Findings Of Fact Petitioner, Frenchy's Rockaway Grill, Inc., is the owner and operator of a restaurant and alcoholic beverage establishment located at 7 Rockaway Street, Clearwater, Florida. Petitioner purchased the property in 1991. Michael Preston is president of Petitioner. Petitioner's establishment is immediately adjacent to the Gulf of Mexico and Clearwater beach on the west, to the north is a public parking lot, to the east is a motel, and to the south is the Clearwater Beach Hotel, which is owned and operated by Hunter Hotel Co., as indicated above. On the beach side of Petitioner's establishment there is an existing 972 sq. ft. wooden deck. The existing deck was initially constructed on or about 1987 by prior owners without receiving appropriate variance approvals. Subsequent alterations to the deck occurred between 1987 and 1991, also without appropriate variance approvals. In 1991 Charles and Ypapanti Alexiou/Anthony Alexiou, former owners of the subject property, filed an application for variance approval with the Board seeking three variances relating to the construction of the deck at the 7 Rockaway establishment. Specifically, the variances sought were: "1) 55.5 ft. to permit deck seaward of the coastal construction control line; 2) 15 ft. to permit a deck zero feet from a street right-of-way; and, 3) seven parking spaces to permit a 1,338 sq. ft. deck at 7 Rockaway Street, Miller's Replat, Lot 2 & vacated beach Drive on W and Lot 3, zoned CR 28 (resort commercial) & OS/R (open space recreation)." At public meeting on August 8, 1991, the application was considered by the Board. At that time Mr. Cline, as counsel for Hunter appeared in opposition to the application stating that approval of the variance requests would adversely impact the Clearwater Beach Hotel, that the request was for economic gain, that any hardship was self-imposed, and that development and traffic in the area was already heavy. The Board, however, granted the variance requests as to variances number 1 and number 2., and as to the third request, the Board denied the proposed 1,338 sq. ft. deck, but approved a variance of five parking spaces to permit the existing deck of 972 sq. ft. On or about July 13, 1993, a variance application was filed with the Board by Howard G. and Jean B. Hamilton and Palm Pavilion of Clearwater, Inc., seeking approval of four variances required for an 800 sq. ft. expansion of an existing deck at a restaurant at 10 Bay Esplanade, Clearwater Beach, Florida. The Palm Pavilion applicants were also represented by Mr. Cline. Like Petitioner's establishment, Palm Pavilion is a beachfront restaurant, which is located directly across the public parking lot to the north of Petitioner's establishment. Unlike Petitioner's establishment, Palm Pavilion is bordered by parking to the south and the east, and is not immediately adjacent to other buildings. On August 26, 1993, the Board granted the Palm Pavilion variance application for expansion of an existing beachfront deck with certain conditions. On October 6, 1994, Petitioner submitted its application to the Board requesting five variances required for a 650 sq. ft. expansion of the existing wooden deck at 7 Rockaway Street. Specifically, the variances sought were: 1) 13.22 ft. to permit a lot depth of 86.78 ft. where 100 ft. is required; 2) 8.2 ft. to permit it a rear setback of 6.8 ft. where 15 ft. is required; 3) 14 percent to permit 11 percent of open space where 25 percent is required; 4) three parking spaces to permit zero parking spaces where three additional are required; and, 5) 52.14 ft. to permit a structure seaward of the coastal construction control line. The subject property at 7 Rockaway Street is properly zoned CR-28 (resort commercial). Any scrivener's error indicating that the property is zoned OSC (open space recreation) has been corrected. Petitioner's restaurant, Frenchy's Rockaway Grill, is a popular beachside establishment. It is one of very few freestanding restaurants fronting the Gulf of Mexico on Clearwater Beach. Some patrons particularly enjoy dining on the open air deck adjacent to the beach. During peak hours, there is often over an hour's waiting time for tables on the deck. Petitioner is currently unable to accommodate the demand for seating on the beachside deck. Petitioner would sustain an economic benefit if more patrons could be accommodated on an expanded deck. Because of the size constraints of the lot and the establishment's location directly on the beach, development and improvement of the facility is highly restricted. The back of some residential rooms of the Clearwater Beach Hotel are immediately adjacent to the south of Petitioner's establishment. There are small bathroom windows from these residential rooms that face Petitioner's establishment. Petitioner's proposed expansion of the open air deck would place the proposed deck in very close proximity to the back of these residential hotel rooms. The City's staff reviewed the Petitioner's application and recommended approval with the following conditions: 1) the applicant shall obtain the requisite occupational license within 12 months; 2) the applicant shall obtain the necessary building permit within 6 months; 3) there shall be no outdoor entertainment and no outdoor speakers; 4) the applicant shall obtain the requisite alcoholic beverage separation distance variance from the City Commission. Petitioner agreed to the conditions recommended by staff. The recommendations of staff are not binding on the Board. In addition to the application for the five variances filed with the Board, Petitioner also filed a conditional use request with the Planning and Zoning Board. The conditional use request was approved on September 13, 1994, and imposed certain other conditions including the construction of a six foot wall on the south side of the proposed deck to buffer the adjoining hotel. Petitioner agreed to the conditions imposed by the Planning and Zoning Board.
Findings Of Fact Jaime Fernandez was transferred in 1977 to Clearwater Traffic Engineering Department as an electrician's helper from the Clearwater Pollution Control Department. Prior to coming to Water Pollution Control, Respondent had been a CETA employee in the Parks Department from which he was fired for incompetence (Respondent's testimony). Although the exact situation was not made clear to the Hearing Officer, it appeared that Respondent appealed his firing from the Parks Department alleging some type of discrimination, and, following a hearing, the City was required to reemploy him. At all times here relevant, Respondent was an employee in the Classified Civil Service of Clearwater. Respondent testified that the evaluations he received at Water Pollution Control were satisfactory overall, and the request for a transfer was initiated by him. As an electrician's helper, Respondent was one of six or seven electrician's helpers. When he was subsequently transferred to the position of ET helper, he was the only ET helper in the Traffic Engineering Department. With a larger number of electrician's helpers it was easier to assign trench digging, painting and other similar menial jobs to Respondent without detracting from the overall efficiency of the Department than it was when Respondent became the only ET helper in a group with two ET's. Respondent served as an electrician's helper in the Traffic Engineering Department for approximately two years before he was transferred to the position of ET helper. During these two years as an electrician's helper, Respondent failed to get a satisfactory overall evaluation and never received a merit pay increase. He was transferred to the electronics shop as an ET helper in late 1979. In the six months follow-up review of Respondent's unsatisfactory evaluation report dated 2-9-80, the Director of the Traffic Engineering Department recommended Fernandez be terminated for incompetence. This recommendation was rejected by the Personnel Department because of insufficient documentation of the events giving rise to the recommendation. On August 25, 1978, Respondent was given a letter of reprimand following an accident involving a truck, driven by Respondent, and a building in which Respondent's inattention contributed to the accident (Exhibit 6). On April 14, 1980, Respondent was suspended from duty without pay for three days on charges of incompetence and inefficiency in his work product, errors in daily time cards and other reports, and continuous performance evaluations indicating improvement needed. On the instant charges the evidence was unrebutted that during the period August 1, 1980, through March 15, 1981, 19 errors were made by Respondent on the time sheets he submitted. Twenty-seven other employees in the same Department fill out time sheets and, during the same period, the next highest number of errors was eight. Most of the employees made only one or two errors in completing their time sheets. During the period February 2, 1981 to February 5, 1981, Respondent was given a work order to construct and install back boards in two transit controllers (Exhibit 1). Included in the work order was a drawing showing how the panel was to be connected and detailed instructions on how the work was to be performed. Despite close supervision, Respondent failed to follow the instructions, cut the wires longer than the maximum three feet lengths as shown on the work order, installed grounding bar in the wrong location, and did not properly lace the harness. This work order was within the capability of a reasonably qualified ET helper to complete in twenty hours. Respondent took forty-seven hours to accomplish this work and made numerous errors which had to be corrected by others. During a period in mid-February; 1981, Respondent was assigned a detector to repair. Repair of this equipment was also within the capability of a reasonably qualified ET helper in about four hours. After working on this detector for twenty-one hours, Respondent was still unable to repair it. It was given to an electronics technician who repaired the detector in approximately one hour. Respondent, in work order 136, was given an LT 169 load pack to repair. Test equipment is set up in the petitioner's shop for trouble shooting this equipment. After testing this load pack, Respondent replaced the part he thought defective but, when tested by someone else, the equipment was still inoperative. The part replaced by Respondent was the part most frequently found defective in this load pack. In this instance, this part was not the cause of the equipment being in operative. This was a routine work order that a reasonably qualified ET helper should have been able to complete. Respondent has been counselled and evaluated numerous times by different supervisors in the Traffic Engineering Department for the past three years and has yet to be assigned a satisfactory evaluation. No other employee has been retained in a position with the City of Clearwater for such an extended period with unsatisfactory evaluations. Respondent testified that he has completed a two-year course in electronics at Pinellas County Vocational School and has one year of college. Accordingly, he deemed himself better qualified as an ET helper than as an electrician's helper. He felt he should have been disciplined for incompetency as an electrician's helper during the two years he worked in that Division, rather than as an ET helper in which position he has worked for approximately one year. Respondent's testimony, that he was denied earned leave or pay for this leave when he was dismissed, was not rebutted. However, the City of Clearwater's regulations relating to leave were not presented to the Hearing Officer, and without access to these regulations, Respondent's claim cannot be resolved.
Findings Of Fact On or about April 5, 1988, Petitioner filed an application for a variance to replace an existing four foot fence extending to the seawall on his property at 643 Harbor Island, Lot 12 Island Estates, Clearwater, Florida. The subject property is zoned RS-6. Petitioner had already replaced his previous fencing prior to the filing of this application with wooden fencing which extends on the north and south side of his property through the setback to the seawall. The Development Code Adjustment Board considered Petitioner's application at its meeting on May 12, 1988, and based upon the Petitioner's explanation that the variance was sought simply to replace an existing fence that had termite damage, the Board approved his application on a 3 to 2 vote. The variance approval was conditioned upon the Petitioner obtaining a building permit within one month of the approval. Petitioner failed to obtain the required building permit, and no excuse was offered for this failure. Therefore, he had to reapply for the variance. On or about July 21, 1988, Petitioner filed his variance reapplication. The Development Code Adjustment Board considered this reapplication on August 25, 1988, at which time Petitioner again stated that he was simply replacing an existing fence. Due to a tie vote, consideration of the reapplication was continued to the Board's meeting of September 8, 1988. At the meeting on September 8, he explained for the first time that while the fencing on the south side of his property was simply the replacement of a previous fence which had extended to the seawall, the fencing on the north side was not. The previous fence on the north side of his property had stopped prior to the fifteen foot setback. With this clarification, the Board approved his variance reapplication for the south side of his property, but denied the variance for the north side. Petitioner has timely appealed the denial of his variance reapplication as it relates to the north side of his property. Petitioner testified at hearing that prior to the construction of his current wooden fence, he had a wood fence all the way to the seawall on the south side of his property. Since he had to replace that fencing due to termite damage, he took the opportunity to also replace and extend the wooden fencing on the northern side of his property through the setback. This action was not based on any hardship, but simply because he and his family felt it would look better if he had the same fencing on both sides of his property. It is clear and undisputed that Petitioner constructed a new fence on the north side of his property through the setback without obtaining a variance or permit. He did this simply for aesthetic reasons, and not due to any hardship. He failed to disclose this in his applications, or when the Board met on May 12 and August 25, 1988 to consider this matter.
The Issue The issue in this case is whether the Department of Environmental Protection (DEP or Department) should exempt Petitioner's alleged maintenance-dredging from wetland resource permitting under Florida Administrative Code Rule 62- 312.050(1)(e).1
Findings Of Fact Petitioner has applied for a maintenance-dredging exemption from wetland resource permitting for two channels in Goose Bayou on the two ends of a U-shaped upland cut canal adjacent to Goose Bayou. Rule 62-312 provides in pertinent part: No permit shall be required under this chapter for dredging or filling . . . for the projects listed below. * * * (e) The performance of maintenance dredging of existing manmade canals, channels, and intake and discharge structures, where the spoil material is to be removed and deposited on a self-contained, upland spoil site which will prevent the escape of the spoil material and return water from the spoil site into surface waters of the state, provided no more dredging is performed than is necessary to restore the canal, channels, and intake and discharge structures to original design specifications, and provided that control devices are used at the dredge site to prevent turbidity and toxic or deleterious substances from discharging into adjacent waters during maintenance dredging. This exemption shall apply to all canals constructed before April 3, 1970, and to those canals constructed on or after April 3, 1970, pursuant to all necessary state permits. This exemption shall not apply to the removal of a natural or manmade barrier separating a canal or canal system from adjacent waters of the state. Where no previous permit has been issued by the Board of Trustees of the Internal Improvement Trust Fund or the United States Army Corps of Engineers for construction or maintenance dredging of the existing manmade canal or intake or discharge structure, such maintenance dredging shall be limited to a depth of no more than 5 feet below mean low water. There was no evidence of any dredging or application for dredging in the vicinity of the proposed alleged "maintenance- dredging" prior to 1971. There was evidence and a stipulation that Heritage Homes of Fort Walton, Inc. (Heritage Homes), applied to the State of Florida in or around 1971 to dredge two navigation channels in Goose Bayou for a project known as Venetian Villas and to remove two plugs separating a land-locked U-shaped canal from Goose Bayou. The navigation channels were to be 50 feet wide by five feet deep. The southern channel was to be 640 feet long, while the northern channel was to be 450 feet long. This proposal did not receive any governmental authorization. There was evidence and the parties stipulated that in 1973, based on the proposed project modifications, the State of Florida Department of Pollution Control (DPC), a predecessor of DEP, issued water quality certification, and the State of Florida Board of Trustees of the Internal Improvement Trust Fund (BOT) issued a permit for the project, as modified. It appears that the issuance of the water qualify certification and BOT permit was part of some kind of settlement reached between Heritage Homes and the State of Florida for dredge-and-fill violations. It appears that the settlement also involved the conveyance of ten acres of land to the State of Florida in lieu of payment for the spoil used in filling the marsh lands between Goose Bayou and the U-shaped canal. There was evidence and the parties stipulated that, at some point in time, the DPC certification and a BOT permit were transferred from Heritage Homes to West Florida Construction Company (West Florida). There was evidence and the parties stipulated that, as of July 13, 1973, neither Heritage Homes nor West Florida had applied to the United States Army Corps of Engineers (Corps) for a permit. There was evidence and the parties stipulated that, over time and after receiving comments from various governmental agencies, West Florida's proposed project changed to involve a yacht basin/marina, a proposed southern channel, elimination of the proposal for a northern channel, and plugging the U-shaped canal to keep it separate from Goose Bayou. The location of the single, southern channel under this proposal was different from the proposed location of the southern channel under the Heritage Homes proposal, which was to start at the southernmost arm of the U-shaped canal. Instead, under West Florida's proposal, the single, southern channel was to be located directly north of the southernmost arm of the U-shaped canal. There was evidence and the parties stipulated that, by August 21, 1974, West Florida applied to the Corps for a permit to dredge the single, southern channel (50 feet wide, 565 feet long, and four feet deep), to keep the northern canal plugged, and to construct a yacht basin/marina. There was evidence and the parties stipulated that, the United States Department of the Interior Fish and Wildlife Service (FWS) and the United States Environmental Protection Agency (EPA) recommended several changes to the project before they could recommend that the Corps issue a permit for the 1974 application; however, it does not appear that the recommended changes were ever made or that the Corps ever took any action on the 1974 application or issued any permit for the proposed project. At some point in time after 1974, the two plugs were removed, which connected the U-shaped canal to Goose Bayou. There is now a wide, shallow channel from the waterward ends of the U-shaped canal into Goose Bayou. The evidence did not prove that these channels, which Petitioner now seeks to maintenance- dredge, were ever dredged by man. Their width and shallow depth are more consistent with natural scouring from surface water runoff leaving the canal system at low and extreme low tides than with dredging. There was no evidence of soil borings, which could have verified whether the channels had been dredged by man. Even if originally dredged, there was no evidence that a dredged channel had been maintained over the years. Mr. Stoutamire testified that DEP does not consider maintenance- dredging to include the restoration or rebuilding of a channel that has not been maintained and no longer exists. This interpretation of the maintenance-dredging exemption is reasonable. Mr. Stoutamire also testified that DEP interprets the last sentence of Rule 62-312.050(1)(e), limiting maintenance- dredging to no more than five feet below mean low water where no previous permit has been issued, to refer to canals constructed before April 3, 1970, since maintenance-dredging of canals constructed after that date would not be exempt if not previously permitted. This interpretation is reasonable.2 Petitioner's application did not state that control devices would be used to prevent turbidity and toxic or deleterious substances from discharging into adjacent waters during dredging.
Recommendation Based upon the foregoing Findings of Fact and Conclusions of Law, it is RECOMMENDED that the Department enter a final order denying Petitioner a maintenance-dredging exemption under Rule 62- 312.050(1)(e). DONE AND ENTERED this 16th day of September, 2009, in Tallahassee, Leon County, Florida. S J. LAWRENCE JOHNSTON Administrative Law Judge Division of Administrative Hearings The DeSoto Building 1230 Apalachee Parkway Tallahassee, Florida 32399-3060 (850) 488-9675 Fax Filing (850) 921-6847 www.doah.state.fl.us Filed with the Clerk of the Division of Administrative Hearings this 16th day of September, 2009.
Findings Of Fact Upon consideration of the oral and documentary evidence in the record, as well as the pleadings and joint prehearing stipulation, the following relevant facts are found: Cast-Crete owns and operates a concrete batch plant in Hillsborough County, Florida, and manufactures concrete products such as reinforced beams, lintels, seals and drainage structures on the property. The plant is located on the west side of State Road 579, 3/4 mile north of Interstate 4, Section 28, Township 28 South, Range 20 East. The concrete products are manufactured in various forms which are laid out over a large portion of Cast-Crete's property. Lubricating oils are utilized to facilitate the removal of the product from the confining forms. During this process some of the lubricating oil is spilled onto the ground. Also, cleaning solutions containing degreasers are utilized to wash the concrete trucks eight to ten times per day. This solution ends up on the ground. Aggregate limerock (crushed limestone) is used in the concrete formulation process and is stored in large piles on the property. In order to contain the dust, water is sprayed on the aggregate piles 24 hours a day. The wash water from the continuous process of wetting the aggregate, other waste water and some stormwater is channeled through the property and into a settling pond in the northwest corner of Cast-Crete's property. This pond discharges continuously off the property by way of a concrete flume into a county maintained ditch. Water in the ditch travels in a westerly direction approximately 200 to 300 yards before it passes under Black Dairy Road, where the watercourse deepens and widens. The ditch discharges into a marshy area which drains into Six Mile Creek and other water bodies. The pond at the northwest corner of Cast-Crete's property is equipped with a metal skimming device to remove oils and greases floating on the surface of the pond. Nevertheless, it is estimated that approximately 100 gallons of oil per year are discharged by Cast-Crete. Oil and grease in the outflow water is occasionally above 5 mg/L. Oil and grease layers have been observed on water at both Black Dairy Road and Six Mile Creek, probably resulting from road run- off. Approximately 90 percent of the water discharged from the property is a result of the wetting or washdown of the aggregate piles. The excess water which comes from the aggregate piles is laden with dissolved limestone, lime and limestone particles. This limestone dust raises the pH level of the water. Because of the continued wetting of the aggregate, water flows through the settling ponds and off of Cast-Crete's property at a rate of approximately 4.8 gallons per minute, or 7,200 gallons per day or 2.5 million gallons per year. During a rain event, the flow increases markedly. Except during times of heavy rainfall, water flowing from the respondent's property provides a thin stream of water in the drainage ditch approximately six inches wide and several inches deep. The pH of the wastewater from Cast-Crete's discharge flume is between 10 and 11 units. During high volume flows, the pH remains at or above 11 units. An increase of one unit of pH in the wastewater means that the wastewater has become 10 times more basic, since pH is measured on a logarithmic scale. The natural background of unaffected streams in the area of and in the same watershed as the Cast-Crete property is less than 8.5 units. Specific conductance or conductivity is the measure of free ions in the water. Typical conductivity readings from other water bodies in Hillsborough County range between 50 and 330 micromhos per centimeter. The specific conductance of Cast-Crete's wastewater ranges from 898 to 2000 micromhos per centimeter. This is due to the presence of calcium carbonate and calcium hydroxide in the water. Blue-green algae is the dominant plant species in the ditch between the Cast-Crete discharge flume and the first 150 meters of the ditch. A biological survey of the ditch system indicates that the diversity of species east of Black Dairy Road is low. This is attributable in part to the high pH of the wastewater. The low diversity can also be attributed to the fact that the County maintains the ditch by use of a dragline on an annual basis. Background samples from a site within one mile to the northwest of the Cast-Crete property were taken. The site (a stream passing under Williams Road) is an appropriate place to take background samples because the water there is unaffected by Cast-Crete's discharge or other man-induced conditions. The pH background sample ranged from 4.6 units to 5.1 units. The specific conductance background samples ranged from 70 to 100 micromhos per centimeter. Samples taken from a site potentially impacted by Cast-Crete's discharge showed a pH level of from 6.35 to 7.37 units and specific conductance of from 592 to 670 micromhos per centimeter. Cast-Crete discharges water from its concrete plants operation without a permit from the DER.
Recommendation Based upon the findings of fact and conclusions of law recited herein, it is RECOMMENDED that a Final Order be entered requiring respondent to submit a complete application for an industrial wastewater permit within thirty (30) days, and that, if it fails to do so, it cease discharging wastewater from its property until such time as an appropriately valid permit is issued by the DER. Respectfully submitted and entered this 3rd day of May, 1985, in Tallahassee, Florida. DIANE D. TREMOR Hearing Officer Division of Administrative Hearings The Oakland Building 2009 Apalachee Parkway Tallahassee, Florida 32301 (904) 488-9675 Filed with the Clerk of the Division of Administrative Hearings this 3rd day of May, 1985. COPIES FURNISHED: David K. Thulman Assistant General Counsel Department of Environmental Regulation Twin Towers Office Building Blairstone Road Tallahassee, FL 32301 W. DeHart Ayala, Jr. 501 E. Jackson Street Suite 200 Tampa, FL 33602 Victoria Tschinkel Secretary Department of Environmental Regulation Twin Towers Office Building 2600 Blairstone Road Tallahassee, FL 32301 ================================================================= AGENCY FINAL ORDER ================================================================= STATE OF FLORIDA DEPARTMENT OF ENVIRONMENTAL REGULATION DEPARTMENT OF ENVIRONMENTAL REGULATION, STATE OF FLORIDA, Petitioner, vs. CASE NO. 84-1647 CAST-CRETE CORPORATION OF FLORIDA Respondent. /
The Issue The issue in this appeal is whether the decision of the City of Clearwater Development Code Adjustment Board denying Petitioner's application for variances for certain signage on his property is supported by the evidence in the record, or whether it departs from the essential requirements of law. See Section 137.014(f)(3), City of Clearwater Land Development Code.
Findings Of Fact Petitioner is the owner of certain property located at 1923-1943 U.S. Highway 19 North, Clearwater, Florida (Section 05-29-16, M&B 23.05). This property is zoned CC (Commercial Center), and is the site of a strip shopping mall. On or about March 23, 1989, Petitioner applied for three variances for the subject property, as follows: 243 square feet to permit a total of 411 square feet of property identification signage; 13.5 feet in height to permit a 33.5 foot high pole sign; permission for a roof mounted sign. The Development Code Adjustment Board denied Petitioner's application for variances on April 13, 1989, and Petitioner timely filed this appeal of the Board's decision. Under the provisions of the City of Clearwater Land Development Code applicable to the Petitioner's property, only 168 square feet of property identification signage and pole signs not to exceed 20 feet in height would be allowed without a variance, and roof signs of any kind are prohibited unless a variance has been granted. Several months prior to Petitioner's filing for these variances, a roof sign was erected on the building located on the subject property. This roof sign consists of individual letters spelling "Harbor Square", which is the name of this shopping mall. The letters are from 3 feet, to 4 feet 9 inches in height, and span a distance of 34 feet 9 inches in width. The roof sign replaced a property identification sign at the right of way which previously carried the name of the shopping center, but the space on the pole sign previously used to identify the mall was not eliminated. That space is now used to identify a uniform business in the mall. Petitioner is seeking these after the fact variances to authorize the roof sign which has already been erected, and to approve the height of an existing pole sign. An enforcement action initiated by the City is pending this variance determination. Tenants in the Harbor Square mall testified that the change in signage has made the mall more visible and accessible, and several of their customers have commented that their businesses are now easier to find. The tenants feel that this change in signage will benefit their businesses financially. The Development Code Adjustment Board has previously granted variances from the signage limitations imposed by the Code, but the evidence produced at hearing indicates that none of these variances were granted after the fact. The two variances which were approved for roof signs were based upon a finding of conditions unique to the property which created a hardship for the applicant. In both instances, the Board found that the applicant had not created his own hardship, but that it arose from the size or positioning of the property involved in each application. In this case, nothing unique about the property can be found. The applicant has caused his own problems by allowing a sign to be erected without first obtaining a permit or variance. The Petitioner urges that it was the responsibility of his sign contractor to obtain all necessary permits or variances, and that the contractor did not inform him that a variance was necessary before he erected the sign. However, neither the sign contractor nor the Petitioner himself was present to testify, and therefore, there can be no finding with regard to his credibility, or with regard to whatever arrangement he had with the contractor. In any event, as the property owner seeking a variance, Petitioner has failed to establish any basis for a finding of a hardship or circumstance unique to his property, other than the fact that he allowed this sign to be erected without obtaining the necessary approvals from the City.
Findings Of Fact Respondent TCI has more than 70 homes completed or under construction in furtherance of plans to build 141 single family residences as part of Tymber Creek Phase I, a development in Volusia County. The development site is partially bounded by the Little Tomoka River, a natural body of water which is navigable in fact. The site of the construction respondent DER proposes to permit is home to wildlife of various kinds, including woodpeckers, great horned owls, herons, mussels, manatees, snakes, turtles and alligators. At the present time, boat traffic on the Little Tomoka River is negligible. The dock TCI proposes to build would have a total area of 120 square feet and would not impede the flow of the river. It would protrude over the water no more than five feet along the bank of the river at a point where the river widens, described by some of the witnesses as a lagoon, and would not constitute a hazard to navigation. With respect to the dock, the foot bridges, the boat ramp and the removal of the agreed upon portion of unauthorized fill, the permit DER proposes to issue would be before the fact. According to DER's appraisal of TCI's original, revised permit application, which was received in evidence as DER's exhibit No. 5, TCI made revised application, on November 29, 1977, for "after-the-fact approval for the placement of approximately 3500 cubic yards of fill After TCI had filled, it constructed parking and recreational facilities. In evaluating TCI's application, Steve Beeman, a DER employee, described the site in January of 1978: Approximately 1.6 acres of filled flood plain is presently covered by a sports complex including tennis courts, swimming pool and recreation building and an asphalt parking lot. An additional 3000 square feet has been filled and paved (asphalt was applied after receipt of DER cease and desist notice) for [access to] a [proposed] boatramp and parking area, and approximately 14,000 square feet of swamps have been filled in the construction of a 1800+ feet "natural trial". DER's exhibit No. 5. By letter dated February 22, 1978, respondent DER notified respondent TCI of its intent to deny TCI's initial application, as revised. Among the reasons DER gave for its intended denial were expected violations of various water quality standards, including a prohibition against oils and greases in concentrations greater than 15 mg. per liter ("or that no visible oil, defined as iridescence, be present to cause taste or odors, or interfere with other beneficial uses.") DER's exhibit No. 4. Rule 17-3.05(2)(r) , Florida Administrative Code. This water quality standard violation was anticipated because of "the [projected] focussing of stormwater runoff into the Little Tomoka River, across paved surfaces, which are high in petroleum based pollutants." DER's exhibit No. 5. In its notice of intent to issue a permit, DER proposes to authorize TCI "to realign (straighten) existing boatramp access road." DER's exhibit No. Mr. Wheeler's letter to Mr. Shirah of April 6, 1978, DER's exhibit No. 2, describes the proposed access road change as part of "discussions and agreements concerning resolution of the initial unauthorized fill and subsequent after-the- fact application." A drawing attached to this letter indicates that the contemplated alteration of the roadway would decrease the amount of paved surface to some unspecified extent. Another part of these "discussions and agreements concerned removal of some 1900 cubic yards of fill. Most of the fill designated for removal had been placed with the idea of creating a dry pathway through the marshy area separating the Little Tomoka River from an asphalt parking area. So placed, the fill dirt acts as a dike, preventing the preexisting communication between the waters of the Little Tomoka River and the waters of the adjacent marsh. At the hearing, Mr. Wheeler testified that, if revised in accordance with DER's exhibit No. 2, TCI's project would pose no threat to water quality, but he conceded that the effects of gasoline boat motors were not considered. An increase in beat traffic would likely result in an increase in oils and greases in the waters of the Little Tomoka River.
Recommendation Upon consideration of the foregoing, it is RECOMMENDED: That respondent DER, deny the permit is proposed to issue to respondent TCI in letters to petitioners dated April 7, 1978. DONE and ENTERED this 23rd day of August, 1978, in Tallahassee, Florida. ROBERT T. BENTON, II Hearing Officer Division of Administrative Hearings Room 530, Carlton Building Tallahassee, Florida 32304 (904) 488-9675 COPIES FURNISHED: Segundo J. Fernandez, Esquire Assistant General Counsel Twin Towers Office Building 2600 Blair Stone Road Tallahassee, Florida Judson I. Woods, Jr., 32301 Esquire Post Office Box 1916 Ormond Beach, Florida 32074 Tymber Creek, Inc. c/o Stan Shirah Route 40 Twin River Drive Ormond Beach, Florida 32074
The Issue The issue to be determined is whether the applicants, William Guererro and Christina Bang, a/k/a Christina Guerrero (Applicants), are entitled to issuance of a Consolidated Environmental Resource Permit and State Lands Approvals for various structures on the Applicants’ property at 58458 Overseas Highway, Marathon, Florida.
Findings Of Fact The Parties Petitioners Bernard Spinrad and Marian Spinrad are the owners of adjoining parcels of property with the addresses of 58418 and 58420 Overseas Highway, Marathon, Florida. They acquired the property in December 2001. They recently completed construction of two residential structures on the properties. The structure at 58418 Overseas Highway is currently listed for sale. The structure at 58420 Overseas Highway is a vacation rental property. Neither structure is Petitioners’ permanent residence. The DEP is the state agency with the power and duty to regulate activities in waters of the state pursuant to chapter 373, Florida Statutes. The DEP also serves as staff to the Board of Trustees of the Internal Improvement Trust Fund (“Board of Trustees”) to review and act on activities on state sovereignty submerged lands under chapter 253. The Applicants, are the owners of adjoining parcels of property with the address of 58478 Overseas Highway, Marathon, Florida (the Property). They purchased the Property in June 2010. The structures that are the subject of the Permit are to be constructed near or waterward of the shoreline of the Property. The Property The Property is located on Grassy Key, an island in the middle Florida Keys, within limits of the city of Marathon, Monroe County, Florida. U.S. Highway 1 passes through Grassy Key. The Property -- as is that of Petitioners -- is situated between U.S. Highway 1 and the open waters of the Atlantic Ocean. In the early part of the 20th century, a portion of Grassy Key was platted as the Crains Subdivision. The properties owned by Applicants and Petitioners are within the Crains Subdivision. During the periods of time directly relevant hereto, the Property has been owned by Burgess Levine, who owned the property during the period prior to the October 2006, landfall of Hurricane Wilma until June 2010, and by Applicants, who have owned the Property since June, 2010. Grassy Key Grassy Key is three-miles long, and has 6800 feet of beaches, none of which are designated as critically eroded. The island fronts the Atlantic Ocean to the east, and the more protected waters of Florida Bay to the west. The waters along the Atlantic Ocean shoreline of Grassy Key in the area at issue are shallow, with an extremely flat bottom having a very gradual slope of approximately 1 to 30, meaning there is a one foot vertical change over 30 horizontal feet. The mean tide range at the Property is about 1.7 feet. Under normal conditions, the stretch of Grassy Key at issue is fairly characterized as a zero-wave energy shoreline. Waves break well offshore and there is negligible wave energy propagating beyond that point. What shoreline energy exists is produced by small tide currents and wind-shear on the water surface that moves water along the shoreline. The direction of the water movement is dependent on tides and wind direction, with the predominant direction being from north to south. Erosive and other significant changes to the shoreline of Grassy Key, including that stretch fronting the Property, are event driven, meaning when there is a coastal storm that causes a rise in the water level, substantially higher than the astronomical tide, waves can propagate onto the shoreline of Grassy Key. The wind and waves can come from virtually any direction depending on the storm. A storm of greater intensity will create higher energy-wave conditions. Although storm conditions may only occur over 1 to 3 percent of a given year, with the rest of the year having zero-wave energy, on average the coastline may be considered to be of moderate-wave energy. The beach sediment along the Grassy Key shoreline in all areas pertinent hereto consists of calcareous material, made up of the breakdown of corals and coralling algae, with a significant fraction of other detrital marine material. The upper beaches of Grassy Key, including that on the Property, generally consist of coarse, calcareous sand with a small fraction of calcareous silt-size particles. The inter-tidal areas along Grassy Key consist of predominantly fine calcareous sand, with a greater fraction of calcareous silt. Extending out into the nearshore area all along Grassy Key, including that fronting the properties owned by Petitioners and Applicants, the sediment becomes a very fine calcareous sand, with a greater fraction of the material being calcareous silts and clays, and with a substantial amount of organic mud of a marine origin, classified as Islamorada muck. Since at least the 1970s, one wading in the nearshore waters along Grassy Key could expect to sink into the surface muck to a depth of anywhere from six inches to two feet. The depth of muck becomes less as one moves further out and approaches the offshore Thalassia beds. Although some areas offer more resistance than others, it is routine to experience difficulty in walking and wading along the coast of Grassy Key because of the high percentage of clays and silts in the substrate. The band of muck narrows as one proceeds towards the northern stretches of Grassy Key, until one reaches the furthest areas to the northeast where the nearshore transitions to exposed rock and hard bottom. The surface muck that exists in the nearshore waters of Grassy Key, having a sizable component of decaying organic material, gives off an odor of hydrogen sulfide when disturbed that some find to be unpleasant. The odor is a naturally- occurring condition of the sediment, and is common in mucky areas all around the southern coasts of Florida. The suggestion that the shoreline in the vicinity of the Petitioners’ property, and that of Applicants, was a naturally occurring white, sandy beach is contrary to the greater weight of the evidence. To the extent the shoreline at Petitioners’ property may have been temporarily altered by the overwash from Hurricane Wilma as discussed herein, Petitioners’ own post-Wilma man-made efforts at beach stabilization, or the redistribution of sediments occasioned by Hurricanes Isaac and Sandy in 2012, the evidence demonstrates the “mucky” condition described herein to be more consistent with the natural and long-standing conditions of Grassy Key. Thus, as Grassy Key exists in the present time, one may expect to encounter six inches to two feet of loose muck anywhere along the nearshore area. Close to shore of Grassy Key are scattered beds of Halodule, a species of seagrass that tends to emerge and grow in shallow waters. The growth of Halodule is influenced by the nature of the sediments, the salinity temperature, and clarity of the water. Storm events have a significant effect on its growth. Given its transient nature, Halodule may vary in any given area from nonexistent, to spotty, to well-established beds. As one moves further offshore, the Halodule transitions to large, continuous beds of Thalassia. Thalassia grows in deeper water, and is common to a depth of about 12 feet. Being deeper and less affected by storm energy, the line of the Thalassia beds off of Grassy Key has not substantially changed over time. As wind and waves come across the grass beds, and as tides ebb and flow, grass blades are cropped. The amount of grass varies seasonally to a degree. The cropped and dislodged seagrasses, along with other organic material entrained therein, are naturally carried by the tides and wind and stranded along the shoreline. The stranded material is known as wrack, and the line of stranded material is known as the wrack line. Grassy Key is well known for the large seagrass wracks that pile up on the shoreline. A wrack line is a normal and natural occurrence in marine environments like that of Grassy Key, and can be a good indicator of the upper edge of the water action at a particular time. The cropping and dislodging of seagrass is accentuated during major or minor storm events. During Hurricane Rita in 2005, a very large seagrass wrack was blown onto the shoreline of Grassy Key. It was subsequently blown back out to sea by the overwash from Hurricane Wilma. The decomposition of the seagrass and other organic materials creates a significant odor that is not uncommon. That odor of decomposing material is well-recognized as being associated with Grassy Key. Areas along the shoreline of Grassy Key have been used by sea turtles for nesting. However, the nature of the substrate in the area of the Property is not optimal for nesting. Generally, sea turtles require a nesting site with 15 to 20 inches of sand above the water table so as to allow them to dig a suitably deep and dry cavity for their eggs. The natural substrate along the section of Grassy Key at issue is coarser and more difficult to dig into, and does not have the depth of sand for the best chance of a successful nest. Despite the nature of the substrate, Petitioner testified as to her observation of turtle nests along her property in each year from 2006 through 2010. Since the SW Groin, the Mid-bulkhead, and the NE Groin were all in existence and functioning during that period, with work to the SW Groin having been completed by 2008, the preponderance of the evidence demonstrates that those structures have no effect on the success or failure of sea turtles to nest along the property. To the extent nesting has been disrupted since 2011, the most logical inference that can be drawn from the evidence is that such disruption is the result of the Mid-Jetty Extension, which is slated for removal under the terms of the Permit. The preponderance of the evidence demonstrates that the structures and activities authorized by the Permit will have no adverse effect on sea turtles. Hurricane Wilma In October, 2005, Grassy Key was pounded by Hurricane Wilma. The storm passed to the north, and created a substantial storm surge that moved from west to east across Grassy Key. The storm surge created a “ridge and runnel” effect on the Atlantic facing shoreline, with the channelization of the storm tide flow creating erosion and gullies on upland shore-adjacent properties. The storm surge and flooding across Grassy Key caused substantial wash-outs of sand; transported a large volume of sandy, upland sediments into the nearshore waters of the Atlantic Ocean; and created washover “fans” of material along the shoreline of Grassy Key. The effects of the Hurricane Wilma storm surge manifested just north of the Property, became substantial at the Property, and continued south down the shoreline for a considerable distance. At the Property, sand was pushed from 50 to 100 feet waterward from the existing shoreline, and a substantial runout was created running parallel and north of the SW Jetty. The sand pushed into the water buried everything in its path, including seagrasses. In short, the post-Wilma shoreline from the Property south along Grassy Key was left in a completely disrupted state. The nearshore waters fronting the properties owned by Petitioners and Applicants were affected by the deposition of sandy, upland sediments, which temporarily created areas of substantially harder-packed sediment. Over time, as the shoreline equilibrated and the sandy sediment distributed through a broader area, more typical shoreline conditions returned. The photographic evidence demonstrates that the Mid- bulkhead and the SW jetty structures were impacted by the Hurricane Wilma storm surge. In addition, the sandy area between the mid-bulkhead and the SW jetty was pushed seaward from its previous location. The scars from Hurricane Wilma remain evident through the most recent aerial photographs received in evidence. It is visually apparent that seagrass, though reappearing in patches, has not reestablished in the nearshore areas along the affected shoreline of Grassy Key -- including the areas in front of the Property and the property owned by Petitioners -- to the extent that it existed prior to the storm. Post-Wilma Activities When Hurricane Wilma hit, the Property was owned by Burgess Lea Levine. Not long after Hurricane Wilma, Ms. Levine shored up the SW Jetty, and performed work in the “beach” area between the mid-bulkhead and the SW jetty. The photographic evidence also supports a finding that the rock outline of the Mid-jetty was reestablished to its pre-Wilma configuration. The repairs to the SW Jetty resulted in a structure that is virtually indistinguishable in size and shape to the SW Jetty as it presently exists. The wrack line at the beach area after it was “worked” following the passage of Wilma, shows the area in which work was done to be generally consistent with -- though slightly seaward of -- the 2005 post-Wilma shoreline. In 2008, Ms. Levine applied for a series of exemptions and for consent of use for state-owned lands for “shoreline repair, replace earthen ramp with a concrete ramp, repair wood deck, replace mooring piles & maintenance dredge existing channel w/in Atlantic Ocean.” On September 19, 2008, the DEP issued a regulatory authorization and proprietary submerged land approval. The Rights of Affected Parties that accompanied the September 19, 2008, notice provided that “[t]his letter acknowledges that the proposed activity is exempt from ERP permitting requirements” and that “this determination shall expire after one year.” The notice of Rights of Affected Parties did not apply to the proprietary authorization. At some time after issuance of the regulatory authorization, Ms. Burgess initiated additional work to repair the SW Jetty. The photographic evidence, which is persuasive, indicates that the work on the SW Jetty, including the concrete cap, was complete by the end of 2008. When Applicants purchased the Property, the determination of exemption issued in 2008 had, by application of the notice of Rights of Affected Parties, expired. Shortly after the Applicants purchased the property, they had the existing family home demolished. Applicants intend to construct a winter vacation home for their personal use on the property. 2012 Storms In August and October 2012, Grassy Key was subject to event-driven conditions as a result of the passage of Hurricanes Isaac and Sandy. Those storms redistributed large areas of sediments that had been moved offshore by the effects of Hurricane Wilma. The Proposed Permit The February 20, 2013, Permit provides that the structures described herein do not require the issuance of an Environmental Resource Permit, subject to the criteria and conditions in Florida Administrative Code Rule 40E-4.051. The Permit provides that the boat ramp is eligible to use the general permit in Florida Administrative Code Rule 62-330.417, the repair and replacement of the dock is exempt pursuant to section 403.813(1)(b), Florida Statutes, the maintenance dredging of the Channel is exempt pursuant to section 403.813(1)(f), and that the repair and replacement of the NW Jetty, the SW Jetty, and the Mid-bulkhead are exempt because the structures are “historic in nature and pre-dates Department regulations.” In addition to the regulatory authorizations, the Permit granted proprietary authorization by Letter of Consent for the dock pursuant to Florida Administrative Code Rule 18- 21.005(1)(c)4., and for the Channel, the NW Jetty, the SW Jetty, and the Mid-bulkhead pursuant to rule 18-21.005(1)(c)7. The Permit established the mean high-water line as that existing in 1974 and depicted on the “Richmond Survey.” Proprietary authorization for the boat ramp was determined to be unnecessary due to its location above the mean high-water line. Finally, proprietary authorization for the “Sandy Area” or beach between the Mid-bulkhead and SW Jetty was granted by Letter of Consent pursuant to rule 18-21.005(1). On September 20, 2013, the DEP filed a Notice of Additional Grounds for Exemption Determination, in which it found each of the structures subject to the regulatory review to “have only minimal or insignificant individual or cumulative adverse impacts on water resources” and to thus be exempt from the need to obtain an Environmental Resource Permit pursuant to section 373.406(6), Florida Statutes. On December 12, 2013, Applicants filed a Notice of Filing Proposed Changes to the Pending Agency Action in which they agreed to certain additional conditions, and which referenced the October 1, 2013, repeal of rule 40E-4.051, and its replacement by the “Statewide ERP rules.” For purposes of this de novo proceeding, the proposed Permit at issue includes the February 20, 2013, Permit; the September 20, 2013, Notice of Additional Grounds for Exemption Determination; and the December 12, 2013, Notice of Filing Proposed Changes to the Pending Agency Action. The Proposed Structures Groins There has been some confusion relating to the names of the structures that are subject to the proposed Permit. Two of the structures are referred to as jetties, the NE Jetty and the SW Jetty, and the middle structure is referred to as the Mid- bulkhead. A jetty is a navigation structure that is constructed at a barrier inlet. Its purpose is to stabilize the inlet and prevent shoaling by “jetting” current and wave-driven sand further offshore, such that the offshore bar is moved into deep enough water to allow navigation in and out of the tidal inlet, and allowing the tidal current between the ocean and the receiving body of water to keep the inlet scoured and open. There are 48 jetties on the open coast of Florida, none of which are in the Florida Keys. A groin is a structure designed for shore protection purposes. A groin is typically aligned perpendicular to the shoreline, or “shore normal.” The structures identified in the Permit as the NE Jetty and the SW Jetty are clearly groins, and not jetties. The mid-bulkhead is a groin, generally for shore confinement, with a channel-facing bulkhead. For purposes of continuity, the structures will be identified by the names given them in the Permit. Since there is negligible wave energy along the shoreline normal conditions, the groins have little or no day- to-day effect on longshore transport. Under storm conditions, the structures affect longshore transport, as evidenced by accretional “fillets,” and function as shoreline protection and confinement structures. The rock groins provide shelter, habitat and structure for corals, sponges, lobster, and fish in the area. The preponderance of the evidence demonstrates that the groins authorized by the Permit will have no adverse effect on fish and wildlife resources. NE Jetty The NE Jetty was originally constructed in the early 1960s, likely concurrent with the dredging of the navigational channel. The quality of the aerial photographs of the period make it difficult to tell if the NE Jetty was a loosely-placed rock embankment or a more well-designed and constructed structure. However, the fillet of sand accreted to the north of the Channel demonstrates that the jetty was in existence and functioning as a shore-protection structure. By the 1970s, the NE Jetty had become overwhelmed by longshore sediment transport from the northeast. Sediment overtopped the NE Jetty and filled in the landward reaches of the Channel. At that point, ability of the NE Jetty to perform as a shore protection structure was compromised to the point that it could no longer hold the shoreline out of the basin or the landward portion of the Channel. The Mid-bulkhead became the dominant structural control over the shoreline and started to accrete the shoreline to the northeast. At some time between 1977 and 1981, the Channel was maintenance dredged pursuant to a permit issued by the Department of Environmental Regulation, DEP’s predecessor agency. The NE Jetty appeared on the plans for the maintenance dredging. Thus, the most reasonable inference that can be drawn from the evidence is that the NE Jetty was repaired and restored in conjunction with the approved maintenance dredging. By 1981, the NE Jetty had been restored as the dominant shore protection structure north of the Channel, and a fillet of accreted material had been reestablished. The aerial photographs from that period are not sufficiently distinct to determine the precise size, shape, and configuration of the NE Jetty at that time. However, there is no evidence of additional work having been performed on the NE Jetty between 1981 and 1985. By 1985, the NE Jetty existed in substantially the size, shape, and configuration as it existed at the time of Hurricane Wilma. Between 1981 and the 2005 arrival of Hurricane Wilma, the evidence is convincing that the NE Jetty was holding up the shoreline to the northeast and preventing sediment from filling in the upper reaches of the Channel. Although the evidence suggests that the NE Jetty had, by 2005, begun to show its age, the continuous presence of an accretional fillet demonstrates that it continued to serve its function as a shore-protection structure. Although the NE Jetty suffered damage from Hurricane Wilma, it continued to perform its shoreline protection function. Aerial photographs taken in 2009 and 2011 show a relatively distinct structure with a well-defined accretional fillet. Thus, the greater weight of the evidence demonstrates that, at the time of its repair in May 2011, the NE Jetty was a functional groin. The NE Jetty, as repaired in 2011, is of substantially the same size, shape, and location as the structure depicted in aerial photographs taken in 1985, 2009, and early 2011. Although the elevation of the structure was increased over its pre-repair elevation, the increase was that reasonably necessary to prevent the function of the structure from being compromised by the effects of age and weather. The work performed on the NE Jetty, consisting of new rock laid on top of the existing rock, constituted repair and maintenance of the existing structure. Since 2005, and at the present time, the shoreline north of the NE Jetty has reached a state of equilibrium and stability, and is not expected to change significantly from its current condition. The preponderance of the competent, substantial evidence demonstrates that the effect of the NE Jetty on the shoreline and water resources of Grassy Key in the vicinity of the properties owned by Applicants and Petitioners is minimal and insignificant. The sand and sediment accreted to the north of the NE Jetty since 1981 is in the range of 250 square feet. SW Jetty The aerial photographs from 19647/ demonstrate that some form of structure then existed at the location of the current SW Jetty. The structure is indistinct due to what appears to be sidecast material from a small channel in front of the property to the immediate south of the Property. By 1971, the SW Jetty had become more distinct. From that time forward, the SW Jetty, and its accompanying fillet of accreted material, appears in roughly the size and shape of the structure as it appeared immediately prior to the arrival of Hurricane Wilma. The SW Jetty was heavily impacted by Hurricane Wilma. The overwash from the storm created a substantial runout alongside the SW Jetty, and the post-storm aerials suggest that the jetty boulders were undermined and shifted from their more uniform 2003 appearance. Immediately after Hurricane Wilma, the owner of the Property commenced restoration and repair activities. As part of the activities, the SW Jetty was repaired with the addition of boulders, which were often three feet and every now and then as much as four feet across. The boulders, being irregularly shaped, could not be stacked like Legos®, so the repairs were not neatly within the precise pre-Wilma footprint. However, the repaired SW Jetty was substantially in the length and location as existed prior to Hurricane Wilma, though it may have had a slightly wider cross-section. By 2007, the work on the SW Jetty was complete, and it had assumed its present appearance with the addition of a concrete cap. Its appearance -- i.e. length, width, and location -- in 2007 and 2008 was not dissimilar from its appearance in 2003. As repaired, the SW Jetty effectively constitutes the same structure that it has been since its initial construction. From a coastal engineering perspective, the work that was performed on the SW Jetty, consisting generally of new rock laid on top of the existing rock, constituted repair and maintenance of the existing structure. Dr. Lin testified that between 1974 and 2011, the area to the southwest of the southwest jetty was “about equalized,” though it was “accreting a little bit.” Thus, the effect of the SW Jetty on the shoreline of Grassy Key in the vicinity of the properties owned by Applicants and Petitioners from 1974 to 2011 was minimal and insignificant. Dr. Lin testified that, since 2011, the same area had eroded. The only substantive shoreline change that logically accounts for that subsequent erosion is the Mid-bulkhead extension, which is slated for removal under the terms of the proposed Permit. Petitioner testified that she observed no adverse effects from activities on the Property until after February 2011.8/ Since work on the SW Jetty was complete by no later than 2008, Petitioner’s testimony supports a finding that the SW Jetty has had no measurable effect on the water resources in the vicinity of the properties owned by Applicants and Petitioners. The preponderance of the competent, substantial evidence demonstrates that the effect of the SW Jetty on the shoreline and water resources of Grassy Key in the vicinity of the properties owned by Applicants and Petitioners is minimal and insignificant. Mid-bulkhead The structure of the Mid-bulkhead first appeared as part of the sidecast material from the excavation of the navigation channel in 1964. It coalesced into a defined but smaller and more rudimentary structure in the 1971-1972 time period. At that time, it was acting as the predominant shore protection structure due to the overtopping of the NE Jetty with sediment, which also filled in the landward reaches of the Channel. By 1981, after the maintenance dredging of the Channel, the Mid-bulkhead had assumed substantially the size, shape, and location that it has currently. The Mid-bulkhead has a navigation function of protecting the landward extent of the Channel from the collapse of adjacent sand and sediment, and a shore protection and compartmentalization function. Those functions have been consistent since 1981. The Mid-bulkhead appears to have been subjected to the overwash of sand and sediment from Hurricane Wilma, though it maintained its shape and form. The outline of the Mid-bulkhead appears to be more well-defined after the initial post-Wilma repairs. In any event, the configuration and size of the Mid-bulkhead is substantially the same as it had been since 1981. At some point, the interior section of the Mid- bulkhead was topped with soil that is inconsistent with that naturally occurring in the area. That fill was confined, and brought the Mid-bulkhead to a more even grade with the rock outline, but could have had no measurable effect on the shoreline and water resources of Grassy Key in the vicinity of the properties owned by Applicants and Petitioners. The preponderance of the competent, substantial evidence demonstrates that the effect of the Mid-bulkhead is minimal and insignificant. Channel In 1961, the Department of the Army authorized dredging of a navigation channel at the Property. The approved channel was to be 700 feet long, 30 feet wide, and to a depth of five feet below mean low water. The Florida Trustees of the Internal Improvement Fund issued a letter of no objection. By 1964, the Channel that is the subject of this proceeding had been dredged, though not to the 700-foot length approved. Rather, the Channel was dredged to a length of approximately 290 feet. Much, if not all of the dredge spoil was sidecast, creating a rock structure alongside the Channel. Measurements taken during the course of this proceeding demonstrate that the initial dredging resulted in near vertical side slopes, which shows that the bailing of the bedrock was accomplished to the limits. The width of the Channel is from 28 feet to 32 feet wide, which is within an acceptable tolerance of the 30-foot approved width. In 1976, the then-owner of the Property sought a permit from the DEP’s predecessor, the Department of Environmental Regulation, to maintenance dredge the Channel to a dimension of 290 feet long and 30 feet wide, to a depth of minus 8-feet mean high water, and to construct a new rock jetty to extend 230 feet waterward from the existing terminus of the NE Jetty. Given the mean tide range of 1.7 feet at the Property, the depth of the proposed dredging would have been minus 6.3 feet mean low water, or 1.3 feet deeper than originally approved. The permit drawings depict the existing NE Jetty, the Channel boundary, the outline of the Mid-bulkhead, and the sidecast rock structure alongside the southern side of the Channel. The permit was denied. In 1977, the owner of the property reapplied for a permit to maintenance dredge the Channel to a dimension of 290 feet long and 30 feet wide, and to a depth of minus 4.0 feet below mean low water nearshore to minus 6 feet below mean low water at the waterward end. The proposal to construct an extension of the NE Jetty was deleted. The permit was issued, and a severance fee for the dredged material was paid based on a projected 700 cubic yards of material removed. The permit drawings and photographs depict the existing NE Jetty, the nearshore Channel boundary, and the general outline of the Mid- bulkhead. By 1981, aerial photographs demonstrate that the maintenance dredging of the Channel was complete, the NE Jetty was in place and functioning to protect the shoreline as evidenced by the accretional fillet, and the Mid-bulkhead had assumed its approximate current shape and configuration. Although the Channel has varied in depth over the years since the maintenance dredging and Hurricane Wilma, the greater weight of the evidence, including photographic evidence, indicates that the Channel was well-defined and remained navigable during that period. The Channel is an open-water exposed channel. Water in the Channel mixes due to direct tidal flow and the sheet flow of water due to shear wind stress. As water passes over the Channel, it sets up gyre, which is a mixing process. The open- water exposed Channel is subject to a high degree of mixing, even on normal waveless conditions, because of the wind transport of water and the tidal transport of water. The Channel is not a semi-enclosed basin. A semi- enclosed basin does not receive the direct forcing functions that an open-water channel receives. A semi-enclosed basin has no direct connection to open waters, but is connected to open waters by a narrower opening. Although a semi-enclosed basin exchanges water via every tidal cycle, the flushing process is one of slow mixing, in which a little bit of water is added to and withdrawn from the larger basin through the narrow opening during each tidal cycle. In such a case, a flushing analysis may be necessary to determine how much time and how many tidal cycles it may take to effect a complete exchange of the water in the semi-enclosed basin, and thus, for example, to dilute a pollutant to an acceptable level. A flushing analysis is not needed in this case because the Channel is an open-water, openly-exposed location subject to a high degree of mixing under normal day-to-day tidal processes. There is no greater basin connected by a restricting connection as with a semi-enclosed basin. Rather, the Channel has direct exposure to the tides, along with wind shear stress moving the water. The evidence in this case is substantial and persuasive, because the Channel is highly exposed to the open water and the tides, and a well-mixed and well-flushed aquatic system, that a flushing analysis is neither required nor necessary. Dock The dock made its first obvious appearance in 1981. It appears in a consistent shape and appearance through 2011. Aerial photographs taken in 2012, after the maintenance dredging of the Channel was conducted, show the dock had been removed. At the time of the hearing, the Applicants had installed new pilings and vent boards for the replacement dock, but the decking had not been installed. Work to complete the replacement of the dock was halted due to the pendency of the litigation challenging the structures. The proposed dock is less than 500 square feet. It is proposed for non-commercial, recreational activities. It is the sole dock proposed on the Property. The proposed dock will not impede the flow of water or create a navigational hazard. Boat Ramp Since the issuance of the 2008 approval, the boat ramp site was graded and stabilized in limerock material. The concrete ramp was not completed due to the pendency of the litigation challenging the structures. However, Applicants propose to pave the ramp with concrete. Based on Mr. Clark’s observations during his site visits, the boat ramp is landward of the mean high waterline depicted on the survey. The preponderance of the evidence demonstrates that the proposed boat ramp will provide access to the Channel, which provides a minimum navigational access of two feet below mean low water to the ramp. Applicants have agreed to install depth indicators at the ramp to identify the controlling depths of the navigational access. The work on the ramp involves no seagrass beds or coral communities. The ramp as proposed will require no more than 100 cubic yards of dredging. The total width of the ramp is to be 20 feet and the ramp surface will be no wider than 12 feet. Beach Area The area between the SW Jetty and the Mid-bulkhead is an accreted beach-type area that has been confined and protected by the Mid-bulkhead and the SW Jetty. The shoreline landward of the mean high water line, from the dry beach and to the upland, is somewhat steeper than adjacent unprotected shorelines, which is indicative of the grooming of the upper beach sediment and the stability of the shoreline between the Mid-bulkhead and the SW Jetty. As a result of the Hurricane Wilma storm surge, a substantial amount of sediment was swept across the Property and into the Atlantic waters. The beach area was inundated with sand and sediment from the overwash, which appears to have moved the shoreline well waterward of its previous position. Along the northern side of the SW Jetty, a substantial channelized gully was created. The configuration of the shoreline post-Wilma suggests that efforts were made by the then-owner of the Property to fill in the gully on the northern side of the SW Jetty, and to groom and restore the shoreline by redistributing sand and sediment on the Property. It is typical, and allowable under DEP emergency final orders, for affected property owners to redistribute overwashed deposits and place them back within the beach system. In that regard, the DEP encourages the redistribution of clean beach sand back onto the beach. The then-owners of the Property were not alone in taking steps to address the effects of Hurricane Wilma on their adjacent shorelines. The photographic evidence demonstrates that Petitioners engaged in similar restorative activities, which included bringing in material purchased from a contractor to fill in a gully created on their property by the overwash. Observation of representative soil samples from the beach area demonstrate that the soils are consistent with those in the upper beach areas found throughout the area. The only areas of inconsistent soils were found in the interior of the rock structure of the Mid-bulkhead, which contained a four to six-inch layer of soil with a different consistency and darker brown color, and small area of similar soil directly adjacent thereto and well above the mean high water line. The greater weight of the competent, substantial, and credible evidence demonstrates that there was no substantial amount of “fill” from off-site placed on or adjacent to the beach area. Rather, the nature, appearance, and composition of the soils suggests that the temporary increase in the size of the beach area after Hurricane Wilma was the result of grooming and redistribution of sand and sediment pushed onto the Property and into the nearshore waters by the Hurricane Wilma storm surge. In the years since Hurricane Wilma, the influence of normal tidal and weather-driven events has returned the beach area between the mid-bulkhead and the SW jetty to roughly the configuration that existed prior to the passage of Wilma, though it remains somewhat waterward of its pre-Wilma location.
Recommendation Based on the foregoing Findings of Fact and Conclusions of Law set forth herein it is RECOMMENDED that the Department of Environmental Protection enter a final order approving the February 20, 2013, proposed Permit, as conditioned by Applicants’ December 12, 2013, Proposed Changes to the Pending Agency Action. DONE AND ENTERED this 25th day of July, 2014, 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 25th day of July, 2014.
The Issue The issue in this case is whether the evidence sustains the decision of the City of Clearwater Development Code Adjustment Board (the Board) to deny the application of the Appellant, Clearwater Bay Marine Ways, Inc., for a 62-space parking requirement variance (200 spaces instead of the 262 required under the Code) for its property located at 900 North Osceola Avenue, Clearwater, Florida. (The variance is required as a result of the Appellant's desire to use a part of the property as a cruise ship docking facility.)
Findings Of Fact On or about October 25, 1993, the Appellant, Clearwater Bay Marine Ways, Inc., applied to the City of Clearwater Development Code Adjustment Board (the Board) for an 81-space parking requirement variance (128 spaces instead of the 209 required under the Code) for its property located at 900 North Osceola Avenue, Clearwater, Florida. After filing the application, the site plan was modified, and the variance application was modified to request a 62-space variance (200 spaces instead of the 262 required under the Code). The variance is required as a result of the Appellant's plan to have Adventure Seaways Corporation use a part of the property for use as a docking facility for its 600-passenger cruise ship, the Majestic Empress. The City of Clearwater Development Code (the Code) has no parking space requirements specifically designed for cruise ship operations. To establish the parking space requirements, it was decided to utilize Section 42.34(6)(d)2.c. of the Code, which addresses certain "retail sales and service uses," and states: Theaters, indoor and outdoor recreation centers, swimming pools, skating rinks and other public or private recreation and amusement facilities: One parking space per three customers or patrons computed on the basis of maximum servicing capacity at any one time, as determined by the requirements of the city, plus one additional space for every two persons employed on the premises at peak period of use. Specific provisions over and above the standard may be required for uses such as movie theaters involving successive changes of patrons with a corresponding overlap in parking required. Under that provision, it was calculated that 200 spaces would be needed for peak capacity for the 600-passenger cruise ship. An additional 62 parking spaces are needed for other uses proposed in the site plan (including boat slips, a dive charter operation, a sail charter operation, a 2,800 square foot parts and service business and three work bays), for a total of 262 parking spaces for the overall site plan. The evidence was that no adjustments to the calculation under the "one space per three customers or patrons" formula were "determined by the requirements of the city," and that no additional spaces were required for "persons employed on the premises." (There was some evidence that the Adventure Seaways employees will park off-site.) Nor was there any evidence that there were any "[s]pecific provisions over and above the standard required for . . . successive changes of patrons with a corresponding overlap in parking required." The Adventure Seaways Corporation plans two excursions of the Majestic Empress a day, one during the day and one in the evening. It is expected that the ship would sail at full capacity only approximately one day a week, on Saturday. At peak capacity, it is expected that 30 percent of the passengers will arrive at the docking facility by tour bus. During the day cruise, the buses would leave the facility and return at the end of the cruise to drop off passengers for the evening cruise and pick up off-loading day cruise passengers. They would not remain at the facility during the times other cruise ship passengers would have their cars parked at the facility. Using only the "one space per three customers or patrons" formula under Section 42.34(6)(d)2.c. of the Code, the 70 percent of the total complement of passengers, who are expected to arrive by personal vehicle on peak days, would require only 140 parking spaces (420 passengers divided by three per parking space), well below the 200 spaces allocated to the cruise ship operation under Clearwater Bay Marine Ways site plan. Since Adventure Seaways has not been able to use the Majestic Empress at the Clearwater Bay Marine Ways facility without the parking space variance, it has transferred a smaller cruise ship, the Crown Empress, from its docking facility at Johns Pass on Treasure Island in the interim. The Crown Empress's capacity is only 400 passengers, and no parking space variance is required to use it at the Clearwater Bay Marine Ways facility. Meanwhile, Adventure Seaways has received temporary permission to utilize the Majestic Empress at the Johns Pass facility on the condition that it make greater than normal use of tour buses to transport passengers to and from the Johns Pass docking facility. Adventure Seaways purchased the Majestic Empress after being encouraged by City officials about the prospects of being able to utilize the Clearwater Bay Marine Ways facility. After purchasing the vessel, it had the vessel reconfigured to reduce its draft to accommodate the shallow waters it would have to navigate getting to and from the facility. Adventure Seaways also closed in the top deck of the vessel to meet Code requirements for noise control. Neither the special shallow draft configuration nor the noise control measures are required for utilization of the Johns Pass facility. Part of the encouragement by City officials about the prospects of Adventure Seaways being able to utilize the Clearwater Bay Marine Ways facility included assurances that the City would help Adventure Seaways gain access to additional parking, or develop or acquire additional parking, in the vicinity, if needed. Another option would be to utilize off-site parking and transport passengers to and from the Clearwater Bay Marine Ways facility by bus.
