The Issue The issues in this case are whether Petitioner was responsible for maintaining a sanitary nuisance on his property by piping sewage onto the ground from the septic system and by ignoring the need to repair a failed septic system; and whether the Department of Health properly issued a citation to Petitioner for violation of Sections 386.041(1)(a) and (b).
Findings Of Fact In November, 1995, a Department of Health, Volusia County Health Department employee, Sherry Rodriguez, was performing a sanitary survey of the water system at 479 Maytown Road, Osteen, Florida, when she observed sewage on the ground. The property in questions consists of a large, two-story house which contains rental units. The house is provided water by a well on the property and sewage is handled by an onsite septic system. On November 6, 1995, Ms. Rodriguez issued a Notice of Violation for the sanitary nuisance which stated that the violation must be corrected by November 20, 1995. The septic system was not repaired by November 20, 1995. Ms. Rodriguez subsequently issued a Notice of Intended Action (NIA), giving Petitioner a deadline of December 5, 1995, to repair his system. When Ms. Rodriguez went to the property to serve the NIA, she observed PVC pipe on the ground, with one end at the septic tank and the other at the read of the property. Sewage was on the ground at the end of the pipe. Ms. Rodriguez took photographs of the pipe before she departed. Agency employee, Britt Williams, visited Petitioner's property on November 1, 1996, and observed sewage on the ground. Mr. Williams issued a follow-up NIA to Petitioner on January 30, 1997, which required Petitioner to repair the septic system by February 3, 1997. Petitioner did not obtain a repair permit to correct the violations, therefore, Mr. Williams issued a citation for the violations of sewage on the ground and having an improperly maintained septic system.
Recommendation Based upon the foregoing Findings of Fact and Conclusions of Law set forth herein, it is RECOMMENDED: That a final order be entered affirming the civil penalty against Petitioner and requiring Petitioner to repair his septic system. DONE AND ENTERED this 8th day of April, 1998, in Tallahassee, Leon County, Florida. STEPHEN F. DEAN Administrative Law Judge Division of Administrative Hearings The DeSoto Building 1230 Apalachee Parkway Tallahassee, Florida 32399-3060 (850) 488-9675 SUNCOM 278-9675 Fax Filing (850) 921-6847 Filed with the Clerk of the Division of Administrative Hearings this 8th day of April, 1998. COPIES FURNISHED: John Gee 1245 Gee Whiz Lane Osteen, Florida 32764 Charlene J. Petersen, Esquire Department of Health 420 Fentress Boulevard Daytona Beach, Florida 32114 Angela T. Hall, Agency Clerk Department of Health Building 6 1317 Winewood Boulevard Tallahassee, Florida 32399-0700 Dr. James Howell, Secretary Department of Health Building 6, Room 306 Tallahassee, Florida 32399-0700
Findings Of Fact The Respondent, Hance B. Jones, is a registered septic tank contractor. The Petitioner is charged with regulating septic tanks, and may initiate charges against septic tank contractors which fail to comply with the statutes and rules regulating septic tanks. The Department's local inspector, Mr. Land, was asked by a representative of Best Septic Tank Contracting to meet with the Best representative and Ms. Inez Quiett at Ms. Quiett's home and confer about a proposed septic tank repair. On March 5, 1992, Mr. Land visited the site, observed water standing around an area which he was advised was the existing septic tank and drain field, and was asked what would have to be done. Mr. Land advised that they would have to obtain a permit, and that the new drain field would have to be separated by at least 24 inches from the wet season water table, and that this would entail placing the drain field in a mound. Mr. Land left the site expecting to have a representative of Best pick up a permit for the repairs within a few days. When Mr. Land did not see anyone come in about the permit, he drove by Quiett's, and observed disturbed soil in the area of the drain field. He stopped, went to the Quiett's house, and spoke with Ms. Quiett's son. The son advised that they had repaired the drain field. Mr. Land asked who had repaired the field, and the son advised him that Mr. Jones had repaired it. On April 22, 1992, Mr. Land then wrote a letter to the Respondent and advised Jones that he had violated the law by repairing Quiett's septic tank and not obtaining a permit for the repair. Mr. Jones spoke with Land at Land's office, and denied that he had repaired the septic tank. Mr. Jones stated he had provided the materials and equipment used to repair the tank. On April 22, 1992, Ms. Quiett called Mr. Land on the telephone, and told Land that Mr. Jones had helped her with the tank, but denied that Jones had been her contractor. The Respondent denied that he was the contractor of the job; denied he was on the site; denied he supervised the work; and denied he received any compensation from Quiett. He indicated that he knew Ms. Quiett's brothers, who were contractors, and admitted that he had provided the materials used on the job and had loaned them his backhoe. Ms. Quiett was asked about the repairs to the system and invoked her privilege against self-incrimination.
Recommendation Having considered the foregoing Findings of Fact, Conclusions of Law, the evidence of record, the candor and demeanor of the witnesses, and the pleadings and arguments of the parties, it is therefore, RECOMMENDED that the Administrative Complaint against the Respondent be DISMISSED. DONE AND ENTERED this 26th day of August, 1992, in Tallahassee, Leon County, Florida. STEPHEN F. DEAN 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 26th day of August, 1992. COPIES FURNISHED: David West, Esquire District 3 Legal Office 1000 N.E. 16th Avenue Gainesville, FL 32609 Bobby Kirby, Esquire Route 2, Box 219 Lake Butler, FL 32054 Sam Power, Agency Clerk Department of Health and Rehabilitative Services 1323 Winewood Boulevard Tallahassee, FL 32399-0700 John Slye, General Counsel Department of Health and Rehabilitative Services 1323 Winewood Boulevard Tallahassee, FL 32399-0700
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 permit application SWO 13-5152, should be granted under Chapter 403, Florida Statutes. This case involves the application of Respondents City of North Miami and Munisport, Inc. to Respondent Department of Environmental Regulation (DER) for an operating permit under the provisions of Chapter 403, Florida Statutes, and Chapter 17-7, Florida Administrative Code, to operate a sanitary landfill located in North Miami, Florida. DER granted provisional approval of the application by the issuance of a Notice of Intent to issue the permit on January 27, 1978. Petitioners filed the instant petition of February 13, 1978, challenging the issuance of the proposed permit. Final hearing herein was originally scheduled for April 7, 1978, but at the instance of the parties was continued and reset to commence on October 18, 1978. During the course of the final hearing, 29 witnesses presented testimony, including six public witnesses. (List of public witnesses - Hearing Officer's Exhibit 3) A total of 35 exhibits were admitted in evidence. Three exhibits (Exhibits 5, 13 and 15) were rejected by the Hearing Officer.
Findings Of Fact By application dated November 14, 1977, Respondent City of North Miami, Florida, as owner, and Respondent Munisport, Inc. as the "responsible operating authority" requested Respondent DER to issue a permit to operate a solid waste resource recovery and management facility consisting of 345.90 acres located at 14301 Biscayne Boulevard, North Miami, Florida. The site, known as the North Miami Recreation Development, had been operating as a sanitary landfill under temporary operating permits (TOP) issued by the DER on May 8, 1975 and September 21, 1976. The 1976 TOP provided for an expiration date of July 1, 1977, and contained various conditions designed to give the permittees a reasonable period of time to conform to the DER regulations relative to sanitary landfills. These included standard requirements such as the rendering of reports on the operation of the facility and prohibiting the deposit of raw and infectious waste, or hazardous waste that had not been rendered safe and sanitary prior to delivery. Additionally, the permit conditions required the facility to be so operated that it would cause minimum adverse effects on the environment, such as objectionable odors, contaminated storm water runoff, or leachates causing degradation of surface of ground waters. Further, the permit provided for a three-month review program after its issuance to consider the feasibility of dumping solid waste in 63 acres of submerged land subject to previous filling with clean fill and/or construction debris, filling of land above mean high water with garbage either above clean fill or above trenches filled with wood and construction debris and covered with clean fill, and a six-week period of weekly water quality monitoring at agreed to sites for analysis by both permittees and the Dade County Environmental Resources Management (DERM). The permit further prohibited the placement of refuse waterward of the mean high water line or in trenches cut below the natural ground water table. (Exhibits 1, 4). By letter of January 27, 1978, DER gave notice to the applicant of its intent to issue the requested operation permit for the solid waste disposal facility and stated therein the following reasons for its determination: The solid waste disposal site is in the public interest. The Department feels that the site will not substantially affect the water quality or interfere with the area's wildlife. The applications and plans for this facility have been evaluated and found to be in conformance with Chapter 403, F.S., Chapter 17-4, FAC, and Chapter 17-7, FAC. The letter stated standard conditions to which the permit would be subject, including special conditions that had been noted in the 1976 TOP. It also prescribed specific conditions that no solid wastes could be placed within 30 feet of any existing or future lake area, no dumping below water at any time nor in any dewatered excavations, and that a quarterly water quality monitoring program at monitoring wells No. 4 through 12 be sampled for specified substances. Proposed Condition 16 stated as follows: Solid waste shall be deposited in locations consistent with those approved in the Army Corps of Engineers' dredge and fill permit #75B-0869. No solid waste shall be deposited in the areas commonly known as the wetlands and transitional zones of said wetlands, as shown on the attached map. Subject to the Corps approval of proposed modifications to permit #75B-0869, a revised DER solid waste permit will be issued consistent with the approved modifications. A sketch of the landfill site purporting to designate the landfill deposal area, wetlands and transitional zone, and mean high water line was attached. (Exhibit 3) The Petitioners consist of the Florida Audubon Society, which has some 2,000 members residing in Dade County, Tropical Audubon Society, which is affiliated with Florida Audubon Society; Keystone Point Homeowners Association, Inc., comprised of approximately 425 owners of mostly waterfront or canal homes in North Miami within a mile of the landfill site; Thomas Pafford, North Miami, Florida, who uses the waters of Biscayne Bay and nearby wetlands for recreational purposes; and Maureen B. Harwitz, who resides within a half mile of the landfill site and uses Biscayne Bay and the mangrove preserve adjacent to the landfill site for recreational purposes. Members of the above-named organizational groups use the waters surrounding the landfill site for recreational purposes and are concerned that the waters and fish and animal life therein will be adversely affected if the operation permit is granted. (Testimony of Lee, Brown, Pafford, Lippelman, Harwitz) Munisport has been operating the North Miami landfill under a lease with the City of North Miami since approximately 1974. The ultimate aim is to convert the area into a recreational complex consisting of golf courses, club house, and other sports facilities. The site was used as an unregulated dump for many years prior to initiation of the Munisport operation. The site has been the subject of previously issued state and Corps of Engineer dredge and fill permits which are not the subject of this proceeding. The landfill site occupies an area generally between Northwest 135th Street on the south and Northwest 151st Street on the north. It lies between Biscayne Boulevard on the west, and state mangrove preserves and land of Florida International University on the east. It is less than a mile to Biscayne Bay on the east side of the landfill. The nearest point of entry is in the southeast area where Arch Creek empties into the Bay. At this time, Munisport has filled approximately 210 acres at the site with ten feet or more of fill material. A final cover has been completed over about 70 acres of this land and a golf course is presently being constructed. Pursuant to the dredge and fill permits, five lakes approximately 35 feet deep are nearly completed and some six or seven more are to be dug in the future pursuant to those permits. These lakes are separated from the solid waste by a 30 foot wide dike of clean fill. Although some cover material has been trucked to the site, about 1.6 million cubic yards of fill from the excavated lakes have been or will be utilized in cover operations for the landfill. The solid waste layer averages 15 feet in depth and lies about two feet above the ground water table. About 230 acres lie within the upland fill area above the mean high water line which is not within the area of jurisdiction of the Army Corps of Engineers. The mean high water line has been established by appropriate procedures under Chapter 177, F.S., and the surveying procedures were approved by the Department of Natural Resources on April 6, 1978. Although not stated in the Notice of Intent to issue the requested permit, DER intends to restrict the life of any permit to the time when the Metropolitan Dade County Resources Recovery Facility commences operation in approximately two years. The applicants and Dade County also have a memorandum of understanding to this effect. (Testimony of Stotts, Checca, Exhibits 1, 2, 35, 36, Hearing Officer's Exhibit 1) Munisport receives solid waste from a variety of firms, institutions, and surrounding municipalities. Its procedures are for vehicles to enter and exit the site from an access road leading to Biscayne Boulevard. A sign is located along the road indicating the operating hours, fee schedule, waste restrictions and other pertinent information. A large portion of the site is virtually inaccessible due to dense mangroves and mosquito control canals and ditches. At the check-in gate, a cursory inspection of vehicle loads is made by Munisport personnel who check the contents for quantity. Each load is directed to a designated place at the site where Munisport employees spread and compact the waste. At this stage, they are instructed to look for any unauthorized materials, such as hazardous and infectious waste. If such wasted is found, the offending party is required to remove it from the site. compactors and bulldozers push the solid waste to the face of the landfill and spread it out to facilitate compaction. During the hours of 6:00 P.M. to 6:00 A.M., a watchman is on duty at the site to accommodate customers. If less than four or five truckloads arrive during the night hours, the material is not processed. If a larger quantity is involved, a Munisport employee moves and covers the material prior to the following workday. Due to the high ground water tabled, the area method is used for filling the site. This is a procedure by which refuse cells are constructed in lifts not to exceed ten feet in vertical height. They are composed of cells which constitute a one-day quantity of refuse. Six inches minimum cover of clean fill is applied daily, and a one foot intermediate cover is applied within a year after compaction. The cells are compacted in two-foot layers and, upon completion of a particular area, a minimum of two feet of final cover is applied. A dike constructed of compacted limerock borders the east side of the site and basically constitutes the present mean high water line. It is designed to protect the adjoining 129 acres of mangrove preserve and Biscayne Bay from any adverse water quality which might occur from runoff of degraded waters from the landfill site in the event of contamination. (Testimony of Haddad, Checca, Exhibit 1, 9) The shallow soil underlying the landfill at depths ranging to almost ten feet consists of a combination of organic matter and debris from prior dump use, muck, and sand. Soil borings taken at the site show that limestone or calcareous rock known as Miami oolite is about eight feet below the soil layer. At this depth is found the Biscayne aquifer that carries the unconfined ground water in the area. The aquifer is approximately 160 feet deep under the site and constitutes the major source of water supply in Dade County. The gradient of the water table for the landfill site runs in a southeasterly direction toward Biscayne Bay. Approximately 75% of the surface soil layer consists of organic muck, whereas in approximately 25% of the area, which was previously filled in the southern and westerly portions before commencement of the Munisport operation, the soil is primarily of a sandy type. (Testimony of Checca, Pitt, Exhibit 1) Leachate is produced in sanitary landfills by precipitation that percolates down through decomposing refuse cells and picks up polluting substances created from the decaying solid waste. It can form a "plume" or "bubble" that takes the course of least resistance in flowing laterally or vertically through a landfill site. The strength and concentration of the leachate is dependent upon various factors including the composition, compaction, and the age of decomposing refuse, and the amount of water being introduced into the area. As it passes slowly through the soil beneath the solid waste material, the unsaturated soils act as filters and permit ion exchange which reduces the quantity of contaminants. Dilution takes place where leachate comes in contact with ground water and leachate movement occurs gradually through the ground water aquifer in its direction of the flow. The presence and movement of leachate normally can be detected by analysis of ground water samples taken at various places throughout the landfill site. (Testimony of Checca, Pitt, Coker, Exhibit 1) Commencing in 1975, a monitoring program was instituted at the sanitary landfill to determine its effects on the ground water regime. A number of monitoring wells at various depths were constructed at different sites at the landfill, and samples were withdrawn and evaluated periodically to determine the types and degrees of pollution being generated by the landfill. Background samples were also obtained from wells off the site to establish the general character of water quality in the area and to compare these samples with those obtained from the site. Additionally, "grab" samples were taken of water from the bay and nearby canals and wetlands. Locations of the background and sampling wells were established by the applicants in conjunction with the DER and the Environmental Protection Agency. To determine the amount of leachate that probably would be generated at the site, the "water balance method" of computing the estimated time required to produce leachate, as well as the quantity that probably would be generated upon completion of the landfill, was made by representatives of the EPA in 1975 utilizing specific climatological and surface conditions at the site. This study indicated that percolation of surface water would increase during the operation of the landfill and before final soil and vegetative cover were in place, and that leachate would occur in about a year in larger quantities than would be produced by a completed landfill. Tests conducted during the ensuing three-year period of both surface and ground water through the monitoring program have failed to produce evidence that water quality is not within acceptable parameters or that water quality in the area surrounding the landfill site has been degraded. No significant differences in the concentrations of various ground water constituents were found between samples obtained at the disposal site and those collected in the adjacent mangrove forest or background areas. Neither was any evidence of contamination from leachate found in samples of surface water collected in the vicinity of the landfill or in nearby natural areas. (Testimony of Checca, Pitt, Linett, Perez, Exhibit 1, Exhibit 33) Three basic factors have undoubtedly accomplished reduction in the amount of leachate generated at the landfill. These are (a) attenuation and filtration of pollutants by unsaturated soils between and beneath the refuse cells, (b) biological assimilation by organisms living within the refuse cells and underlying soils, and (c) dilution upon contact with the ground water. A hydrogeologic study shows that the uppermost 14 feet of the aquifer immediately below the landfill represents only 0.2% of the total discharges with a ground water velocity of less than 0.1 foot per day. This part of the aquifer therefore provides considerable detention time for the water that percolates through the landfill. The strata, as well as the overlying organic marine soils, provide the absorption and assimilation that removes pollutants from the water. After water percolates through this layer, it reaches the highly permeable Miami oolite that carries about 43% of the ground water flow. The effects of soil absorption, filtration through the upper 14 feet of the aquifer, and dilution within the aquifer have demonstrably been sufficient to assimilate the water that percolates through the landfill. It is estimated that the time of travel of ground water from the landfill site to the closest discharge point in Biscayne Bay is approximately 68 years. Although the attenuation capability of the organic muck soil underlying the greater part of the landfill is high, the older area of the site in the southwestern portion which had been filled before the Munisport operation commenced, has no muck and consists primarily of sand with a higher rate of permeability. (Testimony of Checca, Pitt, Teas, Exhibits 1, 33) The fact that the organic muck material under the landfill is not uniform throughout the site, plus the fact that there have been various breaches in the permeable oolite layer below the soil, will, in the opinion of some experts, eventually lead to the generation and movement of a leachate plume into such breaches and ultimately to Biscayne Bay. These breaches consist of the deep lakes at the site, the Arch Creek Canal to the south of the site and a dredged excavation at the exit of that body of water into the bay some 3,600 feet distant from the landfill. Additionally, these experts postulate that the dike located on the eastern border of the site will not prevent leachate from moving into the surrounding mangrove area. It is therefore estimated that in the above ways, large amounts of leachate would enter the bay and adjacent wetlands within a period of five to ten years. (Testimony of Coker, Hudson, Pasley, Browder, Exhibits 12, 14, 29, 30) Although water monitoring at various levels in and at probable discharge points near the site have not found degradation of water quality, the applicants propose to address any future leachate problems in a variety of ways. These include continuous periodic testing of water quality and monitoring wells, excavation of a canal on the upland side of the site to intercept leachate and treatment of any contaminated water therein or by pumping the water to an interior lake for treatment. Based on the particular type of any degradation, chlorination and precipitators would be utilized. Long-range problems will be further reduced by the ultimate construction of the golf courses and placement of final soil and vegetative cover to reduce percolation of surface water. This will be aggravated to an undetermined degree, however, by periodic irrigation of the golf courses. (Testimony of Checca, Pitt, Kelman, Exhibits 1,33) During the early years of the Munisport operation, a number of violations of the conditions of the temporary operating permit occurred, but for the most part these were caused either through simple negligence of landfill personnel, breakdown of equipment, or introduction of unauthorized materials to the site by Munisport customers. In these situations, Munisport usually took prompt and effective action to prevent recurrence and to remedy the problem. For example, on one occasion in 1977, some 12 drums containing residue of a chemical substance deemed to constitute "hazardous waste" was brought into the site by persons unknown and was found leaking into the ground. A number of violations and warning notices were issued to Munisport by the Dade County Department of Environmental Resources Management (DERM), primarily in 1976, involving the placement of tree cuttings and wood scraps into excavations containing water at the south end of the site. These occurred, however, during a period when Munisport was engaging in tests to determine the suitability of such operations in conjunction with DER. Additionally, in 1976 and 1977, Munisport was advised of violations in the placement of garbage in exposed water, uncovered garbage, and delivery of garbage after hours. Munisport has had a continuing problem over the years with the unauthorized delivery of hospital wastes from various customers to the landfill in spite of letters written to hospital facilities and delivery firms cautioning them concerning the prohibition against the introduction of such material to the landfill. DERM personnel concede, however, that the operation has been continuously improved and that it is well-conducted in comparison with other landfills in the country. However, they believe that lakes should not exist in landfills and that the North Miami landfill is too close to the wetlands. (Testimony of Morrissey, Karafel, Sobrino, Haddad, Checca, Exhibits 6-11, 17, 18, 20-24, 27, supplemented by testimony of Pafford and Exhibit 16) In a letter of January 17, 1977, DERM expressed concerns about the Munisport operation to DER. One of these concerns was that leachate would migrate to proposed golf course lakes and the resulting pollution would produce poor water quality. Although 1976 testing of then existing lakes at the site reflected unusually high amounts of fecal coliform, subsequent tests in late 1978 showed very little, but tests again in January, 1979, showed that several lakes were again somewhat high in coliform. Coliform is not considered to be a strong parameter in assessing the presence of leachate and amounts vary considerably from day to day in lake areas. Additionally, great numbers of birds are normally present on the landfill site during operations and contribute in raising coliform readings to some extent. Dade County has a current policy that does not permit lakes to be excavated on landfills operated by the county. (Testimony of Checca, Morrissey, Sobrino, Karafel, Kosakowski, Linett, Newman, Kelman, Perez, Exhibits 17, 19, 20, 24, 25, 31, 32, 37, 38)
Recommendation That a permit be issued to the City of North Miami, Florida and Munisport, Inc. to operate the solid waste disposal facility as described and under the conditions stated in the letter of the Department of Environmental Regulation, dated January 27, 1978, wherein it gave notice of its intent to issue the said permit. DONE and ENTERED, this 13th day of April, 1979, in Tallahassee, Florida. THOMAS C. OLDHAM Hearing Officer Division of Administrative Hearings 530 Carlton Building Tallahassee, Florida 32304 (904) 488-9675 COPIES FURNISHED: David Gluckman, Esquire 5305 Isabelle Drive Ken VanAssenderp, Esquire Tallahassee, Florida Smith, Young and Blue, P.A. Post Office Box 1833 Josepy D. Fleming, Esquire 620 Ingraham Building Marvin Sadur and 25 Southeast Second Avenue Richard J. Potash, Esquires Miami, Florida 33131 2000 L Street NW - Suite 612 Washington, D.C. 20036 Silvia Alderman, Esquire Assistant General Counsel Department of Environmental Regulation 2600 Blair Stone Road Tallahassee, Florida 32301
The Issue The issue addressed in this proceeding is whether Respondent should be fined for violating provisions of Chapters 381, 386 and 489, Florida Statutes, governing septic tank installation and licensure.
Findings Of Fact On August 3, 1989, and again in March, 1992, Respondent was hired by Janet Thompson to perform septic tank work on her septic tank system located at her home at 3168 Pins Lane, Gulf Breeze, Santa Rosa County, Florida. Her system was backing up into her house. Ms. Thompson contacted Mr. Burkett through his advertisement for Working Man Septic Tank in the Southern Bell Yellow Pages. Mr. Burkett recommended that a new drainline or finger be added to her septic system. Mr. Burkett did put in a new finger. However, the new finger was incorrectly installed, in that the drainline exceeded the maximum allowable width and did not have the minimum depth of aggregate in violation of the Rules of the Department regarding the installation of drainlines for septic tank systems. Mr. Burkett's work seemed to solve Ms. Thompson's backup problem. However, a few months later her septic tank system began backing up again. Ms. Thompson again called Mr. Burkett to come and fix the problem. Mr. Burkett recommended another drainline in an "L" shaped configuration. Mr. Burkett installed the new finger. However, he again installed the line incorrectly and violated the Department's Rules, in that the drainline exceeded the maximum allowable width and did not have the minimum depth of aggregate. Ms. Thompson's septic tank problem was corrected for a few months and then began backing up once more. Ms. Thompson called another contractor who finally solved the problem by properly installing an extensive drainline system by building the low area of the drainfield and utilizing three truckloads of aggregate. In May, 1990, William Davenport hired Respondent to do some preventive installation of a new drainfield to the septic tank system located at his home at 6220 East Bay Boulevard, Gulf Breeze, Santa Rosa County, Florida. Mr. Burkett only performed part of the work for which he was hired. The work Respondent did perform was incorrect and violated the Department's Rules regarding the installation of drainfields and lines for septic tank systems. Specifically, the work performed by Respondent was incorrect in that the drainfield exceeded the maximum allowable width, no barrier of building paper or other suitable material was installed to protect the infiltration bed and the aggregate did not meet the minimum depth required. Rules 10D-6.056(4)(a), (d) and (e), Florida Administrative Code. Finally, throughout the time period of the repair work on the Thompson and Davenport properties Respondent was not registered or licensed by the Department to perform such services and was advertising to provide such services under the name "Working Man Septic Tank Co." in the Southern Bell Yellow Pages. Both the lack of a registration and the advertisement of an unlicensed business violate the Rules of the Department. Rule 10D-6.075(4)(a), Florida Administrative Code.
Recommendation Based upon the foregoing Findings of Fact and Conclusions of Law it is, accordingly, RECOMMENDED, that the Department impose on Respondent a fine of $2,000.00. DONE and ORDERED this 9th day of November, 1994, in Tallahassee, Florida. COPIES FURNISHED: Frank C. Bozeman, III Asst. District Legal Counsel D H R S 160 Governmental Center Pensacola, FL 32501 Kenneth P. Walsh Attorney at Law P. O. Box 1208 Shalimar, FL 32505 Robert L. Powell, Clerk Department of Health and Rehabilitative Services 1323 Winewood Boulevard Building One, Room 407 Tallahassee, FL 32399-0700 Kim Tucker General Counsel Department of Health and Rehabilitative Services 1323 Winewood Boulevard Building One, Room 407 Tallahassee, FL 32399-0700 DIANNE CLEAVINGER 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 9th day of November, 1994.
The Issue The issue is whether Respondent should correct a health violation and have a $500.00 fine imposed for violating an agency rule and statute, as alleged in the Citation for Violation issued by Petitioner on December 22, 1999.
Findings Of Fact Based upon all of the evidence, the following findings of fact are determined: This case involves an allegation that Respondent, Steve DeLuca, violated an agency regulation and statute by making repairs to a drainfield on property located at 1444 East New York Avenue, Deland, Florida, without obtaining the necessary permits from the Volusia County Department of Health (Health Department). That department is under the direction and control of Petitioner, Department of Health (Department). Respondent denies the charge and, as clarified for the first time at hearing, contends that the repairs were minor in nature and thus did not require a permit, no authorization was given to the excavation firm which performed the repairs, and the Citation was not issued to the actual owner of the property. On October 29, 1999, William N. VanderLugt (Vanderlugt), a Health Department environmental specialist, received a complaint regarding a septic tank repair being undertaken at 1430 East New York Avenue, Deland, Florida. During the course of inspecting that property, Vanderlugt observed excavation activities on the drainfield located next door at 1444 East New York Avenue. More specifically, Vanderlugt observed an area in the back yard approximately 6 feet by 20 feet in size which had been recently excavated and a large pile of sand nearby. In the excavated site, he saw a rock bed of the size commonly used in drainfields, "clean" and "newly installed" rocks, and a "black paper" covering a part of the rocks. Therefore, he concluded that the excavating firm had just installed a new rock drainfield. This type of activity constitutes a repair to an existing drainfield and requires that such work be performed by a licensed septic tank contractor. It also requires that appropriate permits be obtained from the Health Department. Although Respondent contended that the work was merely to correct a "minor structural flaw" which would not require a permit, Vanderlugt's testimony is more persuasive on this issue, and it is found that a more substantial repair to the drainfield was made. Further inquiry by Vanderlugt revealed that no permits had been obtained for the repair of a drainfield from the Health Department by the excavating company, Collier Enterprises. After a brief conversation with a Collier Enterprises employee, the substance of which is hearsay in nature and cannot be used, Vanderlugt visited the offices of Delco Oil Company and spoke with Respondent, who is employed by that firm. In doing so, Vanderlugt was under the impression that Respondent owned the property in question. During his brief conversation with Repondent, Vanderlugt pointed out that he had to issue a citation because no permit had been obtained for the work at the property in question. DeLuca responded with words to the effect that "they [Collier Enterprises] broke a pipe and they fixed what they broke." Apparently, there was no discussion as to whether Respondent or someone else actually owned the property. Vanderlugt returned to the property in question and performed a second inspection on November 3, 1999. Because no permits had been obtained by that date, and the drainfield site had been covered, a recommendation for a citation was prepared by Vanderlugt. A Citation for Violation was later issued by the Department on December 22, 1999, alleging that Respondent had failed to obtain permits before making a drainfield repair. The Citation was delivered to Respondent at Delco Oil Company. Because Collier Enterprises was not licensed to perform the work, it was given a first violation "warning" letter by the Health Department, as required by a Department rule. During later meetings with Respondent and others, Vanderlugt learned that the actual owner of the property in question was Deluca Properties, Inc., and not Steve DeLuca. For some reason, however, the Department declined to amend its citation and charge the actual owner with the alleged violation. Although Petitioner asserted at hearing and in its Proposed Recommended Order that Respondent is the owner's registered agent, there is no competent evidence of record to support this assertion. According to the general manager of Delco Oil Company, which is apparently owned by Steve Deluca and others, no permission was given to the excavating company to make any repairs. Indeed, Deluca Properties, Inc. has a licensed septic tank contractor who makes all septic tank repairs, when needed.
Recommendation Based on the foregoing Findings of Fact and Conclusions of Law, it is RECOMMENDED that the Department of Health enter a final order dismissing the Administrative Complaint for lack of jurisdiction. DONE AND ENTERED this 14th 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 14th 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 Christopher R. Ditslear, Esquire Post Office Box 41 Deland, Florida 32721-0041 William W. Large, General Counsel Department of Health Bin A02 2020 Capital Circle, Southeast Tallahassee, Florida 32399-1701
Findings Of Fact Petitioner owns and operates a gasoline station located at 4625 U.S. 27 North, Davenport, Florida. The site was constructed in late 1986 and opened in early 1987. The underground tanks storing the gasoline are connected by pipes running underground to the pumps from which the gasoline is dispensed. A small portion of the underground supply pipe is accessible from the surface through a manhole. The excavated area exposing the pipe and what appears to be a valve are separated from the surrounding soil by a large, cylindrical corrugated pipe laid perpendicular to and above the underground supply pump. The leak in question was caused when the lower edge of the corrugated pipe cut into the underground supply pipe for the premium gasoline. The cut was caused by the cumulative effect of vehicular traffic driving over the manhole cover, placing pressure on the corrugated pipe, and eventually forcing the edge of the corrugated pipe to rupture the underground supply pipe with which it was in contact. Petitioner owns and operates a large number of gasoline stations. This incident is the first time that a corrugated pipe has cut into an underground supply pipe. The use of the corrugated pipe is not at issue in the present case. Pursuant to company policy, station employees complete a daily recap each day and forward the recap document to Petitioner. Part of the recap document is devoted to "gas inventory." The daily recap, which covers the preceding 24 hours, requires that an employee determine the amount of gasoline in each underground storage tank, adjust the figure for amounts sold and delivered, and then compare the figure to the amount determined to have been in the tank 24 hours earlier. This reconciliation is normally completed by mid- to late-morning each day. A station employee "sticks" each tank to determine how much gasoline it contains. The procedure requires that the employee insert a pole into the bottom of an underground tank. By observing the length of the pole dampened by gasoline, the employee can calculate approximately the amount of gasoline in the tank. Although stick reading results in an approximation, the results are fairly accurate, leaving at most, in the case of this 12,000-gallon tank, a margin of error of 50 gallons. "Sticking" normally takes place daily between 6:30 a.m. and 7:00 a.m. On the morning of March 6, 1988, which was a Sunday, the employee sticking the tank calculated that the premium tank held 5419 gallons. There had been no deliveries during the preceding 24 hours. During the same period, the station had sold 914 gallons of premium gasoline. However, the last sticking 24 hours earlier had disclosed 7989 gallons. A total of 1656 gallons were thus unaccounted for. The recap document requires that the station notify Respondent's "Dist. Mgr. immediately if shortage of 500 gallons or more appears." The employee failed to do so. On the morning of March 7, 1988, the employee sticking the premium tank calculated that it held 2147 gallons. During the preceding 24 hours, there had been no deliveries and 826 gallons of premium gasoline had been sold. Consequently, 2446 gallons were missing, for a total of 4102 gallons over the past two stickings. As soon as the reconciliation was completed, the employee contacted Respondent's management, which ordered that the pump be shut down during the afternoon of March 7, 1988. Comparing the sales of premium gasoline for the 24- hour period ending March 8 with those ending March 7, which are comparable because the sale of regular gasoline on those two days is almost identical, the station sold about 39% of a normal day's sales of premium gasoline. Reflecting the shutdown of the premium pumps on March 7, the employee sticking the tank on the morning of March 8, 1988, found 593 gallons. During the preceding 24 hours, there had been no deliveries and sales of 321 gallons of premium had been sold, leaving 1233 gallons unaccounted for. The total over the three stickings was 5335 gallons lost. The station had previously not experienced losses even approaching this magnitude. The daily recap for the 24-hour period ending on March 5, 1988, showed no significant loss. Although fluctuations in volume may occur shortly after deliveries due to temperature differentials, such fluctuations could not reasonably have accounted for these vast discrepancies. Theft, measurement errors, and recording errors may also account for variations in readings, but not of the magnitude and repetition involved in this case. Between the time of the reconciliation on the morning of March 6 and the system shutdown on the afternoon of March 7, the system continued operating and, thus, leaking for 28-30 hours. Given that 2446 gallons were lost during the 24-hour period ending on March 7 and 1233 gallons lost during about 9 hours on March 8, at least 100 gallons per hour were escaping from the pipe during these last 28-30 hours, for a total of between 2800 and 3000 gallons. For reasons discussed in the Conclusions of Law, the actions and omissions of the station employees following the reconciliation of inventory figures on March 6 constituted gross negligence in the maintenance of a petroleum storage system. These actions and omissions were in the scope of employment. During the relevant period of time, none of Respondent's employees performed monthly checks of the monitoring wells to determine the presence of leaks. This failure was due to ignorance and was not wilful. This failure in no way contributed to the leak or to any delay in discovering the leak. During the relevant period of time, the monitoring wells had not been properly grouted to prevent introduction of surficial contamination. However, this failure was unknown to Petitioner, which had hired a contractor to construct the wells and reasonably had relied on the contractor to grout properly the monitoring wells. The improper grouting in no way contributed to the leak or to any delay in discovering the leak. During the relevant period of time, Petitioner was not performing weekly or five-day averages of inventory records concerning gasoline. The failure to perform these reconciliations in no way contributed to the leak or to any delay in discovering the leak. Following the discovery of the leak, Petitioner notified Respondent on March 8. Petitioner requested approval to participate in the Early Detection Incentive Program by filing a Notification Application dated March 29, 1988. On July 14, 1988, Respondent completed the Pollutant Storage Tank System Inspection Report Form and Early Detection Incentive Program Compliance Verification Checklist. These documents indicate that Respondent was not monitoring monthly its monitoring wells, failed to grout properly its monitoring wells, was not performing the weekly or five-day averages of inventory (although it was taking daily inventory and reconciling opening and closing inventories), and did not immediately investigate the 1600-gallon shortage disclosed on the morning of March 6, 1988. By letter dated September 30, 1988, Respondent notified Petitioner that its site was ineligible for state-administered cleanup under the Early Detection Incentive Program. The letter cited as reasons the wilful failure to perform monthly checks of the monitoring well, the failure to immediately investigate discrepancies in inventory records while the system continued to operate after initial discovery of the 1600-gallon loss, and the improper construction of the monitoring well with respect to the improper grouting. The letter concludes that these items constitute gross negligence in the maintenance of a petroleum storage system, which precludes participation in the program.
Recommendation Based on the foregoing, it is hereby recommended that the Department of Environmental Regulation enter a Final Order denying the application of Petitioner to participate in the Early Detection Incentive Program. RECOMMENDED this 26th day of March, 1990, in Tallahassee, Florida. ROBERT E. MEALE 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 26th day of March, 1990. APPENDIX TO RECOMMENDED ORDER, CASE NO. 89-1561 Treatment Accorded Proposed Findings of Petitioner 1-4: adopted. 5-6: adopted in substance. 7-16: adopted. 17: rejected as unsupported by the greater weight of the evidence. 18-20: adopted or adopted in substance. 21: to the extent that this proposed finding suggests that Petitioner was performing the five-day or weekly averaging, rejected as unsupported by the greater weight of the evidence. However, in view of the findings and conclusions contained in the Recommended Order, rejected as unnecessary. 22-26: adopted. Treatment Accorded Proposed Findings of Respondent 1-4: rejected as conclusions of law. 5-6: adopted. 7-16: rejected as subordinate. 17: rejected as an inference unsupported by the greater weight of the evidence. 18-26: adopted. 27: rejected as irrelevant. 28-29 and 31: rejected as legal argument. 30: adopted. 32: adopted. 33: adopted except that the system was shut down at some point into the day of the second sticking showing a significant shortage. 34-38: adopted or adopted in substance. 39: rejected as speculation. 40: rejected as irrelevant. 41-42: adopted. 43: rejected as irrelevant. 44-45: rejected as subordinate. 46: adopted. 47-49: rejected as subordinate. 50: adopted. 51-53: rejected as vague with respect to reference to "Racetrac." 54: adopted. 55: rejected as cumulative. 56-57: rejected as unnecessary. COPIES FURNISHED: Dale H. Twachtmann 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 2600 Blair Stone Road Tallahassee, FL 32399-2400 Steven M. Mills Decker & Hallman Suite 1200 Marquis II Tower 285 Peachtree Center Avenue Atlanta, GA 30303 Michael P. Donaldson Assistant General Counsel Twin Towers Office Building 2600 Blair Stone Road Tallahassee, FL 32399-2400
Findings Of Fact B. D. Taylor, Respondent, is the owner of a wastewater treatment facility near Panama City, Florida, which serves a community of some 125-150 mobile homes at Lane Mobile Home Estates. The facility has a 24,000 gallons per day capacity to provide secondary treatment of wastewater with percolating ponds. It was first permitted in 1971 upon construction and has been in continuous operation since that time. In 1980 Respondent employed the services of a consultant to apply for a renewal of its temporary Permit to operate a wastewater treatment facility. This application stated the temporary operating permit (TOP) was needed to give Respondent time to connect to the regional wastewater treatment facility. The schedule contained in the following paragraph was submitted by Respondent at the time needed to accomplish this objective, Following inspection of the facility, a TOP was issued December 5, 1980 (Exhibit 1), and expired January 1, 1983. TOPs are issued to facilities which do not comply with the requirements for Wastewater treatment. Exhibit 1 contained a schedule of compliance to which Respondent was directed to strictly comply to stop the discharge of pollutants from the property on which the facility is located. These conditions are: Date when preliminary engineering to tie into regional will be complete and notification to DER. July 1, 1981; Date when engineering to tie into regional system will be complete and notification to DER - June 1, 1982; Date construction application will be submitted to phase out present facility - March 1, 1982; Date construction will commence - June 1, 1982; Date construction is to be complete and so certified - October 1, 1982; and Date that wastewater effluent disposal system will be certified "in compliance" to permit - January 1, 1903. None of these conditions or schedules has been met by Respondent. The regional wastewater treatment facility was completed in 1982 and Respondent could have connected to this system in the summer of 1982. This wastewater treatment facility is a potential source of pollution. The holding ponds are bordered by a ditch which is connected to Game Farm Greek, which is classified as Class III waters. The size of Game Farm Creek is such that any discharge of pollution to this body of water would reduce its classification below Class III. On several occasions in the past there have been breaks in the berm surrounding the holding ponds which allow the wastewater in the holding ponds to flow into the ditch and into Game Farm Creek. Even without a break in the berm, wastewater from these holding ponds will enter Game Farm Creek either by percolation or overflow of the holding ponds caused by the inability of the soil to absorb the effluent. On January 28, 1983, this facility was inspected and the results of the inspection were discussed with the operators of the facility. The plant was again inspected on February 8 and February 18, 1983. These inspections disclosed solids were not settling out of the wastewater in the settling tanks; inadequate chlorination of the wastewater was being obtained in the chlorination tanks; samples taken from various points in the system, the ditch along side the holding tanks and in Game Farm Creek, disclosed excess fecal coliform counts; and that very poor treatment was being afforded the wastewater received at the plant as evidence by high levels of total Kejhdal nitrogen and ammonia, high levels of phosphates, high biochemical oxygen demand, and low levels of nitrates and nitrites. In July, 1983, in response to a complaint about odors emanating from the plant, the facility was again inspected. This inspector found the aeration tanks anaerobic, effluent had a strong septic odor, the clarifier was cloudy, the chlorine feeder was empty, no chlorine residual in contact tank, final effluent was cloudy, both ponds were covered with duckweed and small pond was discharging in the roadside ditch (Exhibit 14) Expenses to Petitioner resulting from the inspections intended to bring Respondent in compliance with the requirements for wastewater treatment facilities are $280.32 (Exhibit 9)
The Issue The issues are whether Respondent violated Florida Administrative Code Rules 64E-6.022(1)(b)2., 64E-6.022(1)(d), and 64E-6.022(1)(p) by repairing an onsite sewage disposal system without a permit, resulting in missed inspections, and if so, what penalty should be imposed.
Findings Of Fact Petitioner is the state agency charged with enforcing the statutory and regulatory provisions pertaining to the practice of septic tank installations and repairs in Florida. See § 381.0065(3), Fla. Stat. (2003). Repair of onsite sewage treatment and disposal systems must be performed under the supervision and control of a registered septic tank contractor. Respondent is the qualifying registered septic tank contractor for All Florida Septic Tank Service, Inc., having been issued the registration number SR00011389. Respondent has 15 years of experience in the field of septic system construction and repair. The qualifying registered septic tank contractor for Simmons Septic and Tractor Service, Inc., is Joey Wayne Simmons. The qualifying registered septic tank contractor for AA Septic Tank Service, Inc., is Billy Wayne Joyner. However, Mr. Simmons, Mr. Joyner, and Respondent work closely together, sometimes working together on a job and/or acting as the qualifying registered septic tank contractor on each other's behalf. On September 2, 2003, the septic disposal system at the residence of Jack Young was not functioning properly. Mr. Young contracted with one of the above-referenced septic tank services to repair the system. On September 2, 2003, Respondent and another employee of All Florida Septic Tank Service, Inc., along with two employees from AA Septic Tank Service, Inc., went to Mr. Young's residence to repair Mr. Young's onsite sewage disposal system. No one applied for a permit to make any repairs to Mr. Young's system. With Respondent acting as the registered septic tank contractor, the men used a backhoe to dig up the septic tank, which was buried three feet in the ground. Respondent then repaired the pump and ran a new one and one-quarter force main line to the existing header because the old line had been compromised by roots. Respondent also cleaned roots from inside the distribution box. Respondent then sealed the tank and directed the men to cover it up. No one called Petitioner's local office, the Duval County Health Department, to request an inspection of the repair before covering the tank. The work on Mr. Young's septic system involved the replacement of an effluent transmission line. It required a permit because it constituted more than a minor repair to the pump and distribution box. Respondent should not have performed the work without a permit from the Duval County Health Department. Because there was no permit, there was no request for inspection by the Duval County Health Department. When the work was completed, Mr. Young gave Respondent a check in the amount of $1,000, payable to Mr. Simmons. The check reflected payment for repair to the filter bed, otherwise known as the drainfield. Respondent indicated his receipt of the check by signing the AA Septic Tank Service, Inc.'s Daily Truck Log and Maintenance Report. In February 2004, Mr. Young's septic system began to fail once again due to root blockage in the lines. Respondent advised Mr. Young that a permit would be required in order to make any further repairs. Mr. Young refused to pull a permit or to pay for any additional costs. On February 17, 2004, Mr. Young contacted Petitioner to report the failure of his system's drainfield. On February 18, 2004, Petitioner's inspector confirmed that Mr. Young's drainfield had failed and was causing a sanitary nuisance. During the hearing, Respondent admitted that there are no disputed issues of material facts in this case. He stated that he agreed with everything. However, he did not agree that the work he performed for Mr. Young required a permit from and inspections by Petitioner's Duval County Health Department.
Recommendation Based on the foregoing Findings of Fact and Conclusions of Law, it is RECOMMENDED: That Petitioner enter a final order, finding that Respondent violated the standards of practice and imposing an administrative fine in the amount of $1,000. DONE AND ENTERED this 6th day of December, 2005, in Tallahassee, Leon County, Florida. S SUZANNE F. HOOD 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 6th day of December, 2005. COPIES FURNISHED: Catherine R. Berry, Esquire Department of Health 515 West Sixth Street Jacksonville, Florida 32206-4311 James L. Smith All Florida Septic Tank Service, Inc. 8300 West Beaver Street Jacksonville, Florida 32220 R. S. Power, Agency Clerk Department of Health 4052 Bald Cypress Way, Bin A02 Tallahassee, Florida 32399-1701 Timothy M. Cerio, General Counsel Department of Health 4052 Bald Cypress Way, Bin A02 Tallahassee, Florida 32399-1701 Dr. John A. Agwunobi, Secretary Department of Health 4052 Bald Cypress Way, Bin A00 Tallahassee, Florida 32399-1701
Findings Of Fact The Petitioner, Phillip G. Panos, recently moved from Michigan to Florida and is now a Florida resident. On December 9, 1989, prior to moving to Florida, he applied to the Respondent, Department of Environmental Regulation for certification as a Class C domestic waste water treatment plant operator. The Respondent is an agency of the State of Florida charged, among other duties, with regulating the certification, the practice standards and the educational standards of Class C domestic waste water treatment plant operators. The Respondent agency reviewed the Petitioner's application and denied it for failure to demonstrate the requisite three years of experience required by the rule cited below. From April, 1974 to June, 1990 the Petitioner was employed at the Chapaton Pumping Station in St. Clair Shores, Macomb, Michigan. The Chapaton Pumping Station duties involved the Petitioner monitoring the distribution of sewage flows, collecting sludge samples, chlorinating the effluent and pumping it into Lake St. Clair. When the Petitioner left the Chapaton Pumping Station, in June of 1990, he held the position of Senior Station Operator II. The Chapaton Pumping Station receives a combination of storm water flow and sanitary sewage flows. It is a pumping and storm water retention facility for combined sewage. The facility provides primary treatment and disinfection for this combined sewage effluent. The effluent is chlorinated and then pumped to nearby Lake St. Clair while the solids that have settled out of the effluent are retained, collected and sent to the Detroit waste water treatment facility for advanced waste treatment. Chapaton is classified by the state of Michigan's Department of Natural Resources as an "industrial/commercial facility". The industrial classification was originated by the U.S. Environmental Protection Agency (EPA) and has been adopted as a designation or classification by both Michigan and Florida. The Petitioner holds an industrial/commercial waste water treatment certification from the state of Michigan in the category of "plain clarification and disinfection." The Petitioner's experience in Michigan is in the area of industrial waste water treatment and does not constitute actual experience in on-site operational control of a domestic waste water treatment plant (that is a sewage treatment plant). The Petitioner's experience in Michigan does not qualify as industrial waste water treatment plant experience, that could be used to meet the actual experience requirement, because the Chapaton plant performs only primary treatment and disinfection. Secondary or advanced waste treatment is performed at the Detroit waste water treatment plant, with which the Petitioner has no experience. In a typical domestic waste water treatment plant in Florida, "primary treatment" involves primary clarification or settling. Primary clarification occurs in a circular or rectangular tank where soluble solids settle out to the bottom of the tank and floating solids are removed by a skimming device. The soluble solids are called sludge. Primary clarification can remove 40% of BOD and suspended solids. It is not a form of advanced treatment or even secondary treatment. At the Chapaton plant, during primary treatment, a minimum of 70% BOD and suspended solids are removed. The sludge is not treated at the Chapaton plant but is pumped to the Detroit waste water treatment plant. Thus Chapaton could not be classified as a domestic waste water treatment plant by Florida standards, since it only provides primary clarification and no secondary or advanced waste water treatment. Secondary treatment consists of two types. Activated sludge or trickling filter treatment. Both types deal with oxygen being introduced to the sludge to achieve stabilization and more settling out of the sludge elements. Since June 18, 1990 the Petitioner has been employed as a waste water treatment plant operator I in a training program at the George L. Lohmeyer Waste water Treatment Plant in Ft. Lauderdale, Florida. In that training program the Petitioner is being trained in all phases of operation of the Lohmeyer plant. It is a 34-million-gallon-per-day (MGD) activated sludge treatment plant. In his duties, the Petitioner monitors the plant treatment processes, takes samples and submits them to the city's laboratory. The Petitioner is capable of testing the samples himself for dissolved oxygen, chlorine and ph. Reports are signed by the regional chief or the regional facilities manager. The Petitioner's present position qualifies as actual, appropriate experience in the operational control of a waste water treatment plant. The Petitioner has accumulated approximately 3-1/2 months of the 12 months of actual experience required for certification as a Class C waste water treatment plant operator, through the exercise of his duties at the Lohmeyer plant. The Petitioner must accumulate 12 months or 2,080 hours of actual experience before he can qualify for the Class C certification. The Petitioner is a high school graduate and has successfully completed Volumes I and II of the California State University correspondence course in waste water treatment, which is included on the Respondent agency's list of approved courses. Petitioner's 3-1/2 months of actual appropriate experience in Ft. Lauderdale, plus his educational background, including the courses taken in California, yield a total of 36 months or 3 years of constructive experience. Petitioner does not yet have the 12 months of actual experience required by the rules but rather, is approximately 8-1/2 months short of the actual experience requirement. Thus, the Petitioner fails to meet the experience requirement necessary for certification as a Class C domestic waste water treatment plant operator at this time, although in approximately 8-1/2 months, he should be able to meet that requirement.
Recommendation Having considered the foregoing findings of fact, conclusions of law, the evidence of record and the candor and demeanor of the witnesses, it is therefore RECOMMENDED: That a Final Order be entered by the Department of Environmental Regulation denying Petitioner's application for certification as a Class C domestic waste water treatment plant operator without prejudice to reapplication at such time as his one year of actual experience at such a treatment facility is completed. DONE and ENTERED this 11 of December, 1990, in Tallahassee, Florida. P. MICHAEL RUFF Hearing Officer Division of Administrative Hearings The DeSoto Building 1230 Apalachee Parkway Tallahassee, FL 32399-1550 (904) 488-9675 Filed with the Clerk of the Division of Administrative Hearings this 11 day of December, 1990. APPENDIX TO RECOMMENDED ORDER IN CASE NO. 90-479 (The Petitioner filed no proposed findings of fact.) RESPONDENT'S PROPOSED FINDINGS OF FACT 1. - 21. are accepted. COPIES FURNISHED TO: Dale H. Twachtmann, Secretary Department of Environmental Regulation 2600 Blair Stone Road Tallahassee, FL 32399-2400 Daniel H. Thompson, Esq. General Counsel Department of Environmental Regulation 2600 Blair Stone Road Tallahassee, FL 32399-2400 Phillip G. Panos 2315 N.W. 115 Drive Coral Springs, FL 33065 Francine M. Ffolkes, Esq. Assistant General Counsel Department of Environmental Regulation 2600 Blair Stone Road Tallahassee, FL 32399-2400
