurred there within the past 15 months. In the opinion of Mr. Aston, the situation in the Ponce de Leon Inlet, as it pertains to shoaling, is the worst he has seen in any federal channel in 19 years. It is for these reasons that during the 1982-83 time frame, the COE decided to seek permission to proceed with a dredging project. Initially, three different areas were considered for disposal of the 800,000 or so cubic yards of spoil which would result from the dredging. These were: off the beach north of the north jetty; just south of the weir to which the north jetty is attached; and the beach area approximately one mile south of the inlet. For various reasons, Options (a) and (b) were rejected, and Option (c) was the area then intended for the spoil disposal. The initial application, submitted on November 10, 1982, called for the spoil to be transported by pipe over easements down the beach to the disposal area, where it would then be dumped on the beach to fill in the area of beach eroded and eroding. However, because of public objection to that plan, the COE agreed with the local beach advisory board to move the spoil 1,000 feet offshore to an area approximately 800 feet by one mile long, adjacent to the beach approximately one mile south of the inlet. In any event, both the original application and the amendment thereto (to change the location of the spoil disposal area) called for only one procedure--not multiple dredgings and disposals. This proposed permit, which is objected to by Petitioner and Intervenor, indicated permission for more than one procedure. Intervenor protests this even if permission is to be given for the initial dredging. However, Dr. Collins, from DER, indicated that since a determination was made that the action would have no adverse impact on the environment, there was nothing wrong with giving permission for multiple dumpings. In fact, the Notice of Intent to Issue contains Provisions for monitoring the turbidity caused by the operation and also provides for DER modifications to the conditions or other provisions of the permit as necessary, and recognizes COE's assurances that the immediate and long-term effects of the project will not violate state water quality standards. The spoil, which consists almost exclusively of beach quality sand and which is highly valuable, will be laid down in a berm-shaped deposit the top of which will, at low tide, be no less than 6 feet below the surface of the water. In that configuration, it could not be seen from shore and would in no way impede navigation. The decision to dispose of the spoil in this fashion was made partially on the basis that it would tend to put sand back on the eroded beach in the area. Intervenor theorizes that the spoil (sand and water) will not form this neat berm, but will spread out when it comes out of the dredge pipe below the surface of the water. COE indicates that the contractor on this project will use some sort of a buffer to contain the spread upon discharge. It is anticipated that this project will have to be repeated again and again to keen the channel clear. Though the 800,000 cubic yards anticipated for removal on this occasion is great, so much has never been taken out here at one time before. This is because, as was stated previously, the last dredging was in March 1978, and COE estimated that dredging should take place every 16 months or so. If done on that schedule, succeeding dredgings will be of a far less significant amount. Petitioner, whose profession is as a real estate developer, but whose avocation is as a conservationist of marine life, contends he has been involved in environmental research and protection all his life (he is at least 70). He has, he states, developed several environmental concepts which have, he contends, never been disproved. They are not, however, enjoying widespread acceptance, either, though he contends the Rosenstiel School at the University of Miami has said his environmental concepts are sound. This well may be so; however, Mr. Gross neglected to produce any evidence as to what these concepts are or indications of their soundness. Though he admits to having no formal training in any of the sciences or in engineering, and his research consists of bathing and fishing in the area (he uses a device to gather bait which results in his picking up a part of the sea bottom) he has published. The Petitioner's publication introduced into evidence consists of the reward notice reproduced herein. $2,000 REWARD To make the public aware of hypocritical groups who mislead and misinform the public about environmental protection, I will donate $1,000 to the first organization, agency, student or individual who produces evidence to prove beyond reasonable doubt that excessive nutrients consisting of mangrove leaves and pods, algae, slime, scum, silt and bacteria, and decaying bodies of all types of insects and creatures emanating from mangrove swamp area DOES NOT cause destruction of shellfish and all forms of marine plant life when infused in excessive amounts into rivers and estuaries by extremely high tides and heavy rainstorms. $1,000 to the first organization, individual, or student who provides evidence to prove beyond reasonable doubt that recent high tides caused by full moon and heavy rains washing through mangrove swamps DID NOT cause most of the crabs, shrimp, and fish to be destroyed or leave this area when the river became polluted with all types of slime, scum, silt, sludge, and mangreve debris, and droppings of birds and animals and all types of decaying material from the mangrove swamps carried into the river by the tide. John C. Gross PO Box 596 New Smyrna Beach, Fl 32069 Though Petitioner was offered the opportunity by the Hearing Officer to submit additional publications when he indicated he had many and was reminded of this later in the hearing by the Hearing Officer, none were forthcoming. Petitioner professes to be very familiar with the area where the dredging and disposal are to take place, and no doubt he is. He contends the area is in a constant state of change, differing from month to month, and populated by a sea life consisting primarily of shellfish, shrimp, and fish. The beach in the area proposed for disposal, he contends, has already built out some 400 to 500 feet since the jetty was built and has naturally built up dunes which, in his opinion, are due to the COE dredging in the past. This beach buildup is a concern of the Intervenor, as well, who indicated that she can no longer see the ocean from her "oceanfront" house due to the large dunes that have built up between her house and the ocean during the years since the construction of the jetty. She is also fearful that the spoil dumped offshore of her property will come ashore there and add to the already expanded beach. Her concerns and those of her neighbors, including Mrs. Speer, who testified in support of Intervenor's position, include the blocked view already mentioned, the fact that the higher dunes are difficult for older people to climb, the fact that it is further to the water with the new sand, and the concern over who will own the new land built up seaward of the vegetation line. 2/ People are already building closer to the water than she did, blocking her lateral view; and all of this will have, she fears, a negative impact on the value of her property. It is without question that dunes have built up and beach area has accreted since the jetties were put in. This is explained by Dr. Dean as a relatively temporary situation resulting from the movement ashore of a preexisting tidal shoal, formerly located outside the entrance to the Ponce de Leon Inlet, which was destroyed by the interruption of the wave action when the jetty was built. The sand from this shoal came ashore at and around the Intervenor's property, as well as north and south of it, adding to the beach and building the dunes. This accretion has stopped, however, and even reversed, and a beach erosion has begun. In any case, according to Dr. Collins of DER, accretion is not usually a consideration in the decision-making process regarding a permit of this nature. Petitioner indicated his understanding that the spoil was to be deposited 3 feet deep over the bottom in the disposal area and believes this will destroy marine life. As will be seen later, competent expert testimony clearly disproves this one theory. He also does not believe anyone can predict where the spoil will settle, but wherever that is, in his opinion, it will have a devastating effect both on the marine life in the area and on the adjacent beaches. He questions the COE's representation that because of the literal drift's prevailing direction from north to south, the spoil will ultimately settle south of the spoil dumping area. Expert testimony, discussed in detail below, will indicate the correctness of the COE's representations. Petitioner further contends that insufficient surveys have been made of the area. In his opinion, the two or three borings that have been done (in actuality, there were more) are not sufficiently extensive since the area in question is too broad and the bottom is not uniform. Therefore, many more borings are needed, he urges, to accurately determine the makeup of the sea bottom. This bottom makeup has an effect on water quality. Sludge, slime, and silt adversely affect water quality. Clean sand is acceptable. However, Petitioner feels that the dredging proposed may, if the bottom where they dredge is of peer quality, be very bad for the bottom in the deposit area. In that regard, it has been shown that the tests done already indicate that the material to be dredged out of the channel is beach quality sand. Other evidence, in the form of samples of the bottom taken in the disposal area, show it is made up of sand with small shells. In neither location is there any evidence of silt, sludge, or slime. In fact, the expert testimony indicates clearly there would be no damage to water quality in either area. A more comprehensive discussion of this subject will be presented below. Petitioner also fears for the manatees and the sea turtles which sometimes come into the area. The expert testimony to be discussed further below readily shows these fears are groundless. It would appear that there may be some reason for Petitioner's interest in this project other than the stated environmental and ecological concerns stated above. By his own testimony, he revealed he had offered to buy this highly valuable 3/ spoil for $400,000. Mr. Aston, of COE, further testified that as late as one week prior to this hearing, Petitioner called him and indicated the matter could be disposed of quite easily if the COE would put the spoil on his property. The Notice of Intent to Issue and the permit to which it relates are not for a one-time dredge. The permit will be for 5 years, but it 15 subject to extension by letter for an additional 5 years. In the analysis of the application, the environmental concerns and the concerns of the public were not taken lightly. The DNR, by letters dated March 9 and June 28, 1983, expressed its lack of objection to the proposal and granted the authority required under Section 253.77, Florida Statutes. The contract is to begin in September, 1984, and be completed by April, 1985. These months were chosen because (a) they take advantage of the northeast winds prevailing then; and (b) there is no sea turtle nesting during this period. Consequently, there would be no risk of harm to the sea turtles. In addition, the risk of harm to the manatees is minimal. They, as a rule, do not frequent these waters, preferring the quiet backwaters of the rivers and bays to the fast moving waters of the channel or the ocean, and they are generally fast enough to avoid both the dredge and the dump. To be doubly safe, however, the contract calls for a "manatee watch" to be conducted and a log kept of all manatees sighted. Another area covered in the contract is water turbidity. Turbidity will be monitored and actions taken to maintain state water quality standards outside the mixing zone--that area inside of which the water temporarily does not meet state standards and outside of which it must. In this case, this zone would extend not more than 150 meters from each point of interest. COE's application contained reasonable assurances that the state's turbidity standards would not be exceeded more than 150 meters from both the dredge and spoil areas. Tests already run on anticipated turbidity show a rapid (4-minute) settlement out due to the fact that the substance being dredged is heavy sand, not light silt. Continuing with an analysis of the impacts of the project which cannot be avoided, on life in both the dredge and the fill areas, it is seen that: Some nonmobile animal life attached to the sea bottom (worms, etc.) in the spoil area which cannot escape being covered by the spoil will be killed. Some sea life sucked up by the dredge and moved will be killed even though they are dumped back into the water in the spill area. However, wherever some death occurs, it will be individuals, not entire populations, and the dump area will be quickly repopulated by sea life from the surrounding area in addition to the live population brought through the pipeline. Full repopulation can be expected within six months. In a more detailed discussion of the disposal site, it is clear that because of the wave action and the hard bottom, one would expect no grass beds, and there are none, nor are there any natural reefs. A survey of the bottom in the disposal area was done by utilizing loran to accurately locate 12 stations throughout the spoil disposal area with three samples to be taken at each site. At seven of the twelve stations, the scientists found the bottom hard and no sample was produced. At only one of the stations, Station 6, some samples were gathered, and what was acquired was very similar to the surf area near the shore. Dr. Atmar admits that the dumping will create some damage to the bottom life and repeated dumping may have a cumulative effect. However, since, as was stated above, complete repopulation can be expected within six months, the damage caused by dredging and dumping every 16 months, even of large amounts of spoil, will be, in his words, "inconceivably insignificant," and that which does occur will be short-lived. Turning then to the question of the impact of the spoil disposal on the beach property adjacent to the disposal area, Dr. Dean explained the prospective results, as well. In conjunction with other experts in sediment transport and based on at least 20 years of accumulated documentation, he developed a model which, when applied to a given situation with variables, can generally permit accurate predictions of what will happen. Applying this model to the dredging area, it is seen that the primary factor which leads to sediment transport here is the wave action which primarily comes from the northeast. This will transport sediment from the north to the south. When the present channel was dug, it interrupted the normal cycle, which, in an attempt to return to the natural flow, fills up the channel. This necessitates new dredging. Applying the model to the disposal area, again the waves play an important part. Based on all available pertinent information, the spoil deposited would generally transport to the south with a very minor amount, + 5 percent going west and another + 5 percent going north. Both the westward and the northward movement would be very slow. The remaining 90 percent of the spoil would move to the south and would reach the shore a mile or two south of the southern boundary of the proposed disposal area. Of this 90 percent, 50 percent would reach the beach within three to four years--the remainder would take longer. The amount of deposited spoil that would go due west to the adjacent beach would be less than would accrete during the normal seasonal accretien. What is more, the proposed disposal activity would have an imperceptible effect on the elevation of the dunes which already exist. The difference between Dr. Dean's estimate of 10 Percent drift to the north and west and COE's estimate of 20 percent sand drift in those two directions is not significant. Both are estimates, and not specifics. As was stated previously, the spoil in question here is a highly valuable beach quality sand with no evidence of muck, slime or silt. If it were to be deposited further out to sea than is proposed here, where the wave action could not get to it, it would be lost to the littoral transport action and would never come to the beach. This would result in the loss of a high quality resource to the beach in an area to the south where the beach is in need of replenishment, and further beach erosion to the south where the existing dunes are eroding due to the effect of the building of the previously mentioned jetty and because of the worldwide rise in the sea level. Admitting he was hired to testify by the COE after the decision was made as to where to deposit the spoil, Dr. Dean contends that had he been asked where to put it before the decision was made, he would have recommended a site closer to shore, but at the same latitude.
Findings Of Fact Because of a 1984 Thanksgiving Day storm which inflicted damage in coastal areas, Barry Manson-Hing, an area engineer employed by the Department, issued emergency coastal construction permits from a temporary office in the Vero Beach Administration Building. On December 3, 1984, Respondent sought an emergency permit to allow him to place sand and sand-filled bags on his coastal property at 3755 Ocean Drive, Vero Beach, Florida. Respondent asked Mr. Manson-Hing if he could use sand from the beach to restore eroded areas. Mr. Manson-Hing said he could not, and told him that sand would have to be obtained from an upland source. Respondent replied that he had an available source of upland sand and would haul it by truck to the beach site. He also mentioned that he would remove an existing pine tree to allow vehicular access. On the next day, December 4, 1984, Mr. Manson-Hing issued an emergency coastal construction permit, #1R-127E, to Respondent. The permit allowed Respondent to place 1,500 cubic yards of sand fill material to restore eroded beach and dune areas at the site, and also permitted him to temporarily place sand-filled bags on filter cloth. In capital letters, the permit warned, "SCRAPING OF THE BEACH IS PROHIBITED." (Dept. Exhibit 4) On December 5, 1984, Lt. Raymond Barker of the Vero Beach Police Department, observed beach scraping activities being conducted on Respondent's coastal property. Respondent was present on the site. Beach sand seaward of the Coastal Construction Control Line for Indian River County had been scraped and deposited at the face of the sand dune. The removal of the sand created depressions in the beach area seaward of the Coastal Construction Control Line. Lt. Barker ordered Respondent to cease the activity until it could be determined he had the required authorization. Respondent complied with Lt. Barker's order. The scraping of the beach and removal of sand below the coastal construction control line was accomplished without a permit from the Department. On July 17, 1985, the Department entered its "Final Order" assessing Respondent a $500 fine for unauthorized coastal construction activities in violation of Section 161.054, Florida Statutes (1985). Respondent requested a hearing; resulting in this proceeding.
Recommendation Based on the foregoing, it is RECOMMENDED: That the Department assess, impose, and collect an administrative fine of $500, to be paid within 30 days of final agency action. DONE AND ORDERED this 20th day of June, 1986, in Tallahassee, Florida. R. L. CALEEN, JR. Hearing Officer Division of Administrative Hearings The Oakland Building 2009 Apalachee Parkway Tallahassee, Florida 32301 (904) 488-9675 Filed with the Clerk of the Division of Administrative Hearings the 20th day of June, 1986.
The Issue The issue for determination is whether Petitioners are eligible for a permit, pursuant to Section 161.053, Florida Statutes, for construction seaward of the Coastal Construction Control Line in Broward County, Florida.
Findings Of Fact On November 30, 1993, Vander Ploeg and Associates, Inc., on behalf of Paul Leto, Richard Meyer, and Berta Anderes (Petitioners) submitted an application to the Florida Department of Environmental Protection (Respondent) for a permit to perform construction on their property seaward of the Broward County Coastal Construction Control Line. Respondent deemed their application complete on April 18, 1994. Petitioners proposed construction will be seaward of the Coastal Construction Control Line. The proposed construction will occur on two adjacent lots in Broward County. Petitioner Leto is the owner of one of the lots described as Lot 19, Block 196, Hollywood Central Beach, Plat Book 4, Page 20, Public Records of Broward County. Petitioners Meyer and Anderes are the owners of the other lot described as Lot 20, Block 196, Hollywood Central Beach, Plat Book 4, Page 20, Public Records of Broward County. Petitioner Leto purchased his lot in September 1992 and Petitioners Meyer and Anderes purchased their lot in March 1993. The lots were platted in or around the 1920's. Both lots are seaward of the seasonal high water line, on a sandy beach with no frontal dune structure. They are bordered by the Atlantic Ocean on the eastern most side and by a roadway (Surf Road) which is immediately adjacent to the lots on the western most side and landward of the lots. Approximately 200 feet north of the lots is an existing structure and approximately 800 feet south of this first existing structure is another existing structure. Petitioners topographical survey, which was submitted to Respondent in December 1993, showed that Lots 19 and 20, each measured 40 feet in a shore parallel direction and 80 feet in a shore normal direction, i.e., perpendicular to the shoreline. The proposed structure will be located directly on the sandy beach. The City of Hollywood, Florida has granted Petitioners a variance. Further, the proposed construction complies with the rules, zoning regulations, and ordinances of the City of Hollywood. Petitioners' application requests a permit for the construction of a single-family residence on the lots, which will house two families. However, the proposed construction is for a duplex, not a single-family residence. Petitioners are willing, and agreeable, to changing the design of the proposed structure to comply with Respondent's specifications for a single- family residence. Additionally, the proposed construction includes a riprap which will also be located on the sandy beach. A riprap is typically used for protective armoring. No structure presently exists for the riprap to protect. Furthermore, the riprap proposed by Petitioners is not adequately designed as a coastal protection structure, and if the proposed single-family residence is modified in accordance with Respondent's specifications, the proposed modified single-family residence would not be eligible for coastal armoring. The riprap structure is not an integral part of the structural design. Petitioners are willing, and agreeable, to eliminating the riprap structure. No other issues exist as to the structural integrity of the design of the proposed project. The lots on which the proposed structure will be located are a part of the beach-dune system. The natural function of the beach provides protection to upland property. The lots on which the proposed structure will be located are subject to normal storm-induced erosion. Tide and wave forces will impact the proposed structure during storms of minor intensity, including five-year storms. The proposed structure will induce greater erosion on the lots as a result of scour due to the interaction of the storm waves and currents with the proposed structure. During the storm, the normal storm-induced erosion combined with the scour erosion will form a breach or depression in the subject property. In turn, the upland property will be exposed to greater tide and wave forces, increasing the risk of erosion and damage to the upland property. The subject lots and surrounding properties have been subjected to unnatural forces which have added to the erosion. The Port Everglades inlet has inhibited the natural downdrift of sand. The City of Hollywood's beach maintenance division has been regularly pushing sand seaward and in the process, breaking down natural forming cliffs. Even though these unnatural forces are capable of being eliminated, the normal storm-induced erosion and the scour erosion would still exists. The existing developed structures to the north and south of the subject lots appear to create a reasonably uniform line of construction. However, the developed structures have been unduly affected by erosion. The proposed structure will be located within this line of construction. During a major storm along the shoreline, waves remove sand from the beach and dune area and deposit the sand in an offshore bar. After the major storm, a recovery of the beach and dunes takes place. Normal wave activity carries the sand from the offshore bar back to the beach, and the sand is then carried landward by winds and is caught and trapped by dune vegetation; thereby reforming a dune. Constructing the structure as proposed will not locate the structure a sufficient distance landward of the beach-dune system. As a result, the proposed structure will interrupt natural fluctuation in the shoreline and not preserve the natural recovery following the storm-induced erosion. The cumulative impact on the beach-dune system by the proposed structure would be severe, i.e., the effects on the beach-dune system by repeating this same proposed structure along the subject shoreline would be severe. There would be structure-induced scour and general degradation of the beach-dune system. Additionally, the recovery potential of the subject area following a major storm event would be threatened. Over the years, the beach of the subject property has been subjected to a re-nourishment project consisting of pumping sand from offshore. This method of re-nourishment may have negatively impacted the sand bar system immediately offshore affecting the hindrance of erosion. A sand bar system immediately offshore softens wave action on the shore and aids in inhibiting erosion. The proposed structure will hinder lateral public beach access. Currently, lateral beach access exists along the beach between the existing northern developed property and the existing southern developed property. The proposed structure will be located on the sandy beach, and the seaward face of the proposed structure will be within approximately one foot of the wet sand beach. At times, the proposed structure will be surrounded by water on at least three sides. No alternative beach access would be available. The proposed riprap will also be located on the sandy beach and will further hinder lateral public beach access. 2/ Loggerhead turtles, which are nesting marine turtles, engage in nesting activities along the stretch of beach where the subject property is located. They are a threatened species, i. e., close to extension. Although they do not nest every year, the turtles usually provide several nests in a single year. Typically, one hundred eggs comprise a turtle nest. In 1992, approximately 2,221 loggerhead turtle nests were in Broward County, with 22 of these nests located within 1,000 feet of the subject property. Turtle nesting efforts have been observed in the beach area of the subject property. One nest was found within the subject property. Structures located on the sandy beach interfere with marine turtle nesting habits. If female turtles make contact with the structures, they often abort nesting attempts, which results in false crawls. Repetitive false crawls harms successful nesting, which may cause malformed egg chambers, impacting the successful incubation of the nest. Also, interaction with a structure can cause injury or death to a female turtle attempting to nest. Additionally, urbanization activity and lighting on the beach deter nesting. A loss of marine turtle nesting habitat will result if the proposed structure is constructed. Also, armoring, such as the proposed riprap, can result in nests being placed more seaward. 3/ Consequently, the nests would be threatened with tidal inundation, which would affect the mortality of the nest itself. As one nest has been located within the subject property, at least one nest or crawl per year would be affected by the proposed structure. Within 30 years, the proposed structure will be seaward of the seasonal high water line. The location of the proposed structure is seaward of the 30-year erosion projection for the subject property. Beach Defense Fund, Inc. (Intervenor) presented no evidence to show that its interest is different than the public at large and that it has substantial interest separate and apart from the public.
Recommendation Based on the foregoing Findings of Fact and Conclusions of Law, it is RECOMMENDED that the Department of Environmental Protection enter a final order denying the application of Paul Leto, Richard Meyer, and Berta Anderes for a permit, pursuant to Section 161.053, Florida Statutes, for construction seaward of the Coastal Construction Control Line in Broward County, Florida. DONE AND ENTERED this 31st day of May, 1996, in Tallahassee, Leon County, Florida. ERROL H. POWELL, 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 31st day of May, 1996.
The Issue The issues to be determined are whether the U.S. Army Corps of Engineers (“Corps”) has demonstrated its entitlement to place dredged material from the maintenance dredging of the East Pass (“East Pass” or “inlet”) entrance channel conducted pursuant to Department of Environmental Protection (“DEP”) Permit Modification No. 0288799-006-JN (“Permit Modification”), as amended by the DEP’s August 21, 2019, Notice of Proposed Changes to Proposed Agency Action (“Proposed Change”) in the nearshore zone east of East Pass; and whether the East Pass Inlet Management Plan (“East Pass IMP”) is an unadopted rule as described in section 120.57(1)(e), Florida Statutes.
Findings Of Fact Based upon the demeanor and credibility of the witnesses, the stipulations of the parties, and the evidentiary record of this proceeding, the following Findings of Fact are made: The Parties Petitioner, Thomas Wilson, resides at 856 Edgewood Drive, Charleston, West Virginia, and owns a secondary residence at 1530 Miracle Strip Parkway, No. 101-B, Fort Walton Beach, Florida, which is on Santa Rosa Island in the unincorporated community of Okaloosa Island1, and fronts the Gulf of Mexico. Petitioner’s property is in the vicinity of Monument R-14, which is roughly 2.3 miles west of DEP Virtual Monument V-611, and 4.3 miles west of the west side of East Pass. Mr. Wilson uses and enjoys the gulf-front beaches between his property in Okaloosa Island and East Pass. Intervenors, David H. Sherry and Rebecca R. Sherry, own Unit 511 at the Surf Dweller Condominium, 554 Coral Court, Fort Walton Beach, Florida, fronting the Gulf of Mexico and in the Okaloosa Island community. 1 Okaloosa Island is the name of an unincorporated community that stretches about 2.8 miles along Santa Rosa Island from DEP reference monument R-1 through R-16, and is across Santa Rosa Sound from the mainland community of Ft. Walton Beach. Okaloosa Island is the name of the unincorporated community, while Santa Rosa Island is the name of the much longer island of roughly 40 miles in length, which includes U.S. Air Force/Eglin AFB property that extends from the Okaloosa Island community to East Pass. The Surf Dweller Condominium straddles DEP Reference Monument R-7, which is between three and four miles west of DEP Virtual Monument V-611, and is between five and six miles west of the west side of East Pass. The Sherrys use the beach at their condominium on a daily basis for fishing, crabbing, swimming, walking, running, and general recreation. They also walk or run from Monument R-7 along the beaches to East Pass, and occasionally drive to and use the beaches on the east side of East Pass. Intervenor, John S. Donovan, owns Units 131 and 132 at the El Matador Condominium, 909 Santa Rosa Boulevard, Fort Walton Beach, Florida, fronting the Gulf of Mexico and in the Okaloosa Island community. The El Matador Condominium is approximately five miles west of Monument V-611, and is more than six miles west of the west side of East Pass. Mr. Donovan generally walks the beaches west of his condominium, but does occasionally walk along the beach to Monument V-607, which is the location of a seawall constructed by the Air Force on sovereign submerged lands to protect an Air Force tracking facility. Petitioners’ residential properties do not abut either the area established as the zone of influence of East Pass or the stretch of beach that is adjacent to the west fill placement site. Petitioners’ stated injuries are related to the allegation that the lateral movement of sand from the East Pass area of influence is from east to west. Placing dredged material in the eastern disposal site would allegedly deprive the beaches in front of their property -- beaches that are miles from the nearest area of influence or spoil disposal site -- of their natural sand supply by cutting off what they allege to be the natural sand flow, causing the beaches in front of their properties to eventually erode. Petitioners alleged no immediate environmental injuries associated with the Permit Modification. Petitioners’ stated objective in this case is to have any sand dredged from East Past to be placed on the western disposal areas at all times. Respondent, DEP, is an agency of the State of Florida pursuant to section 20.255, Florida Statutes, having the power and duty to protect Florida's air and water resources and to administer and enforce the provisions of chapters 161, 373, and 403, Florida Statutes, and rules promulgated thereunder in Florida Administrative Code Chapters 62 and 62B, regarding activities in surface waters of the state. DEP has been designated by the legislature as the beach and shore preservation authority for the State of Florida and is authorized to take all necessary initiatives to implement the provisions of chapter 161. See § 161.101, Fla. Stat. DEP is the permitting authority in this proceeding and issued the Permit Modification at issue in this proceeding to the Corps. Respondent, the Corps, is a federal agency responsible for maintenance dredging of East Pass, and is the applicant for the Permit Modification. The Corps and DEP are parties to an Interagency Agreement pursuant to which the Corps has agreed that for joint coastal permits, beach compatible dredged material shall be disposed on Florida’s beaches consistent with chapter 161 and other beneficial use criteria specified by the Department and federal standards. Pursuant to the Interagency Agreement, if DEP determines that a permit modification is required to meet state standards, as was the case here, the Corps agrees to apply for and obtain the modification. Intervenor, Destin, is a municipality in Okaloosa County, Florida, and abuts the east side of East Pass. Intervenor, Okaloosa County, is the local sponsor of the federally authorized East Pass Navigation Project. It has a substantial interest in the safety and navigability of the East Pass Navigation Channel and its protection from effects of tropical storm systems. Okaloosa County also has a substantial interest in preserving its recreational and environmental resources. The Permit Modification was issued on November 14, 2016, without publication, or a notice of rights language regarding the right to request a hearing or time limits for doing so. Petitioner, Mr. Wilson, alleged that he received a copy of the Permit Modification on or after May 22, 2019. There was no evidence to the contrary. He, thereafter, filed a challenge with DEP on June 5, 2019, no more than 14 days from the date on which he received notice. East Pass The issue in dispute in this case, as it was in 19-1844, is the determination of whether beaches adjacent to the East Pass inlet are eroding, stable, or accreting, for purposes of meeting the statutory objective of section 161.142. Prior to 1928, the connection from Choctawhatchee Bay to the Gulf of Mexico flowed through what is now Old Pass Lagoon. After a storm in 1928, a high-tide breach of the shoreline near the current location of East Pass was formed. In 1929, a record rain event caused waters to rise in Choctawhatchee Bay. Residents of the area dug a relief channel at roughly the present location of East Pass. The waters releasing through the more hydraulically efficient flow path from Choctawhatchee Bay established a channel, which quickly enlarged to become the prominent inlet to the Gulf of Mexico. The permanent channel, now known as East Pass, is the only navigable passage from Choctawhatchee Bay and the Intercoastal Waterway to the Gulf of Mexico between Panama City, Florida, and Pensacola, Florida. East Pass separates the gulf-fronting beaches of Destin to its east from the beaches owned by the United States as part of Eglin Air Force Base to the west. The entrance to East Pass is protected by two boulder-mount jetties: a 3,860 foot-long jetty on the west side of the inlet, and a 1,210 foot-long jetty on the east side of the inlet. East Pass includes a federal navigation channel. The federal navigation channel requires routine maintenance to prevent it from shoaling. On average, East Pass is dredged in two-year intervals. The last time that East Pass was dredged was in December of 2013. It has now shoaled with sand. Although there was a suggestion that recent storms may have opened the channel to some extent, the evidence was not sufficient to alter the findings based on the 19-1844 record that the channel remains hazardous for marine traffic. East Pass Inlet Management Implementation Plan The East Pass IMP was adopted by Final Order of DEP on July 30, 2013. The East Pass IMP does not require that any quantity of dredged material from the dredging of East Pass be placed at any particular location other than as established in permits issued by DEP. Rather, disposal sites are to be determined on a case-by-case basis based on the best monitoring data available for the beaches in the area of influence of East Pass. Areas of influence are the beach areas east and west of East Pass affected by tidal forces generated by the inlet. The critical element of the East Pass IMP, and that in keeping with the statutory requirement that sand be placed on “adjacent eroding beaches” is the “strategy” that “the recent erosion of adjacent beaches observed over a minimum of five years shall define the placement need in terms of location and volume.” The Permit Modification On October 28, 2009, DEP issued Permit No. 0288799-001-JC to the Corps to perform maintenance dredging of the East Pass Navigation Channel and the Old Pass Lagoon Channel, and to rehabilitate the eastern and western jetties. Materials dredged from the Main Channel south of the U.S. Highway 98 bridge would be primarily bypassed to a portion of the beach on Eglin Air Force Base west of East Pass. As originally issued, the 2009 Permit limited placement of dredged sand to sites west of the inlet, and prohibited placement to the east of the inlet. Contrary to the 2008 amendment to section 161.142 and the 2013 East Pass IMP, the 2009 Permit did not require that sand dredged from the federal navigation channel be placed on the adjacent eroding beach, nor did it extend the life of the proximate West Destin Beach Restoration Project. The Corps requested the Permit Modification in furtherance of an inter-agency agreement between DEP and the Corps, by which the Corps agreed, to the best of its abilities, to act in a manner consistent with state requirements. Pursuant to section 161.142(5), beach compatible sand dredged from federal navigation channels is to be placed on the adjacent eroding beach. On November 14, 2016, DEP issued the Permit Modification to the Corps. The Permit Modification did not change the authorization or requirements for the dredging, but allowed dredged material to be placed on “the Gulf-front beaches on the eastern and western sides of East Pass.” On August 21, 2019, DEP filed the Proposed Change, which amended the Permit Modification to require that “[b]each compatible material dredged from the initial maintenance dredge event following issuance of [the Permit Modification], shall be placed to the east of East Pass.” The Permit Modification provides that, for the first maintenance dredging event following issuance of the Permit Modification, dredged material is to be placed at fill sites east of East Pass, the condition that Petitioners’ find objectionable. The Permit Modification then provides that “[f]or all subsequent maintenance dredging events conducted under this permit, disposal locations shall be supported by physical monitoring data of the beaches east and west of East Pass in order to identify the adjacent eroding beaches that will receive the maintenance dredged material, providing consistency with section 161.142, Florida Statutes.” Thus, the placement of dredged material to the east of East Pass authorized by the Permit Modification applies to the next dredging event, and not necessarily to subsequent periodic dredging events authorized by the Permit Modification. Fill Placement Site The eastern fill placement site authorized by the Permit Modification extends from R-17 to R-20.5. The shoreline adjacent to the eastern fill placement site has been designated as critically eroded for more than ten years. The eastern fill placement site is within the Western Destin Beach Restoration Project and designated as “Reach 1.” The fill placement site west of East Pass is located between V-611 and V-622. The shoreline landward of the western fill site has not been designated as critically eroded by the Department. There are no current beach restoration projects in or adjacent to the western fill site. East Pass is an ebb tide dominated inlet, with a sizable amount of sediment moving in and out. When outgoing tidal flow moves though the constriction formed by the jetties, flow velocities are accelerated. When the water, and any entrained sediment, passes the jetties, flow tends to spread out to the east, west, and south, and naturally loses velocity. When the outgoing tidal waters reach a critical velocity where they can no longer carry the sand, the sand drops out of suspension, which forms the ebb shoal. Essentially, the ebb shoal is a large, semi-circular sandbar extending from the mouth of East Pass that was created by the ebb tide carrying sediments south. East Pass is a highly dynamic inlet system. There are processes spurred by the configuration and location of East Pass, tides, waves, and storms that have resulted in currents running to the east and west that change on a frequent basis. The evidence in this proceeding, which includes the evidence adduced in 19-1844, established, for the period of 1996 through 2007, “a trend of west to east longshore transport, resulting in net gain immediately west of [East Pass] and a significant loss of sand along Holiday Isle east of [East Pass].” The evidence further established that a “drift nodal point” existed at East Pass. Longshore transport at uniform coastal locations is generally in one direction. However, when there are wave events coming from varying angles, and where beach contours are not parallel and uniform, or even linear, it is common for transport reversals to occur. The point at which those reversals occur is referred to as a nodal point. That point can be where east and west transport converges, or where it diverges. The shoreline in the vicinity of East Pass has exhibited “quite a few” nodal points over the past decade, resulting in frequent drift reversals and sand transport to the east and the west. The evidence as to the existence and effect of the East Pass drift nodal point, and its effect on the lateral transport of sand in the area, including the East Pass areas of influence, was substantiated by testimony and other evidence introduced at the final hearing. The testimony and evidence that there is no consistent direction of lateral sand transport in the vicinity of East Pass, and no predominant lateral current transporting sand in a westerly direction, is accepted. Competent substantial evidence in the record of this proceeding includes monitoring data for the eastern beach placement areas from the West Destin Four-Year Post-construction Monitoring Report and earlier annual post-construction reports covering the period from October 2012 to July 2017; data from the Holiday Isle Emergency Beach Fill Two-Year Post- construction Report; historical monitoring data for the area west of East Pass, including the Western Beach Monitoring Report, which covered 2006 to 2017; the Potential Borrow Area Impact Report, which included data from 1996 through 2012; and recent profile data from April 2019. These reports, and the data contained within them, cumulatively provide more than 20 years of data, and demonstrate convincingly that the shoreline to the west of East Pass has been stable or accreting, and the areas to the east are eroded. Mr. Trammell offered testimony, including a discussion of photographic evidence, demonstrating the beaches east of East Pass exhibit the following signs of significant and ongoing erosion: extensive dune erosion; exposed sea oat roots; reduced beach elevation; reduced beach width; crenulate2 bays; newly built dune walkovers that replaced old walkovers claimed by erosion; dune walkovers in close proximity to the shoreline, indicating that the shoreline had receded to the walkover; and beach scarping at the shoreline indicating active erosion. Mr. Trammell’s testimony as to the eastern spoil disposal sites was convincing and is accepted. The eastern areas of influence are currently designated to be “critically eroded” by DEP, a designation maintained for more than 10 years. The photographic evidence supports the data collected over time for the beaches east of East Pass, and the persuasive testimony offered by Mr. Clark, Mr. Trammell, Mr. Garis, and Mr. Trudnak (who testified in 19-1844), collectively establishes, by a preponderance of the evidence, that the beaches east of East Pass, including the eastern area of influence and the proposed dredge material disposal sites at Monuments R-17 to R-20.5, except for the area immediately abutting the eastern jetty, are critically eroded, a condition that is influenced by East Pass and its navigational channel, and are “adjacent eroding beaches” as that term is used in section 161.142. The evidence demonstrates that the shoreline of Santa Rosa Island to the west of East Pass has historically been stable. To be sure, as is the case with any shoreline, there will be some areas of erosion and some areas of accretion. After Hurricanes Ivan and Opal, areas of Santa Rosa Island experienced erosion. DEP declared the shoreline to be critically eroded after the 2004-2005 hurricane seasons, which prompted Okaloosa County to commission a study to monitor the health of the Monuments R-1 through R-16 beach segment, a segment that includes Petitioners’ residences. Despite the fact that no post-storm beach restoration occurred in the area, the beach recovered naturally and gained sand following the post-storm recovery. In addition, Santa Rosa Island is known for “beach cusps,” which are crenulate 2 “Having an irregularly wavy or serrate outline.” See “crenulate,” Merriam-Webster Dictionary, https://www.merriam-webster.com/ dictionary/crenulate (last visited February 2, 2020). shapes along the shoreline. Depending on the season and storm conditions, those beach cusps can have a localized erosive effect on the beach, but those tend to be seasonal. They do not negate what the evidence shows to be the overall stable to accretional conditions of the beaches west of East Pass from Monument V-622 to Petitioners’ residences. Mr. Trammell offered testimony, including a discussion of photographic evidence, demonstrating the beaches west of East Pass have large dunes; multiple dune lines; tall and thickly vegetated dunes indicating established dune growth; pioneering vegetation indicating active, healthy dune growth and accretion; partially buried signs indicating dune advance; and broad and expansive beaches. Those features are indicative of a stable and accretional shoreline. Mr. Trammell’s testimony as to the western spoil disposal site was convincing and is accepted. At present, the Santa Rosa Island shoreline is not deemed by DEP to be “critically eroded.” Mr. Trammel’s photographs offered in 19-1844 were supplemented by a series of photographs taken from several of the same locations after the passage of Tropical Storm Nestor in October 2019. Those photographs are consistent with a finding that the beaches to the east of East Pass are highly eroded and erosional, and that the beaches to the west of East Pass are not. The photographic evidence supports the data collected over time for the beaches west of East Pass, and the testimony offered at the final hearing, which collectively establish, by a preponderance of the evidence, that the beaches to the west of East Pass are stable and accretional, are not subject to erosion caused by East Pass, and are not “adjacent eroding beaches” as that term is used in section 161.142. Petitioners offered testimony of Dr. Douglas and Dr. Young in an effort to shore up weaknesses in the evidence offered in 19-1844. Their testimony and the evidence discussed therein was largely, if not exclusively designed to demonstrate that the direction of lateral sand transport in the vicinity of East Pass was predominantly east to west, which was the prevailing theme of Petitioners’ argument in 19-1844. The evidence adduced from Dr. Douglas was, in many respects, cumulative of that previously offered by Dr. Walton in 19-1844, and considered in the development of the Recommended Order in that case. For example, both Dr. Walton and Dr. Douglas reviewed and assessed information from the Taylor study, the Morang study, and the CP&E report in developing their opinions. Both agreed that sand placed in proximity to the jetties would tend to stay in place. Both ultimately concluded that sand placed to the west of the East Past west jetty would migrate to the west. Dr. Douglas offered new opinion testimony largely based on the Wave Information Study (“WIS”), which is an estimate of wave height and direction from a location two miles off-shore of East Pass. The data is a mathematical estimate, and does not rely on physical measurements from buoys or wave gauges. The wave estimates were then used as inputs in a model developed by the Coastal Engineering Research Center (“CERC”). Dr. Douglas candidly testified that the CERC model, even with normal input data, involves a substantial degree of uncertainty -- up to an order of magnitude. Adding to that uncertainty is that the CERC model assumes bottom contours and offshore volume calculations that were either inapplicable to the area around East Pass, or unavailable. Dr. Douglas was convincing that the CERC model is a tool commonly used by coastal engineers. His testimony, and the evidence on which it was based, was not unreasonable. However, it was not sufficient to outweigh the evidence introduced in support of the Permit Modification. In particular, and in addition to the evidence and testimony introduced in 19-1844, the testimony of Mr. Clark, whose extensive and direct knowledge, observations, and familiarity with the area, and of the data and information collected over periods of years, is found to be more persuasive regarding the processes and conditions in and around East Pass, and supports a finding, by a preponderance of the evidence, that the area to the east of East Pass constitutes “adjacent eroding beaches,” and that the area to the west of East Pass does not. Similarly, the evidence adduced from Dr. Young was largely cumulative, a fact that resulted in sustained objections to questions eliciting such information. He did provide testimony regarding time-lapse images from Google Earth Engine, and a critique on how to balance a sediment budget, though without providing a budget. As was the case with Dr. Douglas, Dr. Young’s testimony and the evidence discussed therein, was not sufficient to outweigh the more persuasive evidence introduced in support of the Permit Modification that the area to the east of East Pass constitutes “adjacent eroding beaches,” and that the area to the west of East Pass does not. The evidence is persuasive that placing dredged material at R-17 to R-20.5 in Holiday Isle on the eastern side of East Pass would not result in erosion on the western side of East Pass. Dredged material placed in the western beach placement area, and in the “shadow” of the western jetty, will tend to remain in that area. It would take a very long time, if at all, for that material to migrate further to the west. However, some -- but certainly not all -- of the dredged material placed on the eroding beaches to the east of East Pass can be introduced into the ebb shoal and move to the west. In that regard, the Google Earth Engine images depict sand moving across the ebb shoal to the western side of the inlet and attaching at various distances from the west jetty. As such, placement of the dredged material on the eastern beach placement areas would, to some degree, accomplish the goals of allowing sand transport to the western beaches, as was the relief sought in the Petition. The evidence was convincing that depositing dredged material onto the eroding beaches east of East Pass, as authorized by the Permit Modification, will not result in significant adverse impacts to areas either east or west of East Pass, nor will it interfere with the use by the public of any area of a beach seaward of the mean high-water line. Furthermore, the evidence introduced in this case and 19-1844 provide reasonable assurance that the Permit Modification is consistent with section 161.142 and will ensure that net long-term erosion or accretion rates on both sides of East Pass remain equal. Ultimate Findings of Fact The greater weight of the competent substantial evidence establishes that the eastern areas of influence of East Pass, including the beach disposal areas at R-17 to R-20.5, are critically eroded, a condition influenced, if not caused, by East Pass, and constitute East Pass’s “adjacent eroding beaches.” Evidence to the contrary was not persuasive. The greater weight of the competent substantial evidence establishes that the western areas of influence of East Pass, including the beach disposal areas at Monuments V-611 to V-622, are stable, if not accreting, and are not East Pass’s “adjacent eroding beaches.” Evidence to the contrary was not persuasive. The greater weight of the competent substantial evidence establishes that the placement of dredged material on the eastern side of East Pass will extend the life of the proximate West Destin Beach Restoration Project. The greater weight of the competent substantial evidence establishes that the Corps met the standards for the Permit Modification as proposed for issuance by DEP on November 14, 2016, and August 21, 2019, including section 161.142 and rules 62B-41.003 and 62B-41.005. Evidence to the contrary was not persuasive. Thus, the Permit Modification should be issued.
Recommendation Based on the foregoing Findings of Fact and Conclusions of Law, it is RECOMMENDED that the Department of Environmental Protection enter a final order approving the November 14, 2018, Permit Modification No. 0288799-006-JN, as amended by the DEP’s August 21, 2019, Notice of Proposed Changes to Proposed Agency Action, for the maintenance dredging of East Pass, subject to the general and specific conditions set forth therein. DONE AND ENTERED this 20th day of February, 2020, in Tallahassee, Leon County, Florida. S E. GARY EARLY Administrative Law Judge Division of Administrative Hearings The DeSoto Building 1230 Apalachee Parkway Tallahassee, Florida 32399-3060 (850) 488-9675 Fax Filing (850) 921-6847 www.doah.state.fl.us Filed with the Clerk of the Division of Administrative Hearings this 20th day of February, 2020. COPIES FURNISHED: Joseph Alexander Brown, Esquire Hopping Green & Sams, P.A. 119 South Monroe Street, Suite 300 Tallahassee, Florida 32301 (eServed) D. Kent Safriet, Esquire Hopping Green & Sams, P.A. 119 South Monroe Street, Suite 300 Tallahassee, Florida 32301 (eServed) Marianna Sarkisyan, Esquire Department of Environmental Protection Mail Station 35 3900 Commonwealth Boulevard Tallahassee, Florida 32399-3900 (eServed) Paul Joseph Polito, Esquire Department of Environmental Protection Mail Station 35 3900 Commonwealth Boulevard Tallahassee, Florida 32399-3900 (eServed) Jay Patrick Reynolds, Esquire Department of Environmental Protection Mail Station 35 3900 Commonwealth Boulevard Tallahassee, Florida 32399-3900 (eServed) Winifred L. Acosta, Esquire United States Attorney's Office Northern District Florida 21 East Garden Street Pensacola, Florida 32502-5676 (eServed) Kathryn Drey, Esquire United States Attorney's Office Northern District Florida 21 East Garden Street Pensacola, Florida 32502-5676 Kenneth G. Oertel, Esquire Oertel, Fernandez, Bryant & Atkinson, P.A. Post Office Box 1110 Tallahassee, Florida 32302 (eServed) Timothy Joseph Perry, Esquire Oertel, Fernandez, Bryant & Atkinson, P.A. Post Office Box 1110 Tallahassee, Florida 32302 (eServed) Carley J. Schrader, Esquire Nabors Giblin & Nickerson, P.A. 1500 Mahan Drive, Suite 200 Tallahassee, Florida 32308 (eServed) Gregory Thomas Stewart, Esquire Nabors, Giblin and Nickerson, P.A. 1500 Mahan Drive, Suite 200 Tallahassee, Florida 32308 (eServed) Elizabeth Desloge Ellis, Esquire Nabors, Giblin and Nickerson, P.A. 1500 Mahan Drive, Suite 200 Tallahassee, Florida 32308 (eServed) Lea Crandall, Agency Clerk Department of Environmental Protection Douglas Building, Mail Station 35 3900 Commonwealth Boulevard Tallahassee, Florida 32399-3000 (eServed) Justin G. Wolfe, General Counsel Department of Environmental Protection Legal Department, Suite 1051-J Douglas Building, Mail Station 35 3900 Commonwealth Boulevard Tallahassee, Florida 32399-3000 (eServed) Noah Valenstein, Secretary Department of Environmental Protection Douglas Building 3900 Commonwealth Boulevard Tallahassee, Florida 32399-3000 (eServed)
The Issue The issue in this case is whether the Department of Environmental Regulation (DER) was provided reasonable assurance as required by Rule 17-4.070, F.A.C., that the granting of a permit pursuant to the requirements of Rule 17- 604, F.A.C., to Volusia County for the construction of a closed wastewater collection and transmission system would not result in discharges or emissions or cause pollution in contravention of DER standards or rules.
Findings Of Fact David Biddulph is a resident of Volusia County, Florida and a resident of the unincorporated area known as Bethune Beach. County of Volusia, a charter county, is the applicant for a proposed wastewater collection and transmission system pursuant to Section 403.0878, F.S. [1991] and Rule 17-604, F.A.C. The Department of Environmental Regulation is the state agency charged with the responsibility of reviewing permits under Chapter 403, F.S. and its applicable rules. Petitioner Biddulph stipulated that the wastewater collection and transmission system as designed met the technical and engineering design requirements of Rule 17-604, F.A.C. Bethune Beach is an unincorporated area located on the barrier island separating the Atlantic Ocean and the Indian River Lagoon. Volusia County contracted with the environmental engineering firm of Marshall McCully & Associates to determine the feasibility of designing and constructing a wastewater collection and transmission system for the Bethune Beach area. The St. Johns River Water Management District is directed by the Indian River Lagoon System and Basin Act, Chapter 90-262, Laws of Florida, to identify areas where existing septic tank systems are considered a threat to the water quality of the Indian River Lagoon System. The St. Johns River Water Management District began developing a general methodology to access areas which are potential sources of pollution in the Indian River Lagoon System. This general methodology was called "Problem Area Index" (PAI). The PAI was intended to be used as an initial screening device in conjunction with other relevant research data or field verification to identify the problem areas. Volusia County's Public Health Unit, a division of the State of Florida Health and Rehabilitative Services Department, (HRS) utilized the proposed PAI to evaluate the southeast area of Volusia County. The Volusia County Public Health Unit entered into a contractual agreement with the St. Johns River Water Management District to research and delineate those areas in the southeast part of Volusia County with the potential to cause pollution to the upper Indian River Lagoon surface waters. The foregoing report concluded that the Bethune Beach area was an area of special concern and recommended that development of sewage treatment facilities be provided to this area. Credible competent evidence shows that the existing soils in Bethune Beach have high shell content and a high water table which are not conducive to installation of septic tank systems for sewage disposal, although the houses there now have such septic tanks. The conceptual plan prepared by Marshall McCully & Associates which was presented to Volusia County concluded there was a need to construct a wastewater collection and transmission system, and this plan was adopted by the Volusia County Council after holding the requisite public hearings. Volusia County Ordinance 79-3 authorizes the Volusia County Council to establish special service districts to provide water services and any and all other essential facilities. The county may initiate service in any area in its discretion without receiving an initiating petition from residents. Volusia County also created a special assessment for the installation of the system. Volusia County contracted with Marshall McCully & Associates to obtain the necessary permits for the construction of the wastewater collection and transmission system. Marshall McCully & Associates on behalf of Volusia County applied for a permit from DER to construct a domestic wastewater collection transmission system. In implementing Rule 17-604, F.A.C., DER policy does not require domestic wastewater collection and transmission system permit applicants to demonstrate that septic tanks simply would not work in the area served by the collection system. If the DER permit is granted, the septic tanks now lawfully present on Bethune Beach would have to be removed. The Volusia County application to construct a domestic wastewater collection and transmission system indicates that the sewage treatment facility serving the project would be the City of New Smyrna Beach Utilities Commission Pollution Control Plant. DER has already permitted that plant pursuant to Rule 17-600 F.A.C. under permit D064-191532 with an expiration date of June 30, 1995. The design capacity permitted under the existing permit for New Smyrna Beach's plant is 4,000,000 gallons a day, and the current average daily flow over the past twelve months has been approximately 2 and 1/2 million gallons a day. The city plant is currently operating within the parameters of its DER permit. Additional flow to the city plant from the county's proposed wastewater collection and transmission system has been reasonably estimated at 250,000 gallons per day. The only evidence of other amounts is speculative and not probative. DER implementation policy is to issue permits for new collection and transmission systems only where construction of a new collection and transmission system would connect to a sewage treatment plant which already has a permit capable of accommodating the new collection and transmission system. DER policy also does not contemplate granting permits to build waste water collection and transmission systems in such a manner as to increase the amount of water running through currently permitted sewage treatment plants beyond the maximum capacity for which the existing sewage treatment plant itself is currently permitted. In the present instance, Volusia County's proposed collection and transmission system, if permitted pursuant to DER's expressed permit conditions or terms (intent to grant), requirements, would not increase the amount of water running through the city receptor plant beyond the 4,000,000 gallon capacity which has already been reviewed by DER, is currently permitted by DER, and is currently subject to enforcement by DER. Although the county's proposed collection and transmittal system would increase the city plant's actual output by 250,000 gallons, the city plant's total output would thereafter still be 1,250,000 gallons below the plant's current permitted capacity. DER implementation policy also is to issue permits for construction of collection and transmission systems only if the sewage treatment plant to which the system would connect is properly treating the waste as required by the plant's current DER operating permit. The New Smyrna Beach Utilities Commission Pollution Control Plant that would receive domestic wastewater from the collection and transmission system proposed by Volusia County's permit application pending in this case is currently properly treating the waste it receives. The city plant currently discharges its effluent into the Indian River Lagoon System as allowed by its DER permit. The city plant also currently has the permitted capacity to receive the level of reasonably anticipated waste which will be transmitted by the collection and transmission system proposed by the county. Under the terms of DER's proposed permit for Volusia County's closed collection and transmission system, the city plant would not be authorized to increase the amount of treated wastewater for which the city plant is currently permitted. In review of permit applications, DER interprets the Indian River Lagoon Act to prohibit any new permitted discharge, or permitted increased loadings. This is a reasonable interpretation and entitled to great weight both as an agency interpretation of a statute it administers and because the agency's statutory interpretation reasonably acknowledges efficacy of the original DER permitting review of the existing city sewage treatment plant, the requirement of DER review of the county's pending application for a collection and transmission system, and the permitting and enforcement oversight of both those governmental entities' operations by the same agency, DER. Although the New Smyrna Beach Utilities Pollution Control Plant is currently operating within the parameters of its DER permit, a Consent Order has previously been negotiated between the city and DER to accomplish upgrading of the pollution control plant to meet new federal regulations for such facilities. The Consent Order requires the New Smyrna Beach Utilities Commission to begin a program of wastewater reuse and provide for land application of the treated effluent by 1995. The pollution control plant is on schedule for the removal of the effluent. No effluent will be discharged into the Indian River Lagoon System, except under limited wet weather discharge permits, which have been applied for. The Indian River Lagoon Act makes provision for wet weather discharge exceptions as do DER's and the city's actions pursuant to the Consent Order. See, Section 2. (3)(c) of the Indian River Lagoon Act. One of the intents of the Consent Order is to ensure that the treatment plant is in compliance with the Indian River Lagoon Act by the date of July 1, 1995 specified within that Act at Section 2. (2). The city plant permit expires June 30, 1995. If the New Smyrna Beach Utilities Commission does not receive wet weather discharge permits for its plant, it has planned to implement alternatives, such as onsite storage, to meet the requirements and anticipated enforcement by DER of the Indian River Lagoon Act. The New Smyrna Beach Utilities Commission Pollution Control Plant has an extensive inspection and maintenance program, which includes a television system that internally inspects the pipes for evidence of seepage. The New Smyrna Beach Utilities Commission Pollution Control Plant is regularly inspected by, and provides monthly operational reports to, DER so that DER can enforce any environmental concerns under the existing plant permit. The plant's operation under its current permit is also subject to review when that permit becomes subject to renewal due to its expiration date of June 30, 1995. Opinion testimony to the effect that increased acidity of the effluent might permeate the county pipes or the city pipes was speculative and unpersuasive.
Recommendation Upon the foregoing Findings of Fact and Conclusions of Law, it is RECOMMENDED That the Department of Environmental Regulation enter a final order dismissing the petition of Petitioner and granting the County of Volusia's application upon the terms and conditions set out in the agency's proposed permit (intent to grant). RECOMMENDED this 22nd day of January, 1993, 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 22nd day of January, 1993. APPENDIX TO RECOMMENDED ORDER 92-5033 DOAH CASE NO. 92-5033 The following constitute specific rulings, pursuant to S120.59 (2), F.S., upon the parties' respective proposed findings of fact (PFOF) Petitioner Biddulph's PFOF: 1-2,6 Accepted excepted for unnecessary, subordinate, or cumulative material. 3-5 Rejected as unreconciled, non-dispositive, and unpersuasive expert testimony, not supported by the greater weight of the credible, competent, record evidence as a whole. 7 Accepted, except the date July 1, 1995 has been correctly substituted. 8 Immaterial; DER permitting does not encompass whether an applicant builds a "cadillac or a volkswagon" system, as long as what is built meets DER regulatory standards. "Reasonable assurances" do not include "best financial investment." This proposal is also rejected as partial and unreconciled material, not supported by the greater weight of the credible, competent record evidence as a whole. 9 Not supported by the greater weight of the competent, credible, persuasive evidence. 10 Accepted that PIA is not completed or formalized. That it was not previously considered is not dispositive a de novo hearing. 11 Accepted but subordinate; not dispositive. This expert admittedly did not consider many other sources. 12, 13, 15 Rejected as irrelevant in part and immaterial in part. See treatment in recommended order of septic tank situation. 14 Rejected as stated as not supported by the greater weight of the competent credible, persuasive evidence. See treatment of target amounts, time frame for effluent reduction, and elimination of contaminants in recommended order. Applicant/Respondent Volusia County's PFOF: 1-11,13-29 Accepted except for unnecessary, subordinate, or cumulative material. 12 Accepted in substance but not as stated. 30-31 Accepted, but irrelevant, immaterial and non- dispositive of the disputed issues of material fact. Respondent DER's PFOF: 1-17,19-29 Accepted except for unnecessary, subordinate, or cumulative material. 18 Rejected as proposed because as proposed, it is a proposal of law, not fact; accepted under "conclusions of law" portion of RO. 30-31 Accepted, but irrelevant, immaterial, and non- dispositive of the disputed issues of material fact. COPIES FURNISHED: Harry A. Stewart, Esquire 5807 South Atlantic Avenue New Smyrna Beach, FL 32169 Douglas A. MacLaughlin, Esquire John Chaves, Esquire Department of Environmental Regulation Twin Towers Office Building 2600 Blair Stone Road Tallahassee, FL 32399-2400 Carol Browner, Secretary Department of Environmental Regulation Twin Towers Office Building 2600 Blair Stone Road Tallahassee, FL 32399-2400 Daniel H. Thompson, Esquire Department of Environmental Regulation Twin Towers Office Building 2600 Blair Stone Road Tallahassee, FL 32399-2400
