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SOUTH WATERFRONT PARK HOMEOWNERS ASSOCIATION, ET AL. vs. DEPARTMENT OF ENVIRONMENTAL REGULATION AND HACIENDA DEL RIO, 84-004230 (1984)
Division of Administrative Hearings, Florida Number: 84-004230 Latest Update: Jul. 10, 1985

Findings Of Fact Respondent HDR has applied to DER for a permit to construct a 60,000 gallon per day extended aeration sewage treatment plant with percolation ponds. The facility would be used to provide secondary treatment of domestic waste from the HDR Mobile Home Park. The project is in Volusia County south of the City of Oak Hill and north of the Town of Edgewater. It is bounded on the east side by the Indian River and the west side by U.S. Highway One. The mobile home project site consists of approximately 156 acres, with the proposed wastewater treatment plant located in the southwest corner of the tract. HDR submitted Application No. 85433 to DER on July 2, 1984, requesting a permit to construct a 0.6 MGD extended aeration sewage treatment plant and associated percolation ponds for the mobile home project. Supplemental information was filed with DER on August 29, 1984. DER issued a notice of intent to permit the project on November 8, 1984. The plant would provide secondary treatment of effluent with a minimum of 90 percent removal of BOD's and suspended solids through aeration, settling and chlorination processes. The system is designed to collect sewage through a gravity system and lift station. The lift station dumps the sewage into the aeration chambers where forced air is mixed with the sewage, resulting in removal of organic materials and solids. The dissolved solids are then separated in the settling tank. From the settling tank, clear effluent enters the chlorine contact chamber where chlorine disinfectant is added prior to discharge into the percolation pond. The method of treatment described above and the design of the plant are standard. If the plant is operated properly, the wastewater will meet all DER criteria for secondary sewage treatment. Plant odor will be minimized by the continual feed of forced air into the system. Silencers will be installed on blowers to minimize any adverse noise effects from the blowers' operation. Aerosol drift is not a factor with the design of this plant. Security lighting will be provided, and the plant site will be surrounded by a six foot security fence. The design provides for effluent sampling access points and there will be a flow meter for measuring effluent discharge on site. A Class C operator will be required to operate the plant. Disposal of the 90 percent treated effluent will be made into two percolation ponds. The ponds will be alternately loaded, with one pond being loaded for seven days and then resting seven days. The total surface area for the two ponds is approximately 130,000 square feet. The ponds are designed with berms of three feet with an emergency overflow one foot from the top of each berm. The two ponds together are designed to handle 200,000 gallons per day which would be the ultimate build out of this project. However, the maximum capacity of the initial phase of the wastewater treatment plant would be 60,000 gallons a day. Any expansion to the sewage treatment plant would require a separate permit. The overall elevation of the area where the ponds are to be located is approximately 14 feet above sea level. Each pond is designed so that the pond bottom is two feet above the underground water table level measured at the highest point for the rainy season. In a 100 year flood, it is expected that the effluent and water can be absorbed without an overflow. The mobile home park has a storm retention system in which any theoretical overflow would be caught. The soil type at the location of the percolation ponds consists of several layers of sands. This type of soil has good permeability in that it provides a good transfer of water through the soil and is therefore suitable for siting of the percolation ponds. Pond design is conservative in that the hydraulic loading rate has a safety factor of at least 300 percent. Once the effluent has percolated into the ponds, the discharge will meet or exceed the level of quality of the G-2 ground water within the 100 foot zone of discharge. The design of the wastewater treatment plant also includes sufficient monitoring wells and provides for adequate buffer zones from residences and drainage ditches. No surface waters of the state are located within 500 feet of the sewage treatment plant or its percolation ponds. The Indian River, which is adjacent to the Hacienda Del Rio project, is approximately 2,500 feet from the sewage treatment plant. There will be no direct discharge by the sewage treatment plant into this body of water or any surface waters, nor would any indirect effect on surface waters be measurable. Shellfish harvesting is a local industry. The waters of the Indian River immediately east of the Hacienda Del Rio property are designated Class II waters suitable for shellfish harvesting. The Indian River is also part of the Canaveral National Seashore Waters, which are designated as Outstanding Florida Waters. Concern was expressed that additional growth in the area might contribute to degradation of these Class II waters. There was, however, no evidence to indicate that the construction or implementation of the wastewater treatment plant by HCD would degrade ore pollute the Indian River (which is both Class II and Outstanding Florida Water) or any other State of Florida surface waters. It should be noted that waters north and south of the property in the Indian River are closed to shellfish harvesting, apparently due to pollution. The Town of Edgewater north of the Hacienda Del Rio project has a secondary wastewater treatment plant which discharges its effluent directly into the Indian River. The City of Oak Hill to the south of the project has no wastewater treatment plant whatsoever. Individual businesses and homes utilize septic tanks, which can cause pollution to the Indian River through seepage. The HDR sewage treatment plant would thus meet higher standards than neighboring community facilities.

Recommendation From the foregoing, it is RECOMMENDED that the Department of Environmental Regulation issue a Final Order granting the application of Hacienda Del Rio. DONE and ENTERED this 31st day of May, 1985, in Tallahassee, Florida. R. T. CARPENTER Hearing Officer Division of Administrative Hearings The Oakland Building 2009 Apalachee Parkway Tallahassee, Florida 32301 (904) 488-9675 Filed with the Clerk of the Division of Administrative Hearings this 31st day of May, 1985. COPIES FURNISHED: Betty J. Steffens, Esquire NABORS, GIBLIN & STEFFENS, P.A. 102 South Monroe Street Tallahassee, Florida 32302 William C. Henderson, Esquire HENDERSON & HENDERSON, P.A. Post Office Box 1840 New Smyrna Beach, Florida 32070 B. J. Owens, Esquire Department of Environmental Regulation 2600 Blairstone Road Tallahassee, Florida 32301 Alva Stewart, Vice President South Waterfront Park Homeowners Association 150 Charles Street Edgewater, Florida 32032 Victoria Tschinkel, Secretary Department of Environmental Regulation Twin Towers Office Building 2600 Blairstone Road Tallahassee, Florida 32301

Florida Laws (3) 258.39258.392403.086
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DEPARTMENT OF ENVIRONMENTAL REGULATION vs. EUGENE HARDY, 78-001209 (1978)
Division of Administrative Hearings, Florida Number: 78-001209 Latest Update: Feb. 26, 1979

Findings Of Fact Respondent is an individual who owns or operates a water system that provides piped water for human consumption to the Hardy House Diner in Washington county, Florida. The water system serves at least 35 persons daily at least 60 days out of the year. Respondent has owned or operated the water system since at least October 28, 1976. Respondent does not continually apply effective disinfectant measure to the water distributed to the customer of the Hardy House Diner, nor is Respondent's water system equipped with any disinfection equipment. Respondent's water system has a daily flow greater than 2,500 gallons per day, but less than 100,000 gallons per day. The operation, maintenance and supervision of the water system is not performed by a person who has passed an examination that entitles such a person to be a certified operator. Neither the Department nor the Washington County, Florida Health Department has received from Respondent reports which contained information about the operation and maintenance of the Respondent's water system. The water system's lack of disinfectant equipment and the absence of a certified operator for the system and Respondent's failure to file operation reports have existed continuously since "October, 1976. Representatives of the Department conducted a public water systems inspection of Respondent's water system on October 26, 1976. At that time, the system was found to be unsatisfactory in several categories, including general plant condition, existence of safety hazards, lack of chlorination, failure to submit regular reports, failure to submit monthly bacteriological samples, failure to perform chemical analysis of drinking water and failure to install a raw water tap between the pump and point of chlorination. A second inspection was performed on April 7, 1977, in which it was determined that Respondent still had not installed a chlorinations system, had failed to submit monthly operating reports had failed to employ a certified operator, had failed to submit monthly bacteriological samples, and had failed to perform annual chemical analysis of water disposed from the system. On December 7, 1977, a representative of the Department whose job responsibilities included inspecting public water systems was refused permission to enter and inspect the water system serving the Hardy house diner and its customer. The Department representative was refused entry after he had identified himself and made his purpose known to Respondent. The Department has incurred expenses of $117.58, including personnel time and travel expense, in the course of investigating Respondent's alleged violations.

Recommendation RECOMMENDED: That a final order be entered by the State of Florida, Department of Environmental Regulation, finding the Respondent to be in violation of the above-referenced statutes and regulations, and requiring Respondent to pay the state its reasonable costs and expenses, in the amount of $117.58 incurred in investigating and prosecuting this administrative proceeding. RECOMMENDED this 26th day of February, 1979, at Tallahassee, Florida. WILLIAM E. WILLIAMS, Hearing Officer Division of Administrative Hearings The DeSoto Building 2230 Apalachee Parkway Tallahassee, Florida 32399-1550 (904) 488-9675 Filed with the Clerk of the Division of Administrative Hearings this 26th day of February, 1979. COPIES FURNISHED: Vance W. Kidder, Esquire Assistant General Counsel Department of Environmental Regulation 2600 Blair Stone Road Tallahassee, Florida 32301 Mr. Eugene Hardy 1005 Highway 90 West Chipley, Florida 32428 ================================================================= AGENCY FINAL ORDER ================================================================= STATE OF FLORIDA DEPARTMENT OF ENVIRONMENTAL REGULATION STATE OF FLORIDA, DEPARTMENT OF ENVIRONMENTAL REGULATION, Petitioner, vs. CASE NO. 78-1209 DER Case No. WC-10-78 EUGENE HARDY, Respondent. /

Florida Laws (5) 120.51120.57403.858403.859403.860
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PHILLIP G. PANOS vs DEPARTMENT OF ENVIRONMENTAL REGULATION, 90-000479 (1990)
Division of Administrative Hearings, Florida Filed:Tallahassee, Florida Jan. 25, 1990 Number: 90-000479 Latest Update: Dec. 11, 1990

Findings Of Fact The Petitioner, Phillip G. Panos, recently moved from Michigan to Florida and is now a Florida resident. On December 9, 1989, prior to moving to Florida, he applied to the Respondent, Department of Environmental Regulation for certification as a Class C domestic waste water treatment plant operator. The Respondent is an agency of the State of Florida charged, among other duties, with regulating the certification, the practice standards and the educational standards of Class C domestic waste water treatment plant operators. The Respondent agency reviewed the Petitioner's application and denied it for failure to demonstrate the requisite three years of experience required by the rule cited below. From April, 1974 to June, 1990 the Petitioner was employed at the Chapaton Pumping Station in St. Clair Shores, Macomb, Michigan. The Chapaton Pumping Station duties involved the Petitioner monitoring the distribution of sewage flows, collecting sludge samples, chlorinating the effluent and pumping it into Lake St. Clair. When the Petitioner left the Chapaton Pumping Station, in June of 1990, he held the position of Senior Station Operator II. The Chapaton Pumping Station receives a combination of storm water flow and sanitary sewage flows. It is a pumping and storm water retention facility for combined sewage. The facility provides primary treatment and disinfection for this combined sewage effluent. The effluent is chlorinated and then pumped to nearby Lake St. Clair while the solids that have settled out of the effluent are retained, collected and sent to the Detroit waste water treatment facility for advanced waste treatment. Chapaton is classified by the state of Michigan's Department of Natural Resources as an "industrial/commercial facility". The industrial classification was originated by the U.S. Environmental Protection Agency (EPA) and has been adopted as a designation or classification by both Michigan and Florida. The Petitioner holds an industrial/commercial waste water treatment certification from the state of Michigan in the category of "plain clarification and disinfection." The Petitioner's experience in Michigan is in the area of industrial waste water treatment and does not constitute actual experience in on-site operational control of a domestic waste water treatment plant (that is a sewage treatment plant). The Petitioner's experience in Michigan does not qualify as industrial waste water treatment plant experience, that could be used to meet the actual experience requirement, because the Chapaton plant performs only primary treatment and disinfection. Secondary or advanced waste treatment is performed at the Detroit waste water treatment plant, with which the Petitioner has no experience. In a typical domestic waste water treatment plant in Florida, "primary treatment" involves primary clarification or settling. Primary clarification occurs in a circular or rectangular tank where soluble solids settle out to the bottom of the tank and floating solids are removed by a skimming device. The soluble solids are called sludge. Primary clarification can remove 40% of BOD and suspended solids. It is not a form of advanced treatment or even secondary treatment. At the Chapaton plant, during primary treatment, a minimum of 70% BOD and suspended solids are removed. The sludge is not treated at the Chapaton plant but is pumped to the Detroit waste water treatment plant. Thus Chapaton could not be classified as a domestic waste water treatment plant by Florida standards, since it only provides primary clarification and no secondary or advanced waste water treatment. Secondary treatment consists of two types. Activated sludge or trickling filter treatment. Both types deal with oxygen being introduced to the sludge to achieve stabilization and more settling out of the sludge elements. Since June 18, 1990 the Petitioner has been employed as a waste water treatment plant operator I in a training program at the George L. Lohmeyer Waste water Treatment Plant in Ft. Lauderdale, Florida. In that training program the Petitioner is being trained in all phases of operation of the Lohmeyer plant. It is a 34-million-gallon-per-day (MGD) activated sludge treatment plant. In his duties, the Petitioner monitors the plant treatment processes, takes samples and submits them to the city's laboratory. The Petitioner is capable of testing the samples himself for dissolved oxygen, chlorine and ph. Reports are signed by the regional chief or the regional facilities manager. The Petitioner's present position qualifies as actual, appropriate experience in the operational control of a waste water treatment plant. The Petitioner has accumulated approximately 3-1/2 months of the 12 months of actual experience required for certification as a Class C waste water treatment plant operator, through the exercise of his duties at the Lohmeyer plant. The Petitioner must accumulate 12 months or 2,080 hours of actual experience before he can qualify for the Class C certification. The Petitioner is a high school graduate and has successfully completed Volumes I and II of the California State University correspondence course in waste water treatment, which is included on the Respondent agency's list of approved courses. Petitioner's 3-1/2 months of actual appropriate experience in Ft. Lauderdale, plus his educational background, including the courses taken in California, yield a total of 36 months or 3 years of constructive experience. Petitioner does not yet have the 12 months of actual experience required by the rules but rather, is approximately 8-1/2 months short of the actual experience requirement. Thus, the Petitioner fails to meet the experience requirement necessary for certification as a Class C domestic waste water treatment plant operator at this time, although in approximately 8-1/2 months, he should be able to meet that requirement.

Recommendation Having considered the foregoing findings of fact, conclusions of law, the evidence of record and the candor and demeanor of the witnesses, it is therefore RECOMMENDED: That a Final Order be entered by the Department of Environmental Regulation denying Petitioner's application for certification as a Class C domestic waste water treatment plant operator without prejudice to reapplication at such time as his one year of actual experience at such a treatment facility is completed. DONE and ENTERED this 11 of December, 1990, in Tallahassee, Florida. P. MICHAEL RUFF 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 11 day of December, 1990. APPENDIX TO RECOMMENDED ORDER IN CASE NO. 90-479 (The Petitioner filed no proposed findings of fact.) RESPONDENT'S PROPOSED FINDINGS OF FACT 1. - 21. are accepted. COPIES FURNISHED TO: Dale H. Twachtmann, Secretary Department of Environmental Regulation 2600 Blair Stone Road Tallahassee, FL 32399-2400 Daniel H. Thompson, Esq. General Counsel Department of Environmental Regulation 2600 Blair Stone Road Tallahassee, FL 32399-2400 Phillip G. Panos 2315 N.W. 115 Drive Coral Springs, FL 33065 Francine M. Ffolkes, Esq. Assistant General Counsel Department of Environmental Regulation 2600 Blair Stone Road Tallahassee, FL 32399-2400

Florida Laws (1) 120.57
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GEORGE H. HOPPER vs. DEPARTMENT OF ENVIRONMENTAL REGULATION, 77-002295 (1977)
Division of Administrative Hearings, Florida Number: 77-002295 Latest Update: May 24, 1979

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

Florida Laws (1) 120.57
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WOOD, CAMPBELL, MILLER, ET AL. vs. THE DELTONA CORPORATION AND DEPARTMENT OF ENVIRONMENTAL REGULATION, 80-000961 (1980)
Division of Administrative Hearings, Florida Number: 80-000961 Latest Update: Jan. 07, 1981

The Issue This case presents two questions for consideration. The first question concerns the Petitioners' contention that the grant of the permit at issue must be considered contemporaneously with the matters of file in the application made by the Respondent, The Deltona Corporation, with the Respondent, State of Florida, Department of Environmental Regulation, File No. 64-24208, pending before the Department. From the point of view of the Petitioners, should this contemporaneous review process be afforded, then the current permit would not be granted due to the alleged deficiencies associated with the application, File No. 64-24208. The second question to be answered in this case concerns the dispute between the Respondents on the issue of water quality monitoring as a condition to granting the permit sought herein. The Respondent Department would have the applicant monitor in six lakes in the area of the project and the applicant would restrict its monitoring activity to three lakes in the project area. The Petitioners support the Department in its position on the monitoring question. 1/

Findings Of Fact The Respondent, The Deltona Corporation, has made application with the Respondent, State of Florida, Department of Environmental Regulation, to effect drainage system improvements to a land locked conveyance network which consists of the enlargement and regrading 990 lineal feet of existing channel cross- section and the installation of additional culverts and control structures at road crossings. The project also involves repairs and replacement of a damaged culvert. The work would be accomplished by land based equipment transported to the work site by existing overland routes. The excavated sand fill would be placed on upland property owned by The Deltona Corporation. The details of the project and data related to the geographical area may be found in the Joint Exhibit I admitted into evidence. The date of the application for permit is December 12, 1979. On January 25, 1980, the Department of Environmental Regulation sent out a notice of the pending review by the Department of the permit application. After receipt of that notice, attorney for the Petitioners, on February 12, 1980, wrote to the Department expressing the objection to the project made by property owners in the area of the project site, together with a list of those owners found in an attached Petition of owners' names and addresses. A copy of this letter and attached Petition may be found as Joint Exhibit No. VII admitted into evidence. Subsequent to the receipt of the statement of objections, the Department issued a construction permit dated April 30, 1980, subject to conditions. A copy of this permit may be found as Joint Exhibit No. VIII admitted into evidence. The Petitioners, through their counsel, then filed a formal petition dated May 6, 1980, which was the vehicle utilized in establishing the details of this dispute and was the basis for the Department Secretary forwarding the case to the Division of Administrative Hearings for consideration by a hearing officer in keeping with the provisions of Section 120.57, Florida Statutes. The hearing was conducted on October 16, 1980, and the Petitioners' position was more specifically defined in the course of that hearing and the claim as described in the issue statement of this order constitutes the substance of the Petitioners' position. 2/ Joint Exhibit No. I; petitioners' Exhibit No. 1 and Respondent Deltona's Exhibits 1, 2 and 4 constitute sketches and aerial photographs of the general project area. Joint Exhibit No. 1 identifies the work area with more particularity. Respondent's Exhibit No. 2 indicates the desired flow pattern of the water through the various lake systems and indicates whether the flow is by gravity flow or pump flow. This drawing depicts the proposed channels and structural improvements that would be involved. The Department has indicated that all the regulatory concerns which it has about the project associated with Permit No. 64-26478-4E, the permit in question, have been adequately addressed, subject to the conditions set forth in the permit document. Joint Exhibit Nos. V and VI; Respondent Deltona's Exhibit Nos. 5, 6 and 7; and the Petitioners Exhibit No. 2 are exhibits pertaining to water quality concerns, to include sample results. The testing and other information provided indicates that the project as contemplaced, would meat the regulatory parameters set forth in Chapter 403, Florida Statutes, and Chapters 17-3 and 17-4, Florida Administrative Code. The Department in expressing its concern that continued water quality monitoring be conducted has indicated that it feels that future periodic monitoring should be done in Jenkins Pond, Lake Big, Lake Diana, McGarity Lake, Sidney Lake and Lake Mitnik. The Respondent Deltona would only conduct this monitoring in the first three lakes named. By looking at the Respondent Deltona's Exhibit No. 2, it could be seen that all of the aforementioned lakes would be in the same basic flow pattern. Of the system of lakes, the area around McGarity Lake is the most highly developed and and has the greatest potential for causing unacceptable pollution. That pollution could be carried through the other lakes within the system as described in view of the potential of the system, if the project is built, to convey a greater volume of water at a higher rate of flow. A more expansive water quality monitoring system within six lakes as opposed to three lakes would increase the opportunity to discover potential hazards from pollutant at an earlier data. This is particularly so by using lakes such as McGarity Lake where there is a higher level of developmental build-out.

Florida Laws (1) 120.57
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DEPARTMENT OF ENVIRONMENTAL PROTECTION vs JEFFREY M. HILL, 14-003013EF (2014)
Division of Administrative Hearings, Florida Filed:Lake City, Florida Jun. 26, 2014 Number: 14-003013EF Latest Update: Dec. 02, 2014

The Issue The issues for determination in this case are whether Respondent Jeffrey Hill should pay the administrative penalty and investigative costs, and should undertake the corrective actions that are demanded by the Florida Department of Environmental Protection (“Department”) in its Notice of Violation, Orders for Corrective Action, and Civil Penalty Assessment (“NOV”).

Findings Of Fact Respondent is the owner and operator of a community water system and its associated piping, designated PWS No. 2124409, located on parcel ID No. 03-4S-17-07486-001 on Country Club Road, in Lake City, Columbia County, Florida (“the property”). Respondent is a “person” as defined in section 403.852(5), Florida Statutes. Respondent is a “supplier of water” as defined in section 403.852(8). The water system is a “public water system” and a “community water system” as defined in sections 403.852(2) and (3), respectively. The community water system is a Category V, Class D water system with a capacity of 28,800 gallons per day that supplies between 25 and 3,300 people, using groundwater as its source. Count I Count I of the NOV charges Respondent with failure to sample for nitrate and nitrite in 2012 and 2013, which was admitted by Respondent. Count II Count II of the NOV charges Respondent with failure to sample for primary inorganic contaminants for the 2011-2013 compliance period, which was admitted by Respondent. Count III Count III of the NOV charges Respondent with failure to analyze for secondary contaminants in the 2011-2013 compliance period, which was admitted by Respondent. Count IV Count IV of the NOV charges Respondent with failure to sample for volatile organic contaminants in the 2011-2013 compliance period, which was admitted by Respondent. Count V Count V of the NOV charges Respondent with failure to sample for synthetic organic contaminants in the 2011-2013 compliance period, which was admitted by Respondent. Count VI Count VI of the NOV charges Respondent with failure to sample for total coliform from June 2013 to date, which was admitted by Respondent. Count VII Count VII of the NOV charges Respondent with failure to employ an operator for the system since May 2013, which was admitted by Respondent. Count VIII Count VIII of the NOV charges Respondent with failure to submit test results required by Florida Administrative Code Chapter 62-550, and failure to file a monthly operation report since April 2013, which was admitted by Respondent. Count IX Count IX of the NOV charges Respondent with failure to issue Tier 3 notices in May 2013 and March 2014, advising customers of the failure to monitor for certain contaminants, which Respondent admitted. Count X Count X of the NOV charges Respondent with failure to provide a consumer confidence report to his customers in 2012 and 2013, which was admitted by Respondent. Count XI In Count XI of the NOV, the Department states that it incurred $530 in investigative costs related to this enforcement matter, which is admitted by Respondent.

Florida Laws (4) 120.57120.68403.121403.852
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JOSEPH DIGERLANDOTO vs DEPARTMENT OF HEALTH AND REHABILITATIVE SERVICES, 94-006483 (1994)
Division of Administrative Hearings, Florida Filed:Tampa, Florida Nov. 18, 1994 Number: 94-006483 Latest Update: Jun. 30, 1995

The Issue The issue in this case is whether the Department of Health and Rehabilitative Services (HRS) should grant the Petitioner's applications, filed under F.A.C. Rule 10D-6.045, for variances from the F.A.C. Rule 10D-6.046(1)(c) requirement that on-site treatment and disposal systems (OSTDS's) be placed no closer than 200 feet from public drinking water wells serving a facility with a sewage flow of more than 2,000 gallons per day (gpd).

Findings Of Fact The Petitioner, Joseph DiGerlando, owns three lots (1, 2 and 26) in the San Remo subdivision in Hillsborough County, which was platted in 1977. There is a public water well located between lots 1, 2 and 26. The well serves the entire San Remo subdivision, a 55-lot residential development having a total sewage flow much greater than 2,000 gallons per day (gpd) (although the sewage flow from homes built on lots 1, 2 and 26 can be expected to total no more than approximately 1350 gpd.) There is no way for the Petitioner to construct an on-site sewage treatment disposal system (OSTDS) on each of the three lots so that no part of any OSTDS will be closer than 200 feet from the San Remo well, measured horizontally across the ground surface to the well head. Measuring horizontally across the ground surface to the well head: an OSTDS on lot 1 could be placed no farther than 156 feet from the well; an OSTDS on lot 2 could be placed no farther than 184 feet from the well; according to drawings in the Petitioners' application, an OSTDS on lot 26 could be placed no farther than approximately 185 feet from the well. (Although lot 26 is larger than the others, it is contiguous to a surface water body, and the required setback from the surface water body decreases the area available for siting an OSTDS on the lot. The evidence was not clear exactly how far an OSTDS on lot 26 would be from the San Remo well.) HRS concedes: (1) that requiring 200-foot setbacks from the San Remo well will place the Petitioner under a hardship that was not caused intentionally by his own actions; and (2) that no reasonable alternative exists for the treatment of sewage on his lots 1, 2 and 26. (It is not clear how or why HRS determined that utilization of a joint OSTDS to serve all three lots through the imposition of cross-easements on the lots would not be a reasonable alternative to at least one or two of the variance applications.) The San Remo well, which is 400 feet deep, has a steel casing from the surface of the well to 100 feet below the ground surface. The steel casing prevents the entry of ground water into the well above the bottom of the casing. If the distances between the proposed OSTDS's and the San Remo well were measured diagonally, through the ground, from the proposed OSTDS's to the bottom of the steel casing of the well: the proposed OSTDS on lot 1 would be 185 feet from the well; the proposed OSTDS on lot 2 would be 209 feet from the well; and the proposed OSTDS on lot 26 would be even farther from the well. (The evidence was not clear exactly how much farther.) In fact, due to the draw-down effect of the well, the path groundwater would travel from the proposed OSTDS's to the bottom of the steel casing of the San Remo well would curve upward somewhat from, and be somewhat longer than, the diagonal line running directly between those two points. (The evidence is not clear exactly how much longer the curved path would be.) If the distances between the proposed OSTDS's and the San Remo well were measured first horizontally across the ground surface to the well head and then vertically down to the bottom of the steel casing of the well: the proposed OSTDS on lot 1 would be 253 feet from the well; the proposed OSTDS on lot 2 would be 281 feet from the well; and the proposed OSTDS on lot 26 would be even farther from the well. (Since the bottom of the OSTDS's will be three feet below the ground surface, the vertical component of the measurement is only 97 feet instead of the full 100 feet between the well head and the bottom of the casing.) When applying the HRS rules on distances required between OSTDS's and existing public water wells, HRS measures from the OSTDS horizontally across the ground surface to the well. The evidence was that HRS's method of measurement is consistent both with the methods used by the federal EPA and with the scientific data on which the technical advisory board based the distances in the HRS rules. The Petitioner's expert witness testified that there is a 17-foot thick layer of sand and clay between 53 and 70 feet below the ground surface in the vicinity of the San Remo well and that the sand and clay layer would prevent contamination from the OSTDS's from reaching the bottom of the steel casing of the well. (He also testified that is a white lime rock layer between 70 and 90 feet below the ground surface and inferred that the white lime rock layer would add some degree of protection.) The opinions of the Petitioner's expert are accepted. Petitioner's expert is a civil, sanitary and environmental engineer, not a geologist or hydrogeologist; however, his experience is in the area of wastewater treatment and disposal is extensive. Meanwhile, HRS presented no competent evidence whatsoever to contradict the Petitioner's expert. The Petitioner proposes to use Norweco Singulair Bio-Kinetic Waste Water Treatment Systems. These systems treat waste better than a standard septic tank system. Instead of the single septic tank, they have three distinct chambers: first, a retreatment chamber; second, an aeration chamber to reduce biological oxygen demand (BOD) and total dissolved solids (TDS); and, finally, a clarification or filter chamber that further reduces BOD and TDS. With the proposed systems, BOD and TDS will be reduced to approximately a fourth of the BOD and TDS levels that would enter the drainfield from a septic tank system. In addition, unlike in a septic tank system, the proposed systems utilize chlorine tablets in conjunction with the clarification chamber to kill bacteria and viruses. It is found that the evidence presented in this case, taken as a whole (and in particular in the absence of any competent evidence to contradict the credible opinions of the Petitioner's expert) was sufficient to prove that the proposed OSTDS's would not adversely affect the health of members of the public. Except for a fleeting reference in its Proposed Recommended Order, HRS has not taken the position that the Petitioner's proposed OSTDS's will significantly degrade the groundwater or surface waters. The reference in the Proposed Recommended Order would seem to reflect that HRS's concern about the impact of the Petitioner's proposed OSTDS's on groundwater quality is limited to its public health concerns.

Recommendation Based on the foregoing Findings of Fact and Conclusions of Law, it is recommended that the Department of Health and Rehabilitative Services (HRS) enter a final order granting the Petitioner's applications for variances, on the condition that the Petitioner utilizes the proposed Norweco Singulair Bio- Kinetic Waste Water Treatment Systems. RECOMMENDED this 30th day of June, 1995, in Tallahassee, Florida. J. LAWRENCE JOHNSTON 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 30th day of June, 1995. APPENDIX TO RECOMMENDED ORDER, CASE NO. 94-6483 To comply with the requirements of Section 120.59(2), Fla. Stat. (1993), the following rulings are made on the parties' proposed findings of fact: Petitioner's Proposed Findings of Fact. Accepted but conclusion of law, subordinate and unnecessary. Accepted and incorporated. 3.-6. Accepted but subordinate and unnecessary. Accepted and incorporated. Rejected as to "significantly degrade the groundwater or surface waters"; HRS did not make this an issue, except with respect to public health concerns. Otherwise, accepted and incorporated. Rejected as not proven and contrary to the greater weight of the evidence. However, accepted that HRS presented no evidence sufficient to support a finding on the issue. See Section 120.58(1)(a), Fla. Stat. (Supp. 1994). Accepted but subordinate and unnecessary. Rejected as to "relevant criteria"; not proven and as contrary to the greater weight of the evidence. Otherwise, accepted and incorporated. Accepted and incorporated. Respondent's Proposed Findings of Fact. Accepted but conclusion of law, subordinate and unnecessary. Accepted and incorporated. 3.-7. Accepted but subordinate and unnecessary. Accepted and incorporated. Rejected as contrary to facts found and as contrary to the greater weight of the evidence. (As found, HRS did not contend that the Petitioner's OSTDS's would "significantly degrade the groundwater or surface waters." HRS only raised this issue with respect to public health concerns.) 10.-12. Accepted but subordinate and unnecessary. (These were hearsay statements that were not sufficient to support findings as to the matters asserted. See Section 120.58(1)(a), Fla. Stat. (Supp. 1994).) COPIES FURNISHED: Raymond R. Deckert, Esquire Department of Health and Rehabilitative Services 4000 W. Dr. Martin Luther King, Jr., Boulevard Tampa, Florida 33614 Nelson D. Blank, Esquire Trenam, Kemker, Scharf, Barkin Frye, O'Neill & Mullis, P.A. 2700 Barnett Plaza 101 E. Kennedy Boulevard Tampa, Florida 33601-1102 Robert L. Powell Agency Clerk Department of Health and Rehabilitative Services 1323 Winewood Boulevard Tallahassee, Florida 32399-0700 Kim Tucker, Esquire General Counsel Department of Health and Rehabilitative Services 1323 Winewood Boulevard Tallahassee, Florida 32399-0700

Florida Laws (1) 381.0065
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CITY OF CLEARWATER AND ANTONIOS MARKOPOULOS vs WILLIAM T. MOONEY, 93-006618 (1993)
Division of Administrative Hearings, Florida Filed:Clearwater, Florida Nov. 17, 1993 Number: 93-006618 Latest Update: May 24, 1994

The Issue The issue for consideration in this case is whether Respondent should be disciplined, to include a three day suspension without pay, because of the misconduct alleged in the Notification of Suspension issued herein.

Findings Of Fact At all times pertinent to the issues herein, Respondent, William T. Mooney, worked as a laboratory technician for the City of Clearwater's Public Works/Water Pollution Control Division. On April 15, 1993, Doreen Spano, the City's utility lab supervisor, held a meeting of her division personnel at which she identified Iracema Drysdale as the lead worker and, in order to clarify any misconceptions among lab workers as to work deadlines, presented a policy letter for the lab, entitled "New Work Schedule". The schedule set guidelines and deadlines for the daily workload. The memorandum contains inconsistent statements, however. For example, while Ms. Spano indicated both in the memo and at hearing that the instructions therein are merely guidelines, she also used such imperatives as "must" and "will" in the memo. Specifically, the memorandum indicates the daily plant BOD must be in the incubator by 12:00 PM, and the daily plant bacteria must be in the incubator by 12:30 PM. Respondent has worked in this City laboratory for approximately 14 years. During this time he has developed a method of accomplishing his tasks which is described by Ms. Drysdale as less than efficient. She indicates he frequently misses his time deadlines and works at his own pace. Respondent, on the other hand, claims he has always completed his tasks according to the Standard Methods Manual, but, due to the time the samples are received in the lab, could not accomplish both the BOD and the bacteria procedures within the guidelines set in that manual and the Environmental Protection Agency standards manual. Either one or both would be late. This controversy, much of which was made by both sides, is, in reality, only peripherally related to the issue in controversy here which is whether Respondent was insubordinate or not on September 9, 1993. Both Ms. Drysdale and the Respondent signed the memorandum in question here indicating their receipt and understanding of the directions contained therein. Thereafter, on September 9, 1993, Ms. Drysdale entered the lab shortly before the lunch period to find the bacteria procedure not done and Respondent working on the BOD procedure. It appears that the bacteria sample was taken at 6:00 AM on this day and, under EPA guidelines, had to be preserved in the incubator within six hours or the results of the procedure would be invalid and not eligible for reporting to the EPA. When Ms. Drysdale asked Respondent why he was doing the BOD when the bacteria procedure had not been accomplished, he indicated that Ms. Spano's memorandum required the BOD to be done by 12:00 noon and the bacteria not until 12:30 PM. He considered this a directive and indicated he would complete his work consistent therewith. Again, there is a contradiction in the testimony as to the nature of the conversation between Ms. Drysdale and the Respondent. Ms. Drysdale asserts that about noon on the day in question, she suggested to Respondent that he start the bacteria procedure first and then do the BOD procedure. Respondent refused because he believed he had to follow the new work schedule prepared by Ms. Spano. Ms. Drysdale then told him to do the bacteria procedure first and she would assume the responsibility. Respondent still refused and, raising his voice to her, completed the BOD procedure. When he finished that, he did the bacteria procedure but by that time, the sample was too old and had to be discarded. Respondent's recounting of the incident is somewhat different. He claims he was approached by Ms. Drysdale who asked him why he did the bacteria procedure after the BOD procedure. When he pointed out the dictates of the memorandum, she claimed to know nothing about it even though her signature, along with that of Respondent and Mr. Olson, appears on the bottom thereof. Nonetheless, according to Respondent, Ms. Drysdale said she would check on it. After lunch, according to Respondent, Ms. Drysdale came back with the Standard Methods book. When he showed her the new work rules, he claims, she admitted she was aware that Ms. Spano had written them. When he asked her what Ms. Spano had said about the situation, she allegedly replied, "Why don't you do it the way I say and if Doreen (Ms. Spano) asks, I'll take the responsibility." Respondent was upset because, he contends, things like this always happen. Respondent, in subsequent testimony, denied ever getting a direct order from Ms. Drysdale or that she indicated she would assume responsibility. On balance, while there is little doubt in Ms. Drysdale's testimony as to what happened, Respondent tells two different stories regarding the conversation. At one point he claims she asked him why he didn't do it her way and that if he did, she'd assume responsibility. At another, he claims she merely asked why he was doing the procedures as he was and made no mention of assuming responsibility. It is clear that Ms. Drysdale wanted the bacteria procedure done first, and while she might not have couched her request in directory language, there can be little doubt she communicated her desires to Respondent, albeit in a perhaps more gentle manner. In any case, she was Respondent's supervisor and he knew it. She wanted the work done as she indicated and her request, made under the authority she had to get the work done as she desired, had the force and effect of a direct order which Respondent disobeyed at his peril. Ms. Spano indicated she discussed not only the appointment of Ms. Drysdale as lead worker at the April 15, 1993 meeting, but also the six hour requirement for specimens. Respondent denies this, but it is found he knew exactly what the requirements were. He claims he has been doing things the way the memorandum calls for ever since it was promulgated and this is not inconsistent with his current position on doing the BOD procedure first. When this incident took place, Mr. Reckenwald, the superintendent of the water and pollution control division, and the overall supervisor of the laboratory operation in question, received a recommendation for discipline, primarily because of Respondent's failure to follow orders. In addition, however, the incident created a problem for the City which has to report to the EPA and other federal agencies. Because of this report requirement, it is imperative the work be done properly. If it is not done properly, the work is worthless and may result in sanction action against the city by federal regulatory agencies. Not the least of concerns, also, is the public health consideration since effluent, the source of samples for both BOD and bacteria procedures, is discharged into the public waterways. On the basis of the above, a recommendations was made that Respondent receive a three day suspension. This is consistent with disciplinary guidelines contained in the City's Guidelines For Disciplinary Action. Respondent appealed the action to the City Manager who reviewed his submittal but nonetheless upheld the disciplinary action proposed.

Recommendation Based on the foregoing Findings of Fact and Conclusions of Law, it is, therefore: RECOMMENDED that the City of Clearwater take final action in this matter to consist of suspension of the Respondent without pay for three days and imposition of 40 disciplinary action points. RECOMMENDED this 24th day of May, 1994, in Tallahassee, Florida. ARNOLD H. POLLOCK, Hearing Officer Division of Administrative Hearings The DeSoto Building 1230 Apalachee Parkway Tallahassee, Florida 32399-1550 (904) 488-9675 Filed with the Clerk of the Division of Administrative Hearings this 24th day of May, 1994. COPIES FURNISHED: Miles A. Lance, Esquire Assistant City Attorney City of Clearwater P.O. Box 4748 Clearwater, Florida 34618 William T. Mooney 1433 Laura Street Clearwater, Florida 34615 Michael J. Wright City Manager City of Clearwater P.O. Box 4748 Clearwater, Florida 34618-4748

Florida Laws (1) 120.57
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L. C. PREVATT, D/B/A RIVERVIEW SPEED WASH, INC. vs. DEPARTMENT OF ENVIRONMENTAL REGULATION, 82-000356 (1982)
Division of Administrative Hearings, Florida Number: 82-000356 Latest Update: Oct. 07, 1982

Findings Of Fact Upon consideration of the oral and documentary evidence adduced at the hearing, the following relevant facts are found: Petitioner L. C. Prevatt is the owner and operator of the Riverview Speed Wash, Inc., a coin operated laundry which has been in existence for over ten years. The facility has twelve top load washers, four double load washers, one triple load washer and seven gas dryers. It is open from 7:00 a.m. to 9:00 p.m., seven days a week. The facility is located in a shopping center in space which petitioner rents on a month-by-month basis. The facility utilizes a 0.0075 mgd waste treatment plant with effluent disposal to a county-owned drainage ditch which is connected and discharges to the Alafia River approximately 0.6 miles south of the facility. On or about May 29, 1981, petitioner submitted an application for a temporary operation permit for his Riverview laundry facility. Temporary operation permits are issued by the DER when a facility is not currently meeting State water quality standards and the applicant needs or desires a period of time to bring the facility up to the applicable standards. Here, the petitioner stated on his application that no upgrade of the waste treatment facility was planned. The application further stated that the facility would be connected to an area wide regional waste treatment system when that system became available. After numerous requests for further information from the applicant and various inspections of the facility, the DER issued its notice of intent to deny petitioner's application for a temporary operation permit. Reasons for the intended denial included failure to provide requested background water quality information, failure to provide a proposed water quality standards compliance schedule, failure to provide reasonable assurance that a municipal sewer would be available as an alternative means of disposal and improper and deficient operation and maintenance of the facility. Numerous inspections of the petitioner's facility by personnel from the DER and the Hillsborough County Environmental Protection Commission revealed that the facility was not functional in terms of operating correctly and that the design of the plant was inadequate to meet State water quality standards. Specifically, these inspections revealed that the chlorination equipment was not operational, that the trickling filter was not operational, that the removal rates for BOD and suspended solids were consistently and significantly less than the State standard of 90 percent, that the discharge and effluent were of a milky color and would not meet the State standards for turbidity and color, that the water quality of the drainage ditch was extremely low and that the water quality results were actually worse after going through the existing system. It was determined that the discharge was degrading the quality of the receiving waters and that, even if the petitioner's operational and maintenance problems were solved, the design of the facility is not adequate to assure future compliance with State standards. Petitioner admits that his facility does not currently meet State water quality standards. In mitigation, it is contended that many other laundries in the area also do not meet State standards, that it is not economically feasible to redesign the facility to attain compliance, that he has no land available upon which to discharge effluent and that he would be willing to install a sand filter and did have the permission of the manager (not the owner) of the property to discharge effluent into the parking lot drain ponds. No written evidence of this agreement was adduced and there was no demonstration that such runoff ponds would be able to hold and/or treat effluent from the petitioner's facility. There was also no evidence offered to demonstrate that a municipal or regional sewer system would be available in the near future to serve the laundry facility.

Recommendation Based upon the findings of fact and conclusions of law recited above, it is RECOMMENDED that petitioner's application for a temporary operation permit for Riverview Speed Wash, Inc. be DENIED. Respectfully submitted and entered this 7th day of September, 1982, in Tallahassee, Florida. DIANE D. TREMOR, Hearing Officer Division of Administrative Hearings The Oakland Building 2009 Apalachee Parkway Tallahassee, Florida 32301 (904) 488-9675 Filed with the Clerk of the Division of Administrative Hearings this 7th day of September, 1982. COPIES FURNISHED: L. C. Prevatt Post Office Box 998 Gibsonton, Florida 33534 William W. Deane, Esquire Assistant General Counsel Department of Environmental Regulation Twin Towers Office Building 2600 Blair Stone Road Tallahassee, Florida 32301 Victoria Tschinkel, Secretary Department of Environmental Regulation Twin Towers Office Building 2600 Blair Stone Road Tallahassee, Florida 32301

Florida Laws (1) 403.088
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