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.
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 is whether Respondent should be required to obtain a current operating permit for his aerobic treatment unit and have a $500.00 fine imposed for violating an agency rule for the reason cited in the Citation for Violation issued by Petitioner on December 1, 1999.
Findings Of Fact Based upon all of the evidence, the following findings of fact are determined: In this dispute, Petitioner, Department of Health (Department), has alleged that Respondent, Dr. Anthony Massaro, a retired public health physician, failed to obtain an annual operating permit for an aerobic treatment unit (ATU) located at his residence at 3402 North Oceanside Boulevard, Flagler Beach, Florida. The Flagler County Health Department (Health Department) is charged with the responsibility of issuing such permits. That department is under the direction and control of Petitioner. While Respondent readily admits that he failed to obtain a permit, he contends that he was misled by the Health Department when he first installed an ATU at his residence; the Health Department is not enforcing the law regarding ATUs and thus another system would be more appropriate; and the law, as he interprets it, allows him to install another type of on-site sewage disposal unit on his property. Respondent purchased his property in Flagler County in 1997. The property is located in Ocean View Estates Subdivision (subdivision), which has an Urban Single-Family Residential District (R-1b) zoning classification under the Flagler County Land Development Code (Code). Section 3.03.05A of the Code requires that owners within the R-1b classification use "public or community water and sewer facilities," but makes an exception for "[s]mall R-1b subdivisions, fifty (50) lots or less, utilizing a public community water system," in which case residents "may utilize Class I aerobic onsite sewage disposal systems." Further, "[t]he use of individual onsite sewage disposal systems must be consistent with adopted county policies and standards." Because the subdivision has 50 lots or less, and public or private sewer facilities were not available in the area, the subdivision's Plat Agreement recorded in 1995 provided that "[i]ndividual aerobic onsite sewage disposal systems are to be permitted and constructed as each lot is developed." Another type of onsite sewage disposal system is the anerobic system, which has a septic tank and larger drainfield, is far less expensive, but does not conform with "county policies and standards" in this locale. Thus, this type of system requires a variance from the zoning regulations before one can be installed in the subdivision. Even so, Respondent says "all" of his neighbors have installed such a system. Because of the Plat Agreement, the zoning restriction, the difficulty in obtaining a variance, and the lack of a sewer line, Respondent had no choice except to use an ATU system for his residence. This meant that he had to apply for a permit from the Health Department. Once a permit is obtained and an ATU installed, the owner must renew his operating permit annually at a cost of $150.00, and he must enter into a maintenance agreement with a licensed contractor. The $150.00 fee is used to defray the costs incurred by the Health Department in making quarterly inspections and performing annual sampling and laboratory analysis of effluent. The record does not reflect precisely when a sewer line became operational across the street from Respondent's property, but the sewer project was accepted "for service" in April 1998, or before Respondent's ATU was installed in August 1998. Had Respondent known this, he would have obviously chosen that option rather than an ATU. The evidence reflects that in November 1997 Respondent made application for an ATU with the Health Department, a permit was issued in December 1997, and the system was installed and approved in August and September 1998, respectively. In early April 1998, the Health Department was advised by the private utility company that it would accept new sewer connections in a service area that included Respondent's home. However, Health Department representatives made no mention of this to Respondent since they were under the impression that he desired to use the ATU option, they do not normally "counsel" applicants on onsite sewage disposal system options, and Respondent had made no inquiry. Disclosure of this fact would have saved Respondent considerable money (and grief) in the long run; unfortunately, however, while good public relations would dictate otherwise, the Health Department had no legal obligation to do anything other than process the pending application. Likewise, it has no obligation in law to now pay the costs for Respondent to hook up to the line because of its non-disclosure. Respondent has now invested more than $5,000.00 in his ATU. This type of system is operated by a compressor in Respondent's garage, which must be run 24 hours per day, and is very noisy. Because of this, Respondent understandably wishes to change to an anerobic system, which has a traditional septic tank, larger drainfield, no unsightly "mound" in the yard, no annual permits, and is far cheaper than an ATU. Also, it does not require a noisy motor to sustain operations. However, this type of system is prohibited by the Code except where a variance from Flagler County (County) has been obtained. It appears to be unlikely that Respondent can obtain a variance from the County. Because Respondent's property is so low in relation to the sewer line, to achieve the proper gravity, he must install a lift station and pay a connection fee, both totaling $3,540.00, before hooking up to the sewer system. Given these costs, and the considerable investment he already has in an ATU, Respondent does not consider this to be a viable alternative. Respondent pointed out that, despite the requirement that they do so, many ATU owners in the County are not running their systems 24-hours per day because of the noise from the compressor. He also pointed out that the Health Department has consistently found numerous violations of such systems during its inspections. He further asserted that while the $150.00 annual fee is to defray certain sampling and laboratory analysis costs associated with inspecting ATUs, the Health Department has done neither on his ATU. Finally, Respondent pointed out that prior to 1999 the regulations were enforced by sampling the compliance of a very small percentage of total ATU systems (ten percent), rather than all systems, in the County. Given these considerations, Respondent concludes that ATUs are the least effective way to treat sewage, and that existing laws and regulations have not been enforced. Assuming these allegations to be true, and they were not seriously disputed, they are legitimate concerns. However, until the law is changed, they do not constitute a lawful basis for allowing Respondent to switch to an anerobic system. Respondent further contended that under his interpretation of the general law, which was not fully understood by the undersigned, he is not required to use an ATU. But local zoning regulations clearly require that he do so, and until the state or local regulations are changed or waived, he cannot use an anerobic system. Finally, Respondent has cooperated with the Department throughout this process. With his lengthy public health background, Respondent initiated this action with good intentions, seeking to point out the flaws in the ATU systems, and to remedy a problem which none of his neighbors apparently have. Given these considerations, a civil penalty should not be imposed.
Recommendation Based on the foregoing Findings of Fact and Conclusions of Law, it is RECOMMENDED that the Department of Health enter a final order sustaining the charge in the Citation for Violation and requiring that Respondent obtain an annual permit for his ATU. A civil penalty is not warranted. DONE AND ENTERED this 20th day of June, 2000, in Tallahassee, Leon County, Florida. DONALD R. ALEXANDER 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 the Clerk of the Division of Administrative Hearings this 20th day of June, 2000. COPIES FURNISHED: Angela T. Hall, Agency Clerk Department of Health Bin A02 2020 Capital Circle, Southeast Tallahassee, Florida 32399-1703 Charlene J. Petersen, Esquire Department of Health 420 Fentress Boulevard Daytona Beach, Florida 32114 Dr. Anthony Massaro 3402 North Oceanside Boulevard Flagler Beach, Florida 32136 Amy M. Jones, General Counsel Department of Health Bin A02 2020 Capital Circle, Southeast Tallahassee, Florida 32399-1701
The Issue The issue is whether Palm Beach County's application for a permit to construct a domestic wastewater collection/transmission system in Palm Beach County should be approved.
Findings Of Fact Based upon all of the evidence, the following findings of fact are determined: Parties The County is a political subdivision of the State of Florida and is the permittee in this matter. The County Water Utilities Department currently serves approximately 425,000 persons, making it the largest utility provider in Palm Beach County and the third largest in the State of Florida. ITID is an independent water control special district created by special act of the legislature in 1957 and whose boundaries lie within the County. Portions of the transmission line to be constructed by the County will cross easements and roads, and pass under canals, owned by ITID. Petitioners Joseph Acqualotta, Michael D'Ordine, Ann Hawkins, and Lisa Lander all live in areas in close proximity to the proposed transmission line. Lander lives adjacent to the proposed route of the line along 40th Street North, while Acqualotta, D'Ordine, and Hawkins live adjacent to the proposed route along 140th Avenue North. Acqualotta, Hawkins (but not D'Ordine, who resides with Hawkins), and Lander own the property where they reside. Petitioners Troy and Tracey Lee (Case No. 05-2979), Lisa Gabler (Case No. 05- 2980), and Anthony and Veronica Daly (Case No. 05-2982) did not appear at the final hearing. The Department is an agency of the State of Florida authorized to administer the provisions of Part I of Chapter 403, Florida Statutes, and is the state agency charged with the responsibility of issuing domestic wastewater collection/ transmission permits under Section 403.087, Florida Statutes (2004).1 Background On December 15, 2004, the County filed its application with the Department for an individual permit to construct a domestic wastewater collection/transmission system (Transmission Line). The Transmission Line is one element of the County's Northern Region Utilities Improvement Project (Project) and will be approximately 41,050 feet long and comprised of approximately 32,350 linear feet of 20-inch force main and 18,700 linear feet of 30-inch force main (or nearly ten miles in length). A primary purpose of the Project is to provide water and wastewater service to the Village, a 1,900 acre parcel located in the unincorporated part of the County several miles west of the Florida Turnpike, south of State Road 710, and north of the Villages of Wellington and Royal Palm Beach. The Village will be the home of the Scripps Project and Campus. The Transmission Line will run from the southeastern corner of the Village south to Northlake Boulevard, then east to 140th Avenue North, then south along that roadway to 40th Street North, where it turns east until it interconnects with existing facilities. The wastewater will be collected in a regional pump station on the Scripps Project site, where it will be pumped through the Transmission Line to the East Central Plant, which will be the primary treatment facility. The East Central Plant is owned and operated by the City of West Palm Beach (City), but the County owns between forty and forty-five percent of the treatment capacity. Because the wastewater system is interconnected, the wastewater could also be treated at the County's Southern Regional Plant. Ultimately, the flow from the Scripps Project will be one or two million gallons per day. The Transmission Line is the only way that wastewater can be handled at the Scripps Project. A preliminary analysis by the Department and the South Florida Water Management District determined that on-site treatment was not feasible because of the environmentally sensitive nature of the area. The Scripps Project will include residential units, commercial entities, and institutional uses, such as medical clinics. Besides serving these customers, the Transmission Line will also serve other customers in the area. The County has already signed agreements with the Beeline Community Development District (which lies a few miles northwest of the Village) and the Village of Royal Palm Beach (which lies several miles south-southeast of the Village). At the time of the hearing, the County anticipated that it would also sign an agreement with Seacoast Utility Authority (whose service area is located just southeast of the Village) to transport wastewater through the Transmission Line. All of the treatment facilities have sufficient existing capacity to treat the estimated amount of domestic wastewater that will be generated by the Scripps Project and the other users that will discharge to the Line. The County commenced construction of the Transmission Line in May 2005 when the Department issued the Permit. On August 2, 2005, the County published the Department's Notice to issue the Permit, and once the Petitions were filed, the County stopped construction pending the outcome of this hearing. Approximately seventy percent of the Transmission Line is now completed. The Permit does not allow the Transmission Line to be used until it is pressure tested and certified complete. Upon completion, the County must receive an Approval to Place a Domestic Wastewater Collection/Transmission System into Operation from the Department. Such approval is given only after the County has given reasonable assurance that adequate transmission, treatment, and disposal is available in accordance with Department standards. See Fla. Admin. Code R. 62-604.700. On August 15, 2005, Petitions challenging the issuance of the Permit were filed by ITID and the individual Petitioners. ITID contends that the Transmission Line will convey not only domestic wastewater, but also industrial waste; that the County did not comply with all applicable technical standards and criteria required under the Department's rules; that the Project will be located on ITID's right-of-way, on which the County has no right to occupy; that the Project will be located within seventy-five feet from private drinking wells and does not provide an equivalent level of reliability and public health protection; and that the pipe material and pressure design is inappropriate for the Transmission Line's requirements. The individual Petitioners (who filed identical Petitions) are mainly concerned about the location of the Transmission Line in relation to their private drinking wells and property, the possibility of the pipe bursting or leaking once it becomes operational, and the restoration of their property to its original condition after construction is completed. As to the property claims by all Petitioners, the County plans to place the Transmission Line in property that it either owns or has an easement, in property that it is in the process of condemning, or in a public right of way. While the County acknowledges that it has already placed, and intends to place other portions of, the Transmission Line in easements that ITID says it has the exclusive right to use and for which a permit from ITID is required, the County alleges that it also has the right to use those easements without an ITID permit. The dispute between the County and ITID is the subject of a circuit court proceeding in Palm Beach County, and neither the Department nor DOAH has the authority to decide property interests. Petitioners' Objections Domestic wastewater and pretreatment The wastewater that will be generated by the Scripps Project is considered domestic wastewater; it will not include industrial wastewater. Waste that is industrial or non- domestic must be pretreated to protect the wastewater plant, collection system, and the health of system workers and the general public. The Department administers a pretreatment program through which it requires a public wastewater utility to police the entities that discharge to their wastewater plants. A central part of the pretreatment program is the local ordinance that gives legal authority to the utility to permit, inspect, and take enforcement action against industrial users who are part of the pretreatment program. The utility files an annual report with an industrial user survey, and the Department periodically inspects and audits local pretreatment programs to ensure they are being operated as intended. The system is not failsafe but is designed to ensure that potentially harmful wastes are rendered harmless before discharge. For example, the utility has the authority to immediately shut water off if a harmful discharge is occurring. Both the County and the City have pretreatment programs approved by the Department. The City has an ordinance that allows it to enforce the pretreatment standards for all entities that discharge to its wastewater system. The County Water Utilities Department has a written pretreatment manual, and the County has zoning restrictions on the discharge of harmful material to the wastewater system. It has also entered into an interlocal agreement under which it agrees to enforce the City ordinance. The County provides wastewater treatment to industrial, educational, and medical facilities, and it has never experienced a discharge from any of these facilities that has caused adverse health or environmental impacts. The County pretreatment program for the Southern Regional Facility was approved in 1997. The City pretreatment program for the East Central Regional Facility was approved in 1980. The Scripps Project must apply for a permit from the County and provide a baseline monitoring report, data on its flow, and information on the flow frequency and raw materials. Medical waste from the Scripps Project will be pretreated to render it safe before it is discharged into the Transmission Line. Transmission Line Design The Transmission Line was designed in accordance with the technical standards and criteria for wastewater transmission lines in Florida Administrative Code Rule 62- 604.300(5). That rule incorporates by reference a set of standards commonly known as the Ten State Standards, which contain several of the standards used in the design of this project. These standards are recommended, but are not mandatory, and a professional engineer should exercise his or her professional judgment in applying them in any particular case. The Transmission Line also meets the design standards promulgated by the America Water Works Association (AWWA). Specifically, the County used the AWWA C-905 design standard for sizing the polyvinyl chloride, or PVC, pipe used in the project. The County has received written certification from the manufacturer that the PVC pipe meets the standards in AWWA C-905. The Transmission Line is designed with stub-outs, which will allow for future connections without an interruption of service, and inline isolation valves, which allow the line to be shut down for maintenance. The Use of PVC Pipe There is no standard regulating the selection of PVC pipe material in the Department's rules. Instead, the Department relies on the certification of the applicant and the engineer's seal that the force main will be constructed to accepted engineering standards. The only specification applicable to the Transmission Line is the Ten State Standard, adopted and incorporated by reference in Florida Administrative Code Rule 62-604.300(5)(g). That document contains a general requirement that the material selected have a pressure rating sufficient to handle anticipated pressures in wastewater transmission lines. The Transmission Line will be constructed with PVC piping with a thickness of Dimension Ratio (DR) 32.5, which is the ratio of the outside diameter of the pipe to its thickness. Higher ratios mean thinner-walled pipes. This is not the first time the County has used 32.5 PVC piping for one of its projects, and other local governments in the State have used 32.5 or thinner pipe. The County is typically conservative in requiring thicker-walled pipe, because most transmission lines are built by developers, and the County is unable to design the entire line or control or inspect its installation. The specifications for wastewater transmission lines built in the County call for the use of DR 25 pipe. On this project, however, the County determined that thicker- walled pipe would have been an over-design of the system because the County controls the pump stations and oversees the installation; therefore, the Director of the Water Utilities Department has waived that requirement. The County considers the use of DR 32.5 PVC to be conservative. Although this pipe will be thinner than what is typically used in the County, it satisfies the Department's requirements. The Department has permitted many miles of similar PVC force mains in South Florida, and none have failed. PVC has benefits over other transmission line material, such as ductile iron. For example, PVC is more corrosion resistant. Wastewater generates hydrogen sulfide as it decomposes, which can form highly corrosive sulfuric acid. Some of the older transmission lines in the County that were made of ductile iron have corroded. PVC also has a superior ability to absorb surges, such as cyclical surges, than ductile iron. It is easier to install, and its interior flow characteristics are smoother than ductile iron or pre-stressed concrete pipe. Mr. Farabee, a professional engineer who testified on behalf of ITID, recommended a DR 14 pipe, which is thicker- walled than the DR 32.5 pipe used by the County. While he opined that the DR 32.5 pipe was too thin for the project, he could not definitively state that it would not pass the 150 per square inch (psi) pressure test. He also opined that the pipe is undersized because it will be unable to withstand the surge pressures during cleaning. The witness further testified that the pipe would be subject to much higher pressures than 150 psi, and therefore it was impossible to know whether the pipe would fail. In his opinion, this means the Department did not have reasonable assurance for the project. The County consulted with the Unibell PVC Pipe Association (Unibell) in the planning of this project. Unibell is a trade association that provides technical support for PVC pipe manufacturers. Robert Walker, a registered professional engineer and Unibell's executive director who testified on behalf of the County, disagreed with Mr. Farabee's conclusions concerning the adequacy of the PVC pipe in this project. The AWWA C-905 standard uses a safety factor of two, which means the pipes are tested at pressures that are at least twice their stated design strength. Mr. Walker explained the different standards that apply to PVC pipe. DR 32.5 pipe, which is used in this project, has a minimum interior pressure rating of 125 pounds per square psi. Each pipe section is tested before it is shipped at 250 psi, and the minimum burst pressure for the material is in excess of 400 psi. The pipe also meets a 1000- hour test at 270 psi. In light of these standards and testing, the pipe will pass the two-hour 150 psi test required by the Department. Mr. Farabee expressed some concern that the PVC pipe would be more prone to breakage than ductile iron or thicker PVC. However, the PVC pipe standards provide that the pipe can be flattened at sixty percent without splitting, cracking, or breaking. At shallow depths on dirt roads, ovalation, which occurs when PVC is flattened through pressure, will initially occur, but over time the soil around the pipe will become compacted and result in re-rounding of the pipe. The joints are three times stiffer than the body of the pipe, which will protect the joint from excessive ovalation and leaking, and the use of mechanical restrained joints will further strengthen the joints. There has been no joint leakage in Florida due to deflection of the joints. Finally, there have been no failures of PVC pipe caused by three-feet of fill, which is the depth to which the Transmission Line pipe will be buried. To further protect the pipe, the County optimized its pumping system to avoid cyclical surges by using variable frequency drive pumps that gradually increase and decrease speed rather than just turning on or off. In addition, the pump stations are fed by two power lines that come from different directions and emergency generators, which should lessen the chances of harmful surging. Testing the Installation The anticipated pressures in the Transmission Line will likely be about 50 psi. After installation, the Line will be pressure tested at 150 psi for two hours, which is sufficient to provide the Department with reasonable assurance that the Line will hold pressure and will not leak. Also, the County contract inspectors are on the construction site daily. If problems with the installation arise later, the County has committed to promptly fix the problem, even if it means digging up the line. During the hearing, ITID asserted that the Uniform Policies and Procedure Manual standards, which the County has adopted for use by developers when constructing wastewater transmission lines, should be applied to the County as well. This standard, which requires pressure testing to 200 psi for PVC pipes larger than 24 inches, has not been adopted by the Department and is not an applicable Department permitting standard. Even if it did apply, the Transmission Line would meet this criterion because it is designed to withstand 270 psi for at least 1,000 hours. Mr. Farabee believed that the entire Transmission Line would be pressure tested after the construction was complete, which would require digging up sections of the pipe to install bulkheads. However, this assessment of the County's testing program is incorrect. Leisha Pica, Deputy Director of the Water Utilities Department, developed the schedule for the project, helped develop the phasing of the work and budget, and oversaw the technical aspects. She stated that the County has successfully tested approximately fifty percent of the line that was already installed at 150 psi for two hours and not a single section of the line failed the test. Compaction The County has stringent backfilling and compaction requirements, which are sufficient to ensure the pipe will be properly installed and that there will be adequate compaction of the fill material. The County plans and specifications provide that compaction must be to ninety-five percent of the American Association of State Highway and Transportation Officials (AASHTO) standards for non-paved surfaces and one hundred percent of AASHTO standards for paved surfaces. Even ITID's expert agreed that the compaction specifications are sufficient. Mr. Farabee contended, however, that even though the standards are stringent, the County cannot properly test the installation for compliance with the standards. Mr. Farabee believed that testing of the backfill would be done after all of the construction was complete. In that case, he did not see how the testing could be done without digging many holes to check for the density of the backfill. These assumptions, however, are incorrect. The evidence shows that a total of two hundred sixty-four compaction tests have already been done on the portion of the Transmission Line that was completed. No part of the installation failed the tests. The County has an inspector who observes the installation and pressure tests. The compaction was tested at every driveway and major roadway, as well as every five hundred feet along the route. While Lander and D'Ordine pointed out at hearing that no compaction tests have been performed on the dirt roads which run adjacent to their property and on which construction has taken place, the Department requires that, before the work is certified as complete, non-paved roads must be compacted in accordance with AASHTO standards in order to assure that there is adequate compaction of the fill material. The Sufficiency of the Application When an application for an individual transmission/ collection line permit is filed with the Department, the applicant certifies that the design of the pipeline complies with the Department's standards. However, not all of the details of the construction will be included in the permit application. The Department relies on the design engineer to certify that the materials used are appropriate. The application form is also signed and sealed by a professional engineer registered in the State of Florida. All plans submitted by the County, including the original, modifications, and final version, were certified by professional engineers registered in the State of Florida. After receiving the application, the Department requested additional information before issuing the permit, and the County provided all requested information. The original construction plans that were submitted with the application were changed in response to the Department's requests for additional information. The Permit issued by the Department indicates the Transmission Line would be constructed with ductile iron pipe, but this was a typographical error. ITID maintains that all of the technical specifications for the project must be included in the application, and because no separate engineering report was prepared by the County with the application, the County did not meet that standard. While the County did not submit an engineering report, it did submit sufficient data to provide reasonable assurance that the project will comply will all applicable rules of the Department. As a part of its application package, the County submitted construction plans, which contain the specifications required by the Department. Also, the general notes included in the construction drawings specify the use of restrained joints where appropriate, the selection of pipe material, the pressure testing of the Transmission Line, and other engineering requirements. In addition, the plans contain numerous other conditions, which are also specifications sufficient to fulfill the Department's requirements. Finally, further explanation and clarification of the technical aspects of the application was given by the County at the final hearing. At the same time, the Department engineer who oversaw the permitting of this project, testified that a detailed engineering report was not necessary. This engineer has extensive experience in permitting transmission lines for the Department and has worked on over five hundred permits for wastewater transmission and collection systems. The undersigned has accepted his testimony that in a relatively straightforward permit such as this, the application and attachments themselves can function as a sufficient engineering evaluation. This is especially true here since the County is seeking only approval of a pipeline project, which would not authorize the receipt of wastewater flow unless other wastewater facilities are permitted. Impacts on Public and Private Drinking Water Wells As part of the design of the Transmission Line, the County located public and private drinking water wells in the area of the line. County personnel walked the route of the Transmission Line and looked for private wells and researched the site plans for all of the properties along the route. No public wells were found within one-hundred feet of the Transmission Line route, but they did find seventeen private wells that are within seventy-five feet of the line. None of the Petitioners have private wells that are within seventy- five feet of the line. While Petitioners D'Ordine and Hawkins initially contended that the well on Hawkins' property was within seventy-five feet of the Transmission Line, at hearing Mr. D'Ordine admitted that he "misread the plans and referred to the wrong property." In order to protect the private drinking water wells, Florida Administrative Code Rule 62-604.400(1)(b) requires that the County provide an extra level of protection for the wells that are within seventy-five feet of the Transmission Line. The County will provide that extra level of protection by installing restrained joints that will restrain the joints between the pipe sections. The restrained joints are epoxy-coated mechanical devices that reduce the tendency for the pipes to separate under pressure. The County has used these restrained joints on its potable water and wastewater lines in other areas of the County and has never experienced problems with the devices. The restrained joints will provide reliable protection of the private wells within seventy-five feet of the Transmission Line. The Department is unaware of any instances where restrained joints have failed in South Florida. If more wells are discovered that are within seventy-five feet of the Transmission Line, then the County will excavate the Line and install restrained joints. Minimum Separation Distances The County has complied with all applicable pipe separation requirements in the installation of the Transmission Line. More specifically, it is not closer than six feet horizontally from any water main and does not intersect or cross any reclaimed water lines. See Fla. Admin. Code R. 62-555.314(1)(a). It will be at least twelve inches below any water main or culvert that it crosses. See Fla. Admin. Code R. 62-555.314(2)(a). Finally, it will be a minimum of twelve inches below any culverts that it crosses. (However, the Department has no separation requirement for culverts crossed by the Transmission Line.) h. The M-Canal Crossing The Transmission Line must cross the M-canal, which runs in an east-west direction approximately midway between 40th Street North and Northlake Boulevard. The original design called for the Transmission Line to cross above the water, but the City and the Department suggested that it be located below the canal to eliminate the chance that the pipe could leak wastewater into the canal. In response to that suggestion, the County redesigned the crossing so that a 24- inch high density polyethylene pipe in a 48-inch casing will be installed fifteen feet below the design bottom of the canal. The polyethylene is fusion-welded, which eliminates joints, and is isolated with a valve on either side of the canal. Appropriate warning signs will be installed. See Fla. Admin. Code R. 62-604.400(2)(k)2.-5. The depth of the subaqueous line and the use of the slip line, or casing, exceeds the Department's minimum standards. See Fla. Admin. Code R. 62-604.400(2)(k)1. i. Flushing Protocol Section 48.1 of the Ten State Standard recommends that wastewater transmission lines maintain a velocity of two feet per second. When the Transmission Line becomes operational, it will not have sufficient flow to flush (or clean) accumulated solids from the lines at the recommended two feet per second velocities. (Sufficient flow will not occur until other customers connect to the Transmission Line during the first one to three years of operation.) Accumulated solids produce gases and odors that could create a problem at the treatment plant and might leak out of the manhole covers. To address this potential problem, Specific Condition 9 of the Permit requires the County to flush the lines periodically. Pursuant to that Condition, the County plans to flush the Transmission Line with additional water which will raise the velocity to three or four feet per second, so that the accumulated solids will be flushed. The water will be supplied by large portable tanks that will be temporarily set up at several locations along the Line. During the purging of the Line, sewage will collect in the pump stations until the purge is finished. There is sufficient capacity in the pump stations to contain the wastewater. In addition, the County will use a cleansing tool known as a pig, which is like a foam bullet that scrapes the sides of the pipe as it is pushed through the line. This protocol will be sufficient to keep the Line clean. ITID asserts that the County's plan for flushing is inadequate, because it does not provide enough water for long enough to flush both the 20-inch and 30-inch lines. Mr. Farabee calculated that the County would need almost twice the proposed volume, or almost six million gallons, to adequately flush the lines. ITID's analysis of the flushing protocol is flawed, however, because it assumes a constant flow in all segments of the pipe, which is not practical. In order to maintain the flushing velocity of three feet per second, the County will introduce water into the Transmission Line at three separate locations, resulting in a more constant flow velocity throughout the Transmission Line. In this way, it can maintain the proper velocity as the lines transition from a 20-inch to 30-inch to 36-inch pipe. The County has flushed other lines in the past using this protocol and has had no problems. This flushing protocol would only be in effect from one to three years. The County estimates that the necessary volumes to maintain a two-feet-per-second velocity in the 20- inch line would be reached in about one year. The 30-inch line should have sufficient flows sometime in 2008. These estimates are based on the signed agreements the County has with other utilities in the area to take their flows into the Transmission Line. Because of these safeguards, the Transmission Line will not accumulate solids that will cause undesirable impacts while flow is less than two feet per second. Other Requirements The construction and operation of the Transmission Line will not result in the release or disposal of sewage or residuals without providing proper treatment. It will not violate the odor prohibition in Florida Administrative Code Rule 62-600.400(2)(a). It will not result in a cross- connection as defined in Florida Administrative Code Rule 62- 550.200. The construction or operation of the Transmission Line will not result in the introduction of stormwater into the Line, and its operation will not result in the acceptance of non-domestic wastewater that has not been properly pretreated. If constructed and permitted, the Transmission Line will be operated so as to provide uninterrupted service and will be maintained so as to function as intended. The record drawings will be available at the Department's district office and to the County operation and maintenance personnel. Finally, concerns by the individual Petitioners that the County may not restore their property to its original condition after construction is completed are beyond the scope of this proceeding. At the hearing, however, the Deputy Director of the Water Utilities Department represented that the County would cooperate with the individual property owners to assure that these concerns are fully addressed. Reasonable Assurance The County has provided the Department with reasonable assurance, based on plans, test results, installation of equipment, and other information that the construction and installation of the Transmission Line will not discharge, emit, or cause pollution in contravention of the Department's standards.
Recommendation Based on the foregoing Findings of Fact and Conclusions of Law, it is RECOMMENDED that the Department of Environmental Protection enter a final order denying all Petitions and issuing Permit No. 0048923-017-DWC. DONE AND ENTERED this 18th day of October, 2005, in Tallahassee, Leon County, Florida. S DONALD R. ALEXANDER 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 the Clerk of the Division of Administrative Hearings this 18th day of October, 2005.
The Issue The issue to be resolved in this proceeding concerns whether the Petitioner violated the provisions of Chapter 381, Florida Statutes, and Chapter 64E-6, Florida Administrative Code, referenced herein, by allegedly illegally connecting a second dwelling to an existing, approved septic system.
Findings Of Fact On January 17, 2002, the Petitioner was given a written Notice of Violation and advised that an illegal sewer connection from a new or second mobile home on her property to her existing sewer system, serving her primary residence would have to be disconnected. It was an illegal second connection on a single, permitted sanitary sewer system. The second home was not occupied and could not be legally occupied until the proper sewer connection and relevant permitting was obtained. On January 30, 2002, the inspector again visited the premises and determined the illegal connection to still exist and the Petitioner was then advised that the illegal connection would have to be disconnected. On February 28, 2002, the inspector returned and found that the illegal connection had been restored to the existing system. He observed a person hurriedly disconnect the system as he approached. The relevant pipe joint had been left un-glued so that it could be readily connected or disconnected. He again notified the Petitioner, in person, that the illegal connection would have to be disconnected. The Respondent cited the Petitioner for the illegally connected sewer system and seeks to impose a $500.00 fine. The Petitioner elected to formally dispute the position of the Respondent agency and pursued a formal hearing to contest the allegations. The Petitioner failed to actually appear at hearing and contest the evidence adduced by the Respondent agency. That evidence is credible and is accepted as unrefuted and supportive of the above Findings of Fact.
Recommendation RECOMMENDED that a final order be entered by the State of Florida Department of Health denying the Petition of Shirley Davis in its entirety and that a final order be entered imposing a $500.00, fine for the violations described in the above Findings of Fact and Conclusions of Law. DONE AND ENTERED this 16th day of September, 2002, in Tallahassee, Leon County, Florida. 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 16th day of September, 2002. COPIES FURNISHED: Shirley Davis 140 West Putnam Grove Road Oak Hill, Florida 32759 John D. Lacko, Esquire Department of Health 420 Fentress Boulevard Daytona Beach, Florida 32114 R. S. Power, Agency Clerk Department of Health 4052 Bald Cypress Way, Bin A02 Tallahassee, Florida 32399-1701 William W. Large, General Counsel Department of Health 4052 Bald Cypress Way, Bin A02 Tallahassee, Florida 32399-1701
The Issue The issues are whether the Consent Order entered into between the Department of Environmental Regulation (DER) and Kenneth Acre (Acre) is an appropriate settlement of the violations addressed therein and whether Acre is entitled to construction permit number IC35-190005 for an Industrial Waste Disposal Facility. The Bradys assert that the Consent Order is not a reasonable exercise of DER's enforcement discretion and that the permit should be denied.
Findings Of Fact Background Acre owns and operates an animal research facility in Eustis, Florida. Acre performs research trials on dogs using a USDA approved heartworm medication sold under the brand name of Heartguard, the chemical name of which is ivermectin. Acre is not in the business of testing or manufacturing new drugs. The Consent Order To handle the waste generated by the animals at the facility, Acre initially constructed a conventional septic tank system. Prior to construction, Acre contacted the Lake County health department to inquire about permitting and was told that he did not need a permit for his facility. With that information, he continued with the project. Subsequently, DER became aware of the facility and notified Acre that a DER industrial waste permit was required and that he should cease the discharge into the septic tank until such a permit was obtained. Acre complied with DER's instructions and plugged the septic tanks. Since the time the septic tanks were plugged, the waste has been collected by Roto Rooter on a periodic basis and disposed of offsite. Acre entered into a Consent Order with DER to resolve the alleged past violation for not obtaining a permit and paid of penalty of $600 as required by DER. The Consent Order is a reasonable and appropriate settlement of the violations alleged therein. The Disposal System Acre has applied for a permit to construct and operate an evapotranspiration disposal system to dispose of the waste from his facility on site. The proposed system is essentially a modified septic tank system using a lined drainfield to capture and hold the liquid waste, allowing it to transpire from the grass or otherwise evaporate into the atmosphere and preventing any discharge to groundwater. The waste will be discharged to a series of modified septic tanks which will provide treatment beyond that of a traditional septic tank system and will reduce the amount of total suspended solids. The first septic tank accepts the waste and provides initial treatment through natural settling of solids. The waste then passes through a filter device and travels by gravity flow to the second septic tank. From the second tank it flows through a second filter device and into a dosing tank. The dosing tank is basically a small holding basin with a pump that disperses the waste to the drainfield in incremental amounts. The dosing tank contains several float mechanisms which monitor the level of liquid in the tank. When the water level in the dosing tank reaches a certain level, one such float mechanism turns on the pump to transport the liquid to the drainfield. The waste is then pumped from the dosing tank through a closed pipe to one of two evapotranspiration cells where it is distributed through a number of perforated pipes. The Evapotranspiration Cells The perforated pipes are situated in a gravel bed approximately 24 inches in depth. On top of the gravel bed is a clay soil mix approximately 15 inches deep. The clay soil mix absorbs the liquid waste in the gravel bed by drawing it up through the process of capillarity. Once the liquid is in the upper clay soil layer, it is evaporated. Grass is planted on top of the soil mix as an additional method for dissipation of the waste. The liquid waste is absorbed by the roots of the grass and transpired through the grass leaves. The clay soil mix in the top layer of the system is relatively impervious. The impervious nature of the soil mix along with a three percent surface slope will prevent rain water from entering the evapotranspiration cells and impacting the effective operation of the system. The entire drainfield has a double liner: one PVC plastic liner and a 6" clay layer. These two liners will ensure that no discharge to groundwater will occur from the system. System Capacity It is estimated that the Acre facility will produce approximately 520 gallons per day (GPD) of waste to be handled by the system. The drainfield is designed to handle twice the volume that will be discharged by the Acre facility and is therefore more than adequate to assimilate the waste received into the system. The drainfield is composed of two independent cells so that loading of each cell will be rotated. Once one cell receives its maximum capacity, the loading of that cell will cease in order to allow that cell to assimilate the waste through evapotranspiration. In this manner, the first cell is permitted to "rest" while the second cell receives further loading from the dosing tank. Safety Features Although the proposed disposal system is innovative in design, it incorporates several safety features which will ensure that no overflow of waste will occur. First, a float mechanism in the dosing tank is designed to trigger an alarm in the event the water level in the dosing tank gets too high. If that occurs, the alarm provides a flashing light as well as a horn which will notify the operator of a problem. Once the float reaches this warning level, the system will automatically shut down, thus preventing further waste from entering the system. Second, each evapotranspiration cell is equipped with a similar device which will automatically close off the dosing tanks and prevent further discharge into the cells in the unlikely event the system were to become too saturated to accept further loading. Finally, the double lined drainfield provides an additional safety measure which will prevent any discharge to groundwater. The numerous permit conditions requiring periodic monitoring of water quantity and quality in the system itself as well as the groundwater in the vicinity of the system provide ample assurance that the system will not pose a threat to the state's water resources. Ivermectin Although the proposed system will not discharge to groundwater, DER required the applicant to determine the amount of ivermectin in the wastestream. Ivermectin binds tightly to soil and does not dissolve in water. A sample of the wastestream from the Acre facility was collected by Bionomics Laboratory, Inc., and analyzed by Analytical Development Corporation using the analytical procedure designed by Merck scientists. The results of this analysis show that the concentration of ivermectin in the Acre wastestream ranges from .6 to 6.1 parts per trillion (ppt). The publication submitted to the Department by Acre entitled, Chapter 11, "Environmental Aspects of Ivermectin Usage in Livestock: General Considerations" by Halley, Nessel and Lu, from William C. Campbell, Ivermectin and Abamectin, documents the results of studies designed to determine whether using ivermectin in animals would result in any harmful or undesirable effects on the environment through excretion in the feces. This publication indicates that: Ivermectin is relatively immobile in soil and will not readily translocate into groundwater. Ivermectin is rapidly decomposed by sunlight and therefore will not accumulate in soil when administered to livestock. Ivermectin has no effect on earthworms at a concentration in soil of 12 parts per million (ppm). (This concentration is approximately two million times higher than that of the Acre waste stream.) Aquatic organisms such as water fleas and fish are highly sensitive to ivermectin toxicity. However, ivermectin is not toxic to the most sensitive species, the Daphnia magna, at a concentration of 0.01 parts per billion (ppb). Ivermectin concentrations in cattle feedlot runoff was less than the no-effect level of 0.01 ppb for Daphnia magna and therefore should cause no adverse environmental effects in surface or subsurface waters. The highest concentration of ivermectin found in the Acre waste stream is 6.1 ppt (or .006 ppb), which is less than the 0.01 ppb non-toxic level for the most sensitive aquatic species. Based on the concentration of ivermectin found in the Acre waste stream and the fact that ivermectin binds tightly to soil, the discharge from the Acre facility would not cause any adverse environmental impact, even if it were discharged to groundwater. Bradys' case Bradys submitted no evidence to show that the Consent Order is not an appropriate settlement of the violations alleged therein. They submitted no evidence that the septic tanks were improperly plugged. Brady offered no expert testimony in support of their claim that the facility had caused an adverse impact to groundwater or that the proposed system would cause any threat to groundwater quality. Bradys apparent concern about standing surface water on their property during heavy rainfalls is not relevant to this proceeding. Their concern that the lining of the drainfield could leak is unsupported by competent evidence. Bradys learned immediately prior to hearing that DER had changed its position and intended to issue the permit. Their failure to present any relevant evidence that the Consent Order was insufficient or that the proposed facility would violate any applicable DER rules or criteria and their ill- prepared participation in the hearing was in part the result of DER's late change in position. Bradys' participation in this proceeding was not shown to be frivolous.
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 and therein: Ratify the terms of the Consent Order as reasonable. Grant Acre construction permit number IC35-190005 for an Industrial Waste Disposal Facility, subject to the special conditions set forth in DER Exhibit 1. RECOMMENDED this 22nd day of July, 1992, 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 22nd day of July, 1992. APPENDIX TO RECOMMENDED ORDER CASE NOS. 91-2608, 92-0958 AND 92-0959 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 Petitioners, Bradys 1. 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: 6 & 7(8) and 15(10). 2. Proposed findings of fact 1-5, 16, 27, 28, 31, 36-42, 44, 46-49, 51, 52, 54, 57-59, 61, and 62 are subordinate to the facts actually found in the Recommended Order. 3. Proposed findings of fact 8, 10-14, 17, 19-21, 26, 29, 30, 32, 33, 35, 43, 53, 55, and 56 are irrelevant. Proposed findings of fact 9, 18, 22-25, 45, and 50 are unnecessary. Proposed findings of fact 34 and 60 are unsupported by the competent and substantial evidence. Specific Rulings on Proposed Findings of Fact Submitted by Respondents, Acre and DER 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: 1-44(1-44). Proposed findings of fact 45 and 46 are unsupported by the competent and substantial evidence. COPIES FURNISHED: Carlyn H. Kowalsky, Attorney at Law Bogin, Munns & Munns 250 North Orange Avenue 11th Floor-P.O. Box 2807 Orlando, FL 32802 Douglas MacLaughlin, Attorney at Law Department of Environmental Regulation 2600 Blair Stone Road Tallahassee, FL 32399-2400 Martha Hunter Formella Attorney at Law FOLEY & LARDNER Post Office Box 2193 Orlando, FL 32802-2193 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
The Issue Whether the objections of the City of Pembroke Pines and the Green Meadows Civic Association to South Broward Utility, Inc.'s, proposal to extend its water and sewer service area should be sustained.
Findings Of Fact South Broward Utility, Inc. (South Broward), is a corporation engaged in the business of providing water and wastewater service to the public in Broward County, Florida. That business is subject to regulation by the Florida Public Service Commission (PSC). South Broward's water and wastewater treatment facilities are located in the Town of Davie, and it currently provides water and sewer services to residents of that municipality. Included within the area of the Town of Davie currently served by South Broward are the lands bordered on the north by Sterling Road, the south by Sheridan Street, and the west by Dykes Road (S.W. 160th Avenue). On February 4, 11, and 18, 1989, South Broward published a notice of extension in the Florida Lauderdale News/Sun-Sentinel, a daily newspaper of general circulation published in Broward County, Florida, in accordance with Rule 25-30.030(2), Florida Administrative Code. The notice provided that South Broward would file an application with the PSC pursuant to Section 367.061, Florida Statutes, to amend its certificates of public convenience and necessity to allow South Broward to provide water and sewer service to the east half of Section 5, Township 51 South, Range 40 East, Broward County, Florida. Such area may commonly be described as those lands lying immediately west of Dykes Road to S.W. 166th Avenue, and from Stirling Road on the north to Sheridan Street on the south. On February 24, 1989, South Broward mailed a copy of the aforementioned notice to all local, county and state governmental agencies and all other persons required by Section 367.041(4), Florida Statutes, and Rule 25-30.030(2), Florida Administrative Code. Objections to the notice were filed with the PSC by the City of Pembroke Pines (Pembroke Pines) and the Green Meadows Civic Association (Green Meadows). In its objection, Pembroke Pines contended that it had invested over 30 million dollars to expand its municipal water and sewer service west to the Conversation Area from Sheridan Street on the north to Pembroke Road on the south, that this expansion project was anticipated to provide water and sewer service for its existing municipal boundaries as well as the area proposed to be served by South Broward, that it was preparing an annexation report for the proposed area, and that if South Broward's application were approved it would be precluded from servicing its own residents should annexation occur. At hearing, the proof demonstrated that Pembroke Pines had expanded its municipal water and sewer service such that its water and wastewater treatment plants and related facilities have adequate present capacity to meet the current and anticipated future water and wastewater needs in the disputed service area. The Pembroke Pines water lines are currently located on the south side of Sheridan Street, which street forms the southerly boundary of the disputed service area. Its wastewater treatment lines are, however, located approximately one and one-half miles south of Sheridan Street and would require several months and considerable expense to extend them to the disputed service area. Notably, however, no proof was offered that Pembroke Pines had any current intention to annex the disputed service area, or that it had otherwise evidenced any intent to, or taken any action to, provide service to the area. Green Meadows is an association of residents of this area of unincorporated Broward County, some of whom reside within the service area in dispute. The gravamen of Green Meadows' objection is its concern that sewer lines for a centralized sewer system would leak into its member's ground water supply, and that the increase in population density caused by a centralized water and sewer system would adversely affect the area's ecosystem. Neither Green Meadows nor Pembroke Pines contended, however, that the subject extension of service would violate any land use plan, zoning ordinance or other state or local law, and no credible proof was offered that, if built consistent with existent law, the sewer lines would adversely impact the ground water supply or ecosystem. Until recently, all of the lands lying in the disputed service area were located in unincorporated Broward County. However, in September 1988 a parcel of approximately 15 acres which abutted Dykes Road was annexed into the Town of Davie, and in May 1989 a parcel of approximately 80 acres, which abutted the previously annexed parcel on the east, Sterling Road on the north, and S.W. 166th Avenue on the west, was annexed into the Town of Davie. These lands comprise approximately 30 percent of the lands within the disputed service area, and it is the desire of the Town of Davie that water and sewer service to such lands be provided by South Broward. To date, South Broward has entered into a developer's agreement with the owner of the 80-acre parcel to provide such services, and is in the process of executing such an agreement with the owner of the 15-acre parcel. Pembroke Pines does not object to South Broward's expansion into these areas. As to the remaining acreage within the proposed service area, the owners of the vast majority of those lands have expressed a preference for South Broward to provide water and sewer service to their properties, and South Broward has expressed its desire and ability to provide such services. South Broward's water plant has an existing capacity of 500,000 gallons per day (GPD), and has sufficient capacity to address the current need for water service in the proposed area. Upon completion of its current expansion, which is anticipated in October 1989, South Broward's water plant will have a capacity of 1,250,000 GPD, and adequate capacity to address any future demand for water service in the proposed area. South Broward's wastewater treatment plant, with a capacity of 500,000 GPD, currently has sufficient capacity to satisfy the present and future demand for such services in the proposed area. An expansion of that plant is expected to be in service by 1991, which will double the plant's capacity and provide additional capacity. Currently, South Broward has water and sewer lines adequate to serve the proposed area in place, and located under Dykes Road at the eastern edge of the service area. Such lines are adequate to meet all present and anticipated future needs for such service in the area, and the water lines are adequate to provide fire protection to the area. South Broward has the present financial, managerial, operational, and technical ability to provide the present and anticipated needs for water and wastewater service in the proposed area, and the public interest will be best served by the extension of South Broward's water and wastewater systems to that area. Such expansion will not be in competition with or a duplication of any other system in the area.
Recommendation Based on the foregoing findings of fact and conclusions of law, it is RECOMMENDED that the objections filed by Pembroke Pines and Green Meadows be denied. DONE AND ENTERED in Tallahassee, Leon County, Florida, this 21st day of August 1989. WILLIAM J. KENDRICK Hearing Officer Division of Administrative Hearings The Oakland Building 2900 Apalachee Parkway Tallahassee, Florida 32399-1550 (904) 488-9675 Filed with the Clerk of the Division of Administrative Hearings this 21st day of August, 1988. APPENDIX The proposed findings of fact filed by South Broward are addressed as follows: Addressed in paragraph 1. Addressed in paragraph 3. Addressed in paragraph 4. Addressed in paragraph 5. 5-10. Addressed in paragraph 9. 11-14. Addressed in paragraphs 10-13. 15 & 16. Addressed in paragraphs 6 and 7. Addressed in paragraph 13. To the extent pertinent, addressed in paragraph 8. Addressed in paragraph 8. 20 & 21. Addressed in paragraph 13. The proposed findings of fact filed by the PSC are addressed as follows: 1 & 2. Addressed in paragraph 3. Addressed in paragraph 9. Addressed in paragraph 3, and paragraphs 2 and 3 of the conclusions of law. Addressed in paragraph 8. 6-12. Addressed in paragraphs 9-13. Addressed in paragraph 7. Addressed in paragraph 9. Addressed in paragraph 8. Addressed in paragraph 12. COPIES FURNISHED: Mitchell S. Kraft, Esquire Josias & Goren, P.A. 3099 East Commercial Boulevard Suite 200 Fort Lauderdale, Florida 32308 Deborah Simone, President Green Meadows Civic Association 5831 S.W. 162nd Avenue Fort Lauderdale, Florida 33331 James L. Ade, Esquire Martin, Ade, Birchfiled & Mickler, P.A. 3000 Independent Square Post Office Box 59 Jacksonville, Florida 32201 Randy Frier, Esquire Public Service Commission Fletcher Building 101 East Gaines Street Tallahassee, Florida 32399-0870 Mr. Steve Tribble, Director Records and Reporting Public Service Commission Fletcher Building 101 East Gaines Street Tallahassee, Florida 32399-0870 David Swafford, Executive Director Public Service Commission Room 116 101 East Gaines Street Tallahassee, Florida 32399-0870 Susan Clark General Counsel Public Service Commission Room 116 101 East Gaines Street Tallahassee, Florida 32399-0870
The Issue Should Petitioner's application for variance from the standards for onsite sewage treatment and disposal systems be granted?
Findings Of Fact Upon consideration of the oral and documentary evidence adduced at the hearing, the following relevant findings of fact are made: The Department, through its local health units, is the agency in the State of Florida responsible for permitting or granting variances from permitting standards set forth in Chapter 64E-6, Florida Administrative Code, for Onsite Sewage Treatment and Disposal Systems (OSTDS). Sometime around 1970, Petitioner purchased a mobile home park (Park) in Winter Haven, Florida. The Park presently contains 68 spaces for mobile homes, all of which are occupied. The Park is situated due south of Lake Shipp. There are two canals running approximately east and west through the interior of the Park. Another canal borders the Park on the north side. Included with the purchase of the Park was a Sewage Treatment System (STS) which is permitted and regulated by the Department of Environmental Protection and is presently operating at its maximum capacity serving the 68 mobile homes located in the Park. Sometime around 1980, Petitioner purchased a parcel of land (Property) immediately north of, and across a canal (this is the canal that borders the north side of the Park) from, the Park. The Property borders a basin to Lake Shipp. The Property is zoned for mobile home usage and such is the purpose for which Petitioner purchased the Property. Petitioner has designed the Property such that it will accommodate three mobile home lots (Lots numbered 69, 70, and 71) which Petitioner intends to operate as part of the Park. Initially, Petitioner requested approval of the Department of Environmental Protection to connect the new lots to the existing STS. However, since the existing STS was already at capacity, the Department of Environmental Protection denied Petitioner's request to connect the additional three lots to that system. However, the Department of Environmental protection advised Petitioner that it would have no objection to the installation of septic tanks approved by the Department of Health to serve the additional lots. Subsequently, Petitioner proceeded to obtain the necessary approvals from the local governing authorities and a permit from the Department for the installation of septic tanks on the Property. Petitioner was successful in obtaining the necessary approvals from the local governing authorities but was not successful in obtaining a permit for the installation of septic tanks on the Property from the Department. By letter dated July 16, 1997, the Polk County Health Department denied Petitioner's Application for Onsite Sewage Treatment Disposal System Permit for the following reason: "Domestic sewage flow exceeds 10,000 gallons per day." The denial letter also advised Petitioner that she could request a variance through the Variance Review Board or request an administrative hearing pursuant to Chapter 120, Florida Statutes, on the Department's denial of her application for a permit to install septic tanks on the Property. Petitioner elected to file an application for a variance from Section 381.0065(3)(b), Florida Statutes, with the Variance Review Board. By letter dated August 7, 1997, the Department denied Petitioner's application for variance for the following reasons: The Variance Review and Advisory Committee for the Onsite Sewage Treatment and Disposal Program has recommended disapproval of your application for variance in the case of the above reference property. The granting of variances from established standards is for relieving hardships where it can be clearly shown that the public's health will not be impaired and where pollution of groundwater or surface water will not result, where no reasonable alternative exists, and where the hardship was not intentionally caused by the action of the applicant. The advisory committee's recommendation was based on the failure of the information provided to satisfy the committee that the hardship was not caused intentionally by the action of the applicant, no reasonable alternative exists for the treatment of the sewage, or the discharge from the system will not adversely affect the health of the public. I concur with the advisory committee's recommendation and hereby deny your variance request. Subsequently, Petitioner requested and was granted a formal hearing pursuant to Chapter 120, Florida Statutes, on the denial of Petitioner's application for a variance. The Petitioner intends to locate the OSTDS on the Property. The tank and drain field for the OSTDS will be located approximately 125 feet from the basin. The City of Winter Haven's Sewage System is not available to the Property. The Park's existing STS does not have adequate capacity to accept the sewage that will be generated by the Property. There is no publicly-owned or investor-owned sewage system capable of being connected to the plumbing of the Property. Petitioner testified that the estimated cost of increasing the capacity of the Park's Sewage System to accommodate service to the three additional lots was $30,000.00 - $40,000.00. However, Petitioner presented no evidence as to how the estimate was determined. The projected daily domestic sewage flow from the Property is less than 1,500 gallons per acre per day. The Property contains 1.78 acres and there will be less than four lots per acre. In a letter dated October 17, 1997, from W. R. Cover, a professional engineer with Cover Engineering, Inc., Mr. Cover expresses the following opinion: The location of these proposed mobile homes is such that a septic system will not cause adverse effects or impacts on the environment or public health. The unit will be located so as not to significantly degrade groundwater or surface waters. There is no reasonable alternative for the treatment of the sewage in view of the fact that it would be an additional financial burden to attempt to connect these units to the existing sewage treatment plant Mr. Cover did not testify at the hearing. However, the letter was received as evidence without objection from the Department. Petitioner has failed to present sufficient evidence to show that: (a) no reasonable alternative exists for the treatment of the sewage, and (b) the discharge from the Onsite Sewage Treatment and Disposal System will not adversely affect the health of the applicant or the public or significantly degrade groundwater or surface waters.
Recommendation Based on the foregoing Findings of Fact and Conclusions of Law, it is recommended that the Department of Health enter a final order denying Petitioner's application for variance from the requirements of Section 381.0065, Florida Statutes and Chapter 64E-6, Florida Administrative Code. DONE AND ENTERED this 30th day of March, 1999, in Tallahassee, Leon County, Florida. WILLIAM R. CAVE 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) 921-6947 www.doah.state.fl.us Filed with the Clerk of the Division of Administrative Hearings this 30th day of March, 1999. COPIES FURNISHED: Angela T. Hall, Agency Clerk Department of Health 2020 Capital Circle, Southeast Bin A02 Tallahassee, Florida 32399-1703 Dr. Robert G. Brooks, Secretary Department of Health 2020 Capital Circle, Southeast Bin A00 Tallahassee, Florida 32399-1701 Pete Peterson, General Counsel Department of Health 2020 Capital Circle, Southeast Bin A02 Tallahassee, Florida 32399-1701 Robert J. Antonello, Esquire Antonello, Fegers and Cea Post Office Box 7692 Winter Haven, Florida 33883-7692 Roland Reis, Esquire Department of Health 1290 Golfview Avenue, 4th Floor Bartow, Florida 33830-0293
