The Issue The issue presented in this case is whether the Petitioner has the requisite experience necessary in order to qualify to take a Class A drinking water treatment plant operator certification exam.
Findings Of Fact On May 11, 1989, Petitioner, Albert Galambos, submitted an application to Respondent, Department of Environmental Regulation ("DER"), to take the prerequisite examination necessary for certification as a Class A drinking water treatment plant operator. On May 20, 1989, Helen Setchfield, Certification Officer for DER mailed to the Petitioner a Notice of Final Order of Denial of Petitioner's Application for Examination and Certification as a Class A drinking water treatment plant operator. The Notice of Final Order of Denial stated that Petitioner was ineligible to sit for the examination and/or was ineligible for certification as a Class A drinking water treatment plant operator because his "actual experience is in an occupation which does not qualify as actual experience as an operator of a treatment plant as defined in Section 17-16.03, Petitioner has worked at the Miami-Dade Water and Sewer Authority Department ("Authority") for 17 years. His current position is Water and Sewer Mechanical Operations Supervisor, a position he has held since 1983. This position entails actual onsite operational control of the equipment and mechanical processes of the Authority's water production plants and overseeing all maintenance of equipment at the Authority's three regional water treatment plants and the smaller interim plants, developing safety procedures for the operation of equipment, training plant personnel in the mechanical operation of the equipment, establishing maintenance schedules and maintaining those records, and taking samples as necessary to determine proper equipment functioning, performing or overseeing the loading of chemicals and the connecting of chlorine cylinders, and the recharging of these systems. He assists the certified operators in remedial action if some aspect of the plant is not functioning properly, but he has no supervisory authority over the certified operators. Petitioner is held responsible by the Division Director for the smooth running of the equipment at the Authority's water treatment plants. He prepares reports, logs and records regarding the mechanical equipment and operations of the plant. Petitioner supervises and manages 36 employees who are mechanics, electricians and laborers. From 1979 to 1983, Petitioner was a plant maintenance foreman for the Authority. This position included responsibility for supervising and performing skilled mechanical tasks on a variety of mechanical equipment at the water plants. From 1976 to 1979, Petitioner was a plant mechanic at the Authority. This position was skilled work at the journeyman level in the installation, repair, and maintenance of mechanical equipment at the water plants. Between 1974 and 1976, Petitioner worked in an unclassified position doing what a diesel plant operator does at the Authority. This position involved responsibility for the operation of large diesel engines used to drive large pumps and related equipment. From 1972 and 1974, Petitioner was a semiskilled laborer with the Authority. This position involved heavy manual work requiring limited skills in various maintenance tasks. Petitioner has never served as a drinking water treatment plant operator nor been licensed as a drinking water treatment plant operator at any classification. Petitioner has not previously applied for, nor obtained any water treatment plant operator certification. Petitioner has successfully completed the required course work for Class A operator certification. Petitioner is a high school graduate and has successfully completed the required coursework for certification. These activities yield three years and four months of constructive experience towards certification. Petitioner's experience prior to 1983 did not constitute actual experience because in those positions, Petitioner did not have operational control of a drinking water treatment plant. Even if Petitioner's current position was accepted as "actual experience" (a determination which is specifically not resolved here,) the combination of Petitioner's constructive and actual experience would be less than the twelve years of experience required for certification as a Class A operator. Thus, Petitioner has failed to prove that he meets the experience requirement necessary for certification as a Class A drinking water treatment plant operator. Petitioner's current position is supervisory and he has a great deal of maintenance experience gained through his various positions at the Authority. Petitioner's current position affords him the opportunity to learn about many aspects of operating a treatment plant efficiently by conducting inspections of the treatment plant processes, monitoring of the treatment plant processes, and adjusting the treatment plant processes. However, the evidence did not establish that Petitioner manages the treatment plant processes as required to constitute actual experience under the existing rules. It is unclear from the evidence presented whether Petitioner's day-to- day onsite experience at the plants constitutes the actual operational control of a water treatment plant. It would appear that Petitioner's current position does not allow him experience in managing the overall treatment process. However, further evidence and/or a better understanding of Petitioner's job responsibilities could alter this observation. In view of the disposition reached in this case, that issue need not be addressed further at this time.
Recommendation Based on the foregoing Findings of Fact and Conclusions of Law, it is RECOMMENDED that the Department of Environmental Regulation issue a final order denying Petitioner's application of May 10, 1989, for certification as a Class A drinking water treatment plant operator. DONE AND ENTERED in Tallahassee, Leon County, Florida, this 3rd day of January 1990. J. STEPHEN MENTON Hearing Officer Division of Administrative Hearings The DeSoto Building 1230 Apalachee Parkway Tallahassee, Florida 32399-1550 (904) 488-9675 Filed with the Clerk of the Division of Administrative Hearings this 3rd day of January, 1990.
The Issue The issue presented is whether Petitioner has the requisite experience necessary for certification by Respondent as a Class A drinking water treatment plant operator.
Findings Of Fact On May 9, 1989, Petitioner, Allen T. Segars, in an attempt to enhance his professional status, applied to Respondent, Department of Environmental Regulation, for certification as a Class A drinking water treatment plant operator. Respondent reviewed Petitioner's application and denied it for failure to demonstrate the requisite twelve years of experience in the operation, supervision and maintenance of a drinking water treatment plant. Since June 30, 1969, Petitioner has been employed by the Miami-Dade Water and Sewer Authority (WASA) in several capacities each dealing with drinking water treatment. However, Petitioner has never served as a drinking water treatment plant operator nor been licensed as a drinking water treatment plant operator at any classification. WASA is composed of three regional drinking water treatment plants and nine interim plants servicing portions of South Florida with a total average production of 320 million gallons per day. From June 30, 1969 through March 21, 1982, Petitioner worked with the electrical component of WASA. For seven of those years, he worked as an electrician. He was then promoted to be an electrical supervisor which position he held for five years. His duties while working in the electrical operation involved performing preventative maintenance, installing and repairing equipment and supervising the personnel working with him in the electrical area. This experience is not in the management of a drinking water treatment plant and does not qualify as actual experience therein. On March 22, 1982, Petitioner was promoted to his current position of Water Production Superintendent to oversee the employees and the entire drinking water treatment operation of WASA. He remains on call twenty-four hours a day and is actually on the job approximately forty-five hours per week. He begins a typical day around 6:00 A.M. by contacting each of the plants to determine their capacity levels and to find out if any problems exist. If the operation is normal, Petitioner begins his daily process of visiting each plant. He begins at the Hialeah Treatment Plant which houses his office. At each stop, Petitioner goes over the operational log with the treatment plant supervisor. He inspects the facility. He collects samples and spot tests the results. If an adjustment is necessary, he prescribes the remedy or goes over it with the operator on duty. He assesses the chemical inventory and places necessary orders. Petitioner also makes repairs and adjustments; he carries his own repair tools. Petitioner performs most all of the functions of the treatment plant supervisor. Added to his responsibilities are the administrative duties of being the Water Production Superintendent. On the average, these administrative duties encumber less than eight hours of his normal forty-five four week Although Petitioner's current position is supervisory in nature, in fact, it is a technical and operational position. Petitioner participates at most all levels of the operation of the drinking water treatment process. In each position that Petitioner has held with WASA, he has been involved in onsite, on-hands activity with the facilities and equipment controlling the operation of WASA. For the seven years and one month that Petitioner has served as Water Production Superintendent, his work has been actual experience in the operation supervision and maintenance of a drinking water treatment plant. Petitioner is a high school graduate and has successfully completed 128 hours of classroom and laboratory work in a course approved by Respondent. Petitioner has also completed 16 classroom hours in a course pertaining to cross connection control in a treatment plant. These activities yield three years and five months of constructive experience. The combination of Petitioner's total experience accounts for ten years and six months of the twelve years of experience required for classification as a Class A operator. Thus, Petitioner's activity fails to meet the experience requirement necessary for certification as a class A drinking water treatment plant operator.
Recommendation Based on the foregoing Findings of Fact and Conclusions of Law, it is: RECOMMENDED that the Department of Environmental Regulation issue a Final Order denying Petitioner's application of May 9, 1989 for certification as a Class A drinking water treatment plant operator. DONE AND ENTERED in Tallahassee, Leon County, Florida, this 7th day of November 1989. JANE C. HAYMAN 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 7th day of November 1989. APPENDIX TO RECOMMENDED ORDER CASE NO. 89-3705 Petitioner's proposed findings of fact are addressed as follows: Addressed in paragraph 5. Addressed in paragraph 1. Addressed in paragraph 1. Addressed in paragraph 1. Subordinate to the result reached. Subordinate to the result reached. Subordinate to the result reached. Subordinate to the result reached. Subordinate to the result reached. Subordinate to the result reached. Addressed in paragraphs 5 and 6. Addressed in paragraph 6. Addressed in paragraph 5. Not supported by competent and substantial evidence. Addressed in paragraph 6. Addressed in paragraphs 4 and 6. Addressed in paragraphs 3 and 8. Respondent's proposed findings of fact are addressed as follows: Addressed in paragraphs 2 and 3. Addressed in paragraphs 5 and 6. Addressed in paragraph 4.- Addressed in paragraph 9. Addressed in paragraph 1. Addressed in paragraph 1. Subordinate to the result reached. Conclusion of law. Subordinate to the result reached and addressed in paragraph 10. Addressed in paragraph 8. Subordinate to the result reached. Subordinate to the result reached. Subordinate to the result reached. Subordinate to the result reached. Subordinate to the result reached. COPIES FURNISHED: Alice Weisman, Esquire Robert A. Sugarman, Esquire Sugarman & Susskind, P.A. 5959 Blue Lagoon Drive Suite 150 Miami, Florida 33126 Cynthia K. Christen, Esquire Department of Environmental Regulation Twin Towers Office Building 2600 Blair Stone Road Tallahassee, Florida 32399-2400 Dale H. Twachtmann, Secretary Department of Environmental Regulation Twin Towers Office Building 2600 Blair Stone Road Tallahassee, Florida 32399-2400 Daniel H. Thompson General Counsel Department of Environmental Regulation Twin Towers Office Building 2600 Blair Stone Road Tallahassee, Florida 32399-2400
Findings Of Fact The Petition herein was filed by Petitioner with PERC on February 14, 1975. (Hearing Officer's Exhibit 1). The hearing in this cause was, scheduled by notice dated May 23, 1975. (Hearing Officer's Exhibit 2). The City of Port St. Joe, Florida, is a Public Employer within the meaning of Florida Statutes, Section 447,002(2). (Stipulation TR 6). The Laborers' Local Union No. 1306 is an employee organization within the meaning of Florida Statutes, Section 447.002(10). (Stipulation, TR 6). There is no contractual bar to hold an election in this case. (Stipulation, TR 6, 7). There is no pertinent bargaining history which affects this matter. (Stipulation, TR 7). PERC has previously concluded that the Petitioner is a duly registered employee organization (See: Hearing Officer Exhibit 3). No evidence was offered at the hearing to rebut the administrative determination previously made by PERC. PERC has previously concluded that the Petitioner filed the requisite showing of interest with its petition (Hearing Officer's Exhibit 4). No evidence was presented to rebut the administrative determination. Petitioner and the Public Employer stipulated and agreed that all employees of the City of Port St. Joe employed at the hospital, or in the Fire and Police Departments should be excluded from any unit ultimately certified. The parties further stipulated that Mr. Brook, the City Clerk-Auditor, and Mr. R. F. Simon, Manager of the Waste Water Treatment Plant, should be excluded from the unit; and, that Mr. Joe Badger, the Janitor at City Hall, who is not identified in the proposed unit designations, should be included within the unit. (Stipulation TR 10, 11). The City of Port St. Joe operates under a city commission form of government with a mayor and four commissioners. The, City has approximately 80 to 85 employees. The functions of government are not rigidly departmentalized in Port St. Joe. The, largest City Department is the Water and Waste Water Treatment Plant. This department is headed by a manager, Mr. R. E. Simon, who answers to the City Commission. Approximately 40 of the city's employees are in this department. The city's other two departments are more vaguely defined. There is a department concerned with parks and Cemeteries, and Water and Sewers, which employs approximately 20 persons; and a department concerned with Roads and streets, garbage and Trash Collection, and Warehouse and Garage, which employs approximately 18 - 20 persons. Each of these latter two departments is headed by the City Auditor-Clerk, Charles W. Brock. Mr. Brock answers to the City Commission. (TR 12-14, 29, 34-35). The Public Employer argued that all city employee other than those employed at the hospitals or in the Police or Fire Departments should be included within an appropriate unit. Only the manager of the Water and Waste Water Treatment Plant, and the City Auditor-Clerk would be excluded. Petitioner asserts that Supervisory employees and clerical employees should be excluded from the unit. Petitioner would exclude from the unit persons who fill the following positions: Assistant Manager of the Waste Water Treatment Plant; Work Superintendent of the Department concerned with streets and Highways, Trash and Garbage Collection, and Garage and Warehouse; Work Superintendent of the Department concerned with Water and Sewers, parks and Cemeteries; Leadmen or Chiefs at the Waste Water Treatment plant; Chief Mechanic; Chief of Instrumentation and Electric; Chief Operator; Chief of the Laboratory; Chief of Sewer Collection; The Inventory and Warehouse Clerk; and the city's seven clerical employees The Public Employer would include the persons holding these positions within the unit. The present Assistant Manager of the Waste Water Treatment Plant is Curtis Lane. Mr. Lane answers directly to Mr. Simon, the Plant Manager. Mr. Lane is charged generally with carrying out the instructions of Mr. Simon, and he performs some supervisory functions based on these instructions. Mr. Lane does not have the authority to hire and fire other employees. He receives an hourly wage, and the same vacation, pension and insurance benefits as other employees receive. His hourly wage rate is higher than that of the other employees at the Waste Water Treatment plant. He wears the same uniform as the other employees. It does not appear that Mr. Lane exercises any significant budgetary role, nor that he would play any part in the collective bargaining process. (TR 14-16, 37-42). The present work Superintendent of the Department concerned with Streets and Highways, Trash and Garbage, and Garage and Warehouses is Dorton Hadden. Mr. Hadden reports directly to Mr. Brock. Mr. Hadden is charged with supervising the 18 to 20 employees in his department. He receives a salary while other employees are compensated on an hourly rate. He does receive the same insurance, vacation, and pension benefits that other employees receive. Mr. Hadden wears the same uniform as other employees in his department. It does not appear that Mr. Hadden has any significant budgetary role, nor any significant role in the collective bargaining process. (TR 16-18, 31-35, 47, 49). The present work Superintendent of the department concerned with Water and Sewers and Parks and Cemeteries is G. L. Scott. Mr. Scott supervises 10 to 12 employees. He answers directly to Mr. Brock. Mr. Scott is paid a salary while all other employees of his department, except one, are paid at an hourly rate. He receives the same insurance, vacation, and pension benefits as other employees. Mr. Scott wears the same uniform as other employees in his department. It does not appear that Mr. Scott has any significant budgetary role, nor any significant role in the collective bargaining process. (TR 18-20, 42-45). Other positions within the Waste Water Treatment Plant Department about which there is a dispute as to inclusions within the bargaining unit are the leadmen or chiefs at the Waste Water Treatment Plant, the Chief Mechanic, the Chief of Instrumentation and Electric, the Chief Operator, Chief of the Laboratory, and Chief of Sewer Collection. These employees are charged with supervising specific aspects of the Waste Water Treatment Plant operation Each of these employees answers to Mr. Simon. Each is compensated at an hourly rate of pay, which is generally higher than that of other employees at the plant. They wear the same uniform and have the same insurance, vacation, and pension benefits as other employees. It does not appear that these employees perform a significant budgetary role, nor play a significant role in the collective bargaining process. (TR 20-24, 59-69). The Inventory and Warehouse Clerk at the Waste Water Treatment Plant is George Padgett. Mr. Padgett answers to Mr. Simon. He is charged generally with maintaining the inventory at the warehouse. He is paid on the same wage scale, and receives the same insurance, vacation, and pension benefits as other employees. He wears the same uniform as other employees. It does not appear that Mr. Padgett exercises any significant budgetary role, nor that he has any significant role to play in the collective bargaining process. (TR 24-26, 47- 49). The Public Employers clerical employees are supervised either by Mr. Brock or by Mr. Simon. These employees do not work directly with other employees in the unit described in the Petition. They are paid on the same wage scale, and receive the same insurance, vacation, and pension benefits as the other employees. It does not appear that these employees play any significant budgetary role, nor that they will have any significant role in the collective bargaining process. (TR 26-29,49-56). ENTERED this 12th day of August, 1975 in Tallahassee, Florida. G. STEVEN PFEIFFER, Hearing Officer Division of Administrative Hearings Room 530, Carlton Building Tallahassee, Florida 32304 (904) 488-9675
Findings Of Fact During 1990, Respondent/Applicant, City of Lynn Haven, filed several applications with the Respondent, Department of Environmental Regulation, seeking the issuance of several permits to build a wastewater collection system and a two million gallon per day advanced wastewater treatment (AWT) plant. The proposed facility is intended to replace the wastewater treatment facility currently being used by the City of Lynn Haven. After a review of the applications the Department proposed several Intents to Issue covering the different aspects of the proposed projects. The Intents to Issue included: A) a variance and dredge and fill permit, pursuant to Sections 403.201, 403.918, 403.919, Florida Statutes, and Rule 17-312, Florida Administrative Code, authorizing a subaqueous crossing of North Bay (Class II waters) and installation of a force main (permit #031716641), B) a collection system permit, pursuant to Chapter 403, Florida Statutes, and Rules 17-4, 17-600 and 17-604, Florida Administrative Code, for the installation of approximately 11 miles of pipe from North Bay to the proposed treatment plant, C) a dredge and fill permit #031785181, pursuant to Sections 403.918, 403.919, Florida Statutes, and Rules 17-4, 17-312, Florida Administrative Code, authorizing 10 incidental wetland crossings associated with the collection system, and, D) a construction permit #DC03-178814, pursuant to Chapter 403, Florida Statutes, and Rules 17-4, 17-302, 17-600 and 17-611, Florida Administrative Code, authorizing the construction of a 2.0 mgd wastewater treatment plant. Sand Hill Community Improvement Association challenged the Department's Intents to Issue. The Sand Hill Community Improvement Association (Sand Hill) is an association composed of 74 formal members plus numerous supporters. Both members and supporters are residents who live near the site of the proposed Lynn Haven sewage treatment plant. They are sufficiently close to the plant site that construction of the proposed project could impact their property. The members are very concerned about any threat of pollution to the aquifer from the proposed plant since all of the members are dependent on private wells for their drinking water. Additionally, members of the association use the proposed site, as well as the associated wetlands, Burnt Mill Creek and the nearby lakes, for a variety of recreational purposes, including hunting, fishing, hiking, bird-watching, boating and swimming. Given these facts, the Association has standing to challenge the Department's Intents to Issue involved in this case. The City of Lynn Haven is located on a peninsular section of the south shore of North Bay and, except for its connection to the land, is surrounded by environmentally sensitive Class II or Class I waters. Lynn Haven's existing wastewater treatment plant was poorly designed, has not worked properly, and is old and outdated. The plant is permitted to treat up to 950,000 gallons per day. However, the existing plant is currently exceeding its originally permitted treatment limits and is treating in excess of 1,200,000 gallons per day. The sewage only receives secondary treatment, Secondary treatment is the minimum state standard for wastewater treatment. The secondarily treated wastewater is pumped several miles to a spray irrigation site located in the eastern portion of the City. The sprayfield site has never worked properly due to a high groundwater table and a confining layer of soil, both of which prevent the effluent from percolating into the ground. Because the sewage effluent cannot percolate into the ground, the existing operation frequently results in direct runoff into a ditch which empties into North Bay, a Class II waterbody. Such discharge of wastewater effluent into Class II waters is prohibited by Department regulations. 1/ At this time, the existing wastewater treatment facility is in violation of both DER and EPA standards and is under enforcement action by both agencies. The existing facility is currently operating without a permit and the Department has advised Lynn Haven that the existing facility as it now operates can not be permitted. In fact, all the parties agree that the City is in serious need of a wastewater treatment facility which works and does not pollute the environment. However, the parties disagree over the method by which proper wastewater treatment could be accomplished by Lynn Haven. Since 1972, the City, through various consultants and with the aid of DER, has reviewed approximately 40 alternatives for wastewater disposal. After this review, the City of Lynn Haven selected the alternative which is the subject of this administrative hearing. The alternative selected by the City of Lynn Haven consists of the construction of a proposed advanced wastewater treatment (AWT) plant and distribution system. The new plant will be on a 640 acre parcel of property located approximately 12 miles north of Lynn Haven. The location of the new plant will necessitate the rerouting of the wastewater from the old plant to the new plant by construction of a new transmission line approximately 12 miles north of the City across North Bay and parallel along State Road 77. 2/ The treatment process proposed for use in the new AWT plant is known as the AO2 process. The process is patented. The AO2 treatment process primarily consists of biological treatment with settling and filtration. The treatment process also includes a chemical backup treatment to further reduce phosphorus if necessary. The evidence demonstrated that this type of facility has been permitted by the Department in at least five other wastewater facilities throughout the state. The treatment facility will have a two million gallon per day, lined holding pond on site for the purposes of holding improperly treated wastewater for recirculation through the proposed facility. Any excess sludge generated by this treatment process would be routed to lined, vacuum-assisted, sludge drying beds. The sludge would then be transported offsite to a permitted landfill for disposal. The evidence demonstrated that this treatment process would not produce any objectionable odors. Once the wastewater is treated, it will be disinfected by chlorination to eliminate pathogens. The chlorination process is expected to meet state standards. After chlorination, a dechlorination process would occur to remove any chlorine residuals which would have a harmful affect on the environment. The treated wastewater would then be re-aerated and discharged through the distribution system indirectly into a wetland located on the 640 acre parcel of property. The quality of the treated wastewater is expected to meet the advanced wastewater treatment (AWT) standards. These standards are five milligrams per liter total suspended solids (T.S.S.), five milligrams per liter BOD, three milligrams per liter nitrogen (N), one milligram per liter phophorus (P). Ph will be in the range of six to eight units on an average annual basis and can be adjusted up or down if necessary to meet the ph levels of the ecology into which the wastewater ultimately flows. This effluent quality is approximately five times cleaner than secondarily treated effluent. Additionally, as a condition of the draft permit, the proposed facility would be operated by a state-licensed operator and would be routinely monitored to insure that the treated wastewater effluent meets advanced wastewater treatment standards. Given these facts, the evidence demonstrated that the applicant has supplied reasonable assurances that the plant will perform as represented and that the effluent will meet the state standards for advanced wastewater treatment. As indicated earlier, the site for the proposed AWT plant contains approximately 640 acres and is located approximately 12 miles north of Lynn Haven in an area known locally as the Sand Hills. The City specifically purchased this parcel of property for the construction of the proposed wastewater treatment plant. The plant itself would be located in the northeast corner of the property. The 640 acre site was previously used for silviculture. The entire area is currently planted in pines except for a low area that is dominated by a pristine, woody wetland system of titi. The titi wetland is approximately 212 acres in size and generally runs through the center of the property from the northeast to the southwest. The wetland is low in acidity, with an estimated ph between 4 and 5. The site consists of hilly, mineralized soils. The soils within the forested wetland are organic in nature. Based on the evidence at the hearing, there does not appear to be any significant confining layers of soil which would prevent the treated wastewater from percolating in the soils and draining towards the wetland and ultimately into Burnt Mill Creek, a Class III waterbody. Once the effluent leaves the plant, it would go through a distribution system. The proposed distribution system will consist of six, 500 foot long, 12 inch diameter perforated pipes. Each 500 foot section of pipe has 100 one and one-half inch orifices which will discharge the treated effluent onto an eight foot wide concrete pad. This concrete pad will dissipate the effluent's energy, prevent erosion at the orifice site and insure that the effluent sheetflows onto and eventually into the sandy soils of the plant site and ultimately into the receiving wetland. The distribution pipes are located around the east, north and western portions of the receiving wetland and are variously set back from the receiving wetland approximately 80 to 200 feet. The distribution system is designed with valves to allow for routing of flow to different branches of the system if it is determined through long term monitoring that there is a need to allow for any of the receiving wetland to dry out. None of the distribution branches are located in any jurisdictional wetlands of the State of Florida. The receiving wetland will receive a hydraulic loading rate of approximately 1.8 inches per week once the new advanced wastewater treatment plant is operating at capacity. Both the surface waters and groundwaters on the 640 acre parcel flow from northeast to southwest across the property. The evidence clearly demonstrated that any treated wastewater discharged on the site would move down hill by surface or groundwater flows towards the wetlands in the central portion of the property and eventually discharge into Burnt Mill Creek located at the southwest corner of the parcel. The evidence demonstrated that it would be highly unlikely for the surface or groundwater to move in any other direction and would be unlikely for the surface or groundwater to move towards any residents located to the north or east of this parcel. Evidence of the topography and its relatively sharp gradient clearly demonstrated that the treated wastewater discharged in the northeast corner of this site would not result in any significant still water ponding and would exit the site at the southwest corner of the property in approximately 14 hours. The evidence did demonstrate that, depending on the wetness of the weather, there may likely be certain times of the year when a flowing type of ponding would occur. However, this wet weather ponding was not shown to be of a duration which would impact to a significant degree on the flora and fauna of the area or increase the number of disease bearing mosquitoes in the area. As indicated earlier the treated effluent from the proposed AWT plant will flow into Burnt Mill Creek. Burnt Mill Creek will ultimately carry the treated wastewater approximately 11 miles down stream to North Bay. The City can directly discharge up to two million gallons per day of AWT water into Burnt Mill Creek without violating state water quality standards. Therefore, the volume of wastewater discharged into Burnt Mill Creek should not have significant impacts on surface and ground water quality. Moreover, Chapter 17-611, Florida Administrative Code, authorizes the discharge of up to 2 inches per week to receiving wetlands provided wastewater is treated to AWT standards. The evidence demonstrated that this rule was developed as an experimental effort to determine if wetlands could be appropriate areas for wastewater effluent to be either discharged or treated. These state limits were intended to be very conservative limits and were designed to insure that the impacts to receiving wetlands would be minimal. The evidence and testimony demonstrated that the receiving wetland system involved in this case should not be adversely impacted beyond those limits set forth in Section 17-611.500, Florida Administrative Code, for flora, fauna, macroinvertebrates, fish or vegetation and will meet all standards set forth in Chapter 17-611, Florida Administrative Code. However, it should be noted that the wetland/wastewater program is highly experimental and very little is known about the actual impacts of wetland/wastewater systems since facilities similar to the one proposed by Lynn Haven have not yet been placed in service. The evidence did show that there would be some long term impacts to flora and fauna in the wetland area primarily due to ponding, changed ph and the introduction of nutrients and pollution in the form of the effluent. However, the regulation does allow for some change within a receiving wetland and the evidence did not demonstrate that these changes would be significant or detrimental. Petitioners' own witness concluded that other deep wetland treatment systems are doing a very good job in meeting state water quality standards. Although Petitioners' expert noted potentially adverse impacts to flora and fauna from other wastewater treatment systems, these other systems were slow moving, impoundment-type systems that are not similar to the wastewater/wetlands system proposed by the City of Lynn Haven. The Lynn Haven system is designed for percolation and sheetflow, not ponding. Though there should be some expected changes, no evidence was provided that the receiving wetlands for the Lynn Haven facility would be affected to the extent there would be violations of any standard as set forth in Chapter 17-611, Florida Administrative Code. In essence, the legislature has determined that such experimentation with wetland areas is appropriate, albeit, even with the conservative limits of DER's rule, may prove to be a mistake. This facility is designed to fit within that rule and in fact is probably the best technology available for use in a wetland/wastewater situation. Finally, in order to avoid any potential impacts on the area which may over time become significant an approved monitoring program for surface water quality and affects on flora and fauna, as well as a groundwater monitoring program are required as conditions of the permit. The groundwater monitoring program has been designed to monitor any potential long term impacts to groundwater. With these protections there should not be any significant adverse impacts to surface or groundwater quality and the applicant is entitled to a construction permit for the AWT plant and distribution system. Lynn Haven's sewage would reach the proposed AWT plant through a transmission line. The transmission line would run from Lynn Haven's existing wastewater treatment plant across North Bay and through the unincorporated area of South Port. The Southport area is not sewered and utilizes individual septic tanks for its sewage. The transmission line would be constructed entirely in state road right-of-way. The line would terminate at the 640 acre site described above. A new, variable speed pumping station would be constructed adjacent to the old wastewater treatment plant. From this pump station, a 24 inch line would be constructed on City right-of-way up to the south shore of North Bay. At this point, the transmission line would be reduced in size to 20 inches and would be embedded approximately three feet below the Bay bottom. An additional variable speed pumping station would be located approximately half way along the 12 mile route of the transmission line to insure adequate pressure to pump wastewater to the new wastewater treatment plant. The pumps are to be employed to insure that the wastewater is continuously pumped uphill to the new site so that waste does not set, become septic, and create odor problems. The pumps are equipped to provide for chemical control of odor if necessary. Also, as a condition of the permit, the pumping stations are required to have backup power supplies should power be lost to the stations. The pumping stations and backup power supplies are to be tested monthly and the pumps are required to be continuously monitored by radio telemetry to insure they are operating properly. Additionally, the City of Lynn Haven will be required, as a condition of the permit, to visually inspect the entire length of the wastewater transmission line three times per day. The portion of the transmission line which would cross North Bay is approximately 3000 feet in length and would be constructed of high density polyethylene pipe (HDPE) with a wall thickness of one and one-half inches. HDPE pipe is used to transport materials such as hazardous wastes where leakage is not permissible. This type of pipe is virtually inert in that it is highly resistant to corrosion and other chemical reactions. It is also impact resistant and has a very high tensile strength. The pipe comes in 40 foot segments and is heat welded (fused) together. This type of joint significantly reduces the chance of any leakage. In fact, leakage around pipe joints is more likely to occur with other types of pipe and pipe connections. HDPE pipe is currently carrying wastewater across Watson Bayou in Bay County, Florida. 3/ There have been no reported problems with leaks or breaks occurring in the pipe crossing Watson Bayou. Given these facts, the probability of the proposed HDPE pipe leaking or breaking is extremely low, albeit not impossible, and such pipe appears to be the best material available for constructing a wastewater treatment transmission line across protected waters of the State. As a condition of the construction permit, the portion of the transmission line crossing North Bay will be required to have isolation valves at each end so that the pipe may be completely isolated in the event that it needs repair. The underwater portion of the line would be visually inspected by a diver twice per year and the line would be pressure tested before being placed into service. Additionally, pressure tests would be performed once a year. The construction permit also requires Lynn Haven to periodically inject dye into the proposed transmission line to check for any small leaks that may not otherwise be detected. Finally, the HDPE pipe would also be equipped so that television cameras could be inserted into the pipe to routinely inspect the interior of the pipe. In the event the HDPE portion of the transmission line would need to be repaired, the line could be immediately, temporarily repaired by a dresser coupling. A permanent repair could then be made in less than 24 hours once the material and equipment were staged at the site. The City intends to locally stockpile all necessary parts and equipment to effect any required repair to prevent any delay beyond four days. Permanent repairs would be accomplished by floating the line to the surface. The area needing repair would be cut out and a new section would be put in place by heat fusion. The line would then be pressure tested to insure the absence of leaks and placed back into service. During this process, the line would be taken out of service by the isolation valves and flow would be diverted to the eight million gallon holding ponds at the City of Lynn Haven's existing facility. These holding ponds can hold four days worth of wastewater from the City of Lynn Haven. Lynn Haven is required, as a condition of the construction permit, to have this reserve capacity as well as have a contractor on standby to make any repairs in the event such repairs are necessary. All of the technical specifications for the transmission system and the operating conditions imposed on it are designed to insure that the system does not fail or develop any leaks which could impact receiving waters, including North Bay. Given the permit conditions, the required inspections for leaks, the sound engineering design and quick repair methods proposed, the evidence demonstrated that the probability of any leak occurring in the portion of the transmission line crossing North Bay is extremely low and that if such a leak does occur any potential harm to the environment will likely be limited and quickly eliminated. The evidence demonstrated that the design of the transmission line and permit conditions provide reasonable assurances that the transmission line will meet or exceed the Department standards set forth in Chapter 17-604, Florida Administrative Code. Therefore, the applicant has provided reasonable assurances that the transmission line/collection system will not violate Department standards or rules and the applicant is entitled to a permit (permit #CS03-178910) for the proposed collection system. In addition to requiring a construction permit/collection system permit for the wastewater transmission line, the line will also require dredge and fill permits and a variance for crossing waters of the state. There are ten incidental crossings of state waters and one major crossing o f North Bay. Of the ten incidental crossings, two are over small creeks (Scurlock and Little Burnt Mill) These two incidental creek crossings will be accomplished by placing the transmission line (ductile iron pipe) on top of pilings placed in the water. Best management practices such as turbidity curtains and other erosion control practices are proposed and required by the permit to minimize construction impacts on water quality. The only impacts to wetland resources would be from the placement of the pilings. The evidence demonstrated that any impact would be minimal and not significant. The evidence did not demonstrate that the aerial crossings would have any long term water quality or environmental impacts. The remaining eight incidental crossings of waters of the state consist of small, seasonally wet ditches which would be traversed by trenching and burying the transmission line. Again, turbidity controls such as curtains and hay bales would be employed to protect water quality. The evidence did not demonstrate that any significant long term or short term impacts to resources of the state would occur. The evidence did demonstrate that the applicant has provided reasonable assurances that water quality standards would not be violated in regards to these 10 incidental water crossings. Likewise, the evidence demonstrated that the construction of these 10 incidental water crossings would not be contrary to the public interest. Therefore, the applicant is entitled to issuance of a dredge and fill permit (permit #031785181) for these 10 water crossing. However, a much harder question arises in relation to the dredge and fill permit and the variance required for the 3,000 foot segment of the wastewater transmission line which crosses North Bay. Pursuant to Rule 17- 312.080(7), Florida Administrative Code, permits for dredging and filling activity directly in Class II waters which are approved for shellfish harvesting by the Department of Natural Resources (DNR) shall not be issued. The reason for the rule is that any pollution caused by dredging and filling and, as in this case, the permanent placement of a sewage pipe in food producing waters could potentially have catastrophic effects on more than just the environment but on local employment in the shellfish industry and the quality of food available to the State. Put simply, the Department has determined by enacting its Rule that the public interest in food producing waters far outweighs any other consideration or criteria under Sections 403.918 and 403.919, Florida Statutes, in determining whether dredging and filling should take place in Class II, shellfish waters. In other words, it is not in the best interest of the public to allow dredging and filling so that a pipe carrying raw sewage can be placed in shellfishing waters. However, irrespective of this determination, the Department believes that, pursuant to Section 403.201(1)(c), Florida Statutes, it may grant a variance from its rules to relieve a hardship. As indicated earlier, North Bay is a Class II waterbody, conditionally approved for shellfishing. North Bay, therefore, falls within the Rule's prohibition against dredging and filling in Class II waters and the City is required to demonstrate the presence of a hardship in order to vary the Rule prohibition and obtain a dredge and fill permit for the North Bay crossing. On issues involving variances, the Department employs a two step analysis. The first part of the analysis is whether a hardship is present and the second is whether, if the variance were granted, would it result in permanent closure of Class II shellfish waters. The Department correctly recognizes that the question of whether a hardship exists is a question of fact and is determined on a case-by-case basis. Surprisingly, in a kind of "what we don't know can't hurt" posture the Department reviews a request for a variance standing alone based on the application as it is presented and does not require analyses of other possible alternatives to the granting of a variance. However, the existence of any alternatives, costs of any alternatives, timeliness of any alternatives, problems with any alternatives, whether an alternative represents a short term or long term solution to a given problem and the implementability of any of the alternatives are all factors utilized by the Department in determining whether or not to grant a variance. The Department's policy of non- review makes no sense, either factually or statutorily, when the Department is faced with varying a prohibition it created in its own rules. Similarly, the Department's policy of not requiring other alternatives to be examined before granting a variance goes against the fact that an applicant has the burden to establish entitlement to a permit and, in the case of a hardship variance, that a hardship exists because reasonable alternatives to granting a variance are not available. 4/ Likewise, the second part of the Department's hardship analysis relating to the permanent closure of shellfishing waters makes no sense given the fact that a non-permanent closure of shellfishing waters may have the same or just as serious effect on employment in the shellfishing industry, the loss of income due to an inability to earn a living in that industry and health risks posed by contaminated seafood. Temporary loss of income or a livelihood can, for all practical purposes, have consequences to the persons directly affected by a temporary closure of shellfishing waters similar in nature those caused by the permanent closure of shellfishing waters. The same can be said for health risks posed by a contaminated food supply. Rule 17-312.080(7), Florida Administrative Code, does not contain any exceptions for the temporary closure of shellfish waters. Nor is the rule limited to instances of permanent closure. Permanent closure is simpy not required in order to support a hardship under Section 403.201, Florida Statutes. Moreover, neither step in the Department's two-step analysis is included in any Rule promulgated by the Department. 5/ Without such a Rule, it is incumbent upon the Department or the applicant to demonstrate the underpinnings for this non-rule policy. No such evidence was presented at the hearing. In fact, the evidence presented at the hearing affirmatively demonstrated that the Department's non-rule policy violated both its own rules and the statute under which it is trying to proceed. As indicated, the issue of hardship is a question of fact and involves a weighing of all the facts and cicumstances involved in this project. In this case, there are shellfishing areas located close to the proposed location of the transmission line. North Bay is sometimes closed to shellfish harvesting by the Department of Natural Resources. These closures generally occur during wet weather conditions and are due to stormwater runoff and the failure of septic tanks in Southport. 6/ Additionally the current Lynn Haven system also contributes to the closure of North Bay. No competent, substantial evidence was provided that issuance of the permit and variance would result in the permanent closure of shellfish waters. The location of the proposed transmission line would be several hundred feet west of the Bailey Bridge embedded in the Bay floor. 7/ The proposed alignment of the transmission line through North Bay is in an area which is relatively biologically unproductive. The proposed placement of the transmission line avoids the few grassbeds that exist in the nearshore shallow areas except for approximately 200 square feet of grass. During construction of the line, these grasses would be removed immediately before the line is placed in a trench and then would be promptly replanted in the same area. The evidence demonstrated that the affected areas of grass should be able to reestablish itself. The evidence further demonstrated that there would not be any long term adverse impacts to these aquatic resources and there should not be any significant long term impacts on the balance of any aquatic life which may exist on the bay bottom. Water quality during construction will be protected by use of turbidity controls to control sediments. Therefore, any short term impacts on aquatic resources are likely to be insignificant. Concerns about long term adverse impacts to Class II waters are greatly reduced by the type of pipe and conditions in the permit which require that the transmission line be routinely inspected and tested to insure that there is no leakage and that in the unlikely event the line should need to be repaired, the line could be easily isolated and quickly repaired. The evidence showed that, to completely avoid Class II waters, the line could be moved several miles to the west or east of the line's proposed location or be placed over or under the Bay. If the line was moved west to the extent that it was in Class III waters, it would be over 40 miles long and would more than double the cost of the project. If the line was moved several miles to the east, it would go through the Deer Point Lake Watershed. The watershed is a Class I water supply for Bay County. Clearly, moving the line either west or east is not practical nor realistically feasible. Tunneling under North Bay would be very risky and is not technically feasible. The length of the tunnel would require steel pipe to be used. If tunneling could be done at all steel pipe would not provide the level of protection afforded by the HDPE pipe proposed by Lynn Haven. Placing the transmission line on pilings for an aerial route over North Bay is uneconomical and would create a potential hazard to navigation. Moreover, an aerial crossing would not solve any pollution problems should the transmission line leak or break and would also still involve a variance request since it would be necessary to dredge and fill in Class II waters for the placement of pilings or supports. Put simply, the evidence, showed that there was no realistic way to avoid Class II waters in North Bay given the location of the proposed wastewater treatment facility. A location which the City knew would require a hardship variance from the rule prohibition of dredging and filling in Class II, shellfishing waters. A hardship which the City created by site selection and which it hoped to overcome by strenuous permit conditions and futuristic speculative benefits to unsewered areas of the County. The existing treatment facility is operating in violation of both EPA and DER requirements, has been issued a notice of violation, is nonpermitted and is destined to be operating under a consent order. The system is hydraulically overloaded, handling approximately 1.2 million gallons per day while its rated capacity is 950,000 gallons per day. Refurbishing Lynn Haven's existing wastewater treatment facility would not be viable since the plant has outlived its useful life, is of a very poor design and probably could not be made to function within Departmental standards and water quality standards. The existing sprayfield does not function and results in overland flow of effluent which discharges to Class II waters. The high water table and presence of a semiconfining layer on the Lynn Haven peninsula virtually guarantee such discharges. Further, the plant only provides secondary treatment. Put simply, Lynn Haven needs another method of handling its sewage. The only remaining alternative to a Bay crossing is to tie into the existing Bay County system and any AWT wastewater treatment plant Bay County may build in the future. 8/ The existing Bay County system provides at most only secondary treatment. The Cherry Street facility, which is part of that system, functions essentially as a lift station rather than a treatment facility. The Military Point Lagoon portion of the system is nonpermitted and is operating under a consent order and has been the subject of enforcement action. The Department has an extensive agreement with Bay County requiring a significant and long term series of actions to deal with their wastewater treatment system. The modifications or improvements to the Bay County system to provide advanced treatment are not imminent and the final system conditions cannot now be determined as they will depend in large measure upon data and analysis remaining to be collected. Currently, the existing Bay County system processes a significant amount of industrial discharge and has a problem with phenols most likely due to industrial waste from two discreet industrial facilities in the County. 9/ However, all of Bay County's wastewater system problems are reasonably solvable and will be corrected in the near future, if they have not already been corrected. Additionally, the amount of sewage Lynn Haven would be sending into the current Bay County system probably would not significantly impact that system and its problems or the County's ability to solve those problems. The County is willing to accept Lynn Haven's sewage into its system and future AWT system. The connection into Bay County's system is a viable alternative currently in existence. Moreover, as indicated, Bay County has a long range plan to build an advanced wastewater treatment plant. As yet the plan remains "just a twinkle in the County's eye" and has not progressed to the design stage. However, this plan, of necessity, will eventually become reality in the next 5 to 10 years. The estimated cost to a Lynn Haven user for the Bay County conceptual system will be $25.00 per month in lieu of $15.00 for the proposed Lynn Haven system. These estimates are at best speculative. However, this cost estimate is not excessive given the fact that a Lynn Haven user lives in an environmentally sensitive area and a Bay County hook-up would eliminate the need to run a sewer pipe through food producing, Class II waters. 10/ Based on these facts, the evidence demonstrated that it was feasible for Lynn Haven to hook into Bay County's wastewater system without creating any more environmental impacts than that system is already experiencing and must solve and which, to a significant degree, have already been solved by Bay County. Given the existence of this alternative to crossing food producing waters and the fact that any future benefits are just as likely to be provided just as quickly by the County through AWT facilities, the applicant has failed to demonstrate the necessity for crossing North Bay and failed to demonstrate entitlement to a hardship variance for that crossing. Therefore, the applicant is not entitled to either a dredge and fill permit or variance for the proposed North Bay crossing.
Recommendation Based on the foregoing findings of fact and conclusions of law, it is, recommended that the Florida Department of Environmental Regulation enter a final order issuing permit applications CS03178910, DC03178814, and 031785181, and denying the variance and permit number 031716641. RECOMMENDED this 27th day of November, 1991, in Tallahassee, Florida. DIANE CLEAVINGER Hearing Officer Division of Administrative Hearings The DeSoto Building 1230 Apalachee Parkway Tallahassee, FL 32399-1550 (904) 488-9675 Filed with the Clerk of the Division of Administrative Hearings this 27th day of November, 1991.
Findings Of Fact The Petitioner is a special tax district created by special act of the Florida Legislature. Chapter 71-822, Laws of Florida. The district covers approximately seventy-two square miles in northern Palm Beach County and southern Martin County, Florida. Petitioner's purpose is to provide water, sewer, drainage and solid waste services within the district. In conformity with its powers, the Petitioner operates an advanced waste water treatment plant on property which it owns in northern Palm Beach County. Petitioner has secured appropriate permits from DER in order to construct and operate the treatment plant. The treatment plant is among the most advanced in southeastern Florida. It has a four million gallon daily capacity, which could be increased to an eight million gallon capacity. In treating waste water the plant utilizes filtration, disinfection, retention in a holding pond, and discharge into a remote off-site area. The present discharge system is to pump effluent from the retaining pond through a canal or drainage system to a recharge or discharge lake which is located approximately three miles north and west of the treatment plant. This is known as the western discharge system, and was installed at a cost of approximately one million dollars. Due to the large amounts of pumping activity, it is an expensive system to utilize. Through its instant application, the Petitioner is seeking a permit allowing it to discharge effluent on-site. Effluent would flow into percolation ponds that have already been constructed. Effluent would settle in the ponds, and eventually would percolate through the soil. This system would he less expensive to operate than the western discharge system. Petitioner is interested in experimenting with the amount of waste water treatment that can be obtained through action of vegetation in the percolation ponds upon the effluent. Such a natural system, if it operated effectively, could save the Petitioner additional money in treating waste water by reducing the need for chemical treatment. Petitioner's waste water treatment presently results in a discharge of effluent which within some parameters meets even drinking water standards. The Petitioner's system very effectively treats bio-chemical oxygen demand ("bod"), suspended solids, nitrogen, and phosphorus in the effluent. Reports have been submitted by the Petitioner to DER which indicate that the system does not meet DER's standards for advanced waste water treatment. Samples upon which these reports were based were taken at a point in the system before the effluent was subjected to the action of the retention pond and the subsequent bumping into the western discharge system. Samples taken beyond the retention pond indicate that DER's standards are met for "bed", suspended solids, total nitrogen, and total phosphorus. The Intervenor owns property adjacent to the Petitioner's waste water treatment plant. The Intervenor operates a well field and drinking water treatment plant on the property, and provides drinking water to residents of the Town of Jupiter and surrounding communities from the well field. The Intervenor acquired its treatment plant, and surrounding well fields from a private utility company. The Petitioner was aware of the well field when it purchased the property upon which it presently operates its waste water treatment plant. While the Petitioner's plant adequately treats waste water in terms of "bod", suspended solids, total nitrogen, and total phosphorus it does not treat the waste water for heavy metals, pesticides, or viruses. These are common elements found in waste water effluent in the south Florida area. The Petitioner's proposal is to discharge its effluent into on-site ponds. The effluent would then percolate into the ground. The retention ponds are located at a distance from 1200 to 1600 feet from the nearest of the Intervenor's wells. Water which percolates from these ponds would flow directly toward the wells, and would eventually find its way into the wells. The flow from the retention ponds to the wells would be increased due to the draw-down effect that the wells have on the surrounding water table. As water is drawn from the wells, the adjoining water table becomes depressed in the area of the wells, and water from the surrounding area flows more rapidly into the area of the wells. Heavy metals will not be filtered out as a result of retention or percolation. Heavy metals in the effluent would eventually find their way into the Intervenor's well fields. Estimates as to the amount of time that it would take for water from the percolation ponds to reach the wells varied from four months to six years. The longer estimate appears the more reasonable; however, the evidence is conclusive that eventually waters from the percolation ponds would reach the wells, and that heavy metals in the water would not be filtered out. The Petitioner proposes to obviate any problems with heavy metals reaching the well fields by operating testing wells between the percolation ponds and the well fields. If any heavy metals were detected in the ground water, Petitioner would again use the western discharge system rather than the percolation ponds. While this would prevent increased contamination of the wells, contamination that had already reached the test wells would reach the Intervenor's wells. It was suggested that the percolation ponds could be drawn down in order to reverse the flow of ground water back into the percolation ponds, thence to be pumped through the western discharge system. In order to accomplish this, however, the percolation ponds would have to be more than forty feet deep, which they are not. The effect of heavy metals intruding into the Intervenor's water supply could be to increase the cost of treatment, or to render the wells unfit for use. Uncontaminated drinking water supplies are rare in the northern Palm Beach County area, and the expense of finding a new water supply is difficult to calculate.
The Issue The ultimate issue is whether Celebrity Resorts, Inc., (Celebrity) is entitled to a permit to construct a wastewater treatment and reuse/disposal facility in Marion County, Florida.
Findings Of Fact Proposed Project Celebrity is seeking a DER permit to construct a 0.065 million gallon per day wastewater treatment and reuse/disposal facility to serve a proposed recreation vehicle (RV) park. The facility is to be located in northern Marion County on the southern border of Orange Lake, an Outstanding Florida Water. The RV park is to be located on 75 acres of land, and is to contain 372 RV and "park model" sites, four bath houses, a clubhouse, and an expanded boathouse. The sewage treatment plant (STP) and effluent disposal system, consisting of a spray irrigation system, are to be located on the southern end of the site, away from Orange Lake. There is a "break" in the watersheds of the Celebrity property caused by a ridge across the approximate center of the project site. The effect of this "break" is that approximately one-half of the property drains toward the lake while the approximate southerly half of the property drains into an independent depression creating a watershed separate from the lake. Some underground pipes for a sewage collection system were installed at the site without an appropriate DER permit. Celebrity stopped the installation upon notice from DER that a permit was required for such installation. The permit needed for the installation of the collection system pipes was not the permit for the sewage treatment project which is being considered in this proceeding. Celebrity was penalized for its collection system violation, which was resolved with a consent order. Sewage Treatment Plant (STP) The STP is an extended aeration plant. It is designed to meet secondary treatment standards (90% removal of BOD and suspended solids from raw sewage) and basic disinfection. This type of treatment plant is very reliable. All mechanical components have a 100% backup so if a pump or blower fails, another is available to operate. The STP is designed to be capable of treating the flow from this RV park. Additionally, the facility has a holding pond for treated sewage effluent that can store five days of flow. Furthermore, because the RV park is a transient facility, it is possible in an emergency to shut down the entire plant and have people leave. By its nature, this is much more convenient in an RV park that in a residential or commercial neighborhood. The holding pond is to be lined with a 60 millimeter high density polyethylene liner, so there should be no leakage to the ground or groundwater even if there is an accident in the STP causing release of untreated sewage into the holding pond. The STP is to be maintained five days a week and must be attended for three nonconsecutive visits a week by a Class D certified plant operator. The amount of dissolved/undissolved heavy metals in the effluent is typically not a problem in domestic sewage effluent such as from the proposed RV park. To the extent that trace amounts of metals will exist, the STP will remove some heavy metals from the effluent during the treatment process and entrain them in the sludge (which will be taken to appropriately licensed landfill). There is no possibility of effluent leaking or discharging from the plant to directly discharge to Orange Lake, even if the STP completely malfunctions. Although the proposed STP is not a highly sophisticated plant, reasonable assurances have been provided that the STP will comply with DER's requirements for secondary treatment and basic disinfection and proper operation. Effluent Disposal System (Spray Irrigation System) Phase I of the effluent disposal system (spray irrigation system) is 3.66 acres in size, with an additional 1.7 acres designated if Phase II is implemented. Approval under this permit authorizes only the 3.66 acres on Phase I. Numerous separate sprinkler heads will spray the treated effluent on the field. The heads can be separately controlled and shut down. The sprayfield is sited on the southwestern corner of the 75-acre site and is separated hydrologically from the Orange Lake drainage basin by the "break" referred to in Paragraph 4 above. Therefore, surface water drainage in the area of the sprayfield drains away from the lake and does not connect back to the lake. The permitted loading rate is 1.7 inches per week, or approximately 24,000 gallons per day at full capacity. This amount corresponds to only approximately 170% of natural rainfall, but is more evenly distributed and controlled. After uptake of nutrients by green plants and evaporation (evapo- transpiration), the average amount of treated effluent that will percolate below the "uptake zone" to the surficial aquifer (to the extent that such exists on the site) is 0.3 to 0.4 inches per week. The surficial water table in the area of the sprayfield generally flows to the north toward the lake, although the flow is not immediately direct toward the lake. The Floridan Aquifer (which is beneath the intermittent surficial water table) in the area of the sprayfield generally flows away from the lake to the south and southeast. There are four sinkholes on the 75-acre site, although none of these four sinkholes have been identified on the 3.66-acre sprayfield. The four sinkholes on the 75-acre site and the majority of sinkholes in the area are "subsidence sinkholes." These sinkholes do not result in an open void down to the limerock after the collapse forming the sinkhole, but instead continue to have unconsolidated material above the limerock, even though a depression forms on the surface. One of the sinkholes has standing water within it and could possibly represent a connection with the lake water table or the Floridan Aquifer, but that sinkhole is separated hydrologically from the sprayfield site by the "break" across the property. There will generally be a slight increase in hydrologic conductivity through a subsidence sinkhole, since the unconsolidated material on the surface remains and is loosened. In some cases there may be even less hydrologic transmissivity due to a "jamming up" of the unconsolidated material, and in some cases there may be an increase in transmissivity when the unconsolidated material falls into an even less consolidated state. A "lineament" may exist on the 75-acre site. A lineament is a fracture zone, which indicates an increase in ground water transmissivity, resulting in an increase in solution of limestone and therefore indicating a more likely location for sinkhole formation. If a sinkhole develops within the sprayfield and if the sinkhole results in an increased area of ground water transmissivity, it could be a conduit for treated effluent to reach the surficial aquifer or Floridan Aquifer. Sinkholes which may form on the site are subject to being repaired with impervious material which prevents their becoming routes of contamination to the aquifer. In addition, the loading rate of any single sinkhole that forms within the spray irrigation field is so light and so easily shut down that there is a high confidence rate that no new sinkhole will act as a conduit for even the small immediate discharge over the area of the new sink to reach the Floridan Aquifer. A spray irrigation effluent disposal system is appropriate for this area which is subject to sinkhole formation. Spray irrigation allows dispersal of the effluent over a large area as opposed to a percolation pond which concentrates in the percolation area and therefore increases the chance of sinkhole formation and the chance of larger amounts of effluent reaching the Floridan Aquifer if all the intervening safeguards should fail simultaneously. In addition, the repair of any sinkhole forming within the sprayfield is simplified by the ability to simply shut off the sprinkler head or heads affecting that sinkhole while repair is being effected. Permit conditions further limit excessive effluent application rates by limiting the amount of flow, prohibiting application during storm events, and requiring monitoring of the flow. Spray irrigation is a common method of effluent disposal which generally has fewer problems than use of percolation ponds. No evidence has been presented that discharge from the sprayfield will cause violations of groundwater quality standards or violations of surface water quality standards, including the Outstanding Florida Water requirements in Orange Lake. Reasonable assurance has been provided that the proposed effluent disposal system will not violate DER water quality standards or other applicable DER rules. Standing Petitioner Suto could be substantially affected by this proposed facility if it causes pollution to Orange Lake since she uses the lake for nature photography. Additionally, she resides to the southeast of the proposed sprayfield and has concerns over contaminated ground water reaching her property and affecting her drinking water. Petitioner Riley could be substantially affected by this proposed facility if there is pollution to the Floridan Aquifer since she lives southeast of the proposed facility and has two drinking water wells on this property. Additionally, Petitioner Riley is a user of Orange Lake and therefore could be substantially affected by the proposed facility if it impacts the lake. Petitioner Solomon could be substantially affected by the proposed project if the project impacts Orange Lake since Mr. Solomon earns his living on the lake as a commercial fisherman and bass fishing guide.
Recommendation Based upon the foregoing Findings of Fact and Conclusions of Law, it is recommended that the Department of Environmental Regulation enter a Final Order granting to Celebrity Resorts, Inc., a permit to construct a wastewater treatment facility and spray irrigation disposal system subject to the conditions set forth in the Intent to Issue. RECOMMENDED this 15th day of July, 1991, in Tallahassee, Florida. DIANE K. KIESLING, Hearing Officer Division of Administrative Hearings The DeSoto Building 1230 Apalachee Parkway Tallahassee, FL 32399-1550 (904) 488-9675 Filed with the Clerk of the Division of Administrative Hearings this 15th day of July, 1991. APPENDIX TO RECOMMENDED ORDER, CASE NO. 91-2722 The following constitutes my specific rulings pursuant to Section 120.59(2), Florida Statutes, on the proposed findings of fact submitted by the parties in this case. Specific Rulings on Proposed Findings of Fact Submitted by Respondent, Celebrity Resorts, Inc. Each of the following proposed findings of fact is adopted in substance as modified in the Recommended Order. The number in parentheses is the Finding of Fact which so adopts the proposed finding of fact: 4(1); 5(2); 6(4); 7(5&6); 8- 12(7-11); 13(12); 14(13); 15(14); 16(15&16); 17(17); 18(18); 19-21(20-22); and 22-27(26-31). Proposed findings of fact 1-3 are unnecessary. Proposed finding of fact 28 is subordinate to the facts actually found in this Recommended Order. Specific Rulings on Proposed Findings of Fact Submitted by Respondent, Department of Environmental Regulation Each of the following proposed findings of fact is adopted in substance as modified in the Recommended Order. The number in parentheses is the Finding of Fact which so adopts the proposed finding of fact: 4-6(1-3); 7-13(5-11); 14(12); 15-17(13-15); 18(17); 19(18); 20-26(19-25); 27-32(26-31); and 33-35(32- 34). Proposed findings of fact 1-3 are unnecessary. COPIES FURNISHED: Delcie J. Suto, Pro Se 2400 N.W. 165th Street Citra, FL 32113 Carol B. Riley, Pro Se 2250 N.W. 165th Street Citra, FL 32113 Crawford Solomon, Pro Se 1303 N.W. 186th Place Citra, FL 32113 Karen English 3680 West Highway 318 Citra, FL 32113 Marilyn Nehring P. O. Box 481 Orange Lake, FL 32112 John Monsees 2400 NW 165 Street Citra, FL 32113 William L. Townsend, Jr. Attorney at Law Post Office Box 250 Palatka, FL 32178-0250 Douglas H. MacLaughlin Assistant General Counsel 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 General Counsel Department of Environmental Regulation Twin Towers Office Building 2600 Blair Stone Road Tallahassee, FL 32399-2400
Findings Of Fact Petitioner, George H. Hopper, submitted an application for a license to operate a Class "C" wastewater treatment plant to the Respondent on or about April 8, 1977. On November 28, 1977, the Respondent issued a letter of intent to deny the license. This letter of intent was subsequently modified by a letter to petitioner from Respondent dated January 4, 1978. The Respondent, in the above-referenced correspondence, based its letters of intent to deny the Petitioner a Class "C" wastewater treatment plant operator's license based upon two primary grounds. Those grounds are as follows: "This Department has concluded that you have not fulfilled the actual experience requirement of section 17-16.03(2)(b), Florida Administrative Code (F.A.C.), as defined by section 17-16.02(8) F.A.C." (See letter dated November 28, 1977.) "In addition to the above referenced deficiency in actual work experience, it has been noted that you have not completed an approved course related to wastewater treatment plant operation as required by Section 17-16.03(2)(c), Florida Administrative Code." (See letter dated January 4, 1978.) Respecting the second allegation, Petitioner presented testimony during the course of the hearing which, in fact, indicates that he did complete an approved coarse related to wastewater treatment plant operation as required by Section 17-16.03(2)(c), Florida Administrative Code. Additionally, Petitioner presented a diploma supporting this contention. This certificate reflects the fact that the Petitioner satisfactorily completed the course on "Operation of Wastewater Treatment Plants" on or about May 2, 1977. Based thereon, and the testimony of Respondent's certification officer, Robert W. Hall, to the effect that the Respondent did comply with the Code requirement which mandates completion of an approved course related to wastewater treatment plant operation, that ground is no longer a basis for the denial of Petitioner's certification. Petitioner testified, and the other documentary evidence introduced during the coarse of the hearing indicates, that Petitioner was employed from January, 1975, through December 25, 1975, as administrator of the Margate Utility Authority. From December 25, 1975, through February 15, 1976, the Petitioner was employed in a position other than as administrator, his resignation being effective on February 15, 1976. Accordingly, the Petitioner was employed at the Authority for a period in excess of one year. What is at issue, is the Respondent's contention that the Petitioner was not actually performing duties tantamount to fulfillment of the actual experience requirement of Section 17-16.03(2)(b), Florida Administrative Cede, inasmuch as his duties as an administrator were more in the nature of being in charge of the facility, with little practical experience as the term "experience" is meant in Chapter 17 of the Florida Administrative Code. Additionally, it was noted that the Petitioner was re-employed by the City of Margate as a supervisor. During the hearing, the Petitioner outlined his duties as an administrator which included being in charge off the overall operation of the wastewater treatment plant. Petitioner testified that when he was first employed at the Margate Utility Authority, the wastewater treatment plants were not operational. He testified that a water-sewer moratorium had been placed by the Board of Health, citing approximately five violations. Petitioner testified that he instituted numerous changes in the operations of the wastewater treatment facilities which included hiring a contractor to supervise deficiencies in the wastewater treatment plant and its injector systems which were over-pressurized. He testified that within approximately two months of his employment with the Authority, he was able to correct approximately 80 percent of the problems and was able to again make the treatment plant operational. Petitioner testified that he normally worked a five day week; however, he was on duty in excess of forty hours weekly for the resolution of all daily operational problems. Evidence introduced during the course of the hearing reveals that the wastewater treatment facility here involved is fully automated and that the operators have very little to do in terms of manual tasks. In this regard, the Petitioner testified that he was on duty at the facility throughout his employment during the period January, 1975, through December, 1975, to operate the wastewater treatment plant. Additionally, the Petitioner testified that his office, as an administrator, was located in close proximity to the wastewater treatment facilities and he was available to in fact operate the wastewater treatment plant, as needed. Finally, Respondent's certification officer, Robert W. Hall, testified that in his opinion, being available to operate as opposed to actual operation is what is required by the actual experience requirements of the Florida Administrative Code. Based thereon, I shall recommend that the Respondent withdraw its notice of intent to deny Petitioner's application for a Class "C" wastewater treatment plant operator's license.
Recommendation Based on the foregoing findings of fact and conclusions of law, it is hereby, RECOMMENDED: That Petitioner's application for a Class "C" wastewater treatment operator's license be GRANTED. RECOMMENDED this 8th day of May, 1979, in Tallahassee, Florida. JAMES E. BRADWELL, Hearing Officer Division of Administrative Hearings Room 101, Collins Building Tallahassee, Florida 32301 (904) 488-9675 COPIES FURNISHED: Russell L. Forkey, Esquire 3081 East Commercial Boulevard Fort Lauderdale, Florida 33308 Randall E. Denker, Esquire Department of Environmental Regulation 2600 Blair Stone Road Tallahassee, Florida 32301
Findings Of Fact Upon consideration of the oral and documentary evidence adduced at the hearing, the following relevant findings of fact are made: The Tamaron wastewater treatment facility (facility), located at 3800 Gatewood Drive, Sarasota, Florida, serves the Tamaron residential subdivision which was originally developed by U. S. Homes Corporation in 1976. The subdivision presently consists of 499 homes and was completely built out in the mid-1980's. The facility was originally owned and operated by U. S. Homes Corporation. Tamaron Utilities, a nonprofit entity comprised of the 499 homeowners, acquired the facility in November, 1987. At that time, the facility's existing operating permit was transferred to Tamaron Utilities. The facility is overseen by an elected board of volunteer homeowners. The Department is the agency of the State of Florida that is authorized to regulate domestic wastewater treatment and disposal facilities and permit their construction and operation. It is the successor agency to the Department of Environmental Regulation. By letter dated November 10, 1987, the Department notified Tamaron of the requirements of Chapter 87-303, Laws of Florida (Grizzle-Figg Amendment), which amended Section 403.086, Florida Statutes, and of the Department's intention to modify Tamaron's operating permit to incorporate a schedule of compliance with Section 403.086, Florida Statutes, as amended by Chapter 87-303, Laws of Florida. On August 23, 1988, an operating permit (D058-141783), which contained secondary water treatment requirements, was issued to the facility. Specific condition 7 of the permit required that the facility be in compliance with the Grizzle-Figg Amendment by October, 1990, or eliminate discharge to surface waters. On September 5, 1990, Tamaron filed an application with the Department to renew its domestic waste water treatment and disposal systems operation permit. Tamaron did not consider its facility as discharging waste into one of the specifically named water bodies set forth in the Grizzle-Figg Amendment or to "water tributary thereto" and thereby required to meet the advanced waste treatment criteria set forth in the Grizzle-Figg Amendment. However, in an abundance of caution, Tamaron proceeded to bring its facility into compliance with the advanced waste treatment criteria as set forth in the Grizzle-Figg Amendment. After numerous requests for additional information and several meetings between Tamaron and the Department, the Department issued its Notice of Permit Denial on April 9, 1991, asserting that Tamaron had not provided: (a) reasonable assurance that the requirements of Section 403.086(1)(c), Florida Statutes, mandating advanced waste treatment (AWT) before discharge to certain designated surface waters, would be met and; (b) reasonable assurance that the discharge to those certain designated surface waters would result in minimal negative impact as required by Section 403.086(5)(a), Florida Statutes. The facility continues to operate under its secondary treatment permit No. DO58-141783. The facility consists of a wastewater treatment plant designed for secondary treatment, with tertiary filtration. The design capacity of the facility is 155,000 gallons per day (0.155MGD) with actual flows of slightly over 100,000 gallons per day (0.100MGD+). Three percolation ponds surround the facility comprising the primary effluent disposal method for the facility. The Tamaron subdivision has a series of excavated surface water bodies (stormwater lakes), hydraulically connected, which eventually discharge at the northeast corner of the subdivision into Phillippi Creek. The direct path of surface water flow is from the subdivision's stormwater lakes to Phillippi Creek. These stormwater lakes are in multiple ownership. Under Department policy, stormwater systems permitted by the Department, its predecessor DER, or a water management district solely as stormwater treatment facilities under Chapter 17-25, Florida Administrative Code, are not considered "waters of the State". However, stormwater systems built prior to Chapter 17-25, Florida Administrative Code, permitting requirements, were considered "waters of the State" if they discharge more frequently than a twenty five year, twenty-four hour storm event. See Petitioner's exhibits 13 & 15. Tamaron's stormwater system was built prior to Chapter 17-25, Florida Administrative Code, permitting requirements, and was designed to discharge at a ten year, twenty-four hour storm event which is more frequent than a twenty five year, twenty-four hour storm event. Discharge of water into Phillippi Creek from the subdivision's stormwater lakes is fairly frequent; however, the volume of the discharge is low. Phillippi Creek is a natural surface water which eventually flows into Roberts Bay. Roberts Bay is a specifically named water body in the Grizzle-Figg Amendment (Section 403.086(1)(c), Florida Statutes). Since September, 1989, Tamaron has retained William Murchie, P.E. of AM Engineering, to evaluate the design and operation of the facility in order to comply with appropriate regulatory requirements. The facility provides biological treatment through a contact stabilization utilizing an activated sludge. This process typically provides high quality advanced secondary biological treatment. A chemical feed tank system utilizing ferrous sulfate was added to the facility several years ago to chemically precipitate out total phosphorus to meet the advanced waste treatment requirements. High-level disinfection is achieved in the large chlorine contact chamber and through two tertiary filters. At the design flow of 0.155MGD, the chlorine contact chamber provides nearly 80 minutes of contact time, while actual contact time for existing flows, not including time in filters, is calculated at 110 minutes. Upon leaving the chlorine contact chamber and the biological treatment components of the facility, the chlorinated effluent is directed through two tertiary filters to reduce the biochemical oxygen demand (BOD) and total suspended solids (TSS). After the tertiary filters, the effluent passes through the sample block where it is sampled for TSS, BOD and chlorine and is then piped sequentially into the first, second and third percolation ponds. The percolation ponds span two acres and provide residence time of 35 to 45 days, during which time the effluent is further biologically treated and nitrogen is reduced. From the percolation ponds, the effluent is pumped into a low pressure system which uniformly distributes effluent over two nitrogen reduction filters. The nitrogen reduction filters are located north of the plant and are immediately adjacent to one of the subdivision's stormwater lakes. The nitrogen reduction filters consist of deep sand beds covered with Bermuda grass to provide high nitrogen uptake. The irrigation of the two nitrogen reduction filters is alternated every half day. These nitrogen reduction systems were modified in October/November, 1990, by adding 3 to 3 1/2 feet of clean sand with a permeability rate of 28 feet per day, planting Bermuda grass, and installing an irrigation/distribution system. These filters replaced two sand pits with shallow layers of very coarse sand, after initial testing demonstrated the sand pits to be inadequate in removing nutrients consistent with statutory requirements. In January, 1992, an underdrain system utilizing perforated pipe was installed in the nitrogen reduction filters to create an aerobic zone and to provide a representative sample port after nutrient reduction in the filters. This sample port, used for the biweekly monitoring, consists of a single solid pipe, that collects effluent from the perforated pipes, with a tap to prevent discharge into the adjacent stormwater lake, except during sampling events. The biweekly sampling event results in effluent being discharged from the pipe for approximately 30 minutes to flush the pipe so as to get a proper sample. The underdrain sampling port at the nitrogen reduction filters replaced two earlier monitor wells between the nitrogen reduction filter and the stormwater pond, which proved ineffective because of their location. The perforated underdrains are situated in filter bed sand of medium grain size with a permeability rate 100 feet per day and located below 3 - 3 1/2 feet of clean sand with a permeability rate of 28 feet per day and above very permeable layers of sand, stone and coarse shell. (See Tamaron's exhibit 23 and Department's exhibit 14) The very permeable layers of sand, coarse shell, the perforated pipe and the single solid pipe are all located above the ground water table. Since the perforated pipe and sample port are both located above the ground water level and the surface of the adjacent stormwater lake, it is unlikely that the effluent sample taken from the sample port would be influenced by the ground water or a back flow of water from the adjacent stormwater lake. The coarse shell layer situated below the nitrogen reduction filters extends to the edge of the adjacent stormwater lake. Therefore, the effluent, other than the effluent trapped in the perforated pipe and carried to the sample port, that is irrigated onto the nitrogen reduction filters passes through the sand and into the coarse shell layer. The effluent is then transported laterally through the coarse shell layer to the underground edge of the adjacent stormwater lake where there is a subsurface discharge into the adjacent stormwater lake. Since the discharge to the stormwater lakes is primarily subsurface in nature, the logical compliance point to measure effluent parameters would be the underground sample port which collects the effluent prior to subsurface discharge into the stormwater lake. See Petitioner's exhibit 15. The direction of ground water flow at the facility is towards the north to the adjacent stormwater lakes as evidenced by the hydraulic gradient of the site determined using ground water table elevations. The location for sampling effluent from the facility for compliance with secondary standards was described in Specific Condition 5 of Tamaron's previous permit No. D058-141783 dated August 23, 1988. Specific Condition 5 states that the discharge from the chlorine contact chamber shall be sampled in accordance with Chapter 17-19, Florida Administrative Code, (now Chapter 17-601, Florida Administrative Code), for compliance with the stated secondary limits. The facility's tertiary filters are located after the chlorine contact chamber. Tamaron samples effluent for compliance with secondary standards (BOD,TSS, chlorine) at the sampling box after disinfection and tertiary filtration. Tertiary filtration is designed to achieve a more efficient removal of TSS and BOD. The resulting effluent is usually of higher quality than secondarily treated effluent. A secondary plant with tertiary filtration is referred to as an "advanced secondary treatment" plant. Data presented by Tamaron titled Tamaron 1991-1993 Data On FDER Permit Compliance (Tamaron's exhibit 17, page 1 of 2) shows reported values, sampled after tertiary filtration at the sample box, which suggest that secondary treatment parameters, including fecal coliform, are not being exceeded. The data actually shows a very high removal rate for the parameters sampled. The United States Environmental Protection Agency issued a National Pollutant Discharge Elimination System (NPDES) permit, number FL0042811, to Tamaron for the facility with an effective date of June 1, 1991, which authorized Tamaron to discharge from the facility to the receiving waters named Phillippi Creek to Roberts Bay in accordance with the effluent limitation, monitoring requirements and other conditions set forth in the permit. Since the facility was located in the Grizzle-Figg Amendment area of Florida certain changes were made from the draft permit to the final permit. Those changes appear in the Amendment To The Statement Of Basis At The Time Of Final Permit Issuance which is made a part of the final permit. The amendment provides for changes in Part I, Effluent Limitations and Monitoring Requirements. These changes, among other things, require that the Grizzle-Figg Amendment annual limits of 5 mg/l BOD, 5mg/l TSS, 3mg/l total nitrogen and 1mg/l total phosphorus be added to the effluent limits to adequately maintain water quality standards, and added monitoring requirements and measurement frequency regulations to give the basis for permit limits and conditions in accordance with Chapters 17-302, 17-600 and 17-601, Florida Administrative Code. Data presented by Tamaron titled Tamaron 1991-1993 Data On NPDES Permit Compliance (Tamaron's exhibit 17, page 2 of 2) show reported values sampled after nitrogen reduction filters which suggest that the maximum values for AWT parameters, including fecal coliform, are not being exceeded, particularly after January, 1992, when Tamaron began sampling effluent collected by the perforated underdrains at the sample port. Tamaron has been monitoring and reporting compliance under its final NPDES permit and providing copies to the Department. There was no evidence that Tamaron was ever in violation of its NPDES permit. Tamaron submitted documentation to the Department with its permit application that demonstrated high-level disinfection within the facility was being achieved. However, TSS was being sampled after the application of the disinfectant. Using this procedure, the facility continued to achieve high- level disinfection until the permit denial. After the permit denial, the facility resumed basic disinfection which was required under Tamaron's permit for secondary treatment. This same data indicates that there was compliance with the requirements for fecal coliform. The record is not clear as to the frequency and number of samples taken to provide the data for reporting compliance with the NPDES permit and the data presented in Petitioner's exhibit 17, page 2 of 2. However, there was no evidence, other than sampling for TSS after the disinfectant was added, that Tamaron was not complying with its NPDES Permit that required, among other things, that the monitoring requirements and measurement frequency of the Department's rules and regulations be followed by Tamaron. Tamaron has modified and upgraded the facility in order to achieve a treatment process which will produce effluent of a quality for discharge under the Grizzle-Figg Amendment. Tamaron has provided reasonable assurances, although not absolute assurance, that the facility can comply with the discharge permit requirements of Chapter 403, Florida Statutes, including Section 403.086, Florida Statutes, notwithstanding the testimony of Jay Thabaraj to the contrary concerning Tamaron's sampling technique and its method of obtaining high-level disinfection which can be addressed as a specific condition, if necessary. Studies conducted by the Tamaron's engineer included in Petitioner's exhibit 21 indicates that there was no adverse impact to the stormwater lakes from the facility's wastewater treatment and disposal system. Tamaron has provided reasonable assurances that the point of discharge is a reasonably access point, where such discharge results only in minimal negative impact.
Recommendation Based on the foregoing Findings of Fact and Conclusions of Law, it is recommended that the Department enter a final order granting Tamaron an operating permit for its facility as secondary treatment facility. In the alternative, that the Department enter a final order granting Tamaron an operating permit for its facility that requires compliance with the advanced waste treatment criteria set forth in Section 403.086(4), Florida Statutes, that, in addition to any general or specific conditions that are normally required, contains specific conditions that: (a) contains specific instructions on sampling technique, sampling frequency and reporting as set forth in Rule 17- 740(1)(b)2., Florida Administrative Code, and (b) sets forth compliance with high-level disinfection, with a time limit for compliance, that accomplishes the intent of the rule, if not the strict letter of the rule, without total redesign of the facility. DONE AND ENTERED this 3rd day of May, 1994, in Tallahassee, Florida. WILLIAM R. CAVE Hearing Officer Division of Administrative Hearings The DeSoto Building 1230 Apalachee Parkway Tallahassee, Florida 32399-1550 (904) 488-9675 Filed with the Clerk of the Division of Administrative Hearings this 3rd day of May, 1994. APPENDIX TO RECOMMENDED ORDER, CASE NO. 91-2968 The following constitutes my specific rulings, pursuant to Section 120.59(2), Florida Statutes, on all of the proposed findings of fact submitted by the parties in this case. Petitioner, Tamaron's Proposed Findings of Fact: The following proposed findings of fact are adopted in substance as modified in the Recommended Order. The number in parentheses is the Finding(s) of Fact which so adopts the proposed finding(s) of fact: 1(1); 2(2); 3(3); 4(5,6); 5(6); 6(7); 8(12); 10(8); 11-12(13-25,38); 13(31-34); 14(8); 15(13); 16(14); 17-18(15); 19(36); 20(16); 21(17); 22(18); 23(19); 24(20); 25(21);26(22); 32(32,7); 33(33); 34(32,32); 36(31); 39-40(34); 41(36); 42- 43(34); 44(35); 47(4); and 51(10). Proposed findings of fact 27-31, and 35 are conclusions of law rather than findings of fact.. Proposed findings of fact 45, 46, 48-50, 56, 57, 59, and 61-72 are arguments rather than findings of fact. Proposed findings of fact 7, 9, 37, 38, 52-55, 58 and 60 are neither material nor relevant. Respondent, Department's Proposed Findings of Fact: The following proposed findings of fact are adopted in substance as modified in the Recommended Order. The number in parentheses is the Finding(s) of Fact which so adopts the proposed finding(s) of fact: 1(1,6); 2(2); 3(4,10); 5(9); 6(9,10); 8(11); 9-17(18-27); 18(8); 19(13); 20(5); 21(17); 22(30); 23(31); 24(14); 25(17); 26(18-23); 27(34); and 32(35,38). Proposed finding of fact 4 is neither material nor relevant but see Findings of Fact 18-25. Proposed findings of fact 7, 31 and 33 are arguments rather than findings of fact. Proposed findings of fact 28-30 are conclusions of law rather than findings of fact. COPIES FURNISHED: Virginia B. Wetherell, Secretary Department of Environmental Protection Twin Towers Office Building 2600 Blair Stone Road Tallahassee, Florida 32399-2400 Kenneth Plante, General Counsel Department of Environmental Protection Twin Towers Office Building 2600 Blair Stone Road Tallahassee, Florida 32399-2400 Charles G. Stephens, Esquire C. Robinson Hall, Esquire Enterprise Plaza, Suite 1516 101 E. Kennedy Blvd. Tampa, Florida 33602 Francine Ffolkes, Esquire Office of General Counsel Department of Environmental Protection Twin Towers Office Building 2600 Blair Stone Road Tallahassee, Florida 32399-2400
The Issue The issue to be resolved in this proceeding concerns whether the Petitioner was discriminated against based upon his age, in the manner addressed by Section 760.10, Florida Statutes.
Findings Of Fact The Petitioner was an employee of the City of Leesburg at times pertinent hereto. He was employed as a waste water operator trainee, commencing employment on or about June 5, 2000. The Respondent is a city government and unit of local government which operates two waste water plants. At times material to this proceeding the Respondent was employed and assigned to the "Canal Street Plant." The Petitioner was required to perform several job functions in his capacity as a waste water operator (trainee). Respondent's Exhibit Nine, in evidence, provides a job description for the Petitioner's employment positions which include the following: Record all flows; constantly survey charts and meter readings; repair leaking waste water pipes; perform building maintenance chores; maintain vigilance over all the department facilities and log or report any unusual situations; take oral and written instructions and carry them out in a quick and responsible manner; load and unload lawn cutting equipment, and cut and trim grass at utility plant sites; make repairs and/or replace parts on plant equipment; and repair leaks and other operations as directed. That job description also required a trainee to have knowledge of the functions and mechanics of pumps and other waste water plant equipment, knowledge of the occupational hazards and safety measures required in plant operations; to have an ability to detect faulty operating characteristics in equipment and to institute remedial action. The trainee is also required to be able to read meters, chart accurately and to adjust procedures to meet plant volume requirements. He must have an ability to understand and follow oral and written instructions. The Respondent's personnel policies and procedures manual (manual), in evidence as Respondent's Exhibit Eight, states at Policy No. 600.2(13) that "poor performance" is a violation of policy sufficient to initiate discipline. Poor performance is described in that section as a failure to perform assigned duties according to prescribed dimensions and standards on the individualized performance plan. Policy No. 600.2 provides for progressive discipline ranging from a verbal warning, to a written warning, a one-to-three day suspension, a four-to-five day suspension, or termination. Thus the discipline for violation of that policy is a range of appropriate actions from verbal warning to termination. On or about July 11, 2001, the Petitioner was the subject of a corrective action performance evaluation by his supervisor, Bob Mirabella. Mr. Mirabella, the Respondent's Operations Supervisor, accorded the Petitioner a grade of zero in several categories of work performance. Those are deficiencies indicating the Petitioner's lack of understanding of basic concepts related to his job position, including failure to following instructions, difficulty making simple decisions, difficulty or failure in following standard procedures, and a poor attitude. Overall his evaluation shows a rating of the Petitioner's performance as "unacceptable." That corrective action evaluation also contains a section that the Petitioner and his supervisor must initial, indicating that the Petitioner had reviewed the evaluation and that the performance deficiencies had been communicated to him. Mr. Mirabella advised the Petitioner of corrective measures to take and that any continued failure to meet expectations might result in termination. Mr. Mirabella created a type-written plan of improvement for the Petitioner with remedial activities, objectives, and developmental activities. Under the Respondent's consistent policy, the action plan would have been reviewed in 60 days, September 11, 2001, in order to determine that the Petitioner was meeting those expectations. On August 13, 2001, the Petitioner received a written reprimand for failure to perform duties assigned to him on July 23, 25, and August 9, 2001. These were duties that were in accordance with the prescribed dimensions and standards of the individual performance plan for the Petitioner. The written reprimand, in evidence as Respondent's Exhibit Two, included a description of the Petitioner's failure to perform duties including lawn maintenance, and again cited his argumentative attitude. On August 29, 2001, the Petitioner received a three-day suspension from duties for failure to perform assigned duties according to prescribed dimensions and standards as set forth in the individual performance plan. The disciplinary action form, in evidence as Respondent's Exhibit Three, specifically referred to the Petitioner's failure to perform lawn maintenance duties, failure to follow established rules and policies, and failure to take appropriate action to correct a leaking pump. It was also noted that the Petitioner was making coffee and watching television instead of performing assigned duties. Mr. Mirabella created a performance evaluation summary in preparation for the Petitioner's September 11, 2001, 60-day review of the initial, unsatisfactory evaluation of July 11, 2001. The summary showed a continuation of the Petitioner's difficulties and problems both in understanding his job and in dealing with other people in the course of his duties. The summary cited an incident where the Petitioner was abrasive, including swearing, toward other employees. It was Mr. Mirabella's intention to give the Petitioner a written reprimand regarding the swearing incident. However, due to the emergency nature of the events occurring on September 12, 2001, at the waste water plant, the written reprimand was not completed prior to the beginning of the investigation that ultimately led to the Petitioner's termination. The Petitioner made no major progress in correcting any of the problems outlined in the action plan that constituted part of the July 11, 2001, evaluation. On or about September 12, 2001, it was determined that there was a near overflow of sewage at the Canal Street Plant. Scott Moss, the employee who worked on the morning shift on September 13, 2001, discovered the problem and took corrective action immediately. Mr. Mirabella learned of the problem and reported it to the Respondent's Director of Environmental Services, Susanna Littell. Upon learning of the potential overflow occurrence, Ms. Littell began an investigation to determine when the overflow problem occurred. She gathered plant flow information and took measurements of the tanks. Employing engineering calculations, based upon the flow rates at the plant, Ms. Littell was able to determine that the problem had occurred on the Petitioner's shift. The Petitioner was the only employee on duty at the time the problem occurred. Ms. Littell consulted two outside engineers (non-city employees) to review her calculations. Those engineers found that her calculations were accurate. According to Ms. Littell, the waste water employees on duty at the plant should have observed the valve positions or otherwise noticed a problem in the plant that needed remediation. This was a regular part of their assigned duties, including the Petitioner. Mr. Mirabella determined a number of valves had been changed, which had caused the "aereation bay" to begin to fill with waste water. The aereation bay almost overflowed, which would have caused a serious environmental hazard and damage. It would have caused irreparable harm to the credibility of the waste water department, and could have engendered a minimum of $10,000.00 dollars in fines imposed by the Department of Environmental Protection. The importance of preventing these types of situations has been emphasized to employees who worked at the waste water plant, including the Petitioner. Because of the Petitioner's failure to notice the obvious serious problem occurring at the plant on his shift, and his failure to take corrective action, he was cited for negligence in performing his assigned duties in violation of the Respondent's policy. The employee who worked as his counter- part on the shift immediately after the Petitioner's, Elmer Wagner, was also cited for negligence in performing his duties because of his failure to notice the problem and to take corrective action. Mr. Wagner at the time in question was 67 years of age. The information obtained during Ms. Littell's investigation was forwarded to Ms. Jakki Cunningham-Perry, the Respondent's Director of Human Resources, in order for her to determine the appropriate disciplinary action to take. Ms. Cunningham-Perry performed an investigation of the September 12, 2001, incident. She spoke to several individuals, including, but not limited to, Mr. Mirabella, Ms. Littell, Jim Richards, who was one of the engineers consulted by Ms. Littell, as well as the Petitioner. She thereafter deliberated and prepared a written memorandum setting forth her investigative findings. Ms. Cunningham-Perry concluded that the closing of the valves occurred during the Petitioner's shift. She also concluded that Mr. Wagner should have noticed the change in the pump flow and valves during his shift. Both the Petitioner and Mr. Wagner were cited for failure to perform assigned duties in violation of city policy 600.0(13), as a result of the investigation performed by Ms. Cummingham-Perry. She reviewed the personnel history of both the Petitioner and Mr. Wagner in order to determine the appropriate levels of discipline. The Petitioner's prior history included the special corrective action evaluation of July 11, 2001, indicating unacceptable performance; the August 13, 2001, written reprimand for violation of policy 600.2(13); and the suspension for violation of that same policy. In light of the past performance of the Petitioner, as well as the September 12, 2001, incident, Ms. Cunningham-Perry recommended that he be terminated. On November 30, 2001, the Petitioner was terminated from his employment with the Respondent. The Petitioner's last day on the payroll with the Respondent was December 6, 2001. Mr. Wagner is older than the Petitioner and has had an exemplary performance record with the Respondent City. He never had any disciplinary problems on his record for 15 years of his employment with the Respondent. Because of his theretofore spotless employment disciplinary record, he was given a written reprimand as a result of his negligent performance of job duties on September 12, 2001. No evidence was adduced indicating that the Respondent treated any employees over the age of 40, including the Petitioner, any differently than employees under the age of 40. During the relevant time period the Respondent had approximately 22 employees in the waste water department. Fifteen of those 22 employees were over the age of 40. The Petitioner actually produced no evidence in his case establishing his date of birth or age. There is no evidence that the Petitioner's age was considered or was a factor in his termination decision. The decision to terminate him was based solely on his failure to perform assigned duties and his prior performance record. Moreover, the Petitioner adduced no evidence to show that he was replaced or otherwise lost his position to a younger individual. The individual who became a waste water trainee after the Petitioner's termination was Scott Moss. Mr. Moss is currently employed as Waste Water Operator with the Respondent. There is no doubt that Mr. Moss is a significantly younger individual, purported to have been in his late 20's when the incident in question occurred. The Petitioner, however, produced no evidence regarding Mr. Moss' date of birth or his age in relationship to the Petitioner's. He also produced no evidence to show that he was actually replaced by Mr. Moss. Mr. Moss had been hired on or about January 29, 2001, nearly one year prior to the date of the Petitioner's termination. Both the Petitioner and Mr. Moss were working at the Canal Street Plant in similar capacities and duties, at the time the Petitioner was terminated. Mr. Moss, therefore, just continued to work there and ultimately was elevated, through his adequate performance, to the position of Waste Water Operator. It was not established that he was hired simply to replace the Petitioner when the Petitioner was terminated. Further, the Petitioner did not adduce sufficient, persuasive evidence to show that he was actually qualified to perform the job. His prior performance had been unacceptable since at least July 11, 2001, and likely before that time. The Petitioner repeatedly failed to comprehend and perform assigned duties of a Waste Water Operator Trainee on multiple occasions. This was despite efforts by the Respondent to help the Petitioner correct his deficiencies. Accordingly, it has not been established that the Petitioner was "qualified" for the position of Waste Water Operator Trainee.
Recommendation Having considered the foregoing Findings of Fact, Conclusions of Law, the evidence of record, the candor and demeanor of the witnesses, and the pleadings and arguments of the parties, it is, therefore, RECOMMENDED that a final order be entered by the Florida Commission on Human Relations dismissing the Petition in its entirety. DONE AND ENTERED this 3rd day of May, 2004, in Tallahassee, Leon County, Florida. S P. MICHAEL RUFF Administrative Law Judge Division of Administrative Hearings The DeSoto Building 1230 Apalachee Parkway Tallahassee, Florida 32399-3060 (850) 488-9675 SUNCOM 278-9675 Fax Filing (850) 921-6847 www.doah.state.fl.us Filed with Clerk of the Division of Administrative Hearings this 3rd day of May, 2004. COPIES FURNISHED: Michael George 25131 Southeast 167th Place Umatilla, Florida 32784 Steven W. Johnson, Esquire McLin & Burnsed, P.A. Post Office Box 491357 Leesburg, Florida 34749-1357 Cecil Howard, General Counsel Florida Commission on Human Relations 2009 Apalachee Parkway, Suite 100 Tallahassee, Florida 32301 Denise Crawford, Agency Clerk Florida Commission on Human Relations 2009 Apalachee Parkway, Suite 100 Tallahassee, Florida 32301
The Issue The ultimate issue to be resolved in this proceeding is whether the Department should issue a permit allowing the construction of a wastewater treatment and disposal system as requested in the modified application filed by Thomas E. Wasdin. The applicant and the Department contend that reasonable assurances have been given that the proposed facility will not result in violations of any of the Department's rules or regulations. The Petitioner contends that the proposed facility is located too near to existing shallow water drinking wells and that the facility otherwise fails to comport with the Department's rules and regulations.
Findings Of Fact Petitioner is the president of Beach Woods of Brevard County, Inc. The corporation is the developer of "Beach Woods," a 376-unit planned unit development located in Melbourne Beach, Brevard County, Florida. One hundred eighty of the units have already been developed. Existing regional sewage treatment facilities operated by Brevard County are not adequate to accommodate the total number of units that the applicant proposes to develop. It appears that 24 more hookups are all that the existing facilities will tolerate. Beyond that number, a sewer moratorium is in effect, and unless the applicant can make some other arrangement for disposing of sewage, the development cannot be completed. The county has approved the planned unit development. In order to meet sewage treatment needs of the proposed development, the applicant is proposing to construct a "package sewage treatment plant" to accommodate waste that exceeds quantities that can be handled by existing regional facilities. Once the regional facilities are upgraded so that the development's sewage treatment needs can be accommodated, the applicant proposes to disassemble the package plant and utilize the regional facilities. The proposed plant would be a 50,000 gallons per day contact stabilization sewage treatment plant. Initially, it would be operated as a 5,000 to 15,000 gallons per day aeration plant. Once loads reach 18,000 gallons per day, it would become a contact stabilization plant. The Present collection and transmission system for sewage that exists at Beach Woods includes an 8-Inch collection station from which sewage flows to an existing lift station that pumps effluent via 6-inch pipes to the regional plant. When the proposed plant is completed, a computerized system would be set up to send effluent to the new plants when the limits that the regional plant can accommodate are met. Once the regional plant is upgraded to sufficient capacity, the bypass to the proposed plant would be eliminated, and all units would then be connected to the original collection system. The proposed treatment plant is based upon proven technology that has been in existence for more than 50 years. The plant should operate reliably, and proper consideration has been given to odor, noise, lighting, and aerosol drift. In close proximity to the plant, it is likely that there would occasionally be a "earthy smell" that would be noticeable, but not objectionable. Outside of the immediate proximity, no odor would be noticeable. Large fans would be operated in connection with the plant, and some noise would result. It does not, however, appear that the noise would be excessive or bothersome, even in the immediate vicinity of the plant. The plant would be lighted by street lights and would not result in any more excessive lights than normal street lights. The plant is not of the sort that aerosol drift is a likely problem. Adequate considerations have been given to providing emergency power to the plant in the event of a power outage. The plant could sit for at least 20 hours without power before any emergency would exist. If there was a power outage in excess of that period, emergency power sources are available. Consideration has been given to the 100-year flood plain. The plant has been placed at an elevation that keeps it outside of the 100-year flood plain. The land application system proposed by the applicant would utilize drain fields that would be alternately rested. Groundwater flows from the area of the proposed drain fields are in a southwesterly direction toward the Indian River. The Indian River in the location of the proposed facility is a "Class III surface water." Groundwater in the area of the proposed facility might be classified as either "G-I" or "G-II." Reasonable assurance has been given that the proposed sewage treatment plant would not operate in such a manner as to degrade surface or ground waters to the extent that any of the Department's specific water quality parameters set out in Chapter 17, Florida Administrative Code, would be violated. The proposed sewage treatment plant comports with local requirements and has been approved by Brevard County. The Allans Subdivision is a residential development that is located directly to the north of the Beach Woods development. Petitioner utilizes a shallow water well as a source of drinking water. The proposed land application site of the sewage treatment plant is located within 500 feet of the Petitioner's well. There are at least two other shallow water wells that serve as drinking water sources located within 500 feet of the proposed land application site. The applicant indicated a willingness to move the proposed facility so that no part of it would be located within 500 feet of the shallow drinking water wells. The evidence establishes that the plant could be moved to accomplish that. No specific plan, however was presented. Potential factual issues could exist respecting appropriate buffer zones for any relocation of the facility, even a minor relocation. The applicant is proposing to develop areas within 100 feet of the proposed facility. The applicant does not, however, propose to locate any public eating, drinking, or bathing facilities within 100 feet of the proposed plant or land application area. No map was presented during the course of proceedings before the Department of Environmental Regulation that preceded the formal administrative hearing or during the hearing itself to establish present and anticipated land uses within one mile of the boundaries of the proposed facility. The facility of such a size that it could not inhibit any conceivable present or proposed future land uses except within 500 feet of the proposed facility. Evidence was offered at the hearing from which it could be concluded that the Department has, in the past, issued permits for sewage treatment plants located within 500 feet of existing shallow drinking water wells. The testimony was that this has occurred despite a requirement in the Department's rules that there be a 500-foot buffer zone between any such plant and a shallow drinking water supply. No specific evidence was presented as to why the Department has allowed such a breach of its rules or why it should be allowed in this proceeding.
